Standards of Performance for New Stationary Sources and Emission Guidelines for Existing Sources: Commercial and Industrial Solid Waste Incineration Units; Technical Amendments, 15846-15918 [2019-05529]

Download as PDF 15846 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations [EPA–HQ–OAR–2003–0119; FRL–9991–32– OAR] to 4:30 p.m. Eastern Standard Time (EST), Monday through Friday. The telephone number for the Public Reading Room is (202) 566–1744, and the telephone number for the Docket Center is (202) 566–1742. RIN 2060–AT84 FOR FURTHER INFORMATION CONTACT: ENVIRONMENTAL PROTECTION AGENCY 40 CFR Part 60 Standards of Performance for New Stationary Sources and Emission Guidelines for Existing Sources: Commercial and Industrial Solid Waste Incineration Units; Technical Amendments Dr. Nabanita Modak Fischer, Fuels and Incineration Group, Sector Policies and Programs Division (E143–05), Environmental Protection Agency, Research Triangle Park, North Carolina 27711; telephone number: (919) 541– 5572; fax number: (919) 541–0516; email address: modak.nabanita@ epa.gov. Environmental Protection Agency (EPA). ACTION: Final rule. SUPPLEMENTARY INFORMATION: Following requests for clarification of its June 2016 final action, the Environmental Protection Agency (EPA) published proposed amendments to several provisions of the 2016 New Source Performance Standards (NSPS) and Emission Guidelines (EG) for Commercial and Industrial Solid Waste Incineration (CISWI). This action finalizes the proposed amendments, which provide clarity and address implementation issues in the final CISWI NSPS and EG, as well as correcting inconsistencies and errors in these provisions. DATES: This final rule is effective on April 16, 2019. The incorporation by reference of certain publications listed in the rule is approved by the Director of the Federal Register as of February 7, 2013. ADDRESSES: The EPA has established a docket for this action under Docket ID No. EPA–HQ–OAR–2003–0119. All documents in the docket are listed on the https://www.regulations.gov website. Although listed, some information is not publicly available, e.g., confidential business information or other information whose disclosure is restricted by statute. Certain other material, such as copyrighted material, is not placed on the internet and will be publicly available only in hard copy form. Publicly available docket materials are available electronically through https://www.regulations.gov, or in hard copy at the EPA Docket Center, WJC West Building, Room Number 3334, 1301 Constitution Ave. NW, Washington, DC. The Public Reading Room hours of operation are 8:30 a.m. ACI air curtain incinerator CAA Clean Air Act CEDRI Compliance and Emissions Data Reporting Interface CEMS Continuous Emissions Monitoring System CFR Code of Federal Regulations CISWI Commercial and Industrial Solid Waste Incineration CO carbon monoxide COMS Continuous Opacity Monitoring System CPMS Continuous Parameter Monitoring System EG Emission Guidelines EPA U.S. Environmental Protection Agency ESP electrostatic precipitator HCl hydrogen chloride Hg mercury mg/dscm milligrams per dry standard cubic meter NAICS North American Industry Classification System NESHAP National Emission Standards for Hazardous Air Pollutants NHSM Non-Hazardous Secondary Material(s) NSPS New Source Performance Standards NTTAA National Technology Transfer and Advancement Act OAQPS Office of Air Quality Planning and Standards OMB Office of Management and Budget PC Portland Cement ppmv parts per million by volume ppmvd parts per million by dry volume RIN Regulatory Information Number UMRA Unfunded Mandates Reform Act U.S.C. United States Code AGENCY: SUMMARY: khammond on DSKBBV9HB2PROD with RULES3 Organization of this Document. The following outline is provided to aid in locating information in this preamble. Acronyms and Abbreviations. A number of acronyms and abbreviations are used in this preamble. While this may not be an exhaustive list, to ease the reading of this preamble and for reference purposes, the following terms and acronyms are defined: I. General Information A. Does this action apply to me? B. Where can I get a copy of this document and other related information? C. Judicial Review II. Background A. What is the statutory authority for taking this action? B. Background Information III. Summary of Final Action A. EG 30-Day Rolling Average Provisions B. Clarification of Operating Parameter Monitoring for a Pollutant’s Control When CEMS Are Being Used for Continuous Compliance Demonstration for the Pollutant IV. Public Comments V. Rationale for Final Amendments to 2016 CISWI Rule A. Discussion of Final Technical Amendments B. Typographical Errors and Corrections C. Environmental, Energy, and Economic Impacts VI. Statutory and Executive Order Reviews A. Executive Order 12866: Regulatory Planning and Review and Executive Order 13563: Improving Regulation and Regulatory Review B. Executive Order 13771: Reducing Regulations and Controlling Regulatory Costs C. Paperwork Reduction Act (PRA) D. Regulatory Flexibility Act (RFA) E. Unfunded Mandates Reform Act (UMRA) F. Executive Order 13132: Federalism G. Executive Order 13175: Consultation and Coordination With Indian Tribal Governments H. Executive Order 13045: Protection of Children From Environmental Health Risks and Safety Risks I. Executive Order 13211: Actions Concerning Regulations That Significantly Affect Energy Supply, Distribution, or Use J. National Technology Transfer and Advancement Act (NTTAA) K. Executive Order 12898: Federal Actions To Address Environmental Justice in Minority Populations and Low-Income Populations L. Congressional Review Act (CRA) I. General Information A. Does this action apply to me? Categories and entities affected by the final action are those that operate CISWI units. The NSPS and EG, herein after referred to as ‘‘standards,’’ for CISWI affect the following categories of sources: Category NAICS 1 code Examples of potentially regulated entities Any industrial or commercial facility using a solid waste incinerator. 211, 212, 486 ........ Oil and gas exploration operations; Mining, pipeline operators. Utility providers. 221 ......................... VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 PO 00000 Frm 00002 Fmt 4701 Sfmt 4700 E:\FR\FM\16APR3.SGM 16APR3 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations Category NAICS 1 code Examples of potentially regulated entities 321, 322, 337 ........ Manufacturers of wood products; Manufacturers of pulp, paper, and paperboard; Manufacturers of furniture and related products. Manufacturers of chemicals and allied products; Manufacturers of plastics and rubber products. Manufacturers of cement; Nonmetallic mineral product manufacturing. Manufacturers of machinery; Manufacturers of transportation equipment. Merchant wholesalers, durable goods; Retail trade. 325, 326 ................. 327 ......................... 333, 336 ................. 423, 44 ................... 1 North American Industry Classification System. This table is not intended to be exhaustive, but rather provides a guide for readers regarding entities likely to be affected by the final action. To determine whether your facility will be affected by this action, you should examine the applicability criteria in 40 Code of Federal Regulations (CFR) 60.2010 of subpart CCCC, 40 CFR 60.2505 of subpart DDDD, and 40 CFR 241. If you have any questions regarding the applicability of the final action to a particular entity, contact the person listed in the preceding FOR FURTHER INFORMATION CONTACT section. B. Where can I get a copy of this document and other related information? The docket number for this final action regarding the CISWI Technical Amendments is Docket ID No. EPA– HQ–OAR–2003–0119. In addition to being available in the docket, an electronic copy of this action is available on the internet. Following signature by the Administrator, the EPA will post a copy of this final action at https://www.epa.gov/stationary-sourcesair-pollution/commercial-andindustrial-solid-waste-incinerationunits-ciswi-new. Following publication in the Federal Register, the EPA will post the Federal Register version and key technical documents at the same website. C. Judicial Review khammond on DSKBBV9HB2PROD with RULES3 15847 Under Clean Air Act (CAA) section 307(b)(1), judicial review of this final rule is available only by filing a petition for review in the United States Court of Appeals for the District of Columbia Circuit (D.C. Circuit) by June 17, 2019. Under CAA section 307(d)(7)(B), only an objection to this final rule that was raised with reasonable specificity during the period for public comment can be raised during judicial review. Any person who believes the final rule contains provisions that were not reasonably forseeable based on the proposed rule should submit a Petition for Reconsideration to the Office of the VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 Administrator, Environmental Protection Agency, Room 3000, EPA WJC South Building, 1200 Pennsylvania Ave. NW, Washington, DC 20460, with a copy to the persons listed in the preceding FOR FURTHER INFORMATION CONTACT section, and the Associate General Counsel for the Air and Radiation Law Office, Office of General Counsel (Mail Code 2344A), Environmental Protection Agency, 1200 Pennsylvania Ave. NW, Washington, DC 20460. Note, under CAA section 307(b)(2), the requirements established by this final rule may not be challenged separately in any civil or criminal proceedings brought by the EPA to enforce these requirements. II. Background A. What is the statutory authority for taking this action? Section 129 of the CAA requires the EPA to establish NSPS and EG pursuant to sections 111 and 129 of the CAA for new and existing solid waste incineration units located at commercial and industrial facilities. This action amends standards developed under these authorities. B. Background Information On March 21, 2011, the EPA promulgated revised NSPS and EG for CISWI units (i.e., solid waste incineration units located at commercial or industrial facilities). Following that action, the Administrator received petitions for reconsideration that identified certain issues that warranted further opportunity for public comment. In response to the petitions, the EPA reconsidered, proposed revisions to, and requested comment on several provisions of the March 2011 final NSPS and EG for CISWI units. These proposed revisions were published on December 23, 2011 (76 FR 80452). On February 7, 2013, the EPA finalized revisions to the CISWI NSPS and EG (78 FR 9112). In that final action, the EPA made additional revisions in response to comments that had not been proposed in the December PO 00000 Frm 00003 Fmt 4701 Sfmt 4700 23, 2011, Federal Register document. Subsequently, the EPA received petitions for reconsideration of the final 2013 action. These petitions assert that the public did not have sufficient opportunity to comment on some of the provisions contained in that final rule. In response, the EPA proposed to reconsider four provisions of the 2013 final revisions to the NSPS and EG for CISWI units (80 FR 3018, January 21, 2015). The EPA took final action on that proposal on June 23, 2016 (81 FR 40956). We will refer to this final CISWI rule, as revised through June 2016, as the 2016 CISWI rule. Following promulgation of the 2016 CISWI rule, the EPA received requests from industry stakeholders and implementing agencies to clarify various issues with implementation of the standards. In addition, the EPA identified certain testing and monitoring issues and inconsistencies within the rules that required further clarification or correction. On June 15, 2018, the EPA proposed amendments to several provisions of the 2016 CISWI rule to address these issues (83 FR 28068). In addition, the EPA identified additional regulatory provisions, beyond those raised by the requests from industry stakeholders and implementing agencies, that require clarification and editorial correction to address inconsistencies and errors in the final rules. In this document, the EPA is taking final action on the June 2018 proposal by promulgating clarifying changes and corrections to the 2016 CISWI rule. For more detailed background and additional information on how this rule is related to other CAA combustion rules issued under CAA section 112 and the Resource Conservation and Recovery Act definition of solid waste, refer to the prior final actions discussed above (76 FR 15704, March 21, 2011; 78 FR 9112, February 7, 2013). III. Summary of Final Action In this final rule, we are amending the 2016 CISWI rule to address certain E:\FR\FM\16APR3.SGM 16APR3 khammond on DSKBBV9HB2PROD with RULES3 15848 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations issues raised by industry stakeholders and implementing agencies, as well as to address other issues identified during implementation of the CISWI rule. Provisions affected by the amendments are: (1) Alternative equivalent emission limit for mercury (Hg) for the wasteburning kiln subcategory; (2) timing of initial test and initial performance evaluation; (3) extension of the date by which electronic data reporting requirements must be met; (4) clarification of non-delegated authorities; (5) demonstration of initial and continuous compliance when using a continuous emissions monitoring system (CEMS); (6) continuous opacity monitoring requirements; (7) other CEMS requirements; (8) clarification of skip testing requirements; (9) deviation reporting requirements for continuous monitoring data; and (10) clarification of air curtain incinerator (ACI) requirements. In addition to these provisions, we are also correcting minor typographical errors identified in the rule as noted in section V.B of this preamble. This final rule provides meaningful burden reduction by providing regulated facilities additional time to complete initial compliance demonstrations and by allowing facilities to comply with productionbased emission limits in lieu of the concentration-based limits in the 2016 CISWI rule. Specifically, cement kilns would be allowed to report mercury emissions on a mass-based production basis (pounds per million (lb/MM) ton of clinker) in lieu of reporting on a concentration based limit (milligrams per dry standard cubic meter (mg/ dscm)). This alternative provision may result in lower costs for the cement industry by making the format of the mercury emission limits consistent with the Portland Cement NESHAP (PC NESHAP). Further, the rule adds flexibilities in the compliance demonstration process by extending the timeline for performance evaluation tests from 60 days to 180 days and allows facilities to use CEMS for demonstrating initial compliance. These provisions may lower compliance testing costs as stack testing could be avoided if the facilities use CEMS. Moreover, facilities with CEMS will not be required to retest in the event of original stack testing failure. The EPA is taking final action on all the amendments discussed in the June 15, 2018 (83 FR 28068), proposed rule and also making two additional changes to clarify provisions of the 2016 CISWI rule. A more detailed discussion of the rationale behind the technical VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 amendments is located in section V.A of this preamble. A. EG 30-Day Rolling Average Provisions A commenter noted that the 30-day rolling average language found in 40 CFR 60.2710(c) was inconsistent with how the averaging period is defined elsewhere in the rule because it contained the additional qualifier ‘‘over the previous 30 days of operation.’’ The EPA realizes that units may not necessarily operate continuously, and that valid operating data exclude periods when a unit is not operating. The EPA has removed the phrase ‘‘over the previous 30 days of operation’’ from 40 CFR 60.2710(c) to be consistent with similar provisions elsewhere in the EG and in the NSPS. B. Clarification of Operating Parameter Monitoring for a Pollutant’s Control When CEMS are Being Used for Continuous Compliance Demonstration for the Pollutant The EPA is clarifying that continuous operating parameter monitoring is not required when CEMS are used for direct and continuous compliance demonstrations for the pollutant. See section V.A.5 of this preamble for further discussion. IV. Public Comments Public comments on the proposed rule and the EPA’s responses to these comments are addressed in a separate response to comment document, available in the docket for this action at Docket ID No. EPA–HQ–OAR–2003– 0119. V. Rationale for Final Amendments to 2016 CISWI Rule A. Discussion of Final Technical Amendments This section of the preamble explains the basis for the changes in this final rule. 1. Alternative Equivalent Emission Limit for Hg for the Waste-Burning Kiln Subcategory The December 23, 2011, proposed CISWI reconsideration rule preamble discussed and presented equivalent emission limits for waste-burning kilns expressed on a production basis (76 FR 80458). In the February 2013 CISWI final reconsideration rule preamble, the EPA again included these equivalent production-based limits, but at that time the EPA decided not to codify these within the rule text. In the process of approving state plans to implement the CISWI EG, the EPA has recognized that there is a benefit to some affected PO 00000 Frm 00004 Fmt 4701 Sfmt 4700 sources and implementing agencies in codifying the emission limit for Hg for waste-burning kilns expressed as a production-based limit (i.e., lb/MM ton clinker) as an alternative equivalent standard to the existing concentrationbased standard (i.e., mg/dscm), because this is the format of the Hg standards found in the PC NESHAP. The EPA strives to make compliance with both CISWI standards and the PC NESHAP as streamlined and consistent as possible to facilitate compliance with both standards because these sources (and energy recovery units) must comply with the CISWI standard when they are combusting solid waste and must comply with the PC NESHAP or Boiler Maximum Achievable Control Technology standards, as applicable, when combusting nonwaste materials. Having an equivalent emission limit in the same units as the PC NESHAP will, thus, aid affected sources in demonstrating compliance with both standards, and will aid implementing agencies in enforcing the standards. As discussed in 2011 and repeated in 2013 (78 FR 9122–3, February 7, 2013), the Hg emission limit of 58 lb/MM ton clinker and 21 lb/MM ton clinker for existing and new sources, respectively, are equivalent to the concentrationbased Hg standards of 0.011 mg/dscm and 0.0037 mg/dscm within the currently published 2016 CISWI rule. To facilitate use of the equivalent production-based emission limits, the EPA is adding these emission limits to the emission limitation tables, and including recordkeeping, calculation, and reporting requirements for clinker production rate as necessary. The regulatory provisions and calculations being made final are consistent with those found in the PC NESHAP, see 40 CFR 63, subpart LLL. 2. Timing of Initial Test and Initial Performance Evaluation The current CISWI NSPS and EG (2016 CISWI Rule) require affected sources to conduct a performance evaluation of each continuous monitoring system within 60 days of installation of the monitoring system (see 40 CFR 60.2135 and 60.2700). The rule also allows up to 180 days from the final compliance date for affected sources to conduct an initial performance test. The EPA received questions from implementing agencies asking whether these requirements can be synchronized to prevent duplicate testing requirements because the continuous monitoring system performance evaluation would require an emissions test being conducted at the same time regardless. We recognize that E:\FR\FM\16APR3.SGM 16APR3 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations the requirement to conduct a performance evaluation within 60 days of installation could present a situation for sources where the deadline for conducting the performance evaluation would precede the deadline for conducting the initial performance test. The EPA did not intend to require sources to conduct duplicative initial performance tests, and we see a benefit to sources and implementing agencies to be able to schedule and conduct both of these demonstrations at the same time. Therefore, the EPA is adjusting the timing of the continuous monitoring system initial performance evaluation to allow 180 days from installation to match the schedule which is allowed for conducting the initial performance test. The EPA has determined that making these timelines consistent (i.e., 180 days from installation) will streamline compliance demonstrations and prevent possible duplicative testing requirements. khammond on DSKBBV9HB2PROD with RULES3 3. Extension of Electronic Data Reporting Requirement In this action, the EPA is extending the electronic reporting requirement dates found in 40 CFR 60.2235(a) and 60.2795(a). The electronic reporting provisions promulgated in CISWI require submittal of initial, annual, and deviation reports electronically through the EPA’s Compliance and Emissions Data Reporting Interface (CEDRI), which is accessed through the EPA’s Central Data Exchange. The existing rule provides that the requirement for electronic submittal will take effect once the relevant forms have been available in CEDRI for 90 calendar days. As stated in the CISWI reconsideration (81 FR 40956), the EPA intended to make the requirements of the CISWI rule consistent with the Electronic Reporting and Recordkeeping Requirements for New Source Performance Standards, which was proposed on March 20, 2015 (80 FR 15100).1 However, the CISWI reconsideration final rule was published on June 23, 2016 (81 FR 40956), before the Electronic Reporting and Recordkeeping Requirements for New Source Performance Standards rule 2 1 Originally, the Electronic Reporting and Recordkeeping Requirements for New Source Performance Standards rule included CISWI as one of the affected subparts. However, because the CISWI reconsideration package was proposed at nearly the same time as that rule, CISWI was removed as an affected subpart, and the language associated with the Electronic Reporting and Recordkeeping Requirements for New Source Performance Standards rule was inserted into the CISWI reconsideration proposal. 2 This final rule was signed on December 21, 2016, but was withdrawn from the Office of the Federal Register prior to publication. VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 was finalized and did not take into account comments received on that rule. The extension for CISWI units in this action is consistent with the EPA’s approach to electronic reporting outlined in the Electronic Reporting and Recordkeeping Requirements for New Source Performance Standards final rule.3 This approach has also been used in recent EPA rulemakings (e.g., National Emissions Standards for Hazardous Air Pollutants for Chemical Recovery Combustion Sources at Kraft, Soda, Sulfite, and Stand-Alone Semi Chemical Pulp Mills, 82 FR 47328 (October 11, 2017); National Emissions Standards for Hazardous Air Pollutants: Publicly Owned Treatment Works Residual Risk and Technology Review, 82 FR 49513, October 26, 2017). The extension requires electronic submission of initial, annual, and deviation reports 2 years from publication of the final rule or 1 year after the reporting form becomes available in CEDRI, whichever date is later. This extension is necessary to allow the EPA time to develop and adequately test the new forms and for regulated entities to become familiar with the forms and reprogram systems that collect data for periodic reports once the forms are available. The extension also allows state, local, and tribal agencies more time to implement electronic reporting and to make any needed permit revisions to accommodate electronic reporting and allows for development of third-party software to populate the reporting forms. 4. Clarification of Non-Delegated Authorities In this action, the EPA is making final corrections to the authorities listed in 40 CFR 60.2030(c). Specifically, the reference to 40 CFR 60.2125(j) is an outdated reference to previously proposed, but never promulgated, performance test waiver provisions. These provisions were included in the June 4, 2010, CISWI proposed rule (see 75 FR 31975), but were not made final in the March 21, 2011, final rule (see 76 FR 15752–3). This reference was inadvertently not included in the final rule to reflect that the proposed 40 CFR 60.2125(j) was not finalized. Another correction relates to the provisions of 40 CFR 60.2030(c)(10) that require obtaining a determination from the EPA of whether a qualifying small power facility or cogeneration facility is 3 The prepublication version of the final rule is available at https://www.epa.gov/sites/production/ files/2017-04/documents/e-reporting-nsps-finalrule-pre-publication.pdf. Accessed November 15, 2018. PO 00000 Frm 00005 Fmt 4701 Sfmt 4700 15849 combusting homogeneous waste. We intended to remove these provisions in the 2013 CISWI final rule as part of the removal of the definition of homogeneous waste (see 78 FR 9124, February 7, 2013). As discussed in the preamble to the February 7, 2013, final revision action, the EPA determined that the proposed ‘‘definition and provisions could be interpreted in a manner that would be unduly restrictive.’’ Therefore, the EPA did not include a definition of ‘‘homogeneous waste’’ in the final CISWI rule and the Agency stated it was (without actually amending the CFR text to reflect its intent) ‘‘removing the requirement that qualifying small power producers and qualifying cogeneration facilities that combust solid waste obtain a determination from the EPA that such waste is homogeneous.’’ Id. Accordingly, the EPA is removing paragraph 40 CFR 60.2030(c)(10). While no other authorities have been added or removed from this list, the EPA is making minor revisions to streamline the section by removing the reserved subparagraphs (i.e., (5) and (10)) and renumbering the subparagraphs sequentially. In this action, we are also clarifying, with respect to the EG, which authorities will not be delegated. Language in 40 CFR 60.2542 simply contains a reference to the analogous paragraph (40 CFR 60.2030(c)) within the CISWI NSPS. However, since the CISWI NSPS applies to new sources, applicability of these non-delegated authorities to state plans implementing the emission guidelines for existing sources was unclear to implementing agencies. To remove this confusion, we have eliminated the cross reference to 40 CFR 60.2030(c) and have instead provided the specific details on which authorities will not be delegated within the text of 40 CFR 60.2542. The final list of authorities in 40 CFR 60.2542 matches the updated list found in 40 CFR 60.2030(c), with the appropriate adjustments made to subpart section cross references. 5. Demonstrating Initial Compliance When Using CEMS As the EPA noted at proposal, (see 83 FR 28072, June 15, 2018), the provisions regarding CEMS monitoring for demonstrating initial compliance are inconsistent and somewhat unclear. The final CISWI rules require some sources to demonstrate compliance using CEMS, and allow the option for any source to use CEMS to demonstrate compliance ‘‘with any of the emission limits of this subpart’’ (see 40 CFR 60.2145(u) and 60.2710(u)). However, for most of the E:\FR\FM\16APR3.SGM 16APR3 15850 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations khammond on DSKBBV9HB2PROD with RULES3 paragraphs containing the pollutantspecific CEMS requirements, the language was unclear on whether these demonstrations were applicable to demonstrating initial compliance, with the exception of carbon monoxide (CO). The EPA’s intent was to allow CEMS for demonstrating initial compliance for any pollutant (i.e., with any of the emission limits of this subpart). To express the EPA’s intent of providing this flexibility for compliance demonstration more clearly, we have revised several sections of the rule in this final action. For example, the initial compliance requirements in 40 CFR 60.2135 and 60.2700 have been revised to also reflect use of CEMS data as an initial compliance demonstration alternative to an emissions test, provided that the initial CEMS performance evaluation has been conducted prior to collecting CEMS data used for the initial performance test. Likewise, language surrounding the CEMS requirements found in 40 CFR 60.2145, 60.2165, 60.2710, and 60.2730, and the emission limitation tables, has been revised and streamlined to clarify that CEMS data may be used to demonstrate compliance (i.e., initial and continuing) with the standards. In addition to clarifying initial compliance demonstrations using CEMS, commenters suggested a similar issue occurs with continuous parametric monitoring requirements for sources that use CEMS to demonstrate compliance for a pollutant. It was not the EPA’s intent to require duplicative operating parameter monitoring for pollutants if emissions for the pollutants are directly and continuously monitored using CEMS. Therefore, the EPA has clarified the CEMS requirements in 40 CFR 60.2165 and 40 CFR 60.2730 to indicate that sources using CEMS to monitor for a pollutant are not required to monitor the associated operating parameters unless it is necessary for compliance with the monitoring requirements of another regulated pollutant. This clarification is not removing any monitoring requirements, but only acknowledging that direct pollutant emission measurement with CEMS is a suitable, if not even preferential, alternative to continuous parameter monitoring. 6. Clarification of Continuous Opacity Monitoring System (COMS) Requirements In addition to the clarifications to CEMS provisions, we are also revising 40 CFR 60.2145(i) and 60.2710(i) to clarify our intent regarding the types of units required to install COMS and to make it consistent with the COMS VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 monitoring requirement language found in 40 CFR 60.2165(m) and 60.2730(m), respectively. We are adding language clarifying that energy recovery units between 10 and 250 million British thermal units/hour design heat input that are equipped with electrostatic precipitators (ESP), particulate matter CEMS, or particulate matter continuous parameter monitoring systems (CPMS) are not required to additionally install and operate COMS because these units have an air pollution control device that has continuous parameter monitoring requirements or are using continuous particulate matter monitoring compliant with provisions within the rule already (see 40 CFR 60.2145(q), for example). The rule currently excludes the COMS requirement for energy recovery units using other types of particulate matter control devices or that use particulate matter CEMS for continuous particulate matter monitoring, but inadvertently omitted ESPs and particulate matter CPMS from the list. Therefore, we are adding ‘‘electrostatic precipitator’’ and ‘‘particulate matter CPMS’’ to the list (that currently includes CO wet scrubbers and fabric filters) found in 40 CFR 60.2165(m) and 60.2730(m) as types of units that do not require COMS. As a further clarification, we are also amending the text to 40 CFR 60.2145(i) and 60.2710(i) to clearly specify that the COMS requirement is applicable to units within the specified size range ‘‘that do not use a wet scrubber, fabric filter with bag leak detection system, an electrostatic precipitator, particulate matter CEMS, or particulate matter CPMS.’’ 7. Clarification of Other CEMS Requirements In addition to the CEMS-related requirements discussed above, the EPA is making two other CEMS-related clarifications in this final rule: (1) To not require CO CEMS for new wasteburning kilns; and (2) to remove outdated notification requirements when particulate matter CEMS are being used. For the CO CEMS issue, the rule as finalized in February 7, 2013, erroneously includes a requirement at 40 CFR 60.2145(j) for new wasteburning kilns to demonstrate compliance with CO emission limits using CEMS. This issue was not corrected in the 2016 final rules and is inconsistent with the requirements found in Table 7 to 40 CFR 60, subpart CCCC, and with the EPA’s intent to remove CO CEMS requirements for new CISWI sources, as stated in the February 7, 2013, final CISWI rules (see 78 FR 9120). Carbon monoxide CEMS are allowed as an alternative compliance PO 00000 Frm 00006 Fmt 4701 Sfmt 4700 demonstration, but sources who adopt this alternative are not required to conduct annual testing using EPA Method 10. To make this clarification, the EPA is revising 40 CFR 60.2145(j) to reflect that CO is one of the pollutants for which an annual test is required and removing CO from the list of pollutants requiring CEMS for demonstrating compliance. Regarding the removal of outdated notification requirements when particulate matter CEMS are used, the EPA is removing the outdated requirements to notify the Administrator prior to beginning and stopping use of an optional particulate matter CEMS. These provisions are 40 CFR 60.2165(n)(1) and (2), and 40 CFR 60.2730(n)(1) and (2). These provisions are an inadvertent holdover from model provisions from a prior rule. CEMS technology and application has progressed to an extent that these notifications are no longer needed or desired by the EPA. Furthermore, these notifications do not appear in the reporting requirements outlined in the reporting requirement tables (Table 4 to 40 CFR part 60, subpart CCCC and Table 3 to 40 CFR part 60, subpart DDDD), nor the other notification requirements, so they introduced an unintended inconsistency within the rule. To resolve this, we are deleting the current subparagraphs (1) and (2) of these sections and renumbering the remaining subparagraphs sequentially to streamline these requirements. 8. Clarification of Reduced Testing Requirements It has come to the EPA’s attention that there is confusion regarding how reduced testing is applied after a source has demonstrated good performance and has skipped testing for 2 years (see 40 CFR 60.2155 and 60.2720). Stakeholders suggest that the current CISWI rule language would have a good-performing source return to an annual testing schedule after being able to skip testing for 2 years, with no opportunity for additional reduced testing. It was not the EPA’s intent to only offer this allowance once when developing these provisions. To the contrary, the EPA intended this allowance to be available for as long as good performance could be reaffirmed with testing every 3 years instead of annually (see 76 FR 15714, March 21, 2011). The intended sequence of testing consisted of two consecutive annual tests showing 75 percent or less of the applicable standard is achieved; followed by 2 years of testing being skipped; followed by an annual test showing that 75 percent of the standard is achieved; followed by 2 years of E:\FR\FM\16APR3.SGM 16APR3 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations testing being skipped; etc. In other words, starting with the initial compliance test (first year), for the first and second years, a source would perform compliance testing; for the third and fourth years, the source could skip testing (if both the first and secondyear results showed that the source achieves 75 percent or less of the applicable standard); for the fifth year a source would perform compliance testing; for the sixth and seventh years, the source could skip testing (if the fifth-year results showed that the source achieves 75 percent or less of the applicable standard); for the eighth year, a source would perform compliance testing, and so on. Since the promulgation of these standards, these skip testing provisions have been refined and promulgated during regulatory development efforts in the CAA section 129 rulemakings for sewage sludge incinerators (40 CFR part 60, subparts LLLL and MMMM). In this action, the EPA is clarifying the ongoing allowance for reduced testing provisions we intended, based largely on language used in the recent sewage sludge incinerator rule (see 81 FR 26039, April 29, 2016). khammond on DSKBBV9HB2PROD with RULES3 9. Clarification of Deviation Reporting Requirements for Continuous Monitoring Data The EPA has become aware of some unclear requirements in the deviation reporting requirements of 40 CFR 60.2215(a) and 60.2775(a). In particular, the requirements for continuously measured parameters or emissions using CEMS are not clearly outlined within these sections. While these provisions are clear for 3-hour average parameters and performance testing, the EPA recognizes that 30-day averages allowed for energy recovery units and particulate matter CEMS were inadvertently omitted, as well as requirements for any other 30-day average measured using CEMS that deviated from an emission limit. The EPA is adding language to these paragraphs to clarify that deviations for these other operating parameters or CEMS measurements that deviate from an operating limit or emissions limitation must be included in a deviation report. 10. Clarification of ACI Requirements Since promulgation of the 2016 CISWI final rule, the EPA has received various questions from implementing agencies regarding the applicability of CISWI to ACI. While the limited requirements of ACIs burning only wood waste, clean lumber, or a mixture of wood waste, clean lumber, and/or yard waste are defined within the rule, ACIs’ status as VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 a CISWI-affected source is unclear to some implementing agencies as they work to prepare state plans and negative declarations because of confusing language in the 2016 CISWI Rule. See 40 CFR 60.2550. Specifically, the section of the EG addressing the units subject to the final CISWI rule includes a reference to ACI in 40 CFR 60.2550(a)(1), but 40 CFR 60.2550(a)(2) further states that only units that meet the definition of a CISWI unit are subject to the final rule, and ACIs do not meet the regulatory definition of a CISWI unit.4 Notwithstanding that provision, the record demonstrates that the EPA considers ACIs located at commercial and industrial facilities and otherwise meeting the definition of an ACI as being CISWI-affected sources. See CAA section 129(g)(1)(C) (defining ACIs) and 40 CFR 60.2245–2260 of the NSPS and 60.2810–2870 of the EG (setting forth the CISWI EG requirements applicable to ACI). Facilities can have CISWIaffected ACIs even if they do not have CISWI units located at the facility. If an ACI begins burning solid waste as defined in the Non Hazardous Secondary Materials rule (see 40 CFR part 241) in addition to, or instead of, wood waste, clean lumber, or a mixture of wood waste, clean lumber, and/or yard waste, it is a solid waste incineration unit that is subject to the applicable numerical emission standards contained in CISWI or another CAA section 129 standard, depending on the type of waste combusted (e.g., such as a unit burning more than 30-percent municipal solid waste would be a municipal solid waste incineration unit instead of a CISWI unit). The EPA’s intent is further demonstrated in a response to comment on title V permitting requirements for ACIs in the preamble to the March 21, 2011, final CISWI rule (76 FR 15741): Commenters are correct that ACIs are not solid waste incineration units pursuant to CAA section 129(g)(1)(C), but that is only correct if the units ‘‘only burn wood wastes, yard wastes and clean lumber and [they] * * * comply with opacity limitations to be established by the Administrator by rule.’’ The EPA has established opacity limitations for ACIs pursuant to CAA sections 111 and 129. Pursuant to CAA section 502(a), sources subject to standards or regulations under CAA section 111 must obtain a title V permit; therefore, ACIs 4 The phrasing of the regulations at 40 CFR 60.2010 and 60.2015 of the NSPS similarly confuse the applicability of the final CISWI rule to new ACIs located at commercial and industrial facilities. PO 00000 Frm 00007 Fmt 4701 Sfmt 4700 15851 are required to obtain a title V permit. As commenters note, the EPA may exempt minor and area sources from the requirement to obtain a title V permit, but the EPA must first determine that compliance with title V requirements is ‘‘impracticable, infeasible, or unnecessarily burdensome’’ for the sources before exempting them (CAA section 502(a)). The EPA has not made the necessary finding pursuant to CAA section 502(a) for ACIs in any of the CAA section 129 rulemakings, and we believe that ACIs exist at CAA section 129 facilities other than at the commercial and industrial facilities subject to this final rule. Because we think it is important to treat all ACIs in the same manner, we decline to consider a title V exemption for minor and area source ACIs at commercial and industrial facilities. As the record demonstrates, the EPA determined that ACIs located at commercial and industrial facilities are CISWI-affected sources that must be included in state plans and regulated consistent with the final CISWI standards applicable to such units. To address the uncertainty created by the CISWI rule, the EPA is clarifying the affected source status of ACIs by revising the regulations to make clear that ‘‘air curtain incinerators’’ do not need to meet the definition of a ‘‘CISWI unit’’ to be subject to the CISWI rule (40 CFR 60.2010 of the NSPS and 40 CFR 60.2500 and 60.2550 of the EG). B. Typographical Errors and Corrections In this action, we are also revising the final rule to correct minor typographical errors and clarify provisions that are unclear. The list of these changes is included in the Typographical Errors and Corrections for Final Technical Amendments memorandum in Docket ID No. EPA–OAR–HQ–2003–0119. C. Environmental, Energy, and Economic Impacts This action makes technical and clarifying corrections to aid in implementation and compliance, but does not make substantive changes to the February 7, 2013, final CISWI rule (78 FR 9112).5 As such, there are no environmental, energy, or economic impacts associated with this final action. The impacts associated with the CISWI rule were discussed in detail in 5 The June 23, 2016, final CISWI rule amendments (81 FR 40956) also did not entail any environmental, energy or economic impacts, and therefore the February 7, 2013, final CISWI rule presents the impacts associated with the CISWI rule. E:\FR\FM\16APR3.SGM 16APR3 15852 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations the February 7, 2013, final CISWI rule document. VI. Statutory and Executive Order Reviews Additional information about these statutes and Executive Orders can be found at https://www.epa.gov/lawsregulations/laws-and-executive-orders. A. Executive Order 12866: Regulatory Planning and Review and Executive Order 13563: Improving Regulation and Regulatory Review This action is not a significant regulatory action and was therefore not submitted to the Office of Management and Budget (OMB) for review. B. Executive Order 13771: Reducing Regulations and Controlling Regulatory Costs This action is considered an Executive Order 13771 deregulatory action. This final rule provides meaningful burden reduction by providing additional regulatory flexibilities that address several implementation issues raised by the stakeholders. khammond on DSKBBV9HB2PROD with RULES3 C. Paperwork Reduction Act (PRA) This action does not impose any new information collection burden under the PRA. OMB has previously approved the information collection activities contained in the existing regulations and has assigned OMB Control number 2060–0662 for 40 CFR part 60, subpart CCCC, and OMB Control number 2060– 0664 for 40 CFR part 60, subpart DDDD. This action is believed to result in no changes to the information collection requirements of the 2016 CISWI rule, so that the information collection estimate of project cost and hour burden from the 2016 CISWI Rule have not been revised. D. Regulatory Flexibility Act (RFA) I certify that this action will not have a significant economic impact on a substantial number of small entities under the RFA. In making this determination, the impact of concern is any significant adverse economic impact on small entities. An agency may certify that a rule will not have a significant economic impact on a substantial number of small entities if the rule relieves regulatory burden, has no net burden, or otherwise has a positive economic effect on the small entities subject to the rule. This final rule will not impose any new requirements on any entities because it does not impose any additional regulatory requirements relative to those specified in the 2016 CISWI rule, which also did not impose any additional VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 regulatory requirements beyond those specified in the February 2013 final CISWI rule. The February 2013 final CISWI rule was certified as not having a significant economic impact on a substantial number of small entities. We have, therefore, concluded that this action will have no net regulatory burden for all directly regulated small entities. E. Unfunded Mandates Reform Act (UMRA) This action does not contain any unfunded mandate as described in UMRA, 2 U.S.C. 1531–1538, and does not significantly or uniquely affect small governments. The action imposes no enforceable duty on any state, local, or tribal governments, or the private sector. F. Executive Order 13132: Federalism This action does not have federalism implications. It will not have substantial direct effects on the states, on the relationship between the national government and the states, or on the distribution of power and responsibilities among the various levels of government. G. Executive Order 13175: Consultation and Coordination With Indian Tribal Governments This action does not have tribal implications as specified in Executive Order 13175. The EPA is not aware of any CISWI in Indian country or owned or operated by Indian tribal governments. The CISWI aspects of this rule may, however, invoke minor indirect tribal implications to the extent that entities generating solid wastes on tribal lands could be affected. Thus, Executive Order 13175 does not apply to this action. H. Executive Order 13045: Protection of Children From Environmental Health Risks and Safety Risks The EPA interprets Executive Order 13045 as applying to those regulatory actions that concern environmental health or safety risks that the EPA has reason to believe may disproportionately affect children, per the definition of ‘‘covered regulatory action’’ in section 2–202 of the Executive Order. This action is not subject to Executive Order 13045 because it does not concern an environmental health risk or safety risk. I. Executive Order 13211: Actions Concerning Regulations That Significantly Affect Energy Supply, Distribution, or Use This action is not subject to Executive Order 13211 because it is not a PO 00000 Frm 00008 Fmt 4701 Sfmt 4700 significant regulatory action under Executive Order 12866. J. National Technology Transfer and Advancement Act (NTTAA) This rulemaking does not involve technical standards. K. Executive Order 12898: Federal Actions To Address Environmental Justice in Minority Populations and Low-Income Populations The EPA believes that this action does not have disproportionately high and adverse human health or environmental effects on minority populations, lowincome populations, and/or indigenous peoples, as specified in Executive Order 12898 (58 FR 7629, February 16, 1994). It does not affect the level of protection provided to human health or the environment. The final corrections do not relax the control measures on sources regulated by the 2016 CISWI rule, which also did not relax any control measures on sources regulated by the February 2013 final CISWI rule. Therefore, this final action will not cause emissions increases from these sources. The February 2013 final CISWI rule reduced emissions of all the listed toxics emitted from this source, thereby helping to further ensure against any disproportionately high and adverse human health or environmental effects on minority or low-income populations. L. Congressional Review Act (CRA) This action is subject to the CRA, and the EPA will submit a rule report to each House of the Congress and to the Comptroller General of the United States. This action is not a ‘‘major rule’’ as defined by 5 U.S.C. 804(2). List of Subjects in 40 CFR Part 60 Environmental protection, Administrative practice and procedure, Air pollution control, Hazardous substances, Incorporation by reference. Dated: March 18, 2019. Andrew R. Wheeler, Administrator. For the reasons stated in the preamble, the Environmental Protection Agency is amending title 40, chapter I, of the Code of Federal Regulations as follows: PART 60—STANDARDS OF PERFORMANCE FOR NEW STATIONARY SOURCES 1. The authority citation for part 60 continues to read as follows: ■ Authority: 42 U.S.C. 7401, et seq. § 60.17 ■ [Amended] 2. Amend § 60.17 by: E:\FR\FM\16APR3.SGM 16APR3 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations a. In paragraph (g)(14), by removing ‘‘60.2710(s), (t), and (w),’’and adding, it its place, ‘‘60.2710(s) and (t),’’; and ■ b. In paragraph (h)(190), by removing ‘‘tables 1, 5,’’ and adding, in its place, ‘‘tables 5,’’. ■ 3. Revise subpart CCCC to read as follows: ■ Sec. Subpart CCCC—Standards of Performance for Commercial and Industrial Solid Waste Incineration Units Applicability 60.2010 Does this subpart apply to my incineration unit? 60.2015 What is a new incineration unit? 60.2020 What combustion units are exempt from this subpart? 60.2030 Who implements and enforces this subpart? 60.2035 How are these new source performance standards structured? 60.2040 Do all eleven components of these new source performance standards apply at the same time? Preconstruction Siting Analysis 60.2045 Who must prepare a siting analysis? 60.2050 What is a siting analysis? khammond on DSKBBV9HB2PROD with RULES3 Operator Training and Qualification 60.2070 What are the operator training and qualification requirements? 60.2075 When must the operator training course be completed? 60.2080 How do I obtain my operator qualification? 60.2085 How do I maintain my operator qualification? 60.2090 How do I renew my lapsed operator qualification? 60.2095 What site-specific documentation is required? 60.2100 What if all the qualified operators are temporarily not accessible? Emission Limitations and Operating Limits 60.2105 What emission limitations must I meet and by when? 60.2110 What operating limits must I meet and by when? 60.2115 What if I do not use a wet scrubber, fabric filter, activated carbon injection, selective noncatalytic reduction, an electrostatic precipitator, or a dry scrubber to comply with the emission limitations? Performance Testing 60.2125 How do I conduct the initial and annual performance test? Jkt 247001 60.2135 How do I demonstrate initial compliance with the emission limitations and establish the operating limits? 60.2140 By what date must I conduct the initial performance test? 60.2141 By what date must I conduct the initial air pollution control device inspection? 60.2145 How do I demonstrate continuous compliance with the emission limitations and the operating limits? 60.2150 By what date must I conduct the annual performance test? 60.2151 By what date must I conduct the annual air pollution control device inspection? 60.2155 May I conduct performance testing less often? 60.2160 May I conduct a repeat performance test to establish new operating limits? Monitoring 60.2165 What monitoring equipment must I install and what parameters must I monitor? 60.2170 Is there a minimum amount of monitoring data I must obtain? Recordkeeping and Reporting Waste Management Plan 60.2055 What is a waste management plan? 60.2060 When must I submit my waste management plan? 60.2065 What should I include in my waste management plan? 18:25 Apr 15, 2019 Initial Compliance Requirements Continuous Compliance Requirements Introduction 60.2000 What does this subpart do? 60.2005 When did this subpart become effective? VerDate Sep<11>2014 60.2130 How are the performance test data used? 60.2175 What records must I keep? 60.2180 Where and in what format must I keep my records? 60.2185 What reports must I submit? 60.2190 What must I submit prior to commencing construction? 60.2195 What information must I submit prior to initial startup? 60.2200 What information must I submit following my initial performance test? 60.2205 When must I submit my annual report? 60.2210 What information must I include in my annual report? 60.2215 What else must I report if I have a deviation from the operating limits or the emission limitations? 60.2220 What must I include in the deviation report? 60.2225 What else must I report if I have a deviation from the requirement to have a qualified operator accessible? 60.2230 Are there any other notifications or reports that I must submit? 60.2235 In what form can I submit my reports? 60.2240 Can reporting dates be changed? Title V Operating Permits 60.2242 Am I required to apply for and obtain a Title V operating permit for my unit? Air Curtain Incinerators (ACIs) 60.2245 What is an air curtain incinerator? 60.2250 What are the emission limitations for air curtain incinerators? 60.2255 How must I monitor opacity for air curtain incinerators? PO 00000 Frm 00009 Fmt 4701 Sfmt 4700 15853 60.2260 What are the recordkeeping and reporting requirements for air curtain incinerators? Definitions 60.2265 What definitions must I know? Tables to Subpart CCCC Table 1 to Subpart CCCC of Part 60— Emission Limitations for Incinerators for Which Construction is Commenced After November 30, 1999, But no Later Than June 4, 2010, or for Which Modification or Reconstruction is Commenced on or After June 1, 2001, But no Later Than August 7, 2013 Table 2 to Subpart CCCC of Part 60— Operating Limits for Wet Scrubbers Table 3 to Subpart CCCC of Part 60— Toxic Equivalency Factors Table 4 to Subpart CCCC of Part 60— Summary of Reporting Requirements Table 5 to Subpart CCCC of Part 60— Emission Limitations for Incinerators That Commenced Construction After June 4, 2010, or That Commenced Reconstruction or Modification After August 7, 2013 Table 6 to Subpart CCCC of Part 60— Emission Limitations for Energy Recovery Units That Commenced Construction After June 4, 2010, or That Commenced Reconstruction or Modification After August 7, 2013 Table 7 to Subpart CCCC of Part 60— Emission Limitations for Wasteburning Kilns That Commenced Construction After June 4, 2010, or Reconstruction or Modification After August 7, 2013 Table 8 to Subpart CCCC of Part 60— Emission Limitations for Small, Remote Incinerators That Commenced Construction After June 4, 2010, Or That Commenced Reconstruction or Modification After August 7, 2013 Subpart CCCC—Standards of Performance for Commercial and Industrial Solid Waste Incineration Units Introduction § 60.2000 What does this subpart do? This subpart establishes new source performance standards for commercial and industrial solid waste incineration units (CISWIs) and air curtain incinerators (ACIs). § 60.2005 When did this subpart become effective? This subpart became effective on August 7, 2013. Some of the requirements in this subpart apply to planning the CISWI or ACI (i.e., the preconstruction requirements in E:\FR\FM\16APR3.SGM 16APR3 15854 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations §§ 60.2045 and 60.2050). Other requirements such as the emission limitations and operating limits apply after the CISWI or ACI begins operation. Applicability § 60.2010 Does this subpart apply to my incineration unit? Yes, this subpart applies if your incineration unit meets all the requirements specified in paragraphs (a) through (c) of this section: (a) Your incineration unit is a new incineration unit as defined in § 60.2015; (b) Your incineration unit is a CISWI as defined in § 60.2265, or an ACI as defined in § 60.2265; and (c) Your incineration unit is not exempt under § 60.2020. § 60.2015 What is a new incineration unit? (a) A new incineration unit is an incineration unit that meets any of the criteria specified in paragraphs (a)(1) through (3) of this section: (1) A CISWI or ACI that commenced construction after June 4, 2010; (2) A CISWI or ACI that commenced reconstruction or modification after August 7, 2013; and (3) Incinerators and ACIs, as defined in this subpart, that commenced construction after November 30, 1999, but no later than June 4, 2010, or that commenced reconstruction or modification on or after June 1, 2001, but no later than August 7, 2013, are considered new incineration units and remain subject to the applicable requirements of this subpart until the units become subject to the requirements of an approved state plan or federal plan that implements subpart DDDD of this part (Emission Guidelines and Compliance Times for Commercial and Industrial Solid Waste Incineration Units). (b) This subpart does not affect your CISWI or ACI if you make physical or operational changes to your incineration unit primarily to comply with subpart DDDD of this part (Emission Guidelines and Compliance Times for Commercial and Industrial Solid Waste Incineration Units). Such changes do not qualify as reconstruction or modification under this subpart. khammond on DSKBBV9HB2PROD with RULES3 § 60.2020 What combustion units are exempt from this subpart? This subpart exempts the types of units described in paragraphs (a) through (j) of this section, but some units are required to provide notifications. (a) Pathological waste incineration units. Incineration units burning 90 percent or more by weight (on a VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 calendar quarter basis and excluding the weight of auxiliary fuel and combustion air) of pathological waste, low-level radioactive waste, and/or chemotherapeutic waste as defined in § 60.2265 are not subject to this subpart if you meet the two requirements specified in paragraphs (a)(1) and (2) of this section: (1) Notify the Administrator that the unit meets these criteria; and (2) Keep records on a calendar quarter basis of the weight of pathological waste, low-level radioactive waste, and/ or chemotherapeutic waste burned, and the weight of all other fuels and wastes burned in the unit. (b) Municipal waste combustion units. Incineration units that are subject to subpart Ea of this part (Standards of Performance for Municipal Waste Combustors); subpart Eb of this part (Standards of Performance for Large Municipal Waste Combustors); subpart Cb of this part (Emission Guidelines and Compliance Time for Large Municipal Combustors); subpart AAAA of this part (Standards of Performance for Small Municipal Waste Combustion Units); or subpart BBBB of this part (Emission Guidelines for Small Municipal Waste Combustion Units). (c) Medical waste incineration units. Incineration units regulated under subpart Ec of this part (Standards of Performance for Hospital/Medical/ Infectious Waste Incinerators for Which Construction is Commenced After June 20, 1996) or subpart Ce of this part (Emission Guidelines and Compliance Times for Hospital/Medical/Infectious Waste Incinerators). (d) Small power production facilities. Units that meet the four requirements specified in paragraphs (d)(1) through (4) of this section: (1) The unit qualifies as a small power-production facility under section 3(17)(C) of the Federal Power Act (16 U.S.C. 796(17)(C)); (2) The unit burns homogeneous waste (not including refuse-derived fuel) to produce electricity; (3) You submit documentation to the Administrator notifying the EPA that the qualifying small power production facility is combusting homogenous waste; and (4) You maintain the records specified in § 60.2175(w). (e) Cogeneration facilities. Units that meet the four requirements specified in paragraphs (e)(1) through (4) of this section: (1) The unit qualifies as a cogeneration facility under section 3(18)(B) of the Federal Power Act (16 U.S.C. 796(18)(B)); PO 00000 Frm 00010 Fmt 4701 Sfmt 4700 (2) The unit burns homogeneous waste (not including refuse-derived fuel) to produce electricity and steam or other forms of energy used for industrial, commercial, heating, or cooling purposes; (3) You submit documentation to the Administrator notifying the Agency that the qualifying cogeneration facility is combusting homogenous waste; and (4) You maintain the records specified in § 60.2175(x). (f) Hazardous waste combustion units. Units for which you are required to get a permit under section 3005 of the Solid Waste Disposal Act. (g) Materials recovery units. Units that combust waste for the primary purpose of recovering metals, such as primary and secondary smelters. (h) Sewage treatment plants. Incineration units regulated under subpart O of this part (Standards of Performance for Sewage Treatment Plants). (i) Sewage sludge incineration units. Incineration units combusting sewage sludge for the purpose of reducing the volume of the sewage sludge by removing combustible matter that are subject to subpart LLLL of this part (Standards of Performance for New Sewage Sludge Incineration Units) or subpart MMMM of this part (Emission Guidelines and Compliance Times for Existing Sewage Sludge Incineration Units). (j) Other solid waste incineration units. Incineration units that are subject to subpart EEEE of this part (Standards of Performance for Other Solid Waste Incineration Units for Which Construction is Commenced After December 9, 2004, or for Which Modification or Reconstruction is Commenced on or After June 16, 2006) or subpart FFFF of this part (Emission Guidelines and Compliance Times for Other Solid Waste Incineration Units That Commenced Construction On or Before December 9, 2004). § 60.2030 Who implements and enforces this subpart? (a) This subpart can be implemented and enforced by the U.S. Environmental Protection Agency (EPA), or a delegated authority such as your state, local, or tribal agency. If the EPA Administrator has delegated authority to your state, local, or tribal agency, then that agency (as well as EPA) has the authority to implement and enforce this subpart. You should contact your EPA Regional Office to find out if this subpart is delegated to your state, local, or tribal agency. (b) In delegating implementation and enforcement authority of this subpart to E:\FR\FM\16APR3.SGM 16APR3 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations a state, local, or tribal agency, the authorities contained in paragraph (c) of this section are retained by the EPA Administrator and are not transferred to the state, local, or tribal agency. (c) The authorities that will not be delegated to state, local, or tribal agencies are specified in paragraphs (c)(1) through (9) of this section: (1) Approval of alternatives to the emission limitations in tables 1, 5, 6, 7, and 8 of this subpart and operating limits established under § 60.2110; (2) Approval of major alternatives to test methods; (3) Approval of major alternatives to monitoring; (4) Approval of major alternatives to recordkeeping and reporting; (5) The requirements in § 60.2115; (6) The requirements in § 60.2100(b)(2); (7) Approval of alternative opacity emission limits in § 60.2105 under § 60.11(e)(6) through (8); (8) Performance test and data reduction waivers under § 60.8(b)(4) and (5); (9) Approval of an alternative to any electronic reporting to the EPA required by this subpart. § 60.2035 How are these new source performance standards structured? These new source performance standards contain the eleven major components listed in paragraphs (a) through (k) of this section: (a) Preconstruction siting analysis; (b) Waste management plan; (c) Operator training and qualification; (d) Emission limitations and operating limits; (e) Performance testing; (f) Initial compliance requirements; (g) Continuous compliance requirements; (h) Monitoring; (i) Recordkeeping and reporting; (j) Definitions; and (k) Tables. khammond on DSKBBV9HB2PROD with RULES3 § 60.2040 Do all eleven components of these new source performance standards apply at the same time? No. You must meet the preconstruction siting analysis and waste management plan requirements before you commence construction of the CISWI. The operator training and qualification, emission limitations, operating limits, performance testing and compliance, monitoring, and most recordkeeping and reporting requirements are met after the CISWI begins operation. VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 15855 Preconstruction Siting Analysis § 60.2065 What should I include in my waste management plan? § 60.2045 Who must prepare a siting analysis? A waste management plan must include consideration of the reduction or separation of waste-stream elements such as paper, cardboard, plastics, glass, batteries, or metals; or the use of recyclable materials. The plan must identify any additional waste management measures and implement those measures the source considers practical and feasible, considering the effectiveness of waste management measures already in place, the costs of additional measures, the emissions reductions expected to be achieved, and any other environmental or energy impacts they might have. (a) You must prepare a siting analysis if you plan to commence construction of an incinerator after December 1, 2000. (b) You must prepare a siting analysis for CISWIs that commenced construction after June 4, 2010, or that commenced reconstruction or modification after August 7, 2013. (c) You must prepare a siting analysis if you are required to submit an initial application for a construction permit under 40 CFR part 51, subpart I, or 40 CFR part 52, as applicable, for the reconstruction or modification of your CISWI. § 60.2050 What is a siting analysis? (a) The siting analysis must consider air pollution control alternatives that minimize, on a site-specific basis, to the maximum extent practicable, potential risks to public health or the environment. In considering such alternatives, the analysis may consider costs, energy impacts, nonair environmental impacts, or any other factors related to the practicability of the alternatives. (b) Analyses of your CISWI’s impacts that are prepared to comply with state, local, or other federal regulatory requirements may be used to satisfy the requirements of this section, provided they include the consideration of air pollution control alternatives specified in paragraph (a) of this section. (c) You must complete and submit the siting requirements of this section as required under § 60.2190(c) prior to commencing construction. Waste Management Plan § 60.2055 plan? What is a waste management A waste management plan is a written plan that identifies both the feasibility and the methods used to reduce or separate certain components of solid waste from the waste stream in order to reduce or eliminate toxic emissions from incinerated waste. § 60.2060 When must I submit my waste management plan? (a) You must submit a waste management plan prior to commencing construction. (b) For CISWIs that commence reconstruction or modification after August 7, 2013, you must submit a waste management plan prior to the commencement of modification or reconstruction. PO 00000 Frm 00011 Fmt 4701 Sfmt 4700 Operator Training and Qualification § 60.2070 What are the operator training and qualification requirements? (a) No CISWI can be operated unless a fully trained and qualified CISWI operator is accessible, either at the facility or can be at the facility within 1 hour. The trained and qualified CISWI operator may operate the CISWI directly or be the direct supervisor of one or more other plant personnel who operate the unit. If all qualified CISWI operators are temporarily not accessible, you must follow the procedures in § 60.2100. (b) Operator training and qualification must be obtained through a stateapproved program or by completing the requirements included in paragraph (c) of this section. (c) Training must be obtained by completing an incinerator operator training course that includes, at a minimum, the three elements described in paragraphs (c)(1) through (3) of this section: (1) Training on the eleven subjects listed in paragraphs (c)(1)(i) through (xi) of this section; (i) Environmental concerns, including types of emissions; (ii) Basic combustion principles, including products of combustion; (iii) Operation of the specific type of incinerator to be used by the operator, including proper startup, waste charging, and shutdown procedures; (iv) Combustion controls and monitoring; (v) Operation of air pollution control equipment and factors affecting performance (if applicable); (vi) Inspection and maintenance of the incinerator and air pollution control devices; (vii) Actions to prevent and correct malfunctions or to prevent conditions that may lead to malfunctions; (viii) Bottom and fly ash characteristics and handling procedures; E:\FR\FM\16APR3.SGM 16APR3 15856 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations (ix) Applicable federal, state, and local regulations, including Occupational Safety and Health Administration workplace standards; (x) Pollution prevention; and (xi) Waste management practices. (2) An examination designed and administered by the instructor. (3) Written material covering the training course topics that may serve as reference material following completion of the course. § 60.2075 When must the operator training course be completed? The operator training course must be completed by the later of the three dates specified in paragraphs (a) through (c) of this section: (a) Six months after your CISWI startup; (b) December 3, 2001; and (c) The date before an employee assumes responsibility for operating the CISWI or assumes responsibility for supervising the operation of the CISWI. § 60.2080 How do I obtain my operator qualification? (a) You must obtain operator qualification by completing a training course that satisfies the criteria under § 60.2070(b). (b) Qualification is valid from the date on which the training course is completed and the operator successfully passes the examination required under § 60.2070(c)(2). § 60.2085 How do I maintain my operator qualification? To maintain qualification, you must complete an annual review or refresher course covering, at a minimum, the five topics described in paragraphs (a) through (e) of this section: (a) Update of regulations; (b) Incinerator operation, including startup and shutdown procedures, waste charging, and ash handling; (c) Inspection and maintenance; (d) Prevention and correction of malfunctions or conditions that may lead to malfunction; and (e) Discussion of operating problems encountered by attendees. khammond on DSKBBV9HB2PROD with RULES3 § 60.2090 How do I renew my lapsed operator qualification? You must renew a lapsed operator qualification by one of the two methods specified in paragraphs (a) and (b) of this section: (a) For a lapse of less than 3 years, you must complete a standard annual refresher course described in § 60.2085; and (b) For a lapse of 3 years or more, you must repeat the initial qualification requirements in § 60.2080(a). VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 § 60.2095 What site-specific documentation is required? (a) Documentation must be available at the facility and readily accessible for all CISWI operators that addresses the ten topics described in paragraphs (a)(1) through (10) of this section. You must maintain this information and the training records required by paragraph (c) of this section in a manner that they can be readily accessed and are suitable for inspection upon request: (1) Summary of the applicable standards under this subpart; (2) Procedures for receiving, handling, and charging waste; (3) Incinerator startup, shutdown, and malfunction procedures; (4) Procedures for maintaining proper combustion air supply levels; (5) Procedures for operating the incinerator and associated air pollution control systems within the standards established under this subpart; (6) Monitoring procedures for demonstrating compliance with the incinerator operating limits; (7) Reporting and recordkeeping procedures; (8) The waste management plan required under §§ 60.2055 through 60.2065; (9) Procedures for handling ash; and (10) A list of the wastes burned during the performance test. (b) You must establish a program for reviewing the information listed in paragraph (a) of this section with each incinerator operator: (1) The initial review of the information listed in paragraph (a) of this section must be conducted within 6 months after the effective date of this subpart or prior to an employee’s assumption of responsibilities for operation of the CISWI, whichever date is later; and (2) Subsequent annual reviews of the information listed in paragraph (a) of this section must be conducted no later than 12 months following the previous review. (c) You must also maintain the information specified in paragraphs (c)(1) through (3) of this section: (1) Records showing the names of CISWI operators who have completed review of the information in § 60.2095(a) as required by § 60.2095(b), including the date of the initial review and all subsequent annual reviews; (2) Records showing the names of the CISWI operators who have completed the operator training requirements under § 60.2070, met the criteria for qualification under § 60.2080, and maintained or renewed their qualification under § 60.2085 or § 60.2090. Records must include PO 00000 Frm 00012 Fmt 4701 Sfmt 4700 documentation of training, the dates of the initial and refresher training, and the dates of their qualification and all subsequent renewals of such qualifications; and (3) For each qualified operator, the phone and/or pager number at which they can be reached during operating hours. § 60.2100 What if all the qualified operators are temporarily not accessible? If all qualified operators are temporarily not accessible (i.e., not at the facility and not able to be at the facility within 1 hour), you must meet one of the two criteria specified in paragraphs (a) and (b) of this section, depending on the length of time that a qualified operator is not accessible: (a) When all qualified operators are not accessible for more than 8 hours, but less than 2 weeks, the CISWI may be operated by other plant personnel familiar with the operation of the CISWI who have completed a review of the information specified in § 60.2095(a) within the past 12 months. However, you must record the period when all qualified operators were not accessible and include this deviation in the annual report as specified under § 60.2210; and (b) When all qualified operators are not accessible for 2 weeks or more, you must take the two actions that are described in paragraphs (b)(1) and (2) of this section: (1) Notify the Administrator of this deviation in writing within 10 days. In the notice, state what caused this deviation, what you are doing to ensure that a qualified operator is accessible, and when you anticipate that a qualified operator will be accessible; and (2) Submit a status report to the Administrator every 4 weeks outlining what you are doing to ensure that a qualified operator is accessible, stating when you anticipate that a qualified operator will be accessible and requesting approval from the Administrator to continue operation of the CISWI. You must submit the first status report 4 weeks after you notify the Administrator of the deviation under paragraph (b)(1) of this section. If the Administrator notifies you that your request to continue operation of the CISWI is disapproved, the CISWI may continue operation for 90 days, then must cease operation. Operation of the unit may resume if you meet the two requirements in paragraphs (b)(2)(i) and (ii) of this section: (i) A qualified operator is accessible as required under § 60.2070(a); and (ii) You notify the Administrator that a qualified operator is accessible and that you are resuming operation. E:\FR\FM\16APR3.SGM 16APR3 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations Emission Limitations and Operating Limits § 60.2105 What emission limitations must I meet and by when? (a) You must meet the emission limitations for each CISWI, including bypass stack or vent, specified in table 1 of this subpart or tables 5 through 8 of this subpart by the applicable date in § 60.2140. You must be in compliance with the emission limitations of this subpart that apply to you at all times. (b) A CISWI or ACI that commenced construction after November 30, 1999, but no later than June 4, 2010, or that commenced reconstruction or modification on or after June 1, 2001 but no later than August 7, 2013, must continue to meet the emission limits in table 1 of this subpart for units in the incinerator subcategory and § 60.2250 for ACIs until the units become subject to the requirements of an approved state plan or federal plan that implements subpart DDDD of this part (Emission Guidelines and Compliance Times for Commercial and Industrial Solid Waste Incineration Units). khammond on DSKBBV9HB2PROD with RULES3 § 60.2110 What operating limits must I meet and by when? (a) If you use a wet scrubber(s) to comply with the emission limitations, you must establish operating limits for up to four operating parameters (as specified in table 2 of this subpart) as described in paragraphs (a)(1) through (4) of this section during the initial performance test: (1) Maximum charge rate, calculated using one of the two different procedures in paragraph (a)(1)(i) or (ii) of this section, as appropriate: (i) For continuous and intermittent units, maximum charge rate is 110 percent of the average charge rate measured during the most recent performance test demonstrating compliance with all applicable emission limitations; and (ii) For batch units, maximum charge rate is 110 percent of the daily charge rate measured during the most recent performance test demonstrating compliance with all applicable emission limitations. (2) Minimum pressure drop across the wet particulate matter scrubber, which is calculated as the lowest 1-hour average pressure drop across the wet scrubber measured during the most recent performance test demonstrating compliance with the particulate matter emission limitations; or minimum amperage to the wet scrubber, which is calculated as the lowest 1-hour average amperage to the wet scrubber measured during the most recent performance test VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 demonstrating compliance with the particulate matter emission limitations; (3) Minimum scrubber liquid flow rate, which is calculated as the lowest 1-hour average liquid flow rate at the inlet to the wet acid gas or particulate matter scrubber measured during the most recent performance test demonstrating compliance with all applicable emission limitations; and (4) Minimum scrubber liquor pH, which is calculated as the lowest 1-hour average liquor pH at the inlet to the wet acid gas scrubber measured during the most recent performance test demonstrating compliance with the hydrogen chloride (HCl) emission limitation. (b) You must meet the operating limits established during the initial performance test 60 days after your CISWI reaches the charge rate at which it will operate, but no later than 180 days after its initial startup. (c) If you use a fabric filter to comply with the emission limitations and you do not use a particulate matter (PM) continuous parameter monitoring system (CPMS) for monitoring PM compliance, you must operate each fabric filter system such that the bag leak detection system alarm does not sound more than 5 percent of the operating time during a 6-month period. In calculating this operating time percentage, if inspection of the fabric filter demonstrates that no corrective action is required, no alarm time is counted. If corrective action is required, each alarm shall be counted as a minimum of 1 hour. If you take longer than 1 hour to initiate corrective action, the alarm time shall be counted as the actual amount of time taken by you to initiate corrective action. (d) If you use an electrostatic precipitator to comply with the emission limitations and you do not use a PM CPMS for monitoring PM compliance, you must measure the (secondary) voltage and amperage of the electrostatic precipitator collection plates during the particulate matter performance test. Calculate the average electric power value (secondary voltage × secondary current = secondary electric power) for each test run. The operating limit for the electrostatic precipitator is calculated as the lowest 1-hour average secondary electric power measured during the most recent performance test demonstrating compliance with the particulate matter emission limitations. (e) If you use activated carbon sorbent injection to comply with the emission limitations, you must measure the sorbent flow rate during the performance testing. The operating limit for the carbon sorbent injection is PO 00000 Frm 00013 Fmt 4701 Sfmt 4700 15857 calculated as the lowest 1-hour average sorbent flow rate measured during the most recent performance test demonstrating compliance with the mercury emission limitations. For energy recovery units, when your unit operates at lower loads, multiply your sorbent injection rate by the load fraction, as defined in this subpart, to determine the required injection rate (e.g., for 50 percent load, multiply the injection rate operating limit by 0.5). (f) If you use selective noncatalytic reduction to comply with the emission limitations, you must measure the charge rate, the secondary chamber temperature (if applicable to your CISWI), and the reagent flow rate during the nitrogen oxides performance testing. The operating limits for the selective noncatalytic reduction are calculated as the highest 1-hour average charge rate, lower secondary chamber temperature, and lowest reagent flow rate measured during the most recent performance test demonstrating compliance with the nitrogen oxides emission limitations. (g) If you use a dry scrubber to comply with the emission limitations, you must measure the injection rate of each sorbent during the performance testing. The operating limit for the injection rate of each sorbent is calculated as the lowest 1-hour average injection rate for each sorbent measured during the most recent performance test demonstrating compliance with the hydrogen chloride emission limitations. For energy recovery units, when your unit operates at lower loads, multiply your sorbent injection rate by the load fraction, as defined in this subpart, to determine the required injection rate (e.g., for 50 percent load, multiply the injection rate operating limit by 0.5). (h) If you do not use a wet scrubber, electrostatic precipitator, or fabric filter to comply with the emission limitations, and if you do not determine compliance with your particulate matter emission limitation with either a particulate matter CEMS or a particulate matter CPMS, you must maintain opacity to less than or equal to 10 percent opacity (1-hour block average). (i) If you use a PM CPMS to demonstrate compliance, you must establish your PM CPMS operating limit and determine compliance with it according to paragraphs (i)(1) through (5) of this section: (1) Determine your operating limit as the average PM CPMS output value recorded during the performance test or at a PM CPMS output value corresponding to 75 percent of the emission limit if your PM performance test demonstrates compliance below 75 percent of the emission limit. You must E:\FR\FM\16APR3.SGM 16APR3 15858 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations verify an existing or establish a new operating limit after each repeated performance test. You must repeat the performance test annually and reassess and adjust the site-specific operating limit in accordance with the results of the performance test: (i) Your PM CPMS must provide a 4– 20 milliamp output, or digital equivalent, and the establishment of its relationship to manual reference method measurements must be determined in units of milliamps; (ii) Your PM CPMS operating range must be capable of reading PM concentrations from zero to a level equivalent to at least two times your allowable emission limit. If your PM CPMS is an auto-ranging instrument capable of multiple scales, the primary range of the instrument must be capable of reading PM concentration from zero to a level equivalent to two times your allowable emission limit; and (iii) During the initial performance test or any such subsequent performance test that demonstrates n = the number of data points. (iii) With your instrument zero expressed in milliamps, or the digital equivalent, your three run average PM CPMS milliamp value, or its digital equivalent, and your three run average Where: R = the relative mg/dscm per milliamp or digital equivalent for your PM CPMS, Y1 = the three run average mg/dscm PM concentration, X1 = the three run average milliamp or digital signal output from you PM CPMS, and z = the milliamp or digital signal equivalent of your instrument zero determined from paragraph (2)(i) of this section. Where: Ol = the operating limit for your PM CPMS on a 30-day rolling average, in milliamps or their digital signal equivalent, L = your source emission limit expressed in mg/dscm, PM concentration from your three compliance tests, determine a relationship of mg/dscm per milliamp or digital signal equivalent with equation 2: digital value from equation 2 in equation 3, below. This sets your operating limit at the PM CPMS output value corresponding to 75 percent of your emission limit: VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 PO 00000 Frm 00014 Fmt 4701 Sfmt 4700 z = your instrument zero in milliamps or the digital equivalent, determined from paragraph (2)(i) of this secction, and E:\FR\FM\16APR3.SGM 16APR3 ER16AP19.007</GPH> ER16AP19.008</GPH> (iv) Determine your source specific 30-day rolling average operating limit using the mg/dscm per milliamp or and monitoring ambient air on a test bench; (B) Zero point data for extractive instruments should be obtained by removing the extractive probe from the stack and drawing in clean ambient air; (C) The zero point can also can be established obtained by performing manual reference method measurements when the flue gas is free of PM emissions or contains very low PM concentrations (e.g., when your process is not operating, but the fans are operating or your source is combusting only natural gas) and plotting these with the compliance data to find the zero intercept; and (D) If none of the steps in paragraphs (i)(2)(i)(A) through (C) of this section are possible, you must use a zero output value provided by the manufacturer. (ii) Determine your PM CPMS instrument average in milliamps, or the digital equivalent, and the average of your corresponding three PM compliance test runs, using equation 1: ER16AP19.006</GPH> khammond on DSKBBV9HB2PROD with RULES3 Where: X1 = the PM CPMS output data points for the three runs constituting the performance test, Y1 = the PM concentration value for the three runs constituting the performance test, and compliance with the PM limit, record and average all milliamp output values, or their digital equivalent, from the PM CPMS for the periods corresponding to the compliance test runs (e.g., average all your PM CPMS output values for three corresponding 2-hour Method 5I test runs). (2) If the average of your three PM performance test runs are below 75 percent of your PM emission limit, you must calculate an operating limit by establishing a relationship of PM CPMS signal to PM concentration using the PM CPMS instrument zero, the average PM CPMS output values corresponding to the three compliance test runs, and the average PM concentration from the Method 5 or performance test with the procedures in (i)(1) through (5) of this section: (i) Determine your instrument zero output with one of the following procedures: (A) Zero point data for in-situ instruments should be obtained by removing the instrument from the stack Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations Where: X1 = the PM CPMS data points for all runs i, n = the number of data points, and Oh = your site specific operating limit, in milliamps or digital signal equivalent. khammond on DSKBBV9HB2PROD with RULES3 (4) To determine continuous compliance, you must record the PM CPMS output data for all periods when the process is operating and the PM CPMS is not out-of-control. You must demonstrate continuous compliance by using all quality-assured hourly average data collected by the PM CPMS for all operating hours to calculate the arithmetic average operating parameter in units of the operating limit (e.g., milliamps or digital signal bits, PM concentration, raw data signal) on a 30day rolling average basis. (5) For PM performance test reports used to set a PM CPMS operating limit, the electronic submission of the test report must also include the make and model of the PM CPMS instrument, serial number of the instrument, analytical principle of the instrument (e.g., beta attenuation), span of the instruments primary analytical range, milliamp or digital signal value equivalent to the instrument zero output, technique by which this zero value was determined, and the average milliamp or digital signals corresponding to each PM compliance test run. Where: Cadj = pollutant concentration adjusted to 7 percent oxygen; VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 must submit all compliance test and PM CPMS data according to the reporting requirements in paragraph (i)(5) of this section: § 60.2115 What if I do not use a wet scrubber, fabric filter, activated carbon injection, selective noncatalytic reduction, an electrostatic precipitator, or a dry scrubber to comply with the emission limitations? these parameters, as well as the relative accuracy and precision of these methods and instruments; and (e) A discussion identifying the frequency and methods for recalibrating the instruments you will use for monitoring these parameters. If you use an air pollution control device other than a wet scrubber, activated carbon injection, selective noncatalytic reduction, fabric filter, an electrostatic precipitator, or a dry scrubber or limit emissions in some other manner, including material balances, to comply with the emission limitations under § 60.2105, you must petition the EPA Administrator for specific operating limits to be established during the initial performance test and continuously monitored thereafter. You must submit the petition at least sixty days before the performance test is scheduled to begin. Your petition must include the five items listed in paragraphs (a) through (e) of this section: (a) Identification of the specific parameters you propose to use as additional operating limits; (b) A discussion of the relationship between these parameters and emissions of regulated pollutants, identifying how emissions of regulated pollutants change with changes in these parameters and how limits on these parameters will serve to limit emissions of regulated pollutants; (c) A discussion of how you will establish the upper and/or lower values for these parameters which will establish the operating limits on these parameters; (d) A discussion identifying the methods you will use to measure and the instruments you will use to monitor Cmeas = pollutant concentration measured on a dry basis; PO 00000 Frm 00015 Fmt 4701 Sfmt 4700 Performance Testing § 60.2125 How do I conduct the initial and annual performance test? (a) All performance tests must consist of a minimum of three test runs conducted under conditions representative of normal operations. (b) You must document that the waste burned during the performance test is representative of the waste burned under normal operating conditions by maintaining a log of the quantity of waste burned (as required in § 60.2175(b)(1)) and the types of waste burned during the performance test. (c) All performance tests must be conducted using the minimum run duration specified in table 1 of this subpart or tables 5 through 8 of this subpart. (d) Method 1 of appendix A of this part must be used to select the sampling location and number of traverse points. (e) Method 3A or 3B of appendix A of this part must be used for gas composition analysis, including measurement of oxygen concentration. Method 3A or 3B of appendix A of this part must be used simultaneously with each method (except when using Method 9 and Method 22). (f) All pollutant concentrations, except for opacity, must be adjusted to 7 percent oxygen using equation 5 of this section: (20.9–7) = 20.9 percent oxygen¥7 percent oxygen (defined oxygen correction basis); E:\FR\FM\16APR3.SGM 16APR3 ER16AP19.010</GPH> (3) If the average of your three PM compliance test runs is at or above 75 percent of your PM emission limit you must determine your operating limit by averaging the PM CPMS milliamp or digital signal output corresponding to your three PM performance test runs that demonstrate compliance with the emission limit using equation 4 and you ER16AP19.009</GPH> R = the relative mg/dscm per milliamp or digital signal output equivalent for your PM CPMS, from equation 2. 15859 15860 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations khammond on DSKBBV9HB2PROD with RULES3 20.9 = oxygen concentration in air, percent; and %O2 = oxygen concentration measured on a dry basis, percent. (g) You must determine dioxins/ furans toxic equivalency by following the procedures in paragraphs (g)(1) through (4) of this section: (1) Measure the concentration of each dioxin/furan tetra-through octachlorinated isomer emitted using EPA Method 23 at 40 CFR part 60, appendix A–7; (2) Quantify isomers meeting identification criteria 2, 3, 4, and 5 in Section 5.3.2.5 of Method 23, regardless of whether the isomers meet identification criteria 1 and 7. You must quantify the isomers per Section 9.0 of Method 23. (Note: You may reanalyze the sample aliquot or split to reduce the number of isomers not meeting identification criteria 1 or 7 of Section 5.3.2.5.); (3) For each dioxin/furan (tetrathrough octa-chlorinated) isomer measured in accordance with paragraphs (g)(1) and (2) of this section, multiply the isomer concentration by its corresponding toxic equivalency factor specified in table 3 of this subpart; and (4) Sum the products calculated in accordance with paragraph (g)(3) of this section to obtain the total concentration of dioxins/furans emitted in terms of toxic equivalency. (h) Method 22 at 40 CFR part 60, appendix A–7 of this part must be used to determine compliance with the fugitive ash emission limit in table 1 of this subpart or tables 5 through 8 of this subpart. (i) If you have an applicable opacity operating limit, you must determine compliance with the opacity limit using Method 9 at 40 CFR part 60, appendix A–4, based on three 1-hour blocks consisting of ten 6-minute average opacity values, unless you are required to install a continuous opacity monitoring system, consistent with §§ 60.2145 and 60.2165. (j) You must determine dioxins/furans total mass basis by following the procedures in paragraphs (j)(1) through (3) of this section: (1) Measure the concentration of each dioxin/furan tetra-through octachlorinated isomer emitted using EPA Method 23 at 40 CFR part 60, appendix A–7; (2) Quantify isomers meeting identification criteria 2, 3, 4, and 5 in Section 5.3.2.5 of Method 23, regardless of whether the isomers meet identification criteria 1 and 7. You must quantify the isomers per Section 9.0 of Method 23. (Note: You may reanalyze the sample aliquot or split to reduce the VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 number of isomers not meeting identification criteria 1 or 7 of Section 5.3.2.5.); and (3) Sum the quantities measured in accordance with paragraphs (j)(1) and (2) of this section to obtain the total concentration of dioxins/furans emitted in terms of total mass basis. § 60.2130 How are the performance test data used? You use results of performance tests to demonstrate compliance with the emission limitations in table 1 of this subpart or tables 5 through 8 of this subpart. Initial Compliance Requirements § 60.2135 How do I demonstrate initial compliance with the emission limitations and establish the operating limits? (a) You must conduct a performance test, as required under §§ 60.2125 and 60.2105to determine compliance with the emission limitations in table 1 of this subpart or tables 5 through 8 of this subpart, to establish compliance with any opacity operating limit in § 60.2110, to establish the kiln-specific emission limit in § 60.2145(y), as applicable, and to establish operating limits using the procedures in § 60.2110 or § 60.2115. The performance test must be conducted using the test methods listed in table 1 of this subpart or tables 5 through 8 of this subpart and the procedures in § 60.2125. The use of the bypass stack during a performance test shall invalidate the performance test. (b) As an alternative to conducting a performance test, as required under §§ 60.2125 and 60.2105, you may use a 30-day rolling average of the 1-hour arithmetic average CEMS data, including CEMS data during startup and shutdown as defined in this subpart, to determine compliance with the emission limitations in Table 1 of this subpart or tables 5 through 8 of this subpart. You must conduct a performance evaluation of each continuous monitoring system within 180 days of installation of the monitoring system. The initial performance evaluation must be conducted prior to collecting CEMS data that will be used for the initial compliance demonstration. § 60.2140 By what date must I conduct the initial performance test? (a) The initial performance test must be conducted within 60 days after your CISWI reaches the charge rate at which it will operate, but no later than 180 days after its initial startup. (b) If you commence or recommence combusting a solid waste at an existing combustion unit at any commercial or PO 00000 Frm 00016 Fmt 4701 Sfmt 4700 industrial facility, and you conducted a test consistent with the provisions of this subpart while combusting the solid waste within the 6 months preceding the reintroduction of that solid waste in the combustion chamber, you do not need to retest until 6 months from the date you reintroduce that solid waste. (c) If you commence or recommence combusting a solid waste at an existing combustion unit at any commercial or industrial facility and you have not conducted a performance test consistent with the provisions of this subpart while combusting the solid waste within the 6 months preceding the reintroduction of that solid waste in the combustion chamber, you must conduct a performance test within 60 days from the date you reintroduce that solid waste. § 60.2141 By what date must I conduct the initial air pollution control device inspection? (a) The initial air pollution control device inspection must be conducted within 60 days after installation of the control device and the associated CISWI reaches the charge rate at which it will operate, but no later than 180 days after the device’s initial startup. (b) Within 10 operating days following an air pollution control device inspection, all necessary repairs must be completed unless the owner or operator obtains written approval from the state agency establishing a date whereby all necessary repairs of the designated facility must be completed. Continuous Compliance Requirements § 60.2145 How do I demonstrate continuous compliance with the emission limitations and the operating limits? (a) General compliance with standards, considering some units may be able to switch between solid waste and non-waste fuel combustion, is specified in paragraph (a)(1) through (6) of this section. (1) The emission standards and operating requirements set forth in this subpart apply at all times; (2) If you cease combusting solid waste, you may opt to remain subject to the provisions of this subpart. Consistent with the definition of CISWI, you are subject to the requirements of this subpart at least 6 months following the last date of solid waste combustion. Solid waste combustion is ceased when solid waste is not in the combustion chamber (i.e., the solid waste feed to the combustor has been cut off for a period of time not less than the solid waste residence time); (3) If you cease combusting solid waste, you must be in compliance with E:\FR\FM\16APR3.SGM 16APR3 khammond on DSKBBV9HB2PROD with RULES3 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations any newly applicable standards on the effective date of the waste-to-fuel switch. The effective date of the wasteto-fuel switch is a date selected by you, that must be at least 6 months from the date that you ceased combusting solid waste, consistent with § 60.2145(a)(2). Your source must remain in compliance with this subpart until the effective date of the waste-to-fuel switch; (4) If you own or operate an existing commercial or industrial combustion unit that combusted a fuel or non-waste material, and you commence or recommence combustion of solid waste, you are subject to the provisions of this subpart as of the first day you introduce or reintroduce solid waste to the combustion chamber, and this date constitutes the effective date of the fuelto-waste switch. You must complete all initial compliance demonstrations for any section 112 standards that are applicable to your facility before you commence or recommence combustion of solid waste. You must provide 30 days prior notice of the effective date of the waste-to-fuel switch. The notification must identify: (i) The name of the owner or operator of the CISWI, the location of the source, the emissions unit(s) that will cease burning solid waste, and the date of the notice; (ii) The currently applicable subcategory under this subpart, and any 40 CFR part 63 subpart and subcategory that will be applicable after you cease combusting solid waste; (iii) The fuel(s), non-waste material(s) and solid waste(s) the CISWI is currently combusting and has combusted over the past 6 months, and the fuel(s) or non-waste materials the unit will commence combusting; (iv) The date on which you became subject to the currently applicable emission limits; and (v) The date upon which you will cease combusting solid waste, and the date (if different) that you intend for any new requirements to become applicable (i.e., the effective date of the waste-tofuel switch), consistent with paragraphs (a)(2) and (3) of this section. (5) All air pollution control equipment necessary for compliance with any newly applicable emissions limits which apply as a result of the cessation or commencement or recommencement of combusting solid waste must be installed and operational as of the effective date of the waste-tofuel, or fuel-to-waste switch. (6) All monitoring systems necessary for compliance with any newly applicable monitoring requirements which apply as a result of the cessation or commencement or recommencement VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 of combusting solid waste must be installed and operational as of the effective date of the waste-to-fuel, or fuel-to-waste switch. All calibration and drift checks must be performed as of the effective date of the waste-to-fuel, or fuel-to-waste switch. Relative accuracy tests must be performed as of the performance test deadline for PM CEMS (if PM CEMS are elected to demonstrate continuous compliance with the particulate matter emission limits). Relative accuracy testing for other CEMS need not be repeated if that testing was previously performed consistent with Clean Air Act section 112 monitoring requirements or monitoring requirements under this subpart. (b) You must conduct an annual performance test for the pollutants listed in table 1 of this subpart or tables 5 through 8 of this subpart and opacity for each CISWI as required under § 60.2125. The annual performance test must be conducted using the test methods listed in table 1 of this subpart or tables 5 through 8 of this subpart and the procedures in § 60.2125. Annual performance tests are not required if you use CEMS or continuous opacity monitoring systems to determine compliance. (c) You must continuously monitor the operating parameters specified in § 60.2110 or established under § 60.2115 and as specified in § 60.2170. Use 3hour block average values to determine compliance (except for baghouse leak detection system alarms) unless a different averaging period is established under § 60.2115 or, for energy recovery units, where the averaging time for each operating parameter is a 30-day rolling, calculated each hour as the average of the previous 720 operating hours. Operation above the established maximum, below the established minimum, or outside the allowable range of operating limits specified in paragraph (a) of this section constitutes a deviation from your operating limits established under this subpart, except during performance tests conducted to determine compliance with the emission and operating limits or to establish new operating limits. Operating limits are confirmed or reestablished during performance tests. (d) You must burn only the same types of waste and fuels used to establish subcategory applicability (for energy recovery units) and operating limits during the performance test. (e) For energy recovery units, incinerators, and small remote units, you must perform an annual visual emissions test for ash handling. PO 00000 Frm 00017 Fmt 4701 Sfmt 4700 15861 (f) For energy recovery units, you must conduct an annual performance test for opacity (except where particulate matter CEMS or continuous opacity monitoring systems are used are used) and the pollutants listed in table 6 of this subpart. (g) You may elect to demonstrate initial and continuous compliance with the carbon monoxide emission limit using a carbon monoxide CEMS, as described in § 60.2165(o). (h) Coal and liquid/gas energy recovery units with average annual heat input rates greater than or equal to 250 million British thermal units/hour (MMBtu/hr) may elect to demonstrate initial and continuous compliance with the particulate matter emissions limit using a particulate matter CEMS according to the procedures in § 60.2165(n) instead of the PM CPMS specified in § 60.2145. Coal and liquid/ gas energy recovery units with annual average heat input rates less than 250 MMBtu/hr, incinerators, and small remote incinerators may also elect to demonstrate initial and continuous compliance using a particulate matter CEMS according to the procedures in § 60.2165(n) instead of particulate matter testing with EPA Method 5 at 40 CFR part 60, appendix A–3 and, if applicable, the continuous opacity monitoring requirements in paragraph (i) of this section. (i) For energy recovery units with annual average heat input rates greater than or equal to 10 MMBtu/hr and less than 250 MMBtu/hr that do not use a wet scrubber, fabric filter with bag leak detection system, an electrostatic precipitator, particulate matter CEMS, or particulate matter CPMS, you must install, operate, certify and maintain a continuous opacity monitoring system (COMS) according to the procedures in § 60.2165(m). (j) For waste-burning kilns, you must conduct an annual performance test for cadmium, lead, carbon monoxide, dioxins/furans and hydrogen chloride as listed in Table 7 of this subpart, unless you choose to demonstrate initial and continuous compliance using CEMS, as allowed in paragraph (u) of this section. If you do not use an acid gas wet scrubber or dry scrubber, you must determine compliance with the hydrogen chloride emissions limit using a HCl CEMS according to the requirements in paragraph (j)(1) of this section. You must determine compliance with the mercury emissions limit using a mercury CEMS or an integrated sorbent trap monitoring system according to paragraph (j)(2) of this section. You must determine compliance with nitrogen oxides and E:\FR\FM\16APR3.SGM 16APR3 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations sulfur dioxide using CEMS. You must determine compliance with particulate matter using CPMS. (1) If you monitor compliance with the HCl emissions limit by operating an HCl CEMS, you must do so in accordance with Performance Specification 15 (PS 15) of appendix B to 40 CFR part 60 or PS 18 of appendix B to 40 CFR part 60. You must operate, maintain, and quality assure a HCl CEMS installed and certified under PS 15 according to the quality assurance requirements in Procedure 1 of appendix F to 40 CFR part 60 except that the Relative Accuracy Test Audit requirements of Procedure 1 must be replaced with the validation requirements and criteria of sections 11.1.1 and 12.0 of PS 15. You must operate, maintain and quality assure a HCl CEMS installed and certified under PS 18 according to the quality assurance requirements in Procedure 6 of appendix F to 40 CFR part 60. For any performance specification that you use, you must use Method 321 of appendix A to 40 CFR part 63 as the reference test method for conducting relative accuracy testing. The span value and calibration requirements in paragraphs (j)(1)(i) and (ii) of this section apply to all HCl CEMS used under this subpart: (i) You must use a measurement span value for any HCl CEMS of 0–10 ppmvw unless the monitor is installed on a kiln without an inline raw mill. Kilns without an inline raw mill may use a higher span value sufficient to quantify all expected emissions concentrations. The HCl CEMS data recorder output range must include the full range of expected HCl concentration values which would include those expected during ‘‘mill off’’ conditions. The corresponding data recorder range shall be documented in the site-specific monitoring plan and associated records; (ii) In order to quality assure data measured above the span value, you must use one of the three options in paragraphs (j)(1)(ii)(A) through (C) of this section: (A) Include a second span that encompasses the HCl emission concentrations expected to be encountered during ‘‘mill off’’ conditions. This second span may be rounded to a multiple of 5 ppm of total HCl. The requirements of the appropriate HCl monitor performance specification shall be followed for this second span with the exception that a RATA with the mill off is not required; (B) Quality assure any data above the span value by proving instrument linearity beyond the span value established in paragraph (j)(1)(i) of this section using the following procedure. Conduct a weekly ‘‘above span linearity’’ calibration challenge of the monitoring system using a reference gas with a certified value greater than your highest expected hourly concentration or greater than 75% of the highest measured hourly concentration. The ‘‘above span’’ reference gas must meet the requirements of the applicable performance specification and must be introduced to the measurement system at the probe. Record and report the results of this procedure as you would for a daily calibration. The ‘‘above span linearity’’ challenge is successful if the value measured by the HCl CEMS falls within 10 percent of the certified value of the reference gas. If the value measured by the HCl CEMS during the above span linearity challenge exceeds 10 percent of the certified value of the reference gas, the monitoring system must be evaluated and repaired and a new ‘‘above span linearity’’ challenge met before returning the HCl CEMS to service, or data above span from the HCl CEMS must be subject to the quality assurance procedures established in (j)(1)(ii)(D) of this section. In this manner values measured by the HCl CEMS during the above span linearity challenge exceeding +/¥20 percent of the certified value of the reference gas must be normalized using equation 6; (C) Quality assure any data above the span value established in paragraph (j)(1)(i) of this section using the following procedure. Any time two consecutive one-hour average measured concentration of HCl exceeds the span value you must, within 24 hours before or after, introduce a higher, ‘‘above span’’ HCl reference gas standard to the HCl CEMS. The ‘‘above span’’ reference gas must meet the requirements of the applicable performance specification and target a concentration level between 50 and 150 percent of the highest expected hourly concentration measured during the period of measurements above span, and must be introduced at the probe. While this target represents a desired concentration range that is not always achievable in practice, it is expected that the intent to meet this range is demonstrated by the value of the reference gas. Expected values may include above span calibrations done before or after the above-span measurement period. Record and report the results of this procedure as you would for a daily calibration. The ‘‘above span’’ calibration is successful if the value measured by the HCl CEMS is within 20 percent of the certified value of the reference gas. If the value measured by the HCl CEMS is not within 20 percent of the certified value of the reference gas, then you must normalize the stack gas values measured above span as described in paragraph (j)(1)(ii)(D) of this section. If the ‘‘above span’’ calibration is conducted during the period when measured emissions are above span and there is a failure to collect the one data point in an hour due to the calibration duration, then you must determine the emissions average for that missed hour as the average of hourly averages for the hour preceding the missed hour and the hour following the missed hour. In an hour where an ‘‘above span’’ calibration is being conducted and one or more data points are collected, the emissions average is represented by the average of all valid data points collected in that hour; (D) In the event that the ‘‘above span’’ calibration is not successful (i.e., the HCl CEMS measured value is not within 20 percent of the certified value of the reference gas), then you must normalize the one-hour average stack gas values measured above the span during the 24hour period preceding or following the ‘‘above span’’ calibration for reporting based on the HCl CEMS response to the reference gas as shown in equation 6: Only one ‘‘above span’’ calibration is needed per 24-hour period. (2) Compliance with the mercury emissions limit must be determined using a mercury CEMS or integrated sorbent trap monitoring system according to the following requirements: (i) You must operate a mercury CEMS system in accordance with performance specification 12A of 40 CFR part 60, appendix B or an integrated sorbent trap monitoring system in accordance with performance specification 12B of 40 CFR part 60, appendix B; these monitoring systems must be quality assured according to procedure 5 of 40 VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 PO 00000 Frm 00018 Fmt 4701 Sfmt 4700 E:\FR\FM\16APR3.SGM 16APR3 ER16AP19.011</GPH> khammond on DSKBBV9HB2PROD with RULES3 15862 khammond on DSKBBV9HB2PROD with RULES3 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations CFR 60, appendix F. For the purposes of emissions calculations when using an integrated sorbent trap monitoring system, the mercury concentration determined for each sampling period must be assigned to each hour during the sampling period. If you choose to comply with the production-rate based mercury limit for your waste-burning kiln, you must also monitor hourly clinker production and determine the hourly mercury emissions rate in pounds per million ton of clinker produced. You must demonstrate compliance with the mercury emissions limit using a 30-day rolling average of these 1-hour mercury concentrations or mass emissions rates, including CEMS and integerated sorbent trap monitoring system data during startup and shutdown as defined in this subpart, calculated using equation 19–19 in section 12.4.1 of EPA Reference Method 19 at 40 CFR part 60, appendix A–7 of this part. Integerated sorbent trap monitoring system and CEMS data during startup and shutdown, as defined in this subpart, are not corrected to 7 percent oxygen, and are measured at stack oxygen content; (ii) Owners or operators using a mercury CEMS or integrated sorbent trap monitoring system to determine mass emission rate must install, operate, calibrate, and maintain an instrument for continuously measuring and recording the mercury mass emissions rate to the atmosphere according to the requirements of performance specification 6 of 40 CFR part 60, appendix B, and conducting an annual relative accuracy test of the continuous emission rate monitoring system according to section 8.2 of performance specification 6; and (iii) The owner or operator of a wasteburning kiln must demonstrate initial compliance by operating a mercury CEMS or integrated sorbent trap monitoring system while the raw mill of the in-line kiln/raw mill is operating under normal conditions and including at least one period when the raw mill is off. (k) If you use an air pollution control device to meet the emission limitations in this subpart, you must conduct an initial and annual inspection of the air pollution control device. The inspection must include, at a minimum, the following: (1) Inspect air pollution control device(s) for proper operation; and (2) Develop a site-specific monitoring plan according to the requirements in paragraph (l) of this section. This requirement also applies to you if you petition the EPA Administrator for VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 alternative monitoring parameters under § 60.13(i). (l) For each continuous monitoring system required in this section, you must develop and submit to the EPA Administrator for approval a sitespecific monitoring plan according to the requirements of this paragraph (l) that addresses paragraphs (l)(1)(i) through (vi) of this section: (1) You must submit this site-specific monitoring plan at least 60 days before your initial performance evaluation of your continuous monitoring system: (i) Installation of the continuous monitoring system sampling probe or other interface at a measurement location relative to each affected process unit such that the measurement is representative of control of the exhaust emissions (e.g., on or downstream of the last control device); (ii) Performance and equipment specifications for the sample interface, the pollutant concentration or parametric signal analyzer and the data collection and reduction systems. (iii) Performance evaluation procedures and acceptance criteria (e.g., calibrations); (iv) Ongoing operation and maintenance procedures in accordance with the general requirements of § 60.11(d); (v) Ongoing data quality assurance procedures in accordance with the general requirements of § 60.13; and (vi) Ongoing recordkeeping and reporting procedures in accordance with the general requirements of § 60.7(b), (c) introductory text, (c)(1) and (4), and (d) through (g). (2) You must conduct a performance evaluation of each continuous monitoring system in accordance with your site-specific monitoring plan. (3) You must operate and maintain the continuous monitoring system in continuous operation according to the site-specific monitoring plan. (m) If you have an operating limit that requires the use of a flow monitoring system, you must meet the requirements in paragraphs (l) and (m)(1) through (4) of this section: (1) Install the flow sensor and other necessary equipment in a position that provides a representative flow; (2) Use a flow sensor with a measurement sensitivity at full scale of no greater than 2 percent; (3) Minimize the effects of swirling flow or abnormal velocity distributions due to upstream and downstream disturbances; and (4) Conduct a flow monitoring system performance evaluation in accordance with your monitoring plan at the time PO 00000 Frm 00019 Fmt 4701 Sfmt 4700 15863 of each performance test but no less frequently than annually. (n) If you have an operating limit that requires the use of a pressure monitoring system, you must meet the requirements in paragraphs (l) and (n)(1) through (6) of this section: (1) Install the pressure sensor(s) in a position that provides a representative measurement of the pressure (e.g., PM scrubber pressure drop); (2) Minimize or eliminate pulsating pressure, vibration, and internal and external corrosion; (3) Use a pressure sensor with a minimum tolerance of 1.27 centimeters of water or a minimum tolerance of 1 percent of the pressure monitoring system operating range, whichever is less; (4) Perform checks at the frequency outlined in your site-specific monitoring plan to ensure pressure measurements are not obstructed (e.g., check for pressure tap plugging daily); (5) Conduct a performance evaluation of the pressure monitoring system in accordance with your monitoring plan at the time of each performance test but no less frequently than annually; and (6) If at any time the measured pressure exceeds the manufacturer’s specified maximum operating pressure range, conduct a performance evaluation of the pressure monitoring system in accordance with your monitoring plan and confirm that the pressure monitoring system continues to meet the performance requirements in your monitoring plan. Alternatively, install and verify the operation of a new pressure sensor. (o) If you have an operating limit that requires a pH monitoring system, you must meet the requirements in paragraphs (l) and (o)(1) through (4) of this section: (1) Install the pH sensor in a position that provides a representative measurement of scrubber effluent pH; (2) Ensure the sample is properly mixed and representative of the fluid to be measured; (3) Conduct a performance evaluation of the pH monitoring system in accordance with your monitoring plan at least once each process operating day; and (4) Conduct a performance evaluation (including a two-point calibration with one of the two buffer solutions having a pH within 1 of the pH of the operating limit) of the pH monitoring system in accordance with your monitoring plan at the time of each performance test but no less frequently than quarterly. (p) If you have an operating limit that requires a secondary electric power monitoring system for an electrostatic E:\FR\FM\16APR3.SGM 16APR3 khammond on DSKBBV9HB2PROD with RULES3 15864 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations precipitator, you must meet the requirements in paragraphs (l) and (p)(1) and (2) of this section: (1) Install sensors to measure (secondary) voltage and current to the precipitator collection plates; and (2) Conduct a performance evaluation of the electric power monitoring system in accordance with your monitoring plan at the time of each performance test but no less frequently than annually. (q) If you have an operating limit that requires the use of a monitoring system to measure sorbent injection rate (e.g., weigh belt, weigh hopper, or hopper flow measurement device), you must meet the requirements in paragraphs (l) and (q)(1) and (2) of this section: (1) Install the system in a position(s) that provides a representative measurement of the total sorbent injection rate; and (2) Conduct a performance evaluation of the sorbent injection rate monitoring system in accordance with your monitoring plan at the time of each performance test but no less frequently than annually. (r) If you elect to use a fabric filter bag leak detection system to comply with the requirements of this subpart, you must install, calibrate, maintain, and continuously operate a bag leak detection system as specified in paragraphs (l) and (r)(1) through (5) of this section: (1) Install a bag leak detection sensor(s) in a position(s) that will be representative of the relative or absolute particulate matter loadings for each exhaust stack, roof vent, or compartment (e.g., for a positive pressure fabric filter) of the fabric filter; (2) Use a bag leak detection system certified by the manufacturer to be capable of detecting particulate matter emissions at concentrations of 10 milligrams per actual cubic meter or less; (3) Conduct a performance evaluation of the bag leak detection system in accordance with your monitoring plan and consistent with the guidance provided in EPA–454/R–98–015 (incorporated by reference, see § 60.17); (4) Use a bag leak detection system equipped with a device to continuously record the output signal from the sensor; and (5) Use a bag leak detection system equipped with a system that will sound an alarm when an increase in relative particulate matter emissions over a preset level is detected. The alarm must be located where it is observed readily by plant operating personnel. (s) For facilities using a CEMS to demonstrate initial and continuous VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 compliance with the sulfur dioxide emission limit, compliance with the sulfur dioxide emission limit may be demonstrated by using the CEMS specified in § 60.2165(l) to measure sulfur dioxide. The sulfur dioxide CEMS must follow the procedures and methods specified in paragraph (s) of this section. For sources that have actual inlet emissions less than 100 parts per million dry volume, the relative accuracy criterion for inlet sulfur dioxide CEMS should be no greater than 20 percent of the mean value of the reference method test data in terms of the units of the emission standard, or 5 parts per million dry volume absolute value of the mean difference between the reference method and the CEMS, whichever is greater: (1) During each relative accuracy test run of the CEMS required by performance specification 2 in appendix B of this part, collect sulfur dioxide and oxygen (or carbon dioxide) data concurrently (or within a 30- to 60minute period) with both the CEMS and the test methods specified in paragraphs (s)(1)(i) and (ii) of this section: (i) For sulfur dioxide, EPA Reference Method 6 or 6C, or as an alternative ANSI/ASME PTC 19.10–1981 (incorporated by reference, see § 60.17) must be used; and (ii) For oxygen (or carbon dioxide), EPA Reference Method 3A or 3B, or as an alternative ANSI/ASME PTC 19.10– 1981 (incorporated by reference, see § 60.17), must be used. (2) The span value of the CEMS at the inlet to the sulfur dioxide control device must be 125 percent of the maximum estimated hourly potential sulfur dioxide emissions of the unit subject to this subpart. The span value of the CEMS at the outlet of the sulfur dioxide control device must be 50 percent of the maximum estimated hourly potential sulfur dioxide emissions of the unit subject to this subpart. (3) Conduct accuracy determinations quarterly and calibration drift tests daily in accordance with procedure 1 in appendix F of this part. (t) For facilities using a CEMS to demonstrate initial and continuous compliance with the nitrogen oxides emission limit, compliance with the nitrogen oxides emission limit may be demonstrated by using the CEMS specified in § 60.2165 to measure nitrogen oxides. The nitrogen oxides CEMS must follow the procedures and methods specified in paragraphs (t)(1) through (4) of this section: (1) During each relative accuracy test run of the CEMS required by performance specification 2 of appendix B of this part, collect nitrogen oxides PO 00000 Frm 00020 Fmt 4701 Sfmt 4700 and oxygen (or carbon dioxide) data concurrently (or within a 30- to 60minute period) with both the CEMS and the test methods specified in paragraphs (t)(1)(i) and (ii) of this section: (i) For nitrogen oxides, EPA Reference Method 7 or 7E at 40 CFR part 60, appendix A–4 must be used; and (ii) For oxygen (or carbon dioxide), EPA Reference Method 3A or 3B at 40 CFR part 60, appendix A–3, or as an alternative ANSI/ASME PTC 19– 10.1981 (incorporated by reference, see § 60.17), as applicable, must be used. (2) The span value of the continuous emission monitoring system must be 125 percent of the maximum estimated hourly potential nitrogen oxide emissions of the unit. (3) Conduct accuracy determinations quarterly and calibration drift tests daily in accordance with procedure 1 in appendix F of this part. (4) The owner or operator of an affected facility may request that compliance with the nitrogen oxides emission limit be determined using carbon dioxide measurements corrected to an equivalent of 7 percent oxygen. If carbon dioxide is selected for use in diluent corrections, the relationship between oxygen and carbon dioxide levels must be established during the initial performance test according to the procedures and methods specified in paragraphs (t)(4)(i) through (iv) of this section. This relationship may be reestablished during performance compliance tests: (i) The fuel factor equation in Method 3B must be used to determine the relationship between oxygen and carbon dioxide at a sampling location. Method 3A or 3B, or as an alternative ANSI/ ASME PTC 19.10–1981 (incorporated by reference, see § 60.17), as applicable, must be used to determine the oxygen concentration at the same location as the carbon dioxide monitor; (ii) Samples must be taken for at least 30 minutes in each hour; (iii) Each sample must represent a 1hour average; and (iv) A minimum of three runs must be performed. (u) For facilities using a CEMS or an integrated sorbent trap monitoring system for mercury to demonstrate initial and continuouscompliance with any of the emission limits of this subpart, you must complete the following: (1) Demonstrate compliance with the appropriate emission limit(s) using a 30day rolling average of 1-hour arithmetic average emission concentrations, including CEMS or integrated sorbent trap monitoring systems data during startup and shutdown as defined in this E:\FR\FM\16APR3.SGM 16APR3 khammond on DSKBBV9HB2PROD with RULES3 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations subpart, calculated using equation 19– 19 in section 12.4.1 of EPA Reference Method 19 at appendix A–7 of this part. The 1-hour arithmetic averages for CEMS must be calculated using the data points required under § 60.13(e)(2). Except for CEMS or integrated sorbent trap monitoring systems data during startup and shutdown, the 1-hour arithmetic averages used to calculate the 30-day rolling average emission concentrations must be corrected to 7 percent oxygen (dry basis). Integrated sorbent trap monitoring systems or CEMS data during startup and shutdown, as defined in the subpart, are not corrected to 7 percent oxygen, and are measured at stack oxygen content; and (2) Operate all CEMS and integrated sorbent trap monitoring systems in accordance with the applicable procedures under appendices B and F of this part. (v) Use of the bypass stack at any time is an emissions standards deviation for PM, HCl, lead, cadmium, mercury, nitrogen oxides, sulfur dioxide, and dioxin/furans. (w) For energy recovery units with a design heat input capacity of 100 MMBtu/hr or greater that do not use a carbon monoxide CEMS, you must install, operate, and maintain a oxygen analyzer system as defined in § 60.2265 according to the procedures in paragraphs (w)(1) through (4) of this section: (1) The oxygen analyzer system must be installed by the initial performance test date specified in § 60.2140; (2) You must operate the oxygen trim system within compliance with paragraph (w)(3) of this section at all times; (3) You must maintain the oxygen level such that the 30-day rolling average that is established as the operating limit for oxygen is not below the lowest hourly average oxygen concentration measured during the most recent CO performance test; and (4) You must calculate and record a 30-day rolling average oxygen concentration using equation 19–19 in section 12.4.1 of EPA Reference Method 19 of Appendix A–7 of this part. (x) For energy recovery units with annual average heat input rates greater than or equal to 250 MMBtu/hr and waste-burning kilns, you must install, calibrate, maintain, and operate a PM CPMS and record the output of the system as specified in paragraphs (x)(1) through (8) of this section. For other energy recovery units, you may elect to use PM CPMS operated in accordance with this section. PM CPMS are suitable in lieu of using other CMS for VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 monitoring PM compliance (e.g., bag leak detectors, ESP secondary power, PM scrubber pressure): (1) Install, calibrate, operate, and maintain your PM CPMS according to the procedures in your approved sitespecific monitoring plan developed in accordance with paragraphs (l) and (x)(1)(i) through (iii) of this section: (i) The operating principle of the PM CPMS must be based on in-stack or extractive light scatter, light scintillation, beta attenuation, or mass accumulation detection of the exhaust gas or representative sample. The reportable measurement output from the PM CPMS must be expressed as milliamps or the digital signal equivalent; (ii) The PM CPMS must have a cycle time (i.e., period required to complete sampling, measurement, and reporting for each measurement) no longer than 60 minutes; and (iii) The PM CPMS must be capable of detecting and responding to particulate matter concentrations increments no greater than 0.5 mg/actual cubic meter. (2) During the initial performance test or any such subsequent performance test that demonstrates compliance with the PM limit, you must adjust the sitespecific operating limit in accordance with the results of the performance test according to the procedures specified in § 60.2110. (3) Collect PM CPMS hourly average output data for all energy recovery unit or waste-burning kiln operating hours. Express the PM CPMS output as milliamps. (4) Calculate the arithmetic 30-day rolling average of all of the hourly average PM CPMS output collected during all energy recovery unit or wasteburning kiln operating hours data (milliamps or their digital equivalent). (5) You must collect data using the PM CPMS at all times the energy recovery unit or waste-burning kiln is operating and at the intervals specified in paragraph (x)(1)(ii) of this section, except for periods of monitoring system malfunctions, repairs associated with monitoring system malfunctions, required monitoring system quality assurance or quality control activities (including, as applicable, calibration checks and required zero and span adjustments), and any scheduled maintenance as defined in your sitespecific monitoring plan. (6) You must use all the data collected during all energy recovery unit or wasteburning kiln operating hours in assessing the compliance with your operating limit except: (i) Any data collected during monitoring system malfunctions, repairs PO 00000 Frm 00021 Fmt 4701 Sfmt 4700 15865 associated with monitoring system malfunctions, or required monitoring system quality assurance or quality control activities conducted during monitoring system malfunctions are not used in calculations (report any such periods in your annual deviation report); (ii) Any data collected during periods when the monitoring system is out of control as specified in your site-specific monitoring plan, repairs associated with periods when the monitoring system is out of control, or required monitoring system quality assurance or quality control activities conducted during outof-control periods are not used in calculations (report emissions or operating levels and report any such periods in your annual deviation report); (iii) Any PM CPMS data recorded during periods of CEMS data during startup and shutdown, as defined in this subpart. (7) You must record and make available upon request results of PM CPMS system performance audits, as well as the dates and duration of periods from when the PM CPMS is out of control until completion of the corrective actions necessary to return the PM CPMS to operation consistent with your site-specific monitoring plan. (8) For any deviation of the 30-day rolling average PM CPMS average value from the established operating parameter limit, you must: (i) Within 48 hours of the deviation, visually inspect the air pollution control device; (ii) If inspection of the air pollution control device identifies the cause of the deviation, take corrective action as soon as possible and return the PM CPMS measurement to within the established value; (iii) Within 30 days of the deviation or at the time of the annual compliance test, whichever comes first, conduct a PM emissions compliance test to determine compliance with the PM emissions limit. Within 45 days of the deviation, you must re-establish the CPMS operating limit. You are not required to conduct additional testing for any deviations that occur between the time of the original deviation and the PM emissions compliance test required under paragraph (x) of this section; and (iv) PM CPMS deviations leading to more than four required performance tests in a 12-month process operating period (rolling monthly) constitute a violation of this subpart. (y) When there is an alkali bypass and/or an in-line coal mill that exhaust emissions through a separate stack(s), E:\FR\FM\16APR3.SGM 16APR3 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations the combined emissions are subject to the emission limits applicable to wasteburning kilns. To determine the kiln- specific emission limit for demonstrating compliance, you must: (1) Calculate a kiln-specific emission limit using equation 7: Where: Cks = Kiln stack concentration (ppmvd, mg/ dscm, ng/dscm, depending on pollutant. Each corrected to 7% O2.) Qab = Alkali bypass flow rate (volume/hr) Cab = Alkali bypass concentration (ppmvd, mg/dscm, ng/dscm, depending on pollutant. Each corrected to 7% O2.) Qcm = In-line coal mill flow rate (volume/hr) Ccm = In-line coal mill concentration (ppmvd, mg/dscm, ng/dscm, depending on pollutant. Each corrected to 7% O2.) Qks = Kiln stack flow rate (volume/hr) specified in § 60.2160. New operating limits become effective on the date that the performance test report is submitted to the EPA’s Central Data Exchange or postmarked, per the requirements of § 60.2235(b). The Administrator may request a repeat performance test at any time; (2) You must repeat the performance test within 60 days of a process change, as defined in § 60.2265; (3) You can conduct performance tests less often if you meet the following conditions: your performance tests for the pollutant for at least 2 consecutive performance tests demonstrates that the emission level for the pollutant is no greater than the emission level specified in paragraph (a)(3)(i) or (ii) of this section, as applicable; there are no changes in the operation of the affected source or air pollution control equipment that could increase emissions; and you are not required to conduct a performance test for the pollutant in response to a request by the Administrator in paragraph (a)(1) of this section or a process change in paragraph (a)(2) of this section. In this case, you do not have to conduct a performance test for that pollutant for the next 2 years. You must conduct a performance test for the pollutant no more than 37 months following the previous performance test for the pollutant. If the emission level for your CISWI continues to meet the emission level specified in paragraph (a)(3)(i) or (ii) of this section, as applicable, you may choose to conduct performance tests for the pollutant every third year, as long as there are no changes in the operation of the affected source or air pollution control equipment that could increase emissions. Each such performance test must be conducted no more than 37 months after the previous performance test. (i) For particulate matter, hydrogen chloride, mercury, nitrogen oxides, sulfur dioxide, cadmium, lead and dioxins/furans, the emission level equal to 75 percent of the applicable emission limit in table 1 or tables 5 through 8 of this subpart, as applicable; and (ii) For fugitive emissions, visible emissions (of combustion ash from the ash conveying system) for 2 percent of the time during each of the three 1-hour observations periods. (4) If you are conducting less frequent testing for a pollutant as provided in paragraph (a)(3) of this section and a subsequent performance test for the pollutant indicates that your CISWI does not meet the emission level specified in paragraph (a)(3)(i) or (ii) of this section, as applicable, you must conduct annual performance tests for the pollutant according to the schedule specified in paragraph (a) of this section until you qualify for less frequent testing for the pollutant as specified in paragraph (a)(3) of this section. (b) [Reserved] (2) Particulate matter concentration must be measured downstream of the in-line coal mill. All other pollutant concentrations must be measured either upstream or downstream of the in-line coal mill; and (3) For purposes of determining the combined emissions from kilns equipped with an alkali bypass or that exhaust kiln gases to a coal mill that exhausts through a separate stack, instead of installing a CEMS or PM CPMS on the alkali bypass stack or inline coal mill stack, the results of the initial and subsequent performance test can be used to demonstrate compliance with the relevant emissions limit. A performance test must be conducted on an annual basis (between 11 and 13 calendar months following the previous performance test). § 60.2150 By what date must I conduct the annual performance test? You must conduct annual performance tests between 11 and 13 months of the previous performance test. § 60.2151 By what date must I conduct the annual air pollution control device inspection? khammond on DSKBBV9HB2PROD with RULES3 On an annual basis (no more than 12 months following the previous annual air pollution control device inspection), you must complete the air pollution control device inspection as described in § 60.2141. § 60.2155 May I conduct performance testing less often? (a) You must conduct annual performance tests according to the schedule specified in § 60.2150, with the following exceptions: (1) You may conduct a repeat performance test at any time to establish new values for the operating limits, as VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 PO 00000 Frm 00022 Fmt 4701 Sfmt 4700 § 60.2160 May I conduct a repeat performance test to establish new operating limits? (a) Yes. You may conduct a repeat performance test at any time to establish new values for the operating limits. The Administrator may request a repeat performance test at any time. (b) You must repeat the performance test if your feed stream is different than the feed streams used during any performance test used to demonstrate compliance. Monitoring § 60.2165 What monitoring equipment must I install and what parameters must I monitor? (a) If you are using a wet scrubber to comply with the emission limitation under § 60.2105, you must install, calibrate (to manufacturers’ specifications), maintain, and operate devices (or establish methods) for monitoring the value of the operating parameters used to determine compliance with the operating limits listed in table 2 of this subpart. These devices (or methods) must measure and record the values for these operating parameters at the frequencies indicated in table 2 of this subpart at all times except as specified in § 60.2170(a). (b) If you use a fabric filter to comply with the requirements of this subpart and you do not use a PM CPMS or PM CEMS for monitoring PM compliance, you must install, calibrate, maintain, and continuously operate a bag leak detection system as specified in paragraphs (b)(1) through (8) of this section: E:\FR\FM\16APR3.SGM 16APR3 ER16AP19.012</GPH> 15866 khammond on DSKBBV9HB2PROD with RULES3 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations (1) You must install and operate a bag leak detection system for each exhaust stack of the fabric filter; (2) Each bag leak detection system must be installed, operated, calibrated, and maintained in a manner consistent with the manufacturer’s written specifications and recommendations; (3) The bag leak detection system must be certified by the manufacturer to be capable of detecting particulate matter emissions at concentrations of 10 milligrams per actual cubic meter or less; (4) The bag leak detection system sensor must provide output of relative or absolute particulate matter loadings; (5) The bag leak detection system must be equipped with a device to continuously record the output signal from the sensor; (6) The bag leak detection system must be equipped with an alarm system that will alert automatically an operator when an increase in relative particulate matter emissions over a preset level is detected. The alarm must be located where it is observed easily by plant operating personnel; (7) For positive pressure fabric filter systems, a bag leak detection system must be installed in each baghouse compartment or cell. For negative pressure or induced air fabric filters, the bag leak detector must be installed downstream of the fabric filter; and (8) Where multiple detectors are required, the system’s instrumentation and alarm may be shared among detectors. (c) If you are using something other than a wet scrubber, activated carbon, selective non-catalytic reduction, an electrostatic precipitator, or a dry scrubber to comply with the emission limitations under § 60.2105, you must install, calibrate (to the manufacturers’ specifications), maintain, and operate the equipment necessary to monitor compliance with the site-specific operating limits established using the procedures in § 60.2115. (d) If you use activated carbon injection to comply with the emission limitations in this subpart, you must measure the minimum mercury sorbent flow rate once per hour. (e) If you use selective noncatalytic reduction to comply with the emission limitations, you must complete the following: (1) Following the date on which the initial performance test is completed or is required to be completed under § 60.2125, whichever date comes first, ensure that the affected facility does not operate above the maximum charge rate, or below the minimum secondary chamber temperature (if applicable to VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 your CISWI) or the minimum reagent flow rate measured as 3-hour block averages at all times; and (2) Operation of the affected facility above the maximum charge rate, below the minimum secondary chamber temperature and below the minimum reagent flow rate simultaneously constitute a violation of the nitrogen oxides emissions limit. (f) If you use an electrostatic precipitator to comply with the emission limits of this subpart and you do not use a PM CPMS for monitoring PM compliance, you must monitor the secondary power to the electrostatic precipitator collection plates and maintain the 3-hour block averages at or above the operating limits established during the mercury or particulate matter performance test. (g) For waste-burning kilns not equipped with a wet scrubber or dry scrubber, you must install, calibrate, maintain, and operate a CEMS for monitoring hydrogen chloride emissions discharged to the atmosphere, as specified in § 60.2145(j), and record the output of the system. You may substitute use of a HCl CEMS for conducting the HCl initial and annual testing with EPA Method 321 at 40 CFR part 63, appendix A. For units other than waste-burning kilns not equipped with a wet scrubber or dry scrubber, a facility may substitute use of a hydrogen chloride CEMS for conducting the hydrogen chloride initial and annual performance test. For units equipped with a hydrogen chloride CEMS, you are not required to monitor the minimum hydrogen chloride sorbent flow rate, the minimum scrubber liquor pH, or the monitoring minimum injection rate. (h) To demonstrate compliance with the particulate matter emissions limit, a facility may substitute use of a particulate matter CEMS for conducting the PM initial and annual performance test. For units equipped with a particulate matter CEMS, you are not required to use other CMS for monitoring PM compliance (e.g., bag leak detectors, ESP secondary power, PM scrubber pressure). (i) To demonstrate initial and continuous compliance with the dioxin/ furan emissions limit, a facility may substitute use of a continuous automated sampling system for the dioxin/furan initial and annual performance tests. You must record the output of the system and analyze the sample according to EPA Method 23 at 40 CFR part 60, Appendix A–7 of this part. This option to use a continuous automated sampling system takes effect on the date a final performance specification applicable to dioxin/furan PO 00000 Frm 00023 Fmt 4701 Sfmt 4700 15867 from continuous monitors is published in the Federal Register. The owner or operator who elects to continuously sample dioxin/furan emissions instead of sampling and testing using EPA Method 23 at 40 CFR part 60, appendix A–7 must install, calibrate, maintain, and operate a continuous automated sampling system and must comply with the requirements specified in § 60.58b(p) and (q). A facility may substitute continuous dioxin/furan monitoring for the minimum sorbent flow rate, if activated carbon sorbent injection is used solely for compliance with the dioxin/furan emission limit. (j) To demonstrate initial and continuous compliance with the mercury emissions limit, a facility may substitute use of a mercury CEMS or an integrated sorbent trap monitoring system for the mercury initial and annual performance test. The owner or operator who elects to continuously measure mercury emissions instead of sampling and testing using EPA Reference Method 29 or 30B at 40 CFR part 60, appendix A–8, ASTM D6784– 02 (Reapproved 2008) (incorporated by reference, see § 60.17), or an approved alternative method for measuring mercury emissions, must install, calibrate, maintain, and operate the mercury CEMS or integrated sorbent trap monitoring system and must comply with performance specification 12A or performance specification 12B, respectively, and quality assurance procedure 5. For the purposes of emissions calculations when using an integrated sorbent trap monitoring system, the mercury concentration determined for each sampling period must be assigned to each hour during the sampling period. Waste-burning kilns must install, calibrate, maintain, and operate a mercury CEMS or an integrated sorbent trap monitoring system as specified in § 60.2145(j). For units equipped with a mercury CEMS or an integrated sorbent trap monitoring system, you are not required to monitor the minimum sorbent flow rate, if activated carbon sorbent injection is used solely for compliance with the mercury emission limit. (k) To demonstrate initial and continuous compliance with the nitrogen oxides emissions limit, a facility may substitute use of a CEMS for the nitrogen oxides initial and annual performance test to demonstrate compliance with the nitrogen oxides emissions limits. For units equipped with a nitrogen oxides CEMS, you are not required to monitor the charge rate, secondary chamber temperature, and reagent flow for selective noncatalytic reduction, if applicable: E:\FR\FM\16APR3.SGM 16APR3 khammond on DSKBBV9HB2PROD with RULES3 15868 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations (1) Install, calibrate, maintain, and operate a CEMS for measuring nitrogen oxides emissions discharged to the atmosphere and record the output of the system. The requirements under performance specification 2 of appendix B of this part, the quality assurance procedure 1 of appendix F of this part and the procedures under § 60.13 must be followed for installation, evaluation, and operation of the CEMS; and (2) Compliance with the emission limit for nitrogen oxides must be determined based on the 30-day rolling average of the hourly emission concentrations using CEMS outlet data, as outlined in § 60.2145(u). (l) To demonstrate initial and continuous compliance with the sulfur dioxide emissions limit, a facility may substitute use of a CEMS for the sulfur dioxide initial and annual performance test to demonstrate compliance with the sulfur dioxide emissions limits: (1) Install, calibrate, maintain, and operate a CEMS for measuring sulfur dioxide emissions discharged to the atmosphere and record the output of the system. The requirements under performance specification 2 of appendix B of this part, the quality assurance requirements of procedure one of appendix F of this part and procedures under § 60.13 must be followed for installation, evaluation, and operation of the CEMS; and (2) Compliance with the sulfur dioxide emission limit shall be determined based on the 30-day rolling average of the hourly arithmetic average emission concentrations using CEMS outlet data, as outlined in § 60.2145(u). (m) For energy recovery units over 10 MMBtu/hr but less than 250 MMBtu/hr annual average heat input rates that do not use a wet scrubber, fabric filter with bag leak detection system, an electrostatic precipitator, particulate matter CEMS, or particulate matter CPMS you must install, operate, certify, and maintain a continuous opacity monitoring system according to the procedures in paragraphs (m)(1) through (5) of this section by the compliance date specified in § 60.2105. Energy recovery units that use a CEMS to demonstrate initial and continuing compliance according to the procedures in § 60.2165(n) are not required to install a continuous opacity monitoring system and must perform the annual performance tests for the opacity consistent with § 60.2145(f): (1) Install, operate, and maintain each continuous opacity monitoring system according to performance specification 1 of 40 CFR part 60, appendix B; (2) Conduct a performance evaluation of each continuous opacity monitoring VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 system according to the requirements in § 60.13 and according to PS–1 of 40 CFR part 60, appendix B; (3) As specified in § 60.13(e)(1), each continuous opacity monitoring system must complete a minimum of one cycle of sampling and analyzing for each successive 10-second period and one cycle of data recording for each successive 6-minute period; (4) Reduce the continuous opacity monitoring system data as specified in § 60.13(h)(1); and (5) Determine and record all the 6minute averages (and 1-hour block averages as applicable) collected. (n) For coal and liquid/gas energy recovery units, incinerators, and small remote incinerators, an owner or operator may elect to install, calibrate, maintain, and operate a CEMS for monitoring particulate matter emissions discharged to the atmosphere and record the output of the system. The owner or operator of an affected facility who continuously monitors particulate matter emissions instead of conducting performance testing using EPA Method 5 at 40 CFR part 60, appendix A–3 or monitoring with a particulate matter CPMS according to paragraph (r) of this section, must install, calibrate, maintain, and operate a PM CEMS and must comply with the requirements specified in paragraphs (n)(1) through (10) of this section: (1) The PM CEMS must be installed, evaluated, and operated in accordance with the requirements of performance specification 11 of appendix B of this part and quality assurance requirements of procedure 2 of appendix F of this part and § 60.13. Use Method 5 or Method 5I of appendix A of this part for the PM CEMS correlation testing; (2) The initial performance evaluation must be completed no later than 180 days after the date of initial startup of the affected facility, as specified under § 60.2125 or within 180 days of notification to the Administrator of use of the continuous monitoring system if the owner or operator was previously determining compliance by Method 5 performance tests, whichever is later; (3) The owner or operator of an affected facility may request that compliance with the particulate matter emission limit be determined using carbon dioxide measurements corrected to an equivalent of 7 percent oxygen. The relationship between oxygen and carbon dioxide levels for the affected facility must be established according to the procedures and methods specified in § 60.2145(t)(4)(i) through (iv); (4) The owner or operator of an affected facility must conduct an initial performance test for particulate matter PO 00000 Frm 00024 Fmt 4701 Sfmt 4700 emissions. If PM CEMS are elected for demonstrating compliance, and the initial performance test has not yet been conducted, then initial compliance must be determined by using the CEMS specified in paragraph (n) of this section to measure particulate matter. You must calculate a 30-day rolling average of 1hour arithmetic average emission concentrations, including CEMS data during startup and shutdown, as defined in this subpart, using equation 19–19 in section 12.4.1 of EPA Reference Method 19 at 40 CFR part 60, appendix A–7; (5) Continuous compliance with the particulate matter emission limit must be determined based on the 30-day rolling average calculated using equation 19–19 in section 12.4.1 of EPA Reference Method 19 at 40 CFR part 60, appendix A–7 from the 1-hour arithmetic average CEMS outlet data; (6) At a minimum, valid continuous monitoring system hourly averages must be obtained as specified in § 60.2170(e); (7) The 1-hour arithmetic averages required under paragraph (n)(5) of this section must be expressed in milligrams per dry standard cubic meter corrected to 7 percent oxygen (dry basis) and must be used to calculate the 30-day rolling average emission concentrations. CEMS data during startup and shutdown, as defined in this subpart, are not corrected to 7 percent oxygen, and are measured at stack oxygen content. The 1-hour arithmetic averages must be calculated using the data points required under § 60.13(e)(2); (8) All valid CEMS data must be used in calculating average emission concentrations even if the minimum CEMS data requirements of paragraph (n)(6) of this section are not met. (9) The CEMS must be operated according to performance specification 11 in appendix B of this part; and, (10) Quarterly and yearly accuracy audits and daily drift, system optics, and sample volume checks must be performed in accordance with procedure 2 in appendix F of this part. (o) To demonstrate initial and continuous compliance with the carbon monoxide emissions limit, you may substitute use of a CEMS for the carbon monoxide initial and annual performance test: (1) Install, calibrate, maintain, and operate a CEMS for measuring carbon monoxide emissions discharged to the atmosphere and record the output of the system. The requirements under performance specification 4A or 4B of appendix B of this part, the quality assurance procedure 1 of appendix F of this part and the procedures under § 60.13 must be followed for E:\FR\FM\16APR3.SGM 16APR3 khammond on DSKBBV9HB2PROD with RULES3 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations installation, evaluation, and operation of the CEMS; and (2) Compliance with the carbon monoxide emission limit shall be determined based on the 30-day rolling average of the hourly arithmetic average emission concentrations, including CEMS data during startup and shutdown as defined in this subpart, using CEMS outlet data, as outlined in § 60.2145(u). (p) The owner/operator of an affected source with a bypass stack shall install, calibrate (to manufacturers’ specifications), maintain, and operate a device or method for measuring the use of the bypass stack including date, time and duration. (q) For energy recovery units with a design heat input capacity of 100 MMBtu/hr or greater that do not use a carbon monoxide CEMS, you must install, operate, and maintain a oxygen analyzer system as defined in § 60.2265 according to the procedures in paragraphs (q)(1) through (4) of this section: (1) The oxygen analyzer system must be installed by the initial performance test date specified in § 60.2140; (2) You must operate the oxygen trim system within compliance with paragraph (q)(3) of this section at all times; (3) You must maintain the oxygen level such that the 30-day rolling average that is established as the operating limit for oxygen according to paragraph (q)(4) of this section is not below the lowest hourly average oxygen concentration measured during the most recent CO performance test; and (4) You must calculate and record a 30-day rolling average oxygen concentration using equation 19–19 in section 12.4.1 of EPA Reference Method 19 of Appendix A–7 of this part. (r) For energy recovery units with annual average heat input rates greater than or equal to 250 MMBtu/hr and waste-burning kilns, you must install, calibrate, maintain, and operate a PM CPMS and record the output of the system as specified in paragraphs (r)(1) through (8) of this section. If you elect to use a particulate matter CEMS as specified in paragraph (n) of this section, you are not required to use a PM CPMS to monitor particulate matter emissions. For other energy recovery units, you may elect to use PM CPMS operated in accordance with this section. PM CPMS are suitable in lieu of using other CMS for monitoring PM compliance (e.g., bag leak detectors, ESP secondary power, PM scrubber pressure): (1) Install, calibrate, operate, and maintain your PM CPMS according to VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 the procedures in your approved sitespecific monitoring plan developed in accordance with § 60.2145(l) and paragraphs (r)(1)(i) through (iii) of this section: (i) The operating principle of the PM CPMS must be based on in-stack or extractive light scatter, light scintillation, beta attenuation, or mass accumulation detection of PM in the exhaust gas or representative sample. The reportable measurement output from the PM CPMS must be expressed as milliamps or a digital signal equivalent; (ii) The PM CPMS must have a cycle time (i.e., period required to complete sampling, measurement, and reporting for each measurement) no longer than 60 minutes; and (iii) The PM CPMS must be capable of detecting and responding to particulate matter concentration increments no greater than 0.5 mg/actual cubic meter. (2) During the initial performance test or any such subsequent performance test that demonstrates compliance with the PM limit, you must adjust the sitespecific operating limit in accordance with the results of the performance test according to the procedures specified in § 60.2110. (3) Collect PM CPMS hourly average output data for all energy recovery unit or waste-burning kiln operating hours. Express the PM CPMS output as milliamps or the digital signal equivalent. (4) Calculate the arithmetic 30-day rolling average of all of the hourly average PM CPMS output collected during all energy recovery unit or wasteburning kiln operating hours data (milliamps or digital bits). (5) You must collect data using the PM CPMS at all times the energy recovery unit or waste-burning kiln is operating and at the intervals specified in paragraph (r)(1)(ii) of this section, except for periods of monitoring system malfunctions, repairs associated with monitoring system malfunctions, required monitoring system quality assurance or quality control activities (including, as applicable, calibration checks and required zero and span adjustments), and any scheduled maintenance as defined in your sitespecific monitoring plan. (6) You must use all the data collected during all energy recovery unit or wasteburning kiln operating hours in assessing the compliance with your operating limit except: (i) Any data collected during monitoring system malfunctions, repairs associated with monitoring system malfunctions, or required monitoring system quality assurance or quality PO 00000 Frm 00025 Fmt 4701 Sfmt 4700 15869 control activities conducted during monitoring system malfunctions are not used in calculations (report any such periods in your annual deviation report); (ii) Any data collected during periods when the monitoring system is out of control as specified in your site-specific monitoring plan, repairs associated with periods when the monitoring system is out of control, or required monitoring system quality assurance or quality control activities conducted during outof-control periods are not used in calculations (report emissions or operating levels and report any such periods in your annual deviation report); and (iii) Any PM CPMS data recorded during periods of CEMS data during startup and shutdown, as defined in this subpart. (7) You must record and make available upon request results of PM CPMS system performance audits, as well as the dates and duration of periods from when the PM CPMS is out of control until completion of the corrective actions necessary to return the PM CPMS to operation consistent with your site-specific monitoring plan. (8) For any deviation of the 30-day rolling average PM CPMS average value from the established operating parameter limit, you must: (i) Within 48 hours of the deviation, visually inspect the air pollution control device; (ii) If inspection of the air pollution control device identifies the cause of the deviation, take corrective action as soon as possible and return the PM CPMS measurement to within the established value; (iii) Within 30 days of the deviation or at the time of the annual compliance test, whichever comes first, conduct a PM emissions compliance test to determine compliance with the PM emissions limit and to verify the operation of the emissions control device(s). Within 45 days of the deviation, you must re-establish the CPMS operating limit. You are not required to conduct additional testing for any deviations that occur between the time of the original deviation and the PM emissions compliance test required under this paragraph; and (iv) PM CPMS deviations leading to more than four required performance tests in a 12-month process operating period (rolling monthly) constitute a violation of this subpart. (s) If you use a dry scrubber to comply with the emission limits of this subpart, you must monitor the injection rate of each sorbent and maintain the 3-hour block averages at or above the operating E:\FR\FM\16APR3.SGM 16APR3 15870 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations limits established during the hydrogen chloride performance test. (t) If you are required to monitor clinker production because you comply with the production-rate based mercury limit for your waste-burning kiln, you must: (1) Determine hourly clinker production by one of two methods: (i) Install, calibrate, maintain, and operate a permanent weigh scale system to measure and record weight rates in tons-mass per hour of the amount of clinker produced. The system of measuring hourly clinker production must be maintained within ±5 percent accuracy, or (ii) Install, calibrate, maintain, and operate a permanent weigh scale system to measure and record weight rates in tons-mass per hour of the amount of feed to the kiln. The system of measuring feed must be maintained within ±5 percent accuracy. Calculate your hourly clinker production rate using a kiln-specific feed to clinker ratio based on reconciled clinker production determined for accounting purposes and recorded feed rates. Update this ratio monthly. Note that if this ratio changes at clinker reconciliation, you must use the new ratio going forward, but you do not have to retroactively change clinker production rates previously estimated. (2) Determine the accuracy of the system of measuring hourly clinker production (or feed mass flow if applicable) before the effective date and during each quarter of source operation. (3) Conduct accuracy checks in accordance with the procedures outlined in your site-specific monitoring plan under § 60.2145(l). khammond on DSKBBV9HB2PROD with RULES3 § 60.2170 Is there a minimum amount of monitoring data I must obtain? For each continuous monitoring system required or optionally allowed under § 60.2165, you must collect data according to this section: (a) You must operate the monitoring system and collect data at all required intervals at all times compliance is required except for periods of monitoring system malfunctions or outof-control periods, repairs associated with monitoring system malfunctions or out-of-control periods (as specified in 60.2210(o)), and required monitoring system quality assurance or quality control activities (including, as applicable, calibration checks and required zero and span adjustments). A monitoring system malfunction is any sudden, infrequent, not reasonably preventable failure of the monitoring system to provide valid data. Monitoring system failures that are caused in part by poor maintenance or VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 careless operation are not malfunctions. You are required to effect monitoring system repairs in response to monitoring system malfunctions or outof-control periods and to return the monitoring system to operation as expeditiously as practicable; (b) You may not use data recorded during monitoring system malfunctions or out-of-control periods, repairs associated with monitoring system malfunctions or out-of-control periods, or required monitoring system quality assurance or control activities in calculations used to report emissions or operating levels. You must use all the data collected during all other periods, including data normalized for above scale readings, in assessing the operation of the control device and associated control system; and (c) Except for periods of monitoring system malfunctions or out-of-control periods, repairs associated with monitoring system malfunctions or outof-control periods, and required monitoring system quality assurance or quality control activities including, as applicable, calibration checks and required zero and span adjustments, failure to collect required data is a deviation of the monitoring requirements. Recordkeeping and Reporting § 60.2175 What records must I keep? You must maintain the items (as applicable) as specified in paragraphs (a), (b), and (e) through (x) of this section for a period of at least 5 years: (a) Calendar date of each record; and (b) Records of the data described in paragraphs (b)(1) through (7) of this section: (1) The CISWI charge dates, times, weights, and hourly charge rates; (2) Liquor flow rate to the wet scrubber inlet every 15 minutes of operation, as applicable; (3) Pressure drop across the wet scrubber system every 15 minutes of operation or amperage to the wet scrubber every 15 minutes of operation, as applicable; (4) Liquor pH as introduced to the wet scrubber every 15 minutes of operation, as applicable; (5) For affected CISWIs that establish operating limits for controls other than wet scrubbers under § 60.2110(d) through (g) or § 60.2115, you must maintain data collected for all operating parameters used to determine compliance with the operating limits. For energy recovery units using activated carbon injection or a dry scrubber, you must also maintain records of the load fraction and PO 00000 Frm 00026 Fmt 4701 Sfmt 4700 corresponding sorbent injection rate records; (6) If a fabric filter is used to comply with the emission limitations, you must record the date, time, and duration of each alarm and the time corrective action was initiated and completed, and a brief description of the cause of the alarm and the corrective action taken. You must also record the percent of operating time during each 6-month period that the alarm sounds, calculated as specified in § 60.2110(c); (7) If you monitor clinker production in accordance with § 60.2165(t): (i) Hourly clinker rate produced if clinker production is measured directly; (ii) Hourly measured kiln feed rates and calculated clinker production rates if clinker production is not measured directly; (iii) 30-day rolling averages for mercury in pounds per million tons of clinker produced; (iv) The initial and quarterly accuracy of the system of measruing hourly clinker production (or feed mass flow). (c)–(d) [Reserved] (e) Identification of calendar dates and times for which data show a deviation from the operating limits in table 2 of this subpart or a deviation from other operating limits established under § 60.2110(d) through (g) or § 60.2115 with a description of the deviations, reasons for such deviations, and a description of corrective actions taken; (f) The results of the initial, annual, and any subsequent performance tests conducted to determine compliance with the emission limits and/or to establish operating limits, as applicable. Retain a copy of the complete test report including calculations; (g) All documentation produced as a result of the siting requirements of §§ 60.2045 and 60.2050; (h) Records showing the names of CISWI operators who have completed review of the information in § 60.2095(a) as required by § 60.2095(b), including the date of the initial review and all subsequent annual reviews; (i) Records showing the names of the CISWI operators who have completed the operator training requirements under § 60.2070, met the criteria for qualification under § 60.2080, and maintained or renewed their qualification under § 60.2085 or § 60.2090. Records must include documentation of training, the dates of the initial and refresher training, and the dates of their qualification and all subsequent renewals of such qualifications; (j) For each qualified operator, the phone and/or pager number at which E:\FR\FM\16APR3.SGM 16APR3 khammond on DSKBBV9HB2PROD with RULES3 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations they can be reached during operating hours; (k) Records of calibration of any monitoring devices as required under § 60.2165; (l) Equipment vendor specifications and related operation and maintenance requirements for the incinerator, emission controls, and monitoring equipment; (m) The information listed in § 60.2095(a); (n) On a daily basis, keep a log of the quantity of waste burned and the types of waste burned (always required); (o) Maintain records of the annual air pollution control device inspections that are required for each CISWI subject to the emissions limits in table 1 of this subpart or tables 5 through 8 of this subpart, any required maintenance, and any repairs not completed within 10 days of an inspection or the timeframe established by the state regulatory agency; (p) For continuously monitored pollutants or parameters, you must document and keep a record of the following parameters measured using continuous monitoring systems. If you monitor emissions with a CEMS, you must indicate which data are CEMS data during startup and shutdown: (1) All 6-minute average levels of opacity; (2) All 1-hour average concentrations of sulfur dioxide emissions; (3) All 1-hour average concentrations of nitrogen oxides emissions; (4) All 1-hour average concentrations of carbon monoxide emissions; (5) All 1-hour average concentrations of particulate matter emissions; (6) All 1-hour average concentrations of mercury emissions; (7) All 1-hour average concentrations of HCl CEMS outputs; (8) All 1-hour average percent oxygen concentrations; and (9) All 1-hour average PM CPMS readings or particulate matter CEMS outputs; (q) Records indicating use of the bypass stack, including dates, times, and durations. (r) If you choose to stack test less frequently than annually, consistent with § 60.2155(a) through (c), you must keep annual records that document that your emissions in the previous stack test(s) were less than 75 percent of the applicable emission limit and document that there was no change in source operations including fuel composition and operation of air pollution control equipment that would cause emissions of the relevant pollutant to increase within the past year. (s) Records of the occurrence and duration of each malfunction of VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 15871 operation (i.e., process equipment) or the air pollution control and monitoring equipment. (t) Records of all required maintenance performed on the air pollution control and monitoring equipment. (u) Records of actions taken during periods of malfunction to minimize emissions in accordance with § 60.11(d), including corrective actions to restore malfunctioning process and air pollution control and monitoring equipment to its normal or usual manner of operation. (v) For operating units that combust non-hazardous secondary materials that have been determined not to be solid waste pursuant to § 241.3(b)(1) of this chapter, you must keep a record which documents how the secondary material meets each of the legitimacy criteria under § 241.3(d)(1). If you combust a fuel that has been processed from a discarded non-hazardous secondary material pursuant to § 241.3(b)(4) of this chapter, you must keep records as to how the operations that produced the fuel satisfies the definition of processing in § 241.2 and each of the legitimacy criteria of § 241.3(d)(1) of this chapter. If the fuel received a non-waste determination pursuant to the petition process submitted under § 241.3(c) of this chapter, you must keep a record that documents how the fuel satisfies the requirements of the petition process. For operating units that combust nonhazardous secondary materials as fuel per § 241.4, you must keep records documenting that the material is a listed non-waste under § 241.4(a). (w) Records of the criteria used to establish that the unit qualifies as a small power production facility under section 3(17)(C) of the Federal Power Act (16 U.S.C. 796(17)(C)) and that the waste material the unit is proposed to burn is homogeneous. (x) Records of the criteria used to establish that the unit qualifies as a cogeneration facility under section 3(18)(B) of the Federal Power Act (16 U.S.C. 796(18)(B)) and that the waste material the unit is proposed to burn is homogeneous. § 60.2190 What must I submit prior to commencing construction? § 60.2180 Where and in what format must I keep my records? You must submit an annual report no later than 12 months following the submission of the information in § 60.2200. You must submit subsequent reports no more than 12 months following the previous report. (If the unit is subject to permitting requirements under title V of the Clean Air Act, you may be required by the permit to submit these reports more frequently.) All records must be available onsite in either paper copy or computer-readable format that can be printed upon request, unless an alternative format is approved by the Administrator. § 60.2185 What reports must I submit? See table 4 of this subpart for a summary of the reporting requirements. PO 00000 Frm 00027 Fmt 4701 Sfmt 4700 You must submit a notification prior to commencing construction that includes the five items listed in paragraphs (a) through (e) of this section: (a) A statement of intent to construct; (b) The anticipated date of commencement of construction; (c) All documentation produced as a result of the siting requirements of § 60.2050; (d) The waste management plan as specified in §§ 60.2055 through 60.2065; and (e) Anticipated date of initial startup. § 60.2195 What information must I submit prior to initial startup? You must submit the information specified in paragraphs (a) through (e) of this section prior to initial startup: (a) The type(s) of waste to be burned; (b) The maximum design waste burning capacity; (c) The anticipated maximum charge rate; (d) If applicable, the petition for sitespecific operating limits under § 60.2115; and (e) The anticipated date of initial startup. § 60.2200 What information must I submit following my initial performance test? You must submit the information specified in paragraphs (a) through (c) of this section no later than 60 days following the initial performance test. All reports must be signed by the facilities manager: (a) The complete test report for the initial performance test results obtained under § 60.2135, as applicable; (b) The values for the site-specific operating limits established in § 60.2110 or § 60.2115; and (c) If you are using a fabric filter to comply with the emission limitations, documentation that a bag leak detection system has been installed and is being operated, calibrated, and maintained as required by § 60.2165(b). § 60.2205 report? E:\FR\FM\16APR3.SGM When must I submit my annual 16APR3 15872 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations khammond on DSKBBV9HB2PROD with RULES3 § 60.2210 What information must I include in my annual report? The annual report required under § 60.2205 must include the items listed in paragraphs (a) through (o) of this section. If you have a deviation from the operating limits or the emission limitations, you must also submit deviation reports as specified in §§ 60.2215, 60.2220, and 60.2225: (a) Company name and address; (b) Statement by a responsible official, with that official’s name, title, and signature, certifying the accuracy of the content of the report; (c) Date of report and beginning and ending dates of the reporting period; (d) The values for the operating limits established pursuant to § 60.2110 or § 60.2115; (e) If no deviation from any emission limitation or operating limit that applies to you has been reported, a statement that there was no deviation from the emission limitations or operating limits during the reporting period; (f) The highest recorded 3-hour average and the lowest recorded 3-hour average (30-day average for energy recovery units), as applicable, for each operating parameter recorded for the calendar year being reported; (g) Information recorded under § 60.2175(b)(6) and (c) through (e) for the calendar year being reported; (h) For each performance test conducted during the reporting period, if any performance test is conducted, the process unit(s) tested, the pollutant(s) tested and the date that such performance test was conducted. Submit, following the procedure specified in § 60.2235(b)(1), the performance test report no later than the date that you submit the annual report; (i) If you met the requirements of § 60.2155(a) or (b), and did not conduct a performance test during the reporting period, you must state that you met the requirements of § 60.2155(a) or (b), and, therefore, you were not required to conduct a performance test during the reporting period; (j) Documentation of periods when all qualified CISWI operators were unavailable for more than 8 hours, but less than 2 weeks; (k) If you had a malfunction during the reporting period, the compliance report must include the number, duration, and a brief description for each type of malfunction that occurred during the reporting period and that caused or may have caused any applicable emission limitation to be exceeded. The report must also include a description of actions taken by an owner or operator during a malfunction of an affected source to minimize VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 emissions in accordance with § 60.11(d), including actions taken to correct a malfunction; (l) For each deviation from an emission or operating limitation that occurs for a CISWI for which you are not using a continuous monitoring system to comply with the emission or operating limitations in this subpart, the annual report must contain the following information: (1) The total operating time of the CISWI at which the deviation occurred during the reporting period; and (2) Information on the number, duration, and cause of deviations (including unknown cause, if applicable), as applicable, and the corrective action taken. (m) If there were periods during which the continuous monitoring system, including the CEMS, was out of control as specified in paragraph (o) of this section, the annual report must contain the following information for each deviation from an emission or operating limitation occurring for a CISWI for which you are using a continuous monitoring system to comply with the emission and operating limitations in this subpart: (1) The date and time that each malfunction started and stopped; (2) The date, time, and duration that each CMS was inoperative, except for zero (low-level) and high-level checks; (3) The date, time, and duration that each continuous monitoring system was out-of-control, including start and end dates and hours and descriptions of corrective actions taken; (4) The date and time that each deviation started and stopped, and whether each deviation occurred during a period of malfunction or during another period; (5) A summary of the total duration of the deviation during the reporting period, and the total duration as a percent of the total source operating time during that reporting period; (6) A breakdown of the total duration of the deviations during the reporting period into those that are due to control equipment problems, process problems, other known causes, and other unknown causes; (7) A summary of the total duration of continuous monitoring system downtime during the reporting period, and the total duration of continuous monitoring system downtime as a percent of the total operating time of the CISWI at which the continuous monitoring system downtime occurred during that reporting period; (8) An identification of each parameter and pollutant that was monitored at the CISWI; PO 00000 Frm 00028 Fmt 4701 Sfmt 4700 (9) A brief description of the CISWI; (10) A brief description of the continuous monitoring system; (11) The date of the latest continuous monitoring system certification or audit; and (12) A description of any changes in continuous monitoring system, processes, or controls since the last reporting period. (n) If there were periods during which the continuous monitoring system, including the CEMS, was not out of control as specified in paragraph (o) of this section, a statement that there were not periods during which the continuous monitoring system was out of control during the reporting period. (o) A continuous monitoring system is out of control in accordance with the procedure in 40 CFR part 60, appendix F of this part, as if any of the following occur: (1) The zero (low-level), mid-level (if applicable), or high-level calibration drift exceeds two times the applicable calibration drift specification in the applicable performance specification or in the relevant standard; (2) The continuous monitoring system fails a performance test audit (e.g., cylinder gas audit), relative accuracy audit, relative accuracy test audit, or linearity test audit; and (3) The continuous opacity monitoring system calibration drift exceeds two times the limit in the applicable performance specification in the relevant standard. § 60.2215 What else must I report if I have a deviation from the operating limits or the emission limitations? (a) You must submit a deviation report if any recorded 3-hour average (30-day average for energy recovery units or for PM CPMS) parameter level is above the maximum operating limit or below the minimum operating limit established under this subpart, if the bag leak detection system alarm sounds for more than 5 percent of the operating time for the 6-month reporting period, if a performance test was conducted that deviated from any emission limitation, if a 30-day average measured using CEMS deviated from any emission limitation. (b) The deviation report must be submitted by August 1 of that year for data collected during the first half of the calendar year (January 1 to June 30), and by February 1 of the following year for data you collected during the second half of the calendar year (July 1 to December 31). E:\FR\FM\16APR3.SGM 16APR3 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations § 60.2220 What must I include in the deviation report? In each report required under § 60.2215, for any pollutant or parameter that deviated from the emission limitations or operating limits specified in this subpart, include the six items described in paragraphs (a) through (d) of this section: (a) The calendar dates and times your unit deviated from the emission limitations or operating limit requirements; (b) The averaged and recorded data for those dates; (c) Durations and causes of the following: (1) Each deviation from emission limitations or operating limits and your corrective actions; (2) Bypass events and your corrective actions; and (d) A copy of the operating limit monitoring data during each deviation and for any test report that documents the emission levels the process unit(s) tested, the pollutant(s) tested and the date that the performance test was conducted. Submit, following the procedure specified in § 60.2235(b)(1), the performance test report no later than the date that you submit the deviation report. khammond on DSKBBV9HB2PROD with RULES3 § 60.2225 What else must I report if I have a deviation from the requirement to have a qualified operator accessible? (a) If all qualified operators are not accessible for 2 weeks or more, you must take the two actions in paragraphs (a)(1) and (2) of this section: (1) Submit a notification of the deviation within 10 days that includes the three items in paragraphs (a)(1)(i) through (iii) of this section: (i) A statement of what caused the deviation; (ii) A description of what you are doing to ensure that a qualified operator is accessible; and (iii) The date when you anticipate that a qualified operator will be available. (2) Submit a status report to the Administrator every 4 weeks that includes the three items in paragraphs (a)(2)(i) through (iii) of this section: (i) A description of what you are doing to ensure that a qualified operator is accessible; (ii) The date when you anticipate that a qualified operator will be accessible; and (iii) Request approval from the Administrator to continue operation of the CISWI. (b) If your unit was shut down by the Administrator, under the provisions of § 60.2100(b)(2), due to a failure to provide an accessible qualified operator, VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 you must notify the Administrator that you are resuming operation once a qualified operator is accessible. § 60.2230 Are there any other notifications or reports that I must submit? (a) Yes. You must submit notifications as provided by § 60.7. (b) If you cease combusting solid waste but continue to operate, you must provide 30 days prior notice of the effective date of the waste-to-fuel switch, consistent with 60.2145(a). The notification must identify: (1) The name of the owner or operator of the CISWI, the location of the source, the emissions unit(s) that will cease burning solid waste, and the date of the notice; (2) The currently applicable subcategory under this subpart, and any 40 CFR part 63 subpart and subcategory that will be applicable after you cease combusting solid waste; (3) The fuel(s), non-waste material(s) and solid waste(s) the CISWI is currently combusting and has combusted over the past 6 months, and the fuel(s) or non-waste materials the unit will commence combusting; (4) The date on which you became subject to the currently applicable emission limits; and (5) The date upon which you will cease combusting solid waste, and the date (if different) that you intend for any new requirements to become applicable (i.e., the effective date of the waste-tofuel switch), consistent with paragraphs (b)(2) and (3) of this section. § 60.2235 reports? In what form can I submit my (a) Submit initial, annual and deviation reports electronically or in paper format, postmarked on or before the submittal due dates. Beginning on April 16, 2021 or once the reporting form has been available in CEDRI for 1 year, whichever is later, you must submit subsequent reports on or before the submittal dates to the EPA via the Compliance and Emissions Data Reporting Interface (CEDRI),which can be accessed through the EPA’s Central Data Exchange (CDX) (https:// cdx.epa.gov/). Use the appropriate electronic report in CEDRI for this subpart or an alternate electronic file format consistent with the extensible markup language (XML) schema listed on the CEDRI website (https:// www3.epa.gov/ttn/chief/cedri/ index.html). The date forms become available in CEDRI will be listed on the CEDRI website. The reports must be submitted by the deadlines specified in this subpart, regardless of the method in which the report is submitted. PO 00000 Frm 00029 Fmt 4701 Sfmt 4700 15873 (b) Submit results of each performance test and CEMS performance evaluation required by this subpart as follows: (1) Within 60 days after the date of completing each performance test (see § 60.8) required by this subpart, you must submit the results of the performance test following the procedure specified in either paragraph (b)(1)(i) or (b)(1)(ii) of this section: (i) For data collected using test methods supported by the EPA’s Electronic Reporting Tool (ERT) as listed on the EPA’s ERT website (https://www3.epa.gov/ttn/chief/ert/ert_ info.html) at the time of the test, you must submit the results of the performance test to the EPA via the CEDRI. (CEDRI can be accessed through the EPA’s CDX (https://cdx.epa.gov/).) Performance test data must be submitted in a file format generated through the use of the EPA’s ERT or an alternate electronic file format consistent with the XML schema listed on the EPA’s ERT website. If you claim that some of the performance test information being submitted is confidential business information (CBI), you must submit a complete file generated through the use of the EPA’s ERT or an alternate electronic file consistent with the XML schema listed on the EPA’s ERT website, including information claimed to be CBI, on a compact disc, flash drive, or other commonly used electronic storage media to the EPA. The electronic media must be clearly marked as CBI and mailed to U.S. EPA/OAQPS/ CORE CBI Office, Attention: Group Leader, Measurement Policy Group, MD C404–02, 4930 Old Page Rd., Durham, NC 27703. The same ERT or alternate file with the CBI omitted must be submitted to the EPA via the EPA’s CDX as described earlier in this paragraph; and (ii) For data collected using test methods that are not supported by the EPA’s ERT as listed on the EPA’s ERT website at the time of the test, you must submit the results of the performance test to the Administrator at the appropriate address listed in § 60.4. (2) Within 60 days after the date of completing each continuous emissions monitoring system performance evaluation you must submit the results of the performance evaluation following the procedure specified in either paragraph (b)(2)(i) or (b)(2)(ii) of this section: (i) For performance evaluations of continuous monitoring systems measuring relative accuracy test audit (RATA) pollutants that are supported by the EPA’s ERT as listed on the EPA’s ERT website at the time of the E:\FR\FM\16APR3.SGM 16APR3 khammond on DSKBBV9HB2PROD with RULES3 15874 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations evaluation, you must submit the results of the performance evaluation to the EPA via the CEDRI. (CEDRI can be accessed through the EPA’s CDX.) Performance evaluation data must be submitted in a file format generated through the use of the EPA’s ERT or an alternate file format consistent with the XML schema listed on the EPA’s ERT website. If you claim that some of the performance evaluation information being submitted is CBI, you must submit a complete file generated through the use of the EPA’s ERT or an alternate electronic file consistent with the XML schema listed on the EPA’s ERT website, including information claimed to be CBI, on a compact disc, flash drive, or other commonly used electronic storage media to the EPA. The electronic storage media must be clearly marked as CBI and mailed to U.S. EPA/ OAQPS/CORE CBI Office, Attention: Group Leader, Measurement Policy Group, MD C404–02, 4930 Old Page Rd., Durham, NC 27703. The same ERT or alternate file with the CBI omitted must be submitted to the EPA via the EPA’s CDX as described earlier in this paragraph; and (ii) For any performance evaluations of continuous monitoring systems measuring RATA pollutants that are not supported by the EPA’s ERT as listed on the EPA’s ERT website at the time of the evaluation, you must submit the results of the performance evaluation to the Administrator at the appropriate address listed in § 60.4. (c) If you are required to electronically submit a report through the Compliance and Emissions Data Reporting Interface (CEDRI) in the EPA’s Central Data Exchange (CDX), and due to a planned or actual outage of either the EPA’s CEDRI or CDX systems within the period of time beginning 5 business days prior to the date that the submission is due, you will be or are precluded from accessing CEDRI or CDX and submitting a required report within the time prescribed, you may assert a claim of EPA system outage for failure to timely comply with the reporting requirement. You must submit notification to the Administrator in writing as soon as possible following the date you first knew, or through due diligence should have known, that the event may cause or caused a delay in reporting. You must provide to the Administrator a written description identifying the date, time and length of the outage; a rationale for attributing the delay in reporting beyond the regulatory deadline to the EPA system outage; describe the measures taken or to be taken to minimize the delay in reporting; and identify a date by which VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 you propose to report, or if you have already met the reporting requirement at the time of the notification, the date you reported. In any circumstance, the report must be submitted electronically as soon as possible after the outage is resolved. The decision to accept the claim of EPA system outage and allow an extension to the reporting deadline is solely within the discretion of the Administrator. (d) If you are required to electronically submit a report through CEDRI in the EPA’s CDX and a force majeure event is about to occur, occurs, or has occurred or there are lingering effects from such an event within the period of time beginning 5 business days prior to the date the submission is due, the owner or operator may assert a claim of force majeure for failure to timely comply with the reporting requirement. For the purposes of this section, a force majeure event is defined as an event that will be or has been caused by circumstances beyond the control of the affected facility, its contractors, or any entity controlled by the affected facility that prevents you from complying with the requirement to submit a report electronically within the time period prescribed. Examples of such events are acts of nature (e.g., hurricanes, earthquakes, or floods), acts of war or terrorism, or equipment failure or safety hazard beyond the control of the affected facility (e.g., large scale power outage). If you intend to assert a claim of force majeure, you must submit notification to the Administrator in writing as soon as possible following the date you first knew, or through due diligence should have known, that the event may cause or caused a delay in reporting. You must provide to the Administrator a written description of the force majeure event and a rationale for attributing the delay in reporting beyond the regulatory deadline to the force majeure event; describe the measures taken or to be taken to minimize the delay in reporting; and identify a date by which you propose to report, or if you have already met the reporting requirement at the time of the notification, the date you reported. In any circumstance, the reporting must occur as soon as possible after the force majeure event occurs. The decision to accept the claim of force majeure and allow an extension to the reporting deadline is solely within the discretion of the Administrator. procedures to seek approval to change your reporting date. Title V Operating Permits § 60.2242 Am I required to apply for and obtain a Title V operating permit for my unit? Yes. Each CISWI and ACI subject to standards under this subpart must operate pursuant to a permit issued under Section 129(e) and Title V of the Clean Air Act. Air Curtain Incinerators (ACIs) § 60.2245 What is an air curtain incinerator? (a) An ACI operates by forcefully projecting a curtain of air across an open chamber or open pit in which combustion occurs. Incinerators of this type can be constructed above or below ground and with or without refractory walls and floor. Air curtain incinerators are not to be confused with conventional combustion devices with enclosed fireboxes and controlled air technology such as mass burn, modular, and fluidized bed combustors. (b) Air curtain incinerators that burn only the materials listed in paragraphs (b)(1) through (3) of this section are only required to meet the requirements under § 60.2242 and under ‘‘Air Curtain Incinerators’’ (§§ 60.2245 through 60.2260): (1) 100 percent wood waste; (2) 100 percent clean lumber; and (3) 100 percent mixture of only wood waste, clean lumber, and/or yard waste. § 60.2250 What are the emission limitations for air curtain incinerators? Within 60 days after your ACI reaches the charge rate at which it will operate, but no later than 180 days after its initial startup, you must meet the two limitations specified in paragraphs (a) and (b) of this section: (a) Maintain opacity to less than or equal to 10 percent opacity (as determined by the average of three 1hour blocks consisting of ten 6-minute average opacity values), except as described in paragraph (b) of this section; and (b) Maintain opacity to less than or equal to 35 percent opacity (as determined by the average of three 1hour blocks consisting of ten 6-minute average opacity values) during the startup period that is within the first 30 minutes of operation. § 60.2240 Can reporting dates be changed? § 60.2255 How must I monitor opacity for air curtain incinerators? If the Administrator agrees, you may change the semiannual or annual reporting dates. See § 60.19(c) for (a) Use Method 9 of appendix A of this part to determine compliance with the opacity limitation. PO 00000 Frm 00030 Fmt 4701 Sfmt 4700 E:\FR\FM\16APR3.SGM 16APR3 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations (b) Conduct an initial test for opacity as specified in § 60.8. (c) After the initial test for opacity, conduct annual tests no more than 12 calendar months following the date of your previous test. § 60.2260 What are the recordkeeping and reporting requirements for air curtain incinerators? (a) Prior to commencing construction on your ACI, submit the three items described in paragraphs (a)(1) through (3) of this section: (1) Notification of your intent to construct the ACI; (2) Your planned initial startup date; and (3) Types of materials you plan to burn in your ACI. (b) Keep records of results of all initial and annual opacity tests onsite in either paper copy or electronic format, unless the Administrator approves another format, for at least 5 years. (c) Make all records available for submittal to the Administrator or for an inspector’s onsite review. (d) You must submit the results (as determined by the average of three 1hour blocks consisting of ten 6-minute average opacity values) of the initial opacity tests no later than 60 days following the initial test. Submit annual opacity test results within 12 months following the previous report. (e) Submit initial and annual opacity test reports as electronic or paper copy on or before the applicable submittal date. (f) Keep a copy of the initial and annual reports onsite for a period of 5 years. Definitions khammond on DSKBBV9HB2PROD with RULES3 § 60.2265 What definitions must I know? Terms used but not defined in this subpart are defined in the Clean Air Act and subpart A (General Provisions) of this part. 30-day rolling average means the arithmetic mean of the previous 720 hours of valid operating data. Valid data excludes periods when this unit is not operating. The 720 hours should be consecutive, but not necessarily continuous if operations are intermittent. Administrator means the Administrator of the U.S. Environmental Protection Agency or his/her authorized representative or Administrator of a State Air Pollution Control Agency. Air curtain incinerator (ACI) means an incinerator that operates by forcefully projecting a curtain of air across an open chamber or pit in which combustion occurs. Incinerators of this VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 type can be constructed above or below ground and with or without refractory walls and floor. Air curtain incinerators are not to be confused with conventional combustion devices with enclosed fireboxes and controlled air technology such as mass burn, modular, and fluidized bed combustors. Annual heat input means the heat input for the 12 months preceding the compliance demonstration. Auxiliary fuel means natural gas, liquified petroleum gas, fuel oil, or diesel fuel. Average annual heat input rate means annual heat input divided by the hours of operation for the 12 months preceding the compliance demonstration. Bag leak detection system means an instrument that is capable of monitoring particulate matter loadings in the exhaust of a fabric filter (i.e., baghouse) in order to detect bag failures. A bag leak detection system includes, but is not limited to, an instrument that operates on triboelectric, light scattering, light transmittance, or other principle to monitor relative particulate matter loadings. Burn-off oven means any rack reclamation unit, part reclamation unit, or drum reclamation unit. A burn-off oven is not an incinerator, wasteburning kiln, an energy recovery unit or a small, remote incinerator under this subpart. Bypass stack means a device used for discharging combustion gases to avoid severe damage to the air pollution control device or other equipment. Calendar quarter means three consecutive months (nonoverlapping) beginning on: January 1, April 1, July 1, or October 1. Calendar year means 365 consecutive days starting on January 1 and ending on December 31. CEMS data during startup and shutdown means the following: (1) For incinerators and small remote incinerators: CEMS data collected during the first hours of a CISWI startup from a cold start until waste is fed to the unit and the hours of operation following the cessation of waste material being fed to the CISWI during a unit shutdown. For each startup event, the length of time that CEMS data may be claimed as being CEMS data during startup must be 48 operating hours or less. For each shutdown event, the length of time that CEMS data may be claimed as being CEMS data during shutdown must be 24 operating hours or less; (2) For energy recovery units: CEMS data collected during the startup or shutdown periods of operation. Startup PO 00000 Frm 00031 Fmt 4701 Sfmt 4700 15875 begins with either the first-ever firing of fuel in a boiler or process heater for the purpose of supplying useful thermal energy (such as steam or heat) for heating, cooling or process purposes, or producing electricity, or the firing of fuel in a boiler or process heater for any purpose after a shutdown event. Startup ends four hours after when the boiler or process heater makes useful thermal energy (such as heat or steam) for heating, cooling, or process purposes, or generates electricity, whichever is earlier. Shutdown begins when the boiler or process heater no longer makes useful thermal energy (such as heat or steam) for heating, cooling, or process purposes and/or generates electricity or when no fuel is being fed to the boiler or process heater, whichever is earlier. Shutdown ends when the boiler or process heater no longer makes useful thermal energy (such as steam or heat) for heating, cooling, or process purposes and/or generates electricity, and no fuel is being combusted in the boiler or process heater; and (3) For waste-burning kilns: CEMS data collected during the periods of kiln operation that do not include normal operations. Startup means the time from when a shutdown kiln first begins firing fuel until it begins producing clinker. Startup begins when a shutdown kiln turns on the induced draft fan and begins firing fuel in the main burner. Startup ends when feed is being continuously introduced into the kiln for at least 120 minutes or when the feed rate exceeds 60 percent of the kiln design limitation rate, whichever occurs first. Shutdown means the cessation of kiln operation. Shutdown begins when feed to the kiln is halted and ends when continuous kiln rotation ceases. Chemical recovery unit means combustion units burning materials to recover chemical constituents or to produce chemical compounds where there is an existing commercial market for such recovered chemical constituents or compounds. A chemical recovery unit is not an incinerator, a waste-burning kiln, an energy recovery unit or a small, remote incinerator under this subpart. The following seven types of units are considered chemical recovery units: (1) Units burning only pulping liquors (i.e., black liquor) that are reclaimed in a pulping liquor recovery process and reused in the pulping process; (2) Units burning only spent sulfuric acid used to produce virgin sulfuric acid; (3) Units burning only wood or coal feedstock for the production of charcoal; (4) Units burning only manufacturing byproduct streams/residue containing E:\FR\FM\16APR3.SGM 16APR3 khammond on DSKBBV9HB2PROD with RULES3 15876 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations catalyst metals that are reclaimed and reused as catalysts or used to produce commercial grade catalysts; (5) Units burning only coke to produce purified carbon monoxide that is used as an intermediate in the production of other chemical compounds; (6) Units burning only hydrocarbon liquids or solids to produce hydrogen, carbon monoxide, synthesis gas, or other gases for use in other manufacturing processes; and (7) Units burning only photographic film to recover silver. Chemotherapeutic waste means waste material resulting from the production or use of antineoplastic agents used for the purpose of stopping or reversing the growth of malignant cells. Clean lumber means wood or wood products that have been cut or shaped and include wet, air-dried, and kilndried wood products. Clean lumber does not include wood products that have been painted, pigment-stained, or pressure-treated by compounds such as chromate copper arsenate, pentachlorophenol, and creosote. Commercial and industrial solid waste incineration unit (CISWI) means any distinct operating unit of any commercial or industrial facility that combusts, or has combusted in the preceding 6 months, any solid waste as that term is defined in 40 CFR part 241. If the operating unit burns materials other than traditional fuels as defined in § 241.2 that have been discarded, and you do not keep and produce records as required by § 60.2175(v), the operating unit is a CISWI. While not all CISWIs will include all of the following components, a CISWI includes, but is not limited to, the solid waste feed system, grate system, flue gas system, waste heat recovery equipment, if any, and bottom ash system. The CISWI does not include air pollution control equipment or the stack. The CISWI boundary starts at the solid waste hopper (if applicable) and extends through two areas: The combustion unit flue gas system, which ends immediately after the last combustion chamber or after the waste heat recovery equipment, if any; and the combustion unit bottom ash system, which ends at the truck loading station or similar equipment that transfers the ash to final disposal. The CISWI includes all ash handling systems connected to the bottom ash handling system. Contained gaseous material means gases that are in a container when that container is combusted. Continuous emission monitoring system (CEMS) means the total equipment that may be required to meet VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 the data acquisition and availability requirements of this subpart, used to sample, condition (if applicable), analyze, and provide a record of emissions. Continuous monitoring system (CMS) means the total equipment, required under the emission monitoring sections in applicable subparts, used to sample and condition (if applicable), to analyze, and to provide a permanent record of emissions or process parameters. A particulate matter continuous parameter monitoring system (PM CPMS) is a type of CMS. Cyclonic burn barrel means a combustion device for waste materials that is attached to a 55 gallon, openhead drum. The device consists of a lid, which fits onto and encloses the drum, and a blower that forces combustion air into the drum in a cyclonic manner to enhance the mixing of waste material and air. A cyclonic burn barrel is not an incinerator, a waste-burning kiln, an energy recovery unit or a small, remote incinerator under this subpart. Deviation means any instance in which an affected source subject to this subpart, or an owner or operator of such a source: (1) Fails to meet any requirement or obligation established by this subpart, including but not limited to any emission limitation, operating limit, or operator qualification and accessibility requirements; and (2) Fails to meet any term or condition that is adopted to implement an applicable requirement in this subpart and that is included in the operating permit for any affected source required to obtain such a permit. Dioxins/furans means tetra- through octa-chlorinated dibenzo-p-dioxins and dibenzofurans. Discard means, for purposes of this subpart and 40 CFR part 60, subpart DDDD, only, burned in an incineration unit without energy recovery. Drum reclamation unit means a unit that burns residues out of drums (e.g., 55 gallon drums) so that the drums can be reused. Dry scrubber means an add-on air pollution control system that injects dry alkaline sorbent (dry injection) or sprays an alkaline sorbent (spray dryer) to react with and neutralize acid gas in the exhaust stream forming a dry powder material. Sorbent injection systems in fluidized bed boilers and process heaters are included in this definition. A dry scrubber is a dry control system. Energy recovery means the process of recovering thermal energy from combustion for useful purposes such as steam generation or process heating. PO 00000 Frm 00032 Fmt 4701 Sfmt 4700 Energy recovery unit means a combustion unit combusting solid waste (as that term is defined by the Administrator in 40 CFR part 241) for energy recovery. Energy recovery units include units that would be considered boilers and process heaters if they did not combust solid waste. Energy recovery unit designed to burn biomass (Biomass) means an energy recovery unit that burns solid waste, biomass, and non-coal solid materials but less than 10 percent coal, on a heat input basis on an annual average, either alone or in combination with liquid waste, liquid fuel or gaseous fuels. Energy recovery unit designed to burn coal (Coal) means an energy recovery unit that burns solid waste and at least 10 percent coal on a heat input basis on an annual average, either alone or in combination with liquid waste, liquid fuel or gaseous fuels. Energy recovery unit designed to burn liquid waste materials and gas (Liquid/ gas) means an energy recovery unit that burns a liquid waste with liquid or gaseous fuels not combined with any solid fuel or waste materials. Energy recovery unit designed to burn solid materials (Solids) includes energy recovery units designed to burn coal and energy recovery units designed to burn biomass. Fabric filter means an add-on air pollution control device used to capture particulate matter by filtering gas streams through filter media, also known as a baghouse. Foundry sand thermal reclamation unit means a type of part reclamation unit that removes coatings that are on foundry sand. A foundry sand thermal reclamation unit is not an incinerator, a waste-burning kiln, an energy recovery unit or a small, remote incinerator under this subpart. Incinerator means any furnace used in the process of combusting solid waste (as that term is defined by the Administrator in 40 CFR part 241) for the purpose of reducing the volume of the waste by removing combustible matter. Incinerator designs include single chamber and two-chamber. In-line coal mill means those coal mills using kiln exhaust gases in their process. Coal mills with a heat source other than the kiln or coal mills using exhaust gases from the clinker cooler alone are not an in-line coal mill. In-line kiln/raw mill means a system in a Portland Cement production process where a dry kiln system is integrated with the raw mill so that all or a portion of the kiln exhaust gases are used to perform the drying operation of the raw mill, with no auxiliary heat source used. In this system the kiln is E:\FR\FM\16APR3.SGM 16APR3 khammond on DSKBBV9HB2PROD with RULES3 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations capable of operating without the raw mill operating, but the raw mill cannot operate without the kiln gases, and consequently, the raw mill does not generate a separate exhaust gas stream. Kiln means an oven or furnace, including any associated preheater or precalciner devices, in-line raw mills, in-line coal mills or alkali bypasses used for processing a substance by burning, firing or drying. Kilns include cement kilns that produce clinker by heating limestone and other materials for subsequent production of Portland Cement. Because the alkali bypass, inline raw mill and in-line coal mill are considered an integral part of the kiln, the kiln emissions limits also apply to the exhaust of the alkali bypass, in-line raw mill and in-line coal mill. Laboratory analysis unit means units that burn samples of materials for the purpose of chemical or physical analysis. A laboratory analysis unit is not an incinerator, waste-burning kiln, an energy recovery unit or a small, remote incinerator under this subpart. Load fraction means the actual heat input of an energy recovery unit divided by heat input during the performance test that established the minimum sorbent injection rate or minimum activated carbon injection rate, expressed as a fraction (e.g., for 50 percent load the load fraction is 0.5). Low-level radioactive waste means waste material which contains radioactive nuclides emitting primarily beta or gamma radiation, or both, in concentrations or quantities that exceed applicable federal or state standards for unrestricted release. Low-level radioactive waste is not high-level radioactive waste, spent nuclear fuel, or byproduct material as defined by the Atomic Energy Act of 1954 (42 U.S.C. 2014(e)(2)). Malfunction means any sudden, infrequent, and not reasonably preventable failure of air pollution control equipment, process equipment, or a process to operate in a normal or usual manner. Failures that are caused, in part, by poor maintenance or careless operation are not malfunctions. Minimum voltage or amperage means 90 percent of the lowest test-run average voltage or amperage to the electrostatic precipitator measured during the most recent particulate matter or mercury performance test demonstrating compliance with the applicable emission limits. Modification or modified CISWI means a CISWI that has been changed later than August 7, 2013 and that meets one of two criteria: (1) The cumulative cost of the changes over the life of the unit exceeds 50 VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 percent of the original cost of building and installing the CISWI (not including the cost of land) updated to current costs (current dollars). To determine what systems are within the boundary of the CISWI used to calculate these costs, see the definition of CISWI; and (2) Any physical change in the CISWI or change in the method of operating it that increases the amount of any air pollutant emitted for which section 129 or section 111 of the Clean Air Act has established standards. Municipal solid waste or municipaltype solid waste means household, commercial/retail, or institutional waste. Household waste includes material discarded by residential dwellings, hotels, motels, and other similar permanent or temporary housing. Commercial/retail waste includes material discarded by stores, offices, restaurants, warehouses, nonmanufacturing activities at industrial facilities, and other similar establishments or facilities. Institutional waste includes materials discarded by schools, by hospitals (nonmedical), by nonmanufacturing activities at prisons and government facilities, and other similar establishments or facilities. Household, commercial/retail, and institutional waste does include yard waste and refuse-derived fuel. Household, commercial/retail, and institutional waste does not include used oil; sewage sludge; wood pallets; construction, renovation, and demolition wastes (which include railroad ties and telephone poles); clean wood; industrial process or manufacturing wastes; medical waste; or motor vehicles (including motor vehicle parts or vehicle fluff). Opacity means the degree to which emissions reduce the transmission of light and obscure the view of an object in the background. Operating day means a 24-hour period between 12 midnight and the following midnight during which any amount of solid waste is combusted at any time in the CISWI. Oxygen analyzer system means all equipment required to determine the oxygen content of a gas stream and used to monitor oxygen in the boiler or process heater flue gas, boiler or process heater, firebox, or other appropriate location. This definition includes oxygen trim systems and certified oxygen CEMS. The source owner or operator is responsible to install, calibrate, maintain, and operate the oxygen analyzer system in accordance with the manufacturer’s recommendations. Oxygen trim system means a system of monitors that is used to maintain excess PO 00000 Frm 00033 Fmt 4701 Sfmt 4700 15877 air at the desired level in a combustion device over its operating range. A typical system consists of a flue gas oxygen and/or carbon monoxide monitor that automatically provides a feedback signal to the combustion air controller or draft controller. Part reclamation unit means a unit that burns coatings off parts (e.g., tools, equipment) so that the parts can be reconditioned and reused. Particulate matter means total particulate matter emitted from CISWIs as measured by Method 5 or Method 29 of appendix A of this part. Pathological waste means waste material consisting of only human or animal remains, anatomical parts, and/ or tissue, the bags/containers used to collect and transport the waste material, and animal bedding (if applicable). Performance evaluation means the conduct of relative accuracy testing, calibration error testing, and other measurements used in validating the continuous monitoring system data. Performance test means the collection of data resulting from the execution of a test method (usually three emission test runs) used to demonstrate compliance with a relevant emission standard as specified in the performance test section of the relevant standard. Process change means any of the following physical or operational changes: (1) A physical change (maintenance activities excluded) to the CISWI which may increase the emission rate of any air pollutant to which a standard applies; (2) An operational change to the CISWI where a new type of nonhazardous secondary material is being combusted; (3) A physical change (maintenance activities excluded) to the air pollution control devices used to comply with the emission limits for the CISWI (e.g., replacing an electrostatic precipitator with a fabric filter); and (4) An operational change to the air pollution control devices used to comply with the emission limits for the affected CISWI (e.g., change in the sorbent injection rate used for activated carbon injection). Rack reclamation unit means a unit that burns the coatings off racks used to hold small items for application of a coating. The unit burns the coating overspray off the rack so the rack can be reused. Raw mill means a ball or tube mill, vertical roller mill or other size reduction equipment, that is not part of an in-line kiln/raw mill, used to grind feed to the appropriate size. Moisture may be added or removed from the feed E:\FR\FM\16APR3.SGM 16APR3 khammond on DSKBBV9HB2PROD with RULES3 15878 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations during the grinding operation. If the raw mill is used to remove moisture from feed materials, it is also, by definition, a raw material dryer. The raw mill also includes the air separator associated with the raw mill. Reconstruction means rebuilding a CISWI and meeting two criteria: (1) The reconstruction begins on or after August 7, 2013; and (2) The cumulative cost of the construction over the life of the incineration unit exceeds 50 percent of the original cost of building and installing the CISWI (not including land) updated to current costs (current dollars). To determine what systems are within the boundary of the CISWI used to calculate these costs, see the definition of CISWI. Refuse-derived fuel means a type of municipal solid waste produced by processing municipal solid waste through shredding and size classification. This includes all classes of refuse-derived fuel including two fuels: (1) Low-density fluff refuse-derived fuel through densified refuse-derived fuel; and (2) Pelletized refuse-derived fuel. Responsible official means one of the following: (1) For a corporation: A president, secretary, treasurer, or vice-president of the corporation in charge of a principal business function, or any other person who performs similar policy or decision-making functions for the corporation, or a duly authorized representative of such person if the representative is responsible for the overall operation of one or more manufacturing, production, or operating facilities applying for or subject to a permit and either: (i) The facilities employ more than 250 persons or have gross annual sales or expenditures exceeding $25 million (in second quarter 1980 dollars); or (ii) The delegation of authority to such representatives is approved in advance by the permitting authority; (2) For a partnership or sole proprietorship: A general partner or the proprietor, respectively; (3) For a municipality, state, federal, or other public agency: Either a principal executive officer or ranking elected official. For the purposes of this part, a principal executive officer of a federal agency includes the chief executive officer having responsibility for the overall operations of a principal geographic unit of the agency (e.g., a Regional Administrator of EPA); or (4) For affected facilities: VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 (i) The designated representative in so far as actions, standards, requirements, or prohibitions under Title IV of the Clean Air Act or the regulations promulgated thereunder are concerned; or (ii) The designated representative for any other purposes under part 60. Shutdown means, for incinerators and small, remote incinerators, the period of time after all waste has been combusted in the primary chamber. Small, remote incinerator means an incinerator that combusts solid waste (as that term is defined by the Administrator in 40 CFR part 241) and combusts 3 tons per day or less solid waste and is more than 25 miles driving distance to the nearest municipal solid waste landfill. Soil treatment unit means a unit that thermally treats petroleumcontaminated soils for the sole purpose of site remediation. A soil treatment unit may be direct-fired or indirect fired. A soil treatment unit is not an incinerator, a waste-burning kiln, an energy recovery unit or a small, remote incinerator under this subpart. Solid waste means the term solid waste as defined in 40 CFR 241.2. Solid waste incineration unit means a distinct operating unit of any facility which combusts any solid waste (as that term is defined by the Administrator in 40 CFR part 241) material from commercial or industrial establishments or the general public (including single and multiple residences, hotels and motels). Such term does not include incinerators or other units required to have a permit under section 3005 of the Solid Waste Disposal Act. The term ‘‘solid waste incineration unit’’ does not include: (1) Materials recovery facilities (including primary or secondary smelters) which combust waste for the primary purpose of recovering metals; (2) Qualifying small power production facilities, as defined in section 3(17)(C) of the Federal Power Act (16 U.S.C. 769(17)(C)), or qualifying cogeneration facilities, as defined in section 3(18)(B) of the Federal Power Act (16 U.S.C. 796(18)(B)), which burn homogeneous waste (such as units which burn tires or used oil, but not including refuse-derived fuel) for the production of electric energy or in the case of qualifying cogeneration facilities which burn homogeneous waste for the production of electric energy and steam or forms of useful energy (such as heat) which are used for industrial, commercial, heating or cooling purposes; or PO 00000 Frm 00034 Fmt 4701 Sfmt 4700 (3) Air curtain incineratorsprovided that such incinerators only burn wood wastes, yard wastes, and clean lumber and that such ACIs comply with opacity limitations to be established by the Administrator by rule. Space heater means a unit that meets the requirements of 40 CFR 279.23. A space heater is not an incinerator, a waste-burning kiln, an energy recovery unit or a small, remote incinerator under this subpart. Standard conditions, when referring to units of measure, means a temperature of 68 °F (20 °C) and a pressure of 1 atmosphere (101.3 kilopascals). Startup period means, for incinerators and small, remote incinerators, the period of time between the activation of the system and the first charge to the unit. Useful thermal energy means energy (i.e., steam, hot water, or process heat) that meets the minimum operating temperature and/or pressure required by any energy use system that uses energy provided by the affected energy recovery unit. Waste-burning kiln means a kiln that is heated, in whole or in part, by combusting solid waste (as that term is defined by the Administrator in 40 CFR part 241). Secondary materials used in Portland cement kilns shall not be deemed to be combusted unless they are introduced into the flame zone in the hot end of the kiln or mixed with the precalciner fuel. Wet scrubber means an add-on air pollution control device that uses an aqueous or alkaline scrubbing liquor to collect particulate matter (including nonvaporous metals and condensed organics) and/or to absorb and neutralize acid gases. Wood waste means untreated wood and untreated wood products, including tree stumps (whole or chipped), trees, tree limbs (whole or chipped), bark, sawdust, chips, scraps, slabs, millings, and shavings. Wood waste does not include: (1) Grass, grass clippings, bushes, shrubs, and clippings from bushes and shrubs from residential, commercial/ retail, institutional, or industrial sources as part of maintaining yards or other private or public lands; (2) Construction, renovation, or demolition wastes; and (3) Clean lumber. E:\FR\FM\16APR3.SGM 16APR3 15879 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations TABLE 1 TO SUBPART CCCC OF PART 60—EMISSION LIMITATIONS FOR INCINERATORS FOR WHICH CONSTRUCTION IS COMMENCED AFTER NOVEMBER 30, 1999, BUT NO LATER THAN JUNE 4, 2010, OR FOR WHICH MODIFICATION OR RECONSTRUCTION IS COMMENCED ON OR AFTER JUNE 1, 2001, BUT NO LATER THAN AUGUST 7, 2013 Using this averaging time 2 And determining compliance using this method 2 3-run average (1 hour minimum sample time per run) ..... Performance test (Method 29 of appendix A of this part). Performance test (Method 10 at 40 CFR part 60, appendix A–4). Performance test (Method 23 of appendix A–7 of this part). Performance test (Method 26 or 26A at 40 CFR part 60, appendix A–8). You must meet this emission limitation 1 For the air pollutant Cadmium ............................... Carbon monoxide .................. Dioxin/Furan (toxic equivalency basis). Hydrogen chloride ................. Lead ...................................... Mercury ................................. Nitrogen oxides ..................... Opacity .................................. Particulate matter .................. Sulfur dioxide ........................ 0.004 milligrams per dry standard cubic meter. 157 parts per million by dry volume. 0.41 nanograms per dry standard cubic meter. 62 parts per million by dry volume. 3-run average (1 hour minimum sample time per run) ..... 0.04 milligrams per dry standard cubic meter. 0.47 milligrams per dry standard cubic meter. 388 parts per million by dry volume. 10 percent ............................ 70 milligrams per dry standard cubic meter. 20 parts per million by dry volume. 3-run average (collect a minimum volume of 4 dry standard cubic meters per run). 3-run average (For Method 26, collect a minimum volume of 120 liters per run. For Method 26A, collect a minimum volume of 1 dry standard cubic meter per run). 3-run average (1 hour minimum sample time per run) ..... Performance test (Method 29 of appendix A of this part). Performance test (Method 29 of appendix A of this part). Performance test (Method 7 or 7E at 40 CFR part 60, appendix A–4). Performance test (Method 9 of appendix A of this part). Performance test (Method 5 or 29 of appendix A of this part). Performance test (Method 6 or 6C at 40 CFR part 60, appendix A–4). 3-run average (1 hour minimum sample time per run) ..... 3-run average (for Method 7E, 1 hour minimum sample time per run). 6-minute averages ............................................................. 3-run average (1 hour minimum sample time per run) ..... 3-run average (For Method 6, collect a minimum volume of 20 liters per run. For Method 6C, collect sample for a minimum duration of 1 hour per run). 1 All emission limitations (except for opacity) are measured at 7 percent oxygen, dry basis at standard conditions. 2 In lieu of performance testing, you may use a CEMS or, for mercury, an integrated sorbent trap monitoring system, to demonstrate initial and continuing compliance with an emissions limit, as long as you comply with the CEMS or integrated sorbent trap monitoring system requirements applicable to the specific pollutant in §§ 60.2145 and 60.2165. As prescribed in § 60.2145(u), if you use a CEMS or an integrated sorbent trap monitoring system to demonstrate compliance with an emissions limit, your averaging time is a 30-day rolling average of 1-hour arithmetic average emission concentrations. TABLE 2 TO SUBPART CCCC OF PART 60—OPERATING LIMITS FOR WET SCRUBBERS And monitoring using these minimum frequencies You must establish these operating limits Data measurement Data recording Averaging time Charge rate ..................................... Maximum charge rate .. Continuous .............. Every hour ............ Pressure drop across the wet scrubber or amperage to wet scrubber. Scrubber liquor flow rate ................. Scrubber liquor pH .......................... Minimum pressure drop or amperage. Continuous .............. Every 15 minutes .. Daily (batch units) 3-hour rolling (continuous and intermittent units).1 3-hour rolling.1 Minimum flow rate ....... Minimum pH ................ Continuous .............. Continuous .............. Every 15 minutes .. Every 15 minutes .. 3-hour rolling.1 3-hour rolling.1 For these operating parameters 1 Calculated each hour as the average of the previous 3 operating hours. TABLE 3 TO SUBPART CCCC OF PART 60—TOXIC EQUIVALENCY FACTORS Toxic equivalency factor khammond on DSKBBV9HB2PROD with RULES3 Dioxin/furan congener 2,3,7,8-tetrachlorinated dibenzo-p-dioxin ............................................................................................................................................ 1,2,3,7,8-pentachlorinated dibenzo-p-dioxin ........................................................................................................................................ 1,2,3,4,7,8-hexachlorinated dibenzo-p-dioxin ...................................................................................................................................... 1,2,3,7,8,9-hexachlorinated dibenzo-p-dioxin ...................................................................................................................................... 1,2,3,6,7,8-hexachlorinated dibenzo-p-dioxin ...................................................................................................................................... 1,2,3,4,6,7,8-heptachlorinated dibenzo-p-dioxin .................................................................................................................................. octachlorinated dibenzo-p-dioxin ......................................................................................................................................................... 2,3,7,8-tetrachlorinated dibenzofuran .................................................................................................................................................. 2,3,4,7,8-pentachlorinated dibenzofuran ............................................................................................................................................. 1,2,3,7,8-pentachlorinated dibenzofuran ............................................................................................................................................. 1,2,3,4,7,8-hexachlorinated dibenzofuran ........................................................................................................................................... 1,2,3,6,7,8-hexachlorinated dibenzofuran ........................................................................................................................................... 1,2,3,7,8,9-hexachlorinated dibenzofuran ........................................................................................................................................... 2,3,4,6,7,8-hexachlorinated dibenzofuran ........................................................................................................................................... 1,2,3,4,6,7,8-heptachlorinated dibenzofuran ....................................................................................................................................... 1,2,3,4,7,8,9-heptachlorinated dibenzofuran ....................................................................................................................................... octachlorinated dibenzofuran ............................................................................................................................................................... VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 PO 00000 Frm 00035 Fmt 4701 Sfmt 4700 E:\FR\FM\16APR3.SGM 16APR3 1 0.5 0.1 0.1 0.1 0.01 0.001 0.1 0.5 0.05 0.1 0.1 0.1 0.1 0.01 0.01 0.001 15880 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations khammond on DSKBBV9HB2PROD with RULES3 TABLE 4 TO SUBPART CCCC OF PART 60—SUMMARY OF REPORTING REQUIREMENTS 1 Report Due date Contents Preconstruction report ................ Prior to commencing construction ............. Startup notification ...................... Prior to initial startup ................................. Initial test report .......................... No later than 60 days following the initial performance test. Annual report .............................. No later than 12 months following the submission of the initial test report. Subsequent reports are to be submitted no more than 12 months following the previous report. Emission limitation or operating limit deviation report. By August 1 of that year for data collected during the first half of the calendar year. By February 1 of the following year for data collected during the second half of the calendar year. • Statement of intent to construct ............. • Anticipated date of commencement of construction. • Documentation for siting requirements .. • Waste management plan ....................... • Anticipated date of initial startup. • Type of waste to be burned ................... • Maximum design waste burning capacity. • Anticipated maximum charge rate ......... • If applicable, the petition for site-specific operating limits. • Complete test report for the initial performance test. • The values for the site-specific operating limits. • Installation of bag leak detection system for fabric filter. • Name and address ................................ • Statement and signature by responsible official. • Date of report ......................................... • Values for the operating limits ............... • Highest recorded 3-hour average and the lowest 3-hour average, as applicable, (or 30-day average, if applicable) for each operating parameter recorded for the calendar year being reported. • For each performance test conducted during the reporting period, if any performance test is conducted, the process unit(s) tested, the pollutant(s) tested, and the date that such performance test was conducted. • If a performance test was not conducted during the reporting period, a statement that the requirements of § 60.2155(a) were met. • Documentation of periods when all qualified CISWI operators were unavailable for more than 8 hours but less than 2 weeks. • If you are conducting performance tests once every 3 years consistent with § 60.2155(a), the date of the last 2 performance tests, a comparison of the emission level you achieved in the last 2 performance tests to the 75 percent emission limit threshold required in § 60.2155(a) and a statement as to whether there have been any operational changes since the last performance test that could increase emissions. • Any malfunction, deviation, or continuous monitoring system out of control periods information as specified in § 60.2210(k) through (o). • Dates and times of deviation ................. • Averaged and recorded data for those dates. • Duration and causes of each deviation and the corrective actions taken. • Copy of operating limit monitoring data and, if any performance test was conducted that documents emission levels, the process unit(s) tested, the pollutant(s) tested, and the date that such performance test was conducted. • Dates, times and causes for monitor downtime incidents. VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 PO 00000 Frm 00036 Fmt 4701 Sfmt 4700 E:\FR\FM\16APR3.SGM 16APR3 Reference § 60.2190. § 60.2195. § 60.2200. §§ 60.2205 and 60.2210. § 60.2215 and 60.2220. 15881 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations TABLE 4 TO SUBPART CCCC OF PART 60—SUMMARY OF REPORTING REQUIREMENTS 1—Continued Report Due date Contents Qualified operator deviation notification. Within 10 days of deviation ....................... Qualified operator deviation status report. Every 4 weeks following deviation ............ Qualified operator deviation notification of resumed operation. Prior to resuming operation ....................... • Statement of cause of deviation ............ • Description of efforts to have an accessible qualified operator. • The date a qualified operator will be accessible. • Description of efforts to have an accessible qualified operator. • The date a qualified operator will be accessible. • Request for approval to continue operation. • Notification that you are resuming operation. 1 This Reference § 60.2225(a)(1). § 60.2225(a)(2). § 60.2225(b). table is only a summary, see the referenced sections of the rule for the complete requirements. TABLE 5 TO SUBPART CCCC OF PART 60—EMISSION LIMITATIONS FOR INCINERATORS THAT COMMENCED CONSTRUCTION AFTER JUNE 4, 2010, OR THAT COMMENCED RECONSTRUCTION OR MODIFICATION AFTER AUGUST 7, 2013 For the air pollutant You must meet this emission limitation 1 Using this averaging time 2 And determining compliance using this method 2 Cadmium ..................... 0.0023 milligrams per dry standard cubic meter. 17 parts per million by dry volume. 0.58 nanograms per dry standard cubic meter. 0.13 nanograms per dry standard cubic meter. Visible emissions for no more than 5 percent of the hourly observation period. 0.091 parts per million by dry volume. 3-run average (collect a minimum volume of 4 dry standard cubic meter per run). 3-run average (1 hour minimum sample time per run). 3-run average (collect a minimum volume of 4 dry standard cubic meters per run). Performance test (Method 29 at 40 CFR part 60, appendix A–8 of this part). Use ICPMS for the analytical finish. Performance test (Method 10 at 40 CFR part 60, appendix A–4). Performance test (Method 23 at 40 CFR part 60, appendix A–7). 3-run average (collect a minimum volume of 4 dry standard cubic meter per run). Performance test (Method 23 at 40 CFR part 60, appendix A–7). Three 1-hour observation periods .................. Visible emission test (Method 22 at 40 CFR part 60, appendix A–7). 3-run average (For Method 26, collect a minimum volume of 360 liters per run. For Method 26A, collect a minimum volume of 3 dry standard cubic meters per run). 3-run average (collect a minimum volume of 4 dry standard cubic meters per run). Performance test (Method 26 or 26A at 40 CFR part 60, appendix A–8). Carbon monoxide ........ Dioxin/furan (Total Mass Basis). Dioxin/furan (toxic equivalency basis). Fugitive ash ................. Hydrogen chloride ....... Lead ............................. Mercury ........................ Nitrogen oxides ........... Particulate matter (filterable). Sulfur dioxide ............... 0.015 milligrams per dry standard cubic meter. 0.00084 milligrams per dry standard cubic meter. 23 parts per million dry volume. 18 milligrams per dry standard cubic meter. 11 parts per million dry volume. 3-run average (collect enough volume to meet a detection limit data quality objective of 0.03 ug/dry standard cubic meter). 3-run average (for Method 7E, 1 hour minimum sample time per run). 3-run average (collect a minimum volume of 2 dry standard cubic meters per run). 3-run average (1 hour minimum sample time per run). Performance test (Method 29 of appendix A– 8 at 40 CFR part 60). Use ICPMS for the analytical finish. Performance test (Method 29 or 30B at 40 CFR part 60, appendix A–8) or ASTM D6784–02 (Reapproved 2008).3 Performance test (Method 7 or 7E at 40 CFR part 60, appendix A–4). Performance test (Method 5 or 29 at 40 CFR part 60, appendix A–3 or appendix A–8 at 40 CFR part 60). Performance test (Method 6 or 6C at 40 CFR part 60, appendix A–4). khammond on DSKBBV9HB2PROD with RULES3 1 All emission limitations are measured at 7 percent oxygen, dry basis at standard conditions. For dioxins/furans, you must meet either the Total Mass Limit or the toxic equivalency basis limit. 2 In lieu of performance testing, you may use a CEMS or, for mercury, an integrated sorbent trap monitoring system to demonstrate initial and continuing compliance with an emissions limit, as long as you comply with the CEMS or integrated sorbent trap monitoring system requirements applicable to the specific pollutant in §§ 60.2145 and 60.2165. As prescribed in § 60.2145(u), if you use a CEMS or an integrated sorbent trap monitoring system to demonstrate compliance with an emissions limit, your averaging time is a 30-day rolling average of 1-hour arithmetic average emission concentrations. 3 Incorporated by reference, see § 60.17. VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 PO 00000 Frm 00037 Fmt 4701 Sfmt 4700 E:\FR\FM\16APR3.SGM 16APR3 15882 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations TABLE 6 TO SUBPART CCCC OF PART 60—EMISSION LIMITATIONS FOR ENERGY RECOVERY UNITS THAT COMMENCED CONSTRUCTION AFTER JUNE 4, 2010, OR THAT COMMENCED RECONSTRUCTION OR MODIFICATION AFTER AUGUST 7, 2013 You must meet this emission limitation 1 For the air pollutant Liquid/gas Solids Cadmium .................. 0.023 milligrams per dry standard cubic meter. Carbon monoxide ..... 35 parts per million dry volume Dioxin/furans (Total Mass Basis). No Total Mass Basis limit, must meet the toxic equivalency basis limit below. Dioxins/furans (toxic equivalency basis). 0.093 nanograms per standard cubic meter. Fugitive ash .............. Visible emissions for no more than 5 percent of the hourly observation period. 14 parts per million dry volume Biomass-0.0014 milligrams per dry standard cubic meter. Coal-0.0017 milligrams per dry standard cubic meter. Biomass-240 parts per million dry volume. Coal-95 parts per million dry volume. Biomass-0.52 nanograms per dry standard cubic meter. Coal-5.1 nanograms per dry standard cubic meter. Biomass-0.076 nanograms per dry standard cubic meter 3. Coal-0.075 nanograms per dry standard cubic meter. Three 1-hour observation periods. Hydrogen chloride .... dry Lead ......................... 0.096 milligrams per dry standard cubic meter. Mercury .................... 0.00056 milligrams per standard cubic meter. Nitrogen oxides ........ 76 parts per million dry volume Particulate matter (filterable). 110 milligrams per dry standard cubic meter. Sulfur dioxide ........... 720 parts per million dry volume. dry Biomass-0.20 parts per million dry volume. Coal-58 parts per million dry volume. Biomass-0.014 milligrams per dry standard cubic meter. Coal-0.057 milligrams per dry standard cubic meter. Biomass-0.0022 milligrams per dry standard cubic meter. Coal-0.013 milligrams per dry standard cubic meter. Biomass-290 parts per million dry volume. Coal-460 parts per million dry volume. Biomass-5.1 milligrams per dry standard cubic meter. Coal-130 milligrams per dry standard cubic meter. Biomass-7.3 parts per million dry volume. Coal-850 parts per million dry volume. Using this averaging time 2 And determining compliance using this method 2 3-run average (collect a minimum volume of 4 dry standard cubic meters per run). Performance test (Method 29 at 40 CFR part 60, appendix A–8). Use ICPMS for the analytical finish. 3-run average (1 hour minimum sample time per run). Performance test (Method 10 at 40 CFR part 60, appendix A–4). 3-run average (collect a minimum volume of 4 dry standard cubic meters). Performance test (Method 23 at 40 CFR part 60, appendix A–7). 3-run average (collect a minimum volume of 4 dry standard cubic meters per run). Performance test (Method 23 of appendix A–7 of this part). Visible emission test (Method 22 at 40 CFR part 60, appendix A–7). 3-run average (For Method 26, collect a minimum volume of 360 liters per run. For Method 26A, collect a minimum volume of 3 dry standard cubic meters per run). 3-run average (collect a minimum volume of 4 dry standard cubic meters per run). Fugitive ash. 3-run average (collect enough volume to meet an in-stack detection limit data quality objective of 0.03 ug/dscm). 3-run average (for Method 7E, 1 hour minimum sample time per run). Performance test (Method 29 or 30B at 40 CFR part 60, appendix A–8) or ASTM D6784–02 (Reapproved 2008).3 3-run average (collect a minimum volume of 1 dry standard cubic meter per run). Performance test (Method 5 or 29 at 40 CFR part 60, appendix A–3 or appendix A–8) if the unit has an annual average heat input rate less than 250 MMBtu/hr; or PM CPMS (as specified in § 60.2145(x)) if the unit has an annual average heat input rate equal to or greater than 250 MMBtu/hr. Performance test (Method 6 or 6C at 40 CFR part 60, appendix A–4). 3-run average (for Method 6, collect a minimum of 60 liters, for Method 6C,1 hour minimum sample time per run). Performance test (Method 26 or 26A at 40 CFR part 60, appendix A–8). Performance test (Method 29 at 40 CFR part 60, appendix A–8). Use ICPMS for the analytical finish. Performance test (Method 7 or 7E at 40 CFR part 60, appendix A–4). 1 All emission limitations are measured at 7 percent oxygen, dry basis at standard conditions. For dioxins/furans, you must meet either the Total Mass Basis limit or the toxic equivalency basis limit. 2 In lieu of performance testing, you may use a CEMS or, for mercury, an integrated sorbent trap monitoring system to demonstrate initial and continuing compliance with an emissions limit, as long as you comply with the CEMS or integrated sorbent trap monitoring system requirements applicable to the specific pollutant in §§ 60.2145 and 60.2165. As prescribed in § 60.2145(u), if you use a CEMS or an integrated sorbent trap monitoring system to demonstrate compliance with an emissions limit, your averaging time is a 30-day rolling average of 1-hour arithmetic average emission concentrations. 3 Incorporated by reference, see § 60.17. TABLE 7 TO SUBPART CCCC OF PART 60—EMISSION LIMITATIONS FOR WASTE-BURNING KILNS THAT COMMENCED CONSTRUCTION AFTER JUNE 4, 2010, OR RECONSTRUCTION OR MODIFICATION AFTER AUGUST 7, 2013 khammond on DSKBBV9HB2PROD with RULES3 For the air pollutant You must meet this emission limitation 1 Using this averaging time 2 And determining compliance using this method 2 3 Performance test (Method 29 at 40 CFR part 60, appendix A–8). Use ICPMS for the analytical finish. Performance test (Method 10 at 40 CFR part 60, appendix A–4). Cadmium ............................... 0.0014 milligrams per dry standard cubic meter. 3-run average (collect a minimum volume of 4 dry standard cubic meters per run). Carbon monoxide .................. 90 (long kilns)/190 (preheater/precalciner) parts per million dry volume. 0.51 nanograms per dry standard cubic meter. 0.075 nanograms per dry standard cubic meter. 3-run average (1 hour minimum sample time per run) ..... Dioxins/furans (total mass basis). Dioxins/furans (toxic equivalency basis). VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 PO 00000 3-run average (collect a minimum volume of 4 dry standard cubic meters per run). 3-run average (collect a minimum volume of 4 dry standard cubic meters). Frm 00038 Fmt 4701 Sfmt 4700 E:\FR\FM\16APR3.SGM Performance test (Method 23 at 40 CFR part 60, appendix A–7). Performance test (Method 23 at 40 CFR part 60, appendix A–7). 16APR3 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations 15883 TABLE 7 TO SUBPART CCCC OF PART 60—EMISSION LIMITATIONS FOR WASTE-BURNING KILNS THAT COMMENCED CONSTRUCTION AFTER JUNE 4, 2010, OR RECONSTRUCTION OR MODIFICATION AFTER AUGUST 7, 2013—Continued For the air pollutant You must meet this emission limitation 1 Using this averaging time 2 And determining compliance using this method 2 3 Hydrogen chloride ................. 3.0 parts per million dry volume. 3-run average (1 hour minimum sample time per run) or 30-day rolling average if HCl CEMS is being used. Lead ...................................... 0.014 milligrams per dry standard cubic meter. 3-run average (collect a minimum volume of 4 dry standard cubic meters). Mercury ................................. 0.0037 milligrams per dry standard cubic meter. Or 21 pounds/million tons of clinker 3. 200 parts per million dry volume. 30-day rolling average ....................................................... If a wet scrubber or dry scrubber is used, performance test (Method 321 at 40 CFR part 63, appendix A). If a wet scrubber or dry scrubber is not used, HCl CEMS as specified in § 60.2145(j). Performance test (Method 29 at 40 CFR part 60, appendix A–8). Use ICPMS for the analytical finish. Mercury CEMS or integrated sorbent trap monitoring system (performance specification 12A or 12B, respectively, of appendix B and procedure 5 of appendix F of this part), as specified in § 60.2145(j). Nitrogen oxides CEMS (performance specification 2 of appendix B and procedure 1 of appendix F of this part). PM CPMS (as specified in § 60.2145(x)). Nitrogen oxides ..................... Particulate matter (filterable) Sulfur dioxide ........................ 4.9 milligrams per dry standard cubic meter. 28 parts per million dry volume. 30-day rolling average ....................................................... 30-day rolling average ....................................................... 30-day rolling average ....................................................... Sulfur dioxide CEMS (performance specification 2 of appendix B and procedure 1 of appendix F of this part). 1 All emission limitations are measured at 7 percent oxygen (except for CEMS and integrated sorbent trap monitoring system data during startup and shutdown), dry basis at standard conditions. For dioxins/furans, you must meet either the Total Mass Basis limit or the toxic equivalency basis limit. 2 In lieu of performance testing, you may use a CEMS or, for mercury, an integrated sorbent trap monitoring system, to demonstrate initial and continuing compliance with an emissions limit, as long as you comply with the CEMS or integrated sorbent trap monitoring system requirements applicable to the specific pollutant in §§ 60.2145 and 60.2165. As prescribed in § 60.2145(u), if you use a CEMS or integrated sorbent trap monitoring system to demonstrate compliance with an emissions limit, your averaging time is a 30-day rolling average of 1-hour arithmetic average emission concentrations. 3 Alkali bypass and in-line coal mill stacks are subject to performance testing only, as specified in § 60.2145(y)(3). They are not subject to the CEMS, integrated sorbent trap monitoring system, or CPMS requirements that otherwise may apply to the main kiln exhaust. TABLE 8 TO SUBPART CCCC OF PART 60—EMISSION LIMITATIONS FOR SMALL, REMOTE INCINERATORS THAT COMMENCED CONSTRUCTION AFTER JUNE 4, 2010, OR THAT COMMENCED RECONSTRUCTION OR MODIFICATION AFTER AUGUST 7, 2013 For the air pollutant You must meet this emission limitation 1 Using this averaging time 2 And determining compliance using this method 2 Cadmium ............................... 0.67 milligrams per dry standard cubic meter. 13 parts per million dry volume. 1,800 nanograms per dry standard cubic meter. 31 nanograms per dry standard cubic meter. Visible emissions for no more than 5 percent of the hourly observation period. 200 parts per million by dry volume. 3-run average (collect a minimum volume of 1 dry standard cubic meters per run). 3-run average (1 hour minimum sample time per run) ..... Performance test (Method 29 at 40 CFR part 60, appendix A–8). Performance test (Method 10 at 40 CFR part 60, appendix A–4). Performance test (Method 23 at 40 CFR part 60, appendix A–7). Performance test (Method 23 at 40 CFR part 60, appendix A–7). Visible emissions test (Method 22 at 40 CFR part 60, appendix A–7). Carbon monoxide .................. Dioxins/furans (total mass basis). Dioxins/furans (toxic equivalency basis). Fugitive ash ........................... Hydrogen chloride ................. Lead ...................................... 2.0 milligrams per dry standard cubic meter. Mercury ................................. 0.0035 milligrams per dry standard cubic meter. Nitrogen oxides ..................... 170 parts per million dry volume. 270 milligrams per dry standard cubic meter. khammond on DSKBBV9HB2PROD with RULES3 Particulate matter (filterable) Sulfur dioxide ........................ 1.2 parts per million dry volume. 3-run average (collect a minimum volume of 1 dry standard cubic meters per run). 3-run average (collect a minimum volume of 1 dry standard cubic meters). Three 1-hour observation periods ..................................... 3-run average (For Method 26, collect a minimum volume of 60 liters per run. For Method 26A, collect a minimum volume of 1 dry standard cubic meter per run). 3-run average (collect a minimum volume of 1 dry standard cubic meters). 3-run average (For Method 29 and ASTM D6784–02 (Reapproved 2008) 2, collect a minimum volume of 2 dry standard cubic meters per run. For Method 30B, collect a minimum volume as specified in Method 30B at 40 CFR part 60, appendix A). 3-run average (for Method 7E, 1 hour minimum sample time per run). 3-run average (collect a minimum volume of 1 dry standard cubic meters). 3-run average (1 hour minimum sample time per run) ..... Performance test (Method 26 or 26A at 40 CFR part 60, appendix A–8). Performance test (Method 29 at 40 CFR part 60, appendix A–8). Use ICPMS for the analytical finish. Performance test (Method 29 or 30B at 40 CFR part 60, appendix A–8) or ASTM D6784–02 (Reapproved 2008).3 Performance test (Method 7 or 7E at 40 CFR part 60, appendix A–4). Performance test (Method 5 or 29 at 40 CFR part 60, appendix A–3 or appendix A–8). Performance test (Method 6 or 6c at 40 CFR part 60, appendix A–4). 1 All emission limitations are measured at 7 percent oxygen, dry basis at standard conditions. For dioxins/furans, you must meet either the Total Mass Basis limit or the toxic equivalency basis limit. 2 In lieu of performance testing, you may use a CEMS or, for mercury, an integrated sorbent trap monitoring system to demonstrate initial and continuing compliance with an emissions limit, as long as you comply with the CEMS or integrated sorbent trap monitoring system requirements applicable to the specific pollutant in §§ 60.2145 and 60.2165. As prescribed in § 60.2145(u), if you use a CEMS or an integrated sorbent trap monitoring system to demonstrate compliance with an emissions limit, your averaging time is a 30-day rolling average of 1-hour arithmetic average emission concentrations. 3 Incorporated by reference, see § 60.17. VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 PO 00000 Frm 00039 Fmt 4701 Sfmt 4700 E:\FR\FM\16APR3.SGM 16APR3 15884 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations 3. Revise subpart DDDD to read as follows: ■ Sec. Subpart DDDD—Emissions Guidelines and Compliance Times for Commercial and Industrial Solid Waste Incineration Units Introduction 60.2500 What is the purpose of this subpart? 60.2505 Am I affected by this subpart? 60.2510 Is a state plan required for all states? 60.2515 What must I include in my state plan? 60.2520 Is there an approval process for my state plan? 60.2525 What if my state plan is not approvable? 60.2530 Is there an approval process for a negative declaration letter? 60.2535 What compliance schedule must I include in my state plan? 60.2540 Are there any state plan requirements for this subpart that apply instead of the requirements specified in subpart B? 60.2541 In lieu of a state plan submittal, are there other acceptable option(s) for a state to meet its Clean Air Act section 111(d)/129(b)(2) obligations? 60.2542 What authorities will not be delegated to state, local, or tribal agencies? 60.2545 Does this subpart directly affect CISWI owners and operators in my state? Applicability of State Plans 60.2550 What CISWIs must I address in my state plan? 60.2555 What combustion units are exempt from my state plan? khammond on DSKBBV9HB2PROD with RULES3 Use of Model Rule 60.2560 What is the ‘‘model rule’’ in this subpart? 60.2565 How does the model rule relate to the required elements of my state plan? 60.2570 What are the principal components of the model rule? Model Rule—Increments of Progress 60.2575 What are my requirements for meeting increments of progress and achieving final compliance? 60.2580 When must I complete each increment of progress? 60.2585 What must I include in the notifications of achievement of increments of progress? 60.2590 When must I submit the notifications of achievement of increments of progress? 60.2595 What if I do not meet an increment of progress? 60.2600 How do I comply with the increment of progress for submittal of a control plan? 60.2605 How do I comply with the increment of progress for achieving final compliance? 60.2610 What must I do if I close my CISWI and then restart it? 60.2615 What must I do if I plan to permanently close my CISWI and not restart it? VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 Model Rule—Waste Management Plan 60.2620 What is a waste management plan? 60.2625 When must I submit my waste management plan? 60.2630 What should I include in my waste management plan? Model Rule—Operator Training and Qualification 60.2635 What are the operator training and qualification requirements? 60.2640 When must the operator training course be completed? 60.2645 How do I obtain my operator qualification? 60.2650 How do I maintain my operator qualification? 60.2655 How do I renew my lapsed operator qualification? 60.2660 What site-specific documentation is required? 60.2665 What if all the qualified operators are temporarily not accessible? Model Rule—Emission Limitations and Operating Limits 60.2670 What emission limitations must I meet and by when? 60.2675 What operating limits must I meet and by when? 60.2680 What if I do not use a wet scrubber, fabric filter, activated carbon injection, selective noncatalytic reduction, an electrostatic precipitator, or a dry scrubber to comply with the emission limitations? Model Rule—Performance Testing 60.2690 How do I conduct the initial and annual performance test? 60.2695 How are the performance test data used? Model Rule—Initial Compliance Requirements 60.2700 How do I demonstrate initial compliance with the amended emission limitations and establish the operating limits? 60.2705 By what date must I conduct the initial performance test? 60.2706 By what date must I conduct the initial air pollution control device inspection? Model Rule—Continuous Compliance Requirements 60.2710 How do I demonstrate continuous compliance with the amended emission limitations and the operating limits? 60.2715 By what date must I conduct the annual performance test? 60.2716 By what date must I conduct the annual air pollution control device inspection? 60.2720 May I conduct performance testing less often? 60.2725 May I conduct a repeat performance test to establish new operating limits? Model Rule—Monitoring 60.2730 What monitoring equipment must I install and what parameters must I monitor? 60.2735 Is there a minimum amount of monitoring data I must obtain? PO 00000 Frm 00040 Fmt 4701 Sfmt 4700 Model Rule—Recordkeeping and Reporting 60.2740 What records must I keep? 60.2745 Where and in what format must I keep my records? 60.2750 What reports must I submit? 60.2755 When must I submit my waste management plan? 60.2760 What information must I submit following my initial performance test? 60.2765 When must I submit my annual report? 60.2770 What information must I include in my annual report? 60.2775 What else must I report if I have a deviation from the operating limits or the emission limitations? 60.2780 What must I include in the deviation report? 60.2785 What else must I report if I have a deviation from the requirement to have a qualified operator accessible? 60.2790 Are there any other notifications or reports that I must submit? 60.2795 In what form can I submit my reports? 60.2800 Can reporting dates be changed? Model Rule—Title V Operating Permits 60.2805 Am I required to apply for and obtain a Title V operating permit for my unit? Model Rule—Air Curtain Incinerators (ACIs) 60.2810 What is an air curtain incinerator? 60.2815 What are my requirements for meeting increments of progress and achieving final compliance? 60.2820 When must I complete each increment of progress? 60.2825 What must I include in the notifications of achievement of increments of progress? 60.2830 When must I submit the notifications of achievement of increments of progress? 60.2835 What if I do not meet an increment of progress? 60.2840 How do I comply with the increment of progress for submittal of a control plan? 60.2845 How do I comply with the increment of progress for achieving final compliance? 60.2850 What must I do if I close my air curtain incinerator and then restart it? 60.2855 What must I do if I plan to permanently close my air curtain incinerator and not restart it? 60.2860 What are the emission limitations for air curtain incinerators? 60.2865 How must I monitor opacity for air curtain incinerators? 60.2870 What are the recordkeeping and reporting requirements for air curtain incinerators? Model Rule—Definitions 60.2875 What definitions must I know? Tables to Subpart DDDD Table 1 to Subpart DDDD of Part 60—Model Rule—Increments of Progress and Compliance Schedules Table 2 to Subpart DDDD of Part 60—Model Rule—Emission Limitations That Apply to Incinerators Before [Date to be specified in state plan] E:\FR\FM\16APR3.SGM 16APR3 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations Table 3 to Subpart DDDD of Part 60—Model Rule—Operating Limits for Wet Scrubbers Table 4 to Subpart DDDD of Part 60—Model Rule—Toxic Equivalency Factors Table 5 to Subpart DDDD of Part 60—Model Rule—Summary of Reporting Requirements Table 6 to Subpart DDDD of Part 60—Model Rule—Emission Limitations That Apply to Incinerators on and After [Date to be specified in state plan] Table 7 to Subpart DDDD of Part 60—Model Rule—Emission Limitations That Apply to Energy Recovery Units After May 20, 2011 [Date to be specified in state plan] Table 8 to Subpart DDDD of Part 60—Model Rule—Emission Limitations That Apply to Waste-Burning Kilns After May 20, 2011 [Date to be specified in state plan.] Table 9 to Subpart DDDD of Part 60—Model Rule—Emission Limitations That Apply to Small, Remote Incinerators After May 20, 2011 [Date to be specified in state plan] Subpart DDDD—Emissions Guidelines and Compliance Times for Commercial and Industrial Solid Waste Incineration Units Introduction § 60.2500 subpart? What is the purpose of this This subpart establishes emission guidelines and compliance schedules for the control of emissions from commercial and industrial solid waste incineration units (CISWIs) and air curtain incinerators (ACIs). The pollutants addressed by these emission guidelines are listed in table 2 of this subpart and tables 6 through 9 of this subpart. These emission guidelines are developed in accordance with sections 111(d) and 129 of the Clean Air Act and subpart B of this part. khammond on DSKBBV9HB2PROD with RULES3 § 60.2505 Am I affected by this subpart? (a) If you are the Administrator of an air quality program in a state or United States protectorate with one or more existing CISWIs that meet the criteria in paragraphs (b) through (d) of this section, you must submit a state plan to U.S. Environmental Protection Agency (EPA) that implements the emission guidelines contained in this subpart. (b) You must submit a state plan to EPA by December 3, 2001 for incinerator units that commenced construction on or before November 30, 1999 and that were not modified or reconstructed after June 1, 2001. (c) You must submit a state plan that meets the requirements of this subpart and contains the more stringent emission limit for the respective pollutant in table 6 of this subpart or table 1 of subpart CCCC of this part to EPA by February 7, 2014 for VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 15885 this subpart. Your state plan must address regulatory applicability, increments of progress for retrofit, operator training and qualification, a waste management plan, emission limitations, performance testing, operating limits, monitoring, recordkeeping and reporting, and ACI requirements. (c) You must follow the requirements of subpart B of this part (Adoption and Submittal of State Plans for Designated Facilities) in your state plan. incinerators that commenced construction after November 30, 1999, but no later than June 4, 2010, or commenced modification or reconstruction after June 1, 2001 but no later than August 7, 2013. (d) You must submit a state plan to EPA that meets the requirements of this subpart and contains the emission limits in tables 7 through 9 of this subpart by February 7, 2014, for CISWIs other than incinerator units that commenced construction on or before June 4, 2010, or commenced modification or reconstruction after June 4, 2010 but no later than August 7, 2013. § 60.2520 Is there an approval process for my state plan? § 60.2510 states? Yes. The EPA will review your state plan according to § 60.27. Is a state plan required for all No. You are not required to submit a state plan if there are no existing CISWIs in your state, and you submit a negative declaration letter in place of the state plan. § 60.2515 plan? What must I include in my state (a) You must include the nine items described in paragraphs (a)(1) through (9) of this section in your state plan: (1) Inventory of affected CISWIs, including those that have ceased operation but have not been dismantled; (2) Inventory of emissions from affected CISWIs in your state; (3) Compliance schedules for each affected CISWI; (4) Emission limitations, operator training and qualification requirements, a waste management plan, and operating limits for affected CISWIs that are at least as protective as the emission guidelines contained in this subpart; (5) Performance testing, recordkeeping, and reporting requirements; (6) Certification that the hearing on the state plan was held, a list of witnesses and their organizational affiliations, if any, appearing at the hearing, and a brief written summary of each presentation or written submission; (7) Provision for state progress reports to EPA; (8) Identification of enforceable state mechanisms that you selected for implementing the emission guidelines of this subpart; and (9) Demonstration of your state’s legal authority to carry out the sections 111(d) and 129 state plan. (b) Your state plan may deviate from the format and content of the emission guidelines contained in this subpart. However, if your state plan does deviate in content, you must demonstrate that your state plan is at least as protective as the emission guidelines contained in PO 00000 Frm 00041 Fmt 4701 Sfmt 4700 § 60.2525 What if my state plan is not approvable? (a) If you do not submit an approvable state plan (or a negative declaration letter) by December 2, 2002, EPA will develop a federal plan according to § 60.27 to implement the emission guidelines contained in this subpart. Owners and operators of CISWIs not covered by an approved state plan must comply with the federal plan. The federal plan is an interim action and will be automatically withdrawn when your state plan is approved. (b) If you do not submit an approvable state plan (or a negative declaration letter) to EPA that meets the requirements of this subpart and contains the emission limits in tables 6 through 9 of this subpart for CISWIs that commenced construction on or before June 4, 2010 and incinerator or ACIs that commenced reconstruction or modification on or after June 1, 2001 but no later than August 7, 2013, then EPA will develop a federal plan according to § 60.27 to implement the emission guidelines contained in this subpart. Owners and operators of CISWIs not covered by an approved state plan must comply with the federal plan. The federal plan is an interim action and will be automatically withdrawn when your state plan is approved. § 60.2530 Is there an approval process for a negative declaration letter? No. The EPA has no formal review process for negative declaration letters. Once your negative declaration letter has been received, EPA will place a copy in the public docket and publish a document in the Federal Register. If, at a later date, an existing CISWI is found in your state, the federal plan implementing the emission guidelines contained in this subpart would automatically apply to that CISWI until your state plan is approved. E:\FR\FM\16APR3.SGM 16APR3 15886 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations § 60.2535 What compliance schedule must I include in my state plan? (a) For CISWIs in the incinerator subcategory and ACIs that commenced construction on or before November 30, 1999, your state plan must include compliance schedules that require CISWIs in the incinerator subcategory and ACIs to achieve final compliance as expeditiously as practicable after approval of the state plan but not later than the earlier of the two dates specified in paragraphs (a)(1) and (2) of this section: (1) December 1, 2005; and (2) Three years after the effective date of state plan approval. (b) For CISWIs in the incinerator subcategory and ACIs that commenced construction after November 30, 1999, but on or before June 4, 2010 or that commenced reconstruction or modification on or after June 1, 2001 but no later than August 7, 2013, and for CISWIs in the small remote incinerator, energy recovery unit, and waste-burning kiln subcategories that commenced construction before June 4, 2010, your state plan must include compliance schedules that require CISWIs to achieve final compliance as expeditiously as practicable after approval of the state plan but not later than the earlier of the two dates specified in paragraphs (b)(1) and (2) of this section: (1) February 7, 2018; and (2) Three years after the effective date of State plan approval. (c) For compliance schedules more than 1 year following the effective date of State plan approval, State plans must include dates for enforceable increments of progress as specified in § 60.2580. khammond on DSKBBV9HB2PROD with RULES3 § 60.2540 Are there any state plan requirements for this subpart that apply instead of the requirements specified in subpart B? Yes. Subpart B establishes general requirements for developing and processing section 111(d) plans. This subpart applies instead of the requirements in subpart B of this part for paragraphs (a) and (b) of this section: (a) State plans developed to implement this subpart must be as protective as the emission guidelines contained in this subpart. State plans must require all CISWIs to comply by the dates specified in § 60.2535. This applies instead of the option for case-bycase less stringent emission standards and longer compliance schedules in § 60.24(f); and (b) State plans developed to implement this subpart are required to include two increments of progress for the affected CISWIs. These two VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 minimum increments are the final control plan submittal date and final compliance date in § 60.21(h)(1) and (5). This applies instead of the requirement of § 60.24(e)(1) that would require a state plan to include all five increments of progress for all CISWIs. § 60.2541 In lieu of a state plan submittal, are there other acceptable option(s) for a state to meet its Clean Air Act section 111(d)/129(b)(2) obligations? Yes, a state may meet its Clean Air Act section 111(d)/129 obligations by submitting an acceptable written request for delegation of the federal plan that meets the requirements of this section. This is the only other option for a state to meet its Clean Air Act section 111(d)/ 129 obligations. (a) An acceptable federal plan delegation request must include the following: (1) A demonstration of adequate resources and legal authority to administer and enforce the federal plan; (2) The items under § 60.2515(a)(1), (2) and (7); (3) Certification that the hearing on the state delegation request, similar to the hearing for a state plan submittal, was held, a list of witnesses and their organizational affiliations, if any, appearing at the hearing, and a brief written summary of each presentation or written submission; and (4) A commitment to enter into a Memorandum of Agreement with the Regional Administrator who sets forth the terms, conditions, and effective date of the delegation and that serves as the mechanism for the transfer of authority. Additional guidance and information is given in EPA’s Delegation Manual, Item 7–139, Implementation and Enforcement of 111(d)(2) and 111(d)/(2)/ 129(b)(3) federal plans. (b) A state with an already approved CISWI Clean Air Act section 111(d)/129 state plan is not precluded from receiving EPA approval of a delegation request for the revised federal plan, providing the requirements of paragraph (a) of this section are met, and at the time of the delegation request, the state also requests withdrawal of EPA’s previous state plan approval. (c) A state’s Clean Air Act section 111(d)/129 obligations are separate from its obligations under Title V of the Clean Air Act. § 60.2542 What authorities will not be delegated to state, local, or tribal agencies? The authorities that will not be delegated to state, local, or tribal agencies are specified in paragraphs (a) through (i) of this section: (a) Approval of alternatives to the emission limitations in tables 2, 6, 7, 8, PO 00000 Frm 00042 Fmt 4701 Sfmt 4700 and 9 of this subpart and operating limits established under § 60.2675; (b) Approval of major alternatives to test methods; (c) Approval of major alternatives to monitoring; (d) Approval of major alternatives to recordkeeping and reporting; (e) The requirements in § 60.2680; (f) The requirements in § 60.2665(b)(2); (g) Approval of alternative opacity emission limits in § 60.2670 under § 60.11(e)(6) through (8); (h) Performance test and data reduction waivers under § 60.8(b)(4) and (5); and (i) Approval of an alternative to any electronic reporting to the EPA required by this subpart. § 60.2545 Does this subpart directly affect CISWI owners and operators in my state? (a) No. This subpart does not directly affect CISWI owners and operators in your state. However, CISWI owners and operators must comply with the state plan you develop to implement the emission guidelines contained in this subpart. States may choose to incorporate the model rule text directly in their state plan. (b) If you do not submit an approvable plan to implement and enforce the guidelines contained in this subpart for CISWIs that commenced construction before November 30, 1999 by December 2, 2002, EPA will implement and enforce a federal plan, as provided in § 60.2525, to ensure that each unit within your state reaches compliance with all the provisions of this subpart by December 1, 2005. (c) If you do not submit an approvable plan to implement and enforce the guidelines contained in this subpart by February 7, 2014, for CISWIs that commenced construction on or before June 4, 2010, EPA will implement and enforce a federal plan, as provided in § 60.2525, to ensure that each unit within your state that commenced construction on or before June 4, 2010, reaches compliance with all the provisions of this subpart by February 7, 2018. Applicability of State Plans § 60.2550 What CISWIs must I address in my state plan? (a) Your state plan must address incineration units that meet all three criteria described in paragraphs (a)(1) through (3) of this section: (1) Commercial and industrial solid waste incineration units and ACIs in your state that commenced construction on or before June 4, 2010, or commenced modification or E:\FR\FM\16APR3.SGM 16APR3 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations reconstruction after June 4, 2010 but no later than August 7, 2013; (2) Incineration units that meet the definition of a CISWI as defined in § 60.2875 or an ACI as defined in § 60.2875; and (3) Incineration units not exempt under § 60.2555. (b) If the owner or operator of a CISWI or ACI makes changes that meet the definition of modification or reconstruction after August 7, 2013, the CISWI or ACI becomes subject to subpart CCCC of this part and the state plan no longer applies to that unit. (c) If the owner or operator of a CISWI or ACI makes physical or operational changes to an existing CISWI or ACI primarily to comply with your state plan, subpart CCCC of this part does not apply to that unit. Such changes do not qualify as modifications or reconstructions under subpart CCCC of this part. khammond on DSKBBV9HB2PROD with RULES3 § 60.2555 What combustion units are exempt from my state plan? This subpart exempts the types of units described in paragraphs (a) through (j) of this section, but some units are required to provide notifications. (a) Pathological waste incineration units. Incineration units burning 90 percent or more by weight (on a calendar quarter basis and excluding the weight of auxiliary fuel and combustion air) of pathological waste, low-level radioactive waste, and/or chemotherapeutic waste as defined in § 60.2875 are not subject to this subpart if you meet the two requirements specified in paragraphs (a)(1) and (2) of this section: (1) Notify the Administrator that the unit meets these criteria; and (2) Keep records on a calendar quarter basis of the weight of pathological waste, low-level radioactive waste, and/ or chemotherapeutic waste burned, and the weight of all other fuels and wastes burned in the unit. (b) Municipal waste combustion units. Incineration units that are subject to subpart Ea of this part (Standards of Performance for Municipal Waste Combustors); subpart Eb of this part (Standards of Performance for Large Municipal Waste Combustors); subpart Cb of this part (Emission Guidelines and Compliance Time for Large Municipal Combustors); AAAA of this part (Standards of Performance for Small Municipal Waste Combustion Units); or subpart BBBB of this part (Emission Guidelines for Small Municipal Waste Combustion Units). (c) Medical waste incineration units. Incineration units regulated under VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 subpart Ec of this part (Standards of Performance for Hospital/Medical/ Infectious Waste Incinerators for Which Construction is Commenced After June 20, 1996) or subpart Ca of this part (Emission Guidelines and Compliance Times for Hospital/Medical/Infectious Waste Incinerators). (d) Small power production facilities. Units that meet the four requirements specified in paragraphs (d)(1) through (4) of this section: (1) The unit qualifies as a small power-production facility under section 3(17)(C) of the Federal Power Act (16 U.S.C. 796(17)(C)); (2) The unit burns homogeneous waste (not including refuse-derived fuel) to produce electricity; (3) You submit documentation to the Administrator notifying the Agency that the qualifying small power production facility is combusting homogenous waste; and (4) You maintain the records specified in § 60.2740(v). (e) Cogeneration facilities. Units that meet the four requirements specified in paragraphs (e)(1) through (4) of this section: (1) The unit qualifies as a cogeneration facility under section 3(18)(B) of the Federal Power Act (16 U.S.C. 796(18)(B)); (2) The unit burns homogeneous waste (not including refuse-derived fuel) to produce electricity and steam or other forms of energy used for industrial, commercial, heating, or cooling purposes; (3) You submit documentation to the Administrator notifying the Agency that the qualifying cogeneration facility is combusting homogenous waste; and (4) You maintain the records specified in § 60.2740(w). (f) Hazardous waste combustion units. Units for which you are required to get a permit under section 3005 of the Solid Waste Disposal Act. (g) Materials recovery units. Units that combust waste for the primary purpose of recovering metals, such as primary and secondary smelters. (h) Sewage treatment plants. Incineration units regulated under subpart O of this part (Standards of Performance for Sewage Treatment Plants). (i) Sewage sludge incineration units. Incineration units combusting sewage sludge for the purpose of reducing the volume of the sewage sludge by removing combustible matter that are subject to subpart LLLL of this part (Standards of Performance for New Sewage Sludge Incineration Units) or subpart MMMM of this part (Emission Guidelines and Compliance Times for PO 00000 Frm 00043 Fmt 4701 Sfmt 4700 15887 Existing Sewage Sludge Incineration Units). (j) Other solid waste incineration units. Incineration units that are subject to subpart EEEE of this part (Standards of Performance for Other Solid Waste Incineration Units for Which Construction is Commenced After December 9, 2004, or for Which Modification or Reconstruction is Commenced on or After June 16, 2006) or subpart FFFF of this part (Emission Guidelines and Compliance Times for Other Solid Waste Incineration Units That Commenced Construction On or Before December 9, 2004). Use of Model Rule § 60.2560 subpart? What is the ‘‘model rule’’ in this (a) The model rule is the portion of these emission guidelines (§§ 60.2575 through 60.2875 of this part) that addresses the regulatory requirements applicable to CISWIs. The model rule provides these requirements in regulation format. You must develop a state plan that is at least as protective as the model rule. You may use the model rule language as part of your state plan. Alternative language may be used in your state plan if you demonstrate that the alternative language is at least as protective as the model rule contained in this subpart. (b) In the model rule of §§ 60.2575 to 60.2875, ‘‘you’’ means the owner or operator of a CISWI. § 60.2565 How does the model rule relate to the required elements of my state plan? Use the model rule to satisfy the state plan requirements specified in § 60.2515(a)(4) and (5) of this part. § 60.2570 What are the principal components of the model rule? The model rule contains the eleven major components listed in paragraphs (a) through (k) of this section: (a) Increments of progress toward compliance; (b) Waste management plan; (c) Operator training and qualification; (d) Emission limitations and operating limits; (e) Performance testing; (f) Initial compliance requirements; (g) Continuous compliance requirements; (h) Monitoring; (i) Recordkeeping and reporting; (j) Definitions; and (k) Tables. E:\FR\FM\16APR3.SGM 16APR3 15888 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations Model Rule—Increments of Progress § 60.2575 What are my requirements for meeting increments of progress and achieving final compliance? If you plan to achieve compliance more than 1 year following the effective date of state plan approval, you must meet the two increments of progress specified in paragraphs (a) and (b) of this section: (a) Submit a final control plan; and (b) Achieve final compliance. § 60.2580 When must I complete each increment of progress? Table 1 of this subpart specifies compliance dates for each of the increments of progress. § 60.2585 What must I include in the notifications of achievement of increments of progress? Your notification of achievement of increments of progress must include the three items specified in paragraphs (a) through (c) of this section: (a) Notification that the increment of progress has been achieved; (b) Any items required to be submitted with each increment of progress; and (c) Signature of the owner or operator of the CISWI. § 60.2590 When must I submit the notifications of achievement of increments of progress? Notifications for achieving increments of progress must be postmarked no later than 10 business days after the compliance date for the increment. § 60.2595 What if I do not meet an increment of progress? If you fail to meet an increment of progress, you must submit a notification to the Administrator postmarked within 10 business days after the date for that increment of progress in table 1 of this subpart. You must inform the Administrator that you did not meet the increment, and you must continue to submit reports each subsequent calendar month until the increment of progress is met. khammond on DSKBBV9HB2PROD with RULES3 § 60.2600 How do I comply with the increment of progress for submittal of a control plan? For your control plan increment of progress, you must satisfy the two requirements specified in paragraphs (a) and (b) of this section: (a) Submit the final control plan that includes the five items described in paragraphs (a)(1) through (5) of this section: (1) A description of the devices for air pollution control and process changes that you will use to comply with the VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 emission limitations and other requirements of this subpart; (2) The type(s) of waste to be burned; (3) The maximum design waste burning capacity; (4) The anticipated maximum charge rate; and (5) If applicable, the petition for sitespecific operating limits under § 60.2680. (b) Maintain an onsite copy of the final control plan. § 60.2605 How do I comply with the increment of progress for achieving final compliance? For the final compliance increment of progress, you must complete all process changes and retrofit construction of control devices, as specified in the final control plan, so that, if the affected CISWI is brought online, all necessary process changes and air pollution control devices would operate as designed. § 60.2610 What must I do if I close my CISWI and then restart it? (a) If you close your CISWI but will restart it prior to the final compliance date in your state plan, you must meet the increments of progress specified in § 60.2575. (b) If you close your CISWI but will restart it after your final compliance date, you must complete emission control retrofits and meet the emission limitations and operating limits on the date your unit restarts operation. § 60.2615 What must I do if I plan to permanently close my CISWI and not restart it? If you plan to close your CISWI rather than comply with the state plan, submit a closure notification, including the date of closure, to the Administrator by the date your final control plan is due. Model Rule—Waste Management Plan § 60.2620 plan? What is a waste management A waste management plan is a written plan that identifies both the feasibility and the methods used to reduce or separate certain components of solid waste from the waste stream in order to reduce or eliminate toxic emissions from incinerated waste. § 60.2625 When must I submit my waste management plan? You must submit a waste management plan no later than the date specified in table 1 of this subpart for submittal of the final control plan. § 60.2630 What should I include in my waste management plan? A waste management plan must include consideration of the reduction PO 00000 Frm 00044 Fmt 4701 Sfmt 4700 or separation of waste-stream elements such as paper, cardboard, plastics, glass, batteries, or metals; or the use of recyclable materials. The plan must identify any additional waste management measures, and the source must implement those measures considered practical and feasible, based on the effectiveness of waste management measures already in place, the costs of additional measures, the emissions reductions expected to be achieved, and any other environmental or energy impacts they might have. Model Rule—Operator Training and Qualification § 60.2635 What are the operator training and qualification requirements? (a) No CISWI can be operated unless a fully trained and qualified CISWI operator is accessible, either at the facility or can be at the facility within 1 hour. The trained and qualified CISWI operator may operate the CISWI directly or be the direct supervisor of one or more other plant personnel who operate the unit. If all qualified CISWI operators are temporarily not accessible, you must follow the procedures in § 60.2665. (b) Operator training and qualification must be obtained through a stateapproved program or by completing the requirements included in paragraph (c) of this section. (c) Training must be obtained by completing an incinerator operator training course that includes, at a minimum, the three elements described in paragraphs (c)(1) through (3) of this section: (1) Training on the eleven subjects listed in paragraphs (c)(1)(i) through (xi) of this section: (i) Environmental concerns, including types of emissions; (ii) Basic combustion principles, including products of combustion; (iii) Operation of the specific type of incinerator to be used by the operator, including proper startup, waste charging, and shutdown procedures; (iv) Combustion controls and monitoring; (v) Operation of air pollution control equipment and factors affecting performance (if applicable); (vi) Inspection and maintenance of the incinerator and air pollution control devices; (vii) Actions to prevent and correct malfunctions or to prevent conditions that may lead to malfunctions; (viii) Bottom and fly ash characteristics and handling procedures; (ix) Applicable federal, state, and local regulations, including Occupational Safety and Health Administration workplace standards; E:\FR\FM\16APR3.SGM 16APR3 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations (x) Pollution prevention; and (xi) Waste management practices. (2) An examination designed and administered by the instructor. (3) Written material covering the training course topics that can serve as reference material following completion of the course. § 60.2640 When must the operator training course be completed? The operator training course must be completed by the later of the three dates specified in paragraphs (a) through (c) of this section: (a) The final compliance date (Increment 2); (b) Six months after CISWI startup; and (c) Six months after an employee assumes responsibility for operating the CISWI or assumes responsibility for supervising the operation of the CISWI. § 60.2645 How do I obtain my operator qualification? (a) You must obtain operator qualification by completing a training course that satisfies the criteria under § 60.2635(b). (b) Qualification is valid from the date on which the training course is completed and the operator successfully passes the examination required under § 60.2635(c)(2). § 60.2650 How do I maintain my operator qualification? To maintain qualification, you must complete an annual review or refresher course covering, at a minimum, the five topics described in paragraphs (a) through (e) of this section: (a) Update of regulations; (b) Incinerator operation, including startup and shutdown procedures, waste charging, and ash handling; (c) Inspection and maintenance; (d) Prevention and correction of malfunctions or conditions that may lead to malfunction; and (e) Discussion of operating problems encountered by attendees. khammond on DSKBBV9HB2PROD with RULES3 § 60.2655 How do I renew my lapsed operator qualification? You must renew a lapsed operator qualification by one of the two methods specified in paragraphs (a) and (b) of this section: (a) For a lapse of less than 3 years, you must complete a standard annual refresher course described in § 60.2650; and (b) For a lapse of 3 years or more, you must repeat the initial qualification requirements in § 60.2645(a). VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 § 60.2660 What site-specific documentation is required? (a) Documentation must be available at the facility and readily accessible for all CISWI operators that addresses the ten topics described in paragraphs (a)(1) through (10) of this section. You must maintain this information and the training records required by paragraph (c) of this section in a manner that they can be readily accessed and are suitable for inspection upon request: (1) Summary of the applicable standards under this subpart; (2) Procedures for receiving, handling, and charging waste; (3) Incinerator startup, shutdown, and malfunction procedures; (4) Procedures for maintaining proper combustion air supply levels; (5) Procedures for operating the incinerator and associated air pollution control systems within the standards established under this subpart; (6) Monitoring procedures for demonstrating compliance with the incinerator operating limits; (7) Reporting and recordkeeping procedures; (8) The waste management plan required under §§ 60.2620 through 60.2630; (9) Procedures for handling ash; and (10) A list of the wastes burned during the performance test. (b) You must establish a program for reviewing the information listed in paragraph (a) of this section with each incinerator operator: (1) The initial review of the information listed in paragraph (a) of this section must be conducted by the later of the three dates specified in paragraphs (b)(1)(i) through (iii) of this section: (i) The final compliance date (Increment 2); (ii) Six months after CISWI startup; and (iii) Six months after being assigned to operate the CISWI. (2) Subsequent annual reviews of the information listed in paragraph (a) of this section must be conducted no later than 12 months following the previous review. (c) You must also maintain the information specified in paragraphs (c)(1) through (3) of this section: (1) Records showing the names of CISWI operators who have completed review of the information in § 60.2660(a) as required by § 60.2660(b), including the date of the initial review and all subsequent annual reviews; (2) Records showing the names of the CISWI operators who have completed the operator training requirements under § 60.2635, met the criteria for PO 00000 Frm 00045 Fmt 4701 Sfmt 4700 15889 qualification under § 60.2645, and maintained or renewed their qualification under § 60.2650 or § 60.2655. Records must include documentation of training, the dates of the initial refresher training, and the dates of their qualification and all subsequent renewals of such qualifications; and (3) For each qualified operator, the phone and/or pager number at which they can be reached during operating hours. § 60.2665 What if all the qualified operators are temporarily not accessible? If all qualified operators are temporarily not accessible (i.e., not at the facility and not able to be at the facility within 1 hour), you must meet one of the two criteria specified in paragraphs (a) and (b) of this section, depending on the length of time that a qualified operator is not accessible: (a) When all qualified operators are not accessible for more than 8 hours, but less than 2 weeks, the CISWI may be operated by other plant personnel familiar with the operation of the CISWI who have completed a review of the information specified in § 60.2660(a) within the past 12 months. However, you must record the period when all qualified operators were not accessible and include this deviation in the annual report as specified under § 60.2770; (b) When all qualified operators are not accessible for 2 weeks or more, you must take the two actions that are described in paragraphs (b)(1) and (2) of this section: (1) Notify the Administrator of this deviation in writing within 10 days. In the notice, state what caused this deviation, what you are doing to ensure that a qualified operator is accessible, and when you anticipate that a qualified operator will be accessible; and (2) Submit a status report to the Administrator every 4 weeks outlining what you are doing to ensure that a qualified operator is accessible, stating when you anticipate that a qualified operator will be accessible and requesting approval from the Administrator to continue operation of the CISWI. You must submit the first status report 4 weeks after you notify the Administrator of the deviation under paragraph (b)(1) of this section. If the Administrator notifies you that your request to continue operation of the CISWI is disapproved, the CISWI may continue operation for 90 days, then must cease operation. Operation of the unit may resume if you meet the two requirements in paragraphs (b)(2)(i) and (ii) of this section: E:\FR\FM\16APR3.SGM 16APR3 15890 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations (i) A qualified operator is accessible as required under § 60.2635(a); and (ii) You notify the Administrator that a qualified operator is accessible and that you are resuming operation. Model Rule—Emission Limitations and Operating Limits § 60.2670 What emission limitations must I meet and by when? (a) You must meet the emission limitations for each CISWI, including bypass stack or vent, specified in table 2 of this subpart or tables 6 through 9 of this subpart by the final compliance date under the approved state plan, federal plan, or delegation, as applicable. The emission limitations apply at all times the unit is operating including and not limited to startup, shutdown, or malfunction. (b) Units that do not use wet scrubbers must maintain opacity to less than or equal to the percent opacity (three 1-hour blocks consisting of ten 6minute average opacity values) specified in table 2 of this subpart, as applicable. khammond on DSKBBV9HB2PROD with RULES3 § 60.2675 What operating limits must I meet and by when? (a) If you use a wet scrubber(s) to comply with the emission limitations, you must establish operating limits for up to four operating parameters (as specified in table 3 of this subpart) as described in paragraphs (a)(1) through (4) of this section during the initial performance test: (1) Maximum charge rate, calculated using one of the two different procedures in paragraph (a)(1)(i) or (ii) of this section, as appropriate: (i) For continuous and intermittent units, maximum charge rate is 110 percent of the average charge rate measured during the most recent performance test demonstrating compliance with all applicable emission limitations; and (ii) For batch units, maximum charge rate is 110 percent of the daily charge rate measured during the most recent performance test demonstrating compliance with all applicable emission limitations. (2) Minimum pressure drop across the wet particulate matter scrubber, which is calculated as the lowest 1-hour average pressure drop across the wet scrubber measured during the most recent performance test demonstrating compliance with the particulate matter emission limitations; or minimum amperage to the wet scrubber, which is calculated as the lowest 1-hour average amperage to the wet scrubber measured during the most recent performance test demonstrating compliance with the particulate matter emission limitations. VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 (3) Minimum scrubber liquid flow rate, which is calculated as the lowest 1-hour average liquid flow rate at the inlet to the wet acid gas or particulate matter scrubber measured during the most recent performance test demonstrating compliance with all applicable emission limitations. (4) Minimum scrubber liquor pH, which is calculated as the lowest 1-hour average liquor pH at the inlet to the wet acid gas scrubber measured during the most recent performance test demonstrating compliance with the hydrogen chloride (HCl) emission limitation. (b) You must meet the operating limits established on the date that the performance test report is submitted to the EPA’s Central Data Exchange or postmarked, per the requirements of § 60.2795(b). (c) If you use a fabric filter to comply with the emission limitations and you do not use a particulate matter (PM) continuous parameter monitoring system (CPMS) for monitoring PM compliance, you must operate each fabric filter system such that the bag leak detection system alarm does not sound more than 5 percent of the operating time during a 6-month period. In calculating this operating time percentage, if inspection of the fabric filter demonstrates that no corrective action is required, no alarm time is counted. If corrective action is required, each alarm shall be counted as a minimum of 1 hour. If you take longer than 1 hour to initiate corrective action, the alarm time shall be counted as the actual amount of time taken by you to initiate corrective action. (d) If you use an electrostatic precipitator to comply with the emission limitations and you do not use a PM CPMS for monitoring PM compliance, you must measure the (secondary) voltage and amperage of the electrostatic precipitator collection plates during the particulate matter performance test. Calculate the average electric power value (secondary voltage × secondary current = secondary electric power) for each test run. The operating limit for the electrostatic precipitator is calculated as the lowest 1-hour average secondary electric power measured during the most recent performance test demonstrating compliance with the particulate matter emission limitations. (e) If you use activated carbon sorbent injection to comply with the emission limitations, you must measure the sorbent flow rate during the performance testing. The operating limit for the carbon sorbent injection is calculated as the lowest 1-hour average sorbent flow rate measured during the PO 00000 Frm 00046 Fmt 4701 Sfmt 4700 most recent performance test demonstrating compliance with the mercury emission limitations. For energy recovery units, when your unit operates at lower loads, multiply your sorbent injection rate by the load fraction, as defined in this subpart, to determine the required injection rate (e.g., for 50 percent load, multiply the injection rate operating limit by 0.5). (f) If you use selective noncatalytic reduction to comply with the emission limitations, you must measure the charge rate, the secondary chamber temperature (if applicable to your CISWI), and the reagent flow rate during the nitrogen oxides performance testing. The operating limits for the selective noncatalytic reduction are calculated as the highest 1-hour average charge rate, lowest secondary chamber temperature, and lowest reagent flow rate measured during the most recent performance test demonstrating compliance with the nitrogen oxides emission limitations. (g) If you use a dry scrubber to comply with the emission limitations, you must measure the injection rate of each sorbent during the performance testing. The operating limit for the injection rate of each sorbent is calculated as the lowest 1-hour average injection rate of each sorbent measured during the most recent performance test demonstrating compliance with the hydrogen chloride emission limitations. For energy recovery units, when your unit operates at lower loads, multiply your sorbent injection rate by the load fraction, as defined in this subpart, to determine the required injection rate (e.g., for 50 percent load, multiply the injection rate operating limit by 0.5). (h) If you do not use a wet scrubber, electrostatic precipitator, or fabric filter to comply with the emission limitations, and if you do not determine compliance with your particulate matter emission limitation with either a particulate matter CEMS or a particulate matter CPMS, you must maintain opacity to less than or equal to ten percent opacity (1-hour block average). (i) If you use a PM CPMS to demonstrate compliance, you must establish your PM CPMS operating limit and determine compliance with it according to paragraphs (i)(1) through (5) of this section: (1) During the initial performance test or any such subsequent performance test that demonstrates compliance with the PM limit, record all hourly average output values (milliamps, or the digital signal equivalent) from the PM CPMS for the periods corresponding to the test runs (e.g., three 1-hour average PM CPMS output values for three 1-hour test runs): E:\FR\FM\16APR3.SGM 16APR3 15891 (i) Your PM CPMS must provide a 4–20 milliamp output, or the digital signal equivalent, and the establishment of its relationship to manual reference method measurements must be determined in units of milliamps or digital bits; (ii) Your PM CPMS operating range must be capable of reading PM concentrations from zero to a level equivalent to at least two times your allowable emission limit. If your PM CPMS is an auto-ranging instrument capable of multiple scales, the primary range of the instrument must be capable of reading PM concentration from zero to a level equivalent to two times your allowable emission limit; and (iii) During the initial performance test or any such subsequent performance test that demonstrates compliance with the PM limit, record and average all milliamp output values, or their digital equivalent, from the PM CPMS for the periods corresponding to the compliance test runs (e.g., average all your PM CPMS output values for three corresponding 2-hour Method 5I test runs). (2) If the average of your three PM performance test runs are below 75 percent of your PM emission limit, you must calculate an operating limit by establishing a relationship of PM CPMS signal to PM concentration using the PM CPMS instrument zero, the average PM CPMS output values corresponding to the three compliance test runs, and the average PM concentration from the Method 5 or performance test with the procedures in (i)(1)through (5) of this section: (i) Determine your instrument zero output with one of the following procedures: (A) Zero point data for in-situ instruments should be obtained by removing the instrument from the stack and monitoring ambient air on a test bench; (B) Zero point data for extractive instruments should be obtained by removing the extractive probe from the stack and drawing in clean ambient air; (C) The zero point can also can be established obtained by performing manual reference method measurements when the flue gas is free of PM emissions or contains very low PM concentrations (e.g., when your process is not operating, but the fans are operating or your source is combusting only natural gas) and plotting these with the compliance data to find the zero intercept; and (D) If none of the steps in paragraphs (i)(2)(i)(A) through (C) of this section are possible, you must use a zero output value provided by the manufacturer. (ii) Determine your PM CPMS instrument average in milliamps, or the digital equivalent, and the average of your corresponding three PM compliance test runs, using equation 1: Where: X1 = the PM CPMS output data points for the three runs constituting the performance test, Y1 = the PM concentration value for the three runs constituting the performance test, and n = the number of data points. PM concentration from your three compliance tests, determine a relationship of mg/dscm per milliamp or digital signal equivalent, with equation 2: Where: R = the relative mg/dscm per milliamp, or the digital equivalent, for your PM CPMS, Y1 = the three run average mg/dscm PM concentration, X1 = the three run average milliamp output, or the digital equivalent, from you PM CPMS, and z = the milliamp or digital signal equivalent of your instrument zero determined from paragraph (i)(2)(i) of this section. Where: Ol = the operating limit for your PM CPMS on a 30-day rolling average, in milliamps or their digital signal equivalent, (iii) With your instrument zero expressed in milliamps, or the digital equivalent, your three run average PM CPMS milliamp value, or its digital equivalent, and your three run average VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 PO 00000 Frm 00047 Fmt 4701 Sfmt 4700 L = your source emission limit expressed in mg/dscm, E:\FR\FM\16APR3.SGM 16APR3 ER16AP19.014</GPH> ER16AP19.015</GPH> (iv) Determine your source specific 30-day rolling average operating limit using the mg/dscm per milliamp value, or per digital signal equivalent, from equation 2 in equation 3, below. This sets your operating limit at the PM CPMS output value corresponding to 75 percent of your emission limit: ER16AP19.013</GPH> khammond on DSKBBV9HB2PROD with RULES3 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations z = your instrument zero in milliamps or digital equivalent, determined from paragraph (i)(2)(i) of this section, and R = the relative mg/dscm per milliamp, or per digital signal output equivalent, for your PM CPMS, from equation 2. (3) If the average of your three PM compliance test runs is at or above 75 percent of your PM emission limit you must determine your operating limit by averaging the PM CPMS milliamp or digital signal output corresponding to your three PM performance test runs that demonstrate compliance with the emission limit using equation 4 and you must submit all compliance test and PM CPMS data according to the reporting requirements in paragraph (i)(5) of this section: Where: X1 = the PM CPMS data points for all runs i, n = the number of data points, and Oh = your site specific operating limit, in milliamps or digital signal equivalent. § 60.2680 What if I do not use a wet scrubber, fabric filter, activated carbon injection, selective noncatalytic reduction, an electrostatic precipitator, or a dry scrubber to comply with the emission limitations? these parameters, as well as the relative accuracy and precision of these methods and instruments; and (5) A discussion identifying the frequency and methods for recalibrating the instruments you will use for monitoring these parameters. (b) [Reserved] Where: Cadj = pollutant concentration adjusted to 7 percent oxygen; VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 (a) If you use an air pollution control device other than a wet scrubber, activated carbon injection, selective noncatalytic reduction, fabric filter, an electrostatic precipitator, or a dry scrubber or limit emissions in some other manner, including mass balances, to comply with the emission limitations under § 60.2670, you must petition the EPA Administrator for specific operating limits to be established during the initial performance test and continuously monitored thereafter. You must submit the petition at least sixty days before the performance test is scheduled to begin. Your petition must include the five items listed in paragraphs (a)(1) through (5) of this section: (1) Identification of the specific parameters you propose to use as additional operating limits; (2) A discussion of the relationship between these parameters and emissions of regulated pollutants, identifying how emissions of regulated pollutants change with changes in these parameters and how limits on these parameters will serve to limit emissions of regulated pollutants; (3) A discussion of how you will establish the upper and/or lower values for these parameters which will establish the operating limits on these parameters; (4) A discussion identifying the methods you will use to measure and the instruments you will use to monitor Cmeas = pollutant concentration measured on a dry basis; PO 00000 Frm 00048 Fmt 4701 Sfmt 4700 Model Rule—Performance Testing § 60.2690 How do I conduct the initial and annual performance test? (a) All performance tests must consist of a minimum of three test runs conducted under conditions representative of normal operations. (b) You must document that the waste burned during the performance test is representative of the waste burned under normal operating conditions by maintaining a log of the quantity of waste burned (as required in § 60.2740(b)(1)) and the types of waste burned during the performance test. (c) All performance tests must be conducted using the minimum run duration specified in tables 2 and 6 through 9 of this subpart. (d) Method 1 of appendix A of this part must be used to select the sampling location and number of traverse points. (e) Method 3A or 3B of appendix A of this part must be used for gas composition analysis, including measurement of oxygen concentration. Method 3A or 3B of appendix A of this part must be used simultaneously with each method (except when using Method 9 and Method 22). (f) All pollutant concentrations, except for opacity, must be adjusted to 7 percent oxygen using equation 5 of this section: (20.9¥7) = 20.9 percent oxygen¥7 percent oxygen (defined oxygen correction basis); E:\FR\FM\16APR3.SGM 16APR3 ER16AP19.017</GPH> khammond on DSKBBV9HB2PROD with RULES3 (4) To determine continuous compliance, you must record the PM CPMS output data for all periods when the process is operating and the PM CPMS is not out-of-control. You must demonstrate continuous compliance by using all quality-assured hourly average data collected by the PM CPMS for all operating hours to calculate the arithmetic average operating parameter in units of the operating limit (e.g., milliamps or digital signal bits, PM concentration, raw data signal) on a 30day rolling average basis. (5) For PM performance test reports used to set a PM CPMS operating limit, the electronic submission of the test report must also include the make and model of the PM CPMS instrument, serial number of the instrument, analytical principle of the instrument (e.g., beta attenuation), span of the instruments primary analytical range, milliamp or digital signal value equivalent to the instrument zero output, technique by which this zero value was determined, and the average milliamp or digital signals corresponding to each PM compliance test run. ER16AP19.016</GPH> 15892 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations khammond on DSKBBV9HB2PROD with RULES3 20.9 = oxygen concentration in air, percent; and %O2 = oxygen concentration measured on a dry basis, percent. (g) You must determine dioxins/ furans toxic equivalency by following the procedures in paragraphs (g)(1) through (4) of this section: (1) Measure the concentration of each dioxin/furan tetra- through octa-isomer emitted using EPA Method 23 at 40 CFR part 60, appendix A; (2) Quantify isomers meeting identification criteria 2, 3, 4, and 5 in Section 5.3.2.5 of Method 23, regardless of whether the isomers meet identification criteria 1 and 7. You must quantify the isomers per Section 9.0 of Method 23. [Note: You may reanalyze the sample aliquot or split to reduce the number of isomers not meeting identification criteria 1 or 7 of Section 5.3.2.5.]; (3) For each dioxin/furan (tetrathrough octa-chlorinated) isomer measured in accordance with paragraph (g)(1) and (2) of this section, multiply the isomer concentration by its corresponding toxic equivalency factor specified in table 4 of this subpart; and (4) Sum the products calculated in accordance with paragraph (g)(3) of this section to obtain the total concentration of dioxins/furans emitted in terms of toxic equivalency. (h) Method 22 at 40 CFR part 60, appendix A–7 must be used to determine compliance with the fugitive ash emission limit in table 2 of this subpart or tables 6 through 9 of this subpart. (i) If you have an applicable opacity operating limit, you must determine compliance with the opacity limit using Method 9 at 40 CFR part 60, appendix A–4, based on three 1-hour blocks consisting of ten 6-minute average opacity values, unless you are required to install a continuous opacity monitoring system, consistent with § 60.2710 and § 60.2730. (j) You must determine dioxins/furans total mass basis by following the procedures in paragraphs (j)(1) through (3) of this section: (1) Measure the concentration of each dioxin/furan tetra- through octachlorinated isomer emitted using EPA Method 23 at 40 CFR part 60, appendix A–7; (2) Quantify isomers meeting identification criteria 2, 3, 4, and 5 in Section 5.3.2.5 of Method 23, regardless of whether the isomers meet identification criteria 1 and 7. You must quantify the isomers per Section 9.0 of Method 23. (Note: You may reanalyze the sample aliquot or split to reduce the number of isomers not meeting VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 identification criteria 1 or 7 of Section 5.3.2.5.); and (3) Sum the quantities measured in accordance with paragraphs (j)(1) and (2) of this section to obtain the total concentration of dioxins/furans emitted in terms of total mass basis. § 60.2695 How are the performance test data used? You use results of performance tests to demonstrate compliance with the emission limitations in table 2 of this subpart or tables 6 through 9 of this subpart. Model Rule—Initial Compliance Requirements § 60.2700 How do I demonstrate initial compliance with the amended emission limitations and establish the operating limits? (a) You must conduct a performance test, as required under §§ 60.2670 and 60.2690, to determine compliance with the emission limitations in table 2 of this subpart and tables 6 through 9 of this subpart, to establish compliance with any opacity operating limits in § 60.2675, to establish the kiln-specific emission limit in § 60.2710(y), as applicable, and to establish operating limits using the procedures in § 60.2675 or § 60.2680. The performance test must be conducted using the test methods listed in table 2 of this subpart and tables 6 through 9 of this subpart and the procedures in § 60.2690. The use of the bypass stack during a performance test shall invalidate the performance test. (b) As an alternative to conducting a performance test, as required under §§ 60.2690 and 60.2670, you may use a 30-day rolling average of the 1-hour arithmetic average CEMS data, including CEMS data during startup and shutdown as defined in this subpart, to determine compliance with the emission limitations in Table 1 of this subpart or Tables 5 through 8 of this subpart. You must conduct a performance evaluation of each continuous monitoring system within 180 days of installation of the monitoring system. The initial performance evaluation must be conducted prior to collecting CEMS data that will be used for the initial compliance demonstration. § 60.2705 By what date must I conduct the initial performance test? (a) The initial performance test must be conducted no later than 180 days after your final compliance date. Your final compliance date is specified in table 1 of this subpart. PO 00000 Frm 00049 Fmt 4701 Sfmt 4700 15893 (b) If you commence or recommence combusting a solid waste at an existing combustion unit at any commercial or industrial facility and you conducted a test consistent with the provisions of this subpart while combusting the given solid waste within the 6 months preceding the reintroduction of that solid waste in the combustion chamber, you do not need to retest until 6 months from the date you reintroduce that solid waste. (c) If you commence or recommence combusting a solid waste at an existing combustion unit at any commercial or industrial facility and you have not conducted a performance test consistent with the provisions of this subpart while combusting the given solid waste within the 6 months preceding the reintroduction of that solid waste in the combustion chamber, you must conduct a performance test within 60 days from the date you reintroduce solid waste. § 60.2706 By what date must I conduct the initial air pollution control device inspection? (a) The initial air pollution control device inspection must be conducted within 60 days after installation of the control device and the associated CISWI reaches the charge rate at which it will operate, but no later than 180 days after the final compliance date for meeting the amended emission limitations. (b) Within 10 operating days following an air pollution control device inspection, all necessary repairs must be completed unless the owner or operator obtains written approval from the state agency establishing a date whereby all necessary repairs of the designated facility must be completed. Model Rule—Continuous Compliance Requirements § 60.2710 How do I demonstrate continuous compliance with the amended emission limitations and the operating limits? (a) General compliance with standards, considering some units may be able to switch between solid waste and non-waste fuel combustion, is specified in paragraph (a)(1) through (6) of this section. (1) The emission standards and operating requirements set forth in this subpart apply at all times. (2) If you cease combusting solid waste you may opt to remain subject to the provisions of this subpart. Consistent with the definition of CISWI, you are subject to the requirements of this subpart at least 6 months following the last date of solid waste combustion. Solid waste combustion is ceased when solid waste is not in the combustion E:\FR\FM\16APR3.SGM 16APR3 khammond on DSKBBV9HB2PROD with RULES3 15894 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations chamber (i.e., the solid waste feed to the combustor has been cut off for a period of time not less than the solid waste residence time). (3) If you cease combusting solid waste you must be in compliance with any newly applicable standards on the effective date of the waste-to-fuel switch. The effective date of the wasteto-fuel switch is a date selected by you, that must be at least 6 months from the date that you ceased combusting solid waste, consistent with § 60.2710(a)(2). Your source must remain in compliance with this subpart until the effective date of the waste-to-fuel switch. (4) If you own or operate an existing commercial or industrial combustion unit that combusted a fuel or non-waste material, and you commence or recommence combustion of solid waste, you are subject to the provisions of this subpart as of the first day you introduce or reintroduce solid waste to the combustion chamber, and this date constitutes the effective date of the fuelto-waste switch. You must complete all initial compliance demonstrations for any Section 112 standards that are applicable to your facility before you commence or recommence combustion of solid waste. You must provide 30 days prior notice of the effective date of the waste-to-fuel switch. The notification must identify: (i) The name of the owner or operator of the CISWI, the location of the source, the emissions unit(s) that will cease burning solid waste, and the date of the notice; (ii) The currently applicable subcategory under this subpart, and any 40 CFR part 63 subpart and subcategory that will be applicable after you cease combusting solid waste; (iii) The fuel(s), non-waste material(s) and solid waste(s) the CISWI is currently combusting and has combusted over the past 6 months, and the fuel(s) or non-waste materials the unit will commence combusting; (iv) The date on which you became subject to the currently applicable emission limits; (v) The date upon which you will cease combusting solid waste, and the date (if different) that you intend for any new requirements to become applicable (i.e., the effective date of the waste-tofuel switch), consistent with paragraphs (a)(2) and (3) of this section. (5) All air pollution control equipment necessary for compliance with any newly applicable emissions limits which apply as a result of the cessation or commencement or recommencement of combusting solid waste must be installed and operational VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 as of the effective date of the waste-tofuel, or fuel-to-waste switch. (6) All monitoring systems necessary for compliance with any newly applicable monitoring requirements which apply as a result of the cessation or commencement or recommencement of combusting solid waste must be installed and operational as of the effective date of the waste-to-fuel, or fuel-to-waste switch. All calibration and drift checks must be performed as of the effective date of the waste-to-fuel, or fuel-to-waste switch. Relative accuracy tests must be performed as of the performance test deadline for PM CEMS (if PM CEMS are elected to demonstrate continuous compliance with the particulate matter emission limits). Relative accuracy testing for other CEMS need not be repeated if that testing was previously performed consistent with section 112 monitoring requirements or monitoring requirements under this subpart. (b) You must conduct an annual performance test for the pollutants listed in table 2 of this subpart or tables 6 through 9 of this subpart and opacity for each CISWI as required under § 60.2690. The annual performance test must be conducted using the test methods listed in table 2 of this subpart or tables 6 through 9 of this subpart and the procedures in § 60.2690. Opacity must be measured using EPA Reference Method 9 at 40 CFR part 60. Annual performance tests are not required if you use CEMS or continuous opacity monitoring systems to determine compliance. (c) You must continuously monitor the operating parameters specified in § 60.2675 or established under § 60.2680 and as specified in § 60.2735. Operation above the established maximum or below the established minimum operating limits constitutes a deviation from the established operating limits. Three-hour block average values are used to determine compliance (except for baghouse leak detection system alarms) unless a different averaging period is established under § 60.2680 or, for energy recovery units, where the averaging time for each operating parameter is a 30-day rolling, calculated each hour as the average of the previous 720 operating hours. Operation above the established maximum, below the established minimum, or outside the allowable range of the operating limits specified in paragraph (a) of this section constitutes a deviation from your operating limits established under this subpart, except during performance tests conducted to determine compliance with the emission and operating limits or to establish new PO 00000 Frm 00050 Fmt 4701 Sfmt 4700 operating limits. Operating limits are confirmed or reestablished during performance tests. (d) You must burn only the same types of waste and fuels used to establish subcategory applicability (for ERUs) and operating limits during the performance test. (e) For energy recovery units, incinerators, and small remote units, you must perform annual visual emissions test for ash handling. (f) For energy recovery units, you must conduct an annual performance test for opacity using EPA Reference Method 9 at 40 CFR part 60 (except where particulate matter continuous monitoring system or CPMS are used) and the pollutants listed in table 7 of this subpart. (g) For facilities using a CEMS to demonstrate compliance with the carbon monoxide emission limit, compliance with the carbon monoxide emission limit may be demonstrated by using the CEMS, as described in § 60.2730(o). (h) Coal and liquid/gas energy recovery units with annual average heat input rates greater than 250 MMBtu/hr may elect to demonstrate continuous compliance with the particulate matter emissions limit using a particulate matter CEMS according to the procedures in § 60.2730(n) instead of the CPMS specified in § 60.2710(i). Coal and liquid/gas energy recovery units with annual average heat input rates less than 250 MMBtu/hr, incinerators, and small remote incinerators may also elect to demonstrate compliance using a particulate matter CEMS according to the procedures in § 60.2730(n) instead of particulate matter testing with EPA Method 5 at 40 CFR part 60, appendix A–3 and, if applicable, the continuous opacity monitoring requirements in paragraph (i) of this section. (i) For energy recovery units with annual average heat input rates greater than or equal to 10 MMBtu/hr but less than 250 MMBtu/hr that do not use a wet scrubber, fabric filter with bag leak detection system, an electrostatic precipitator, particulate matter CEMS, or particulate matter CPMS, you must install, operate, certify and maintain a continuous opacity monitoring system (COMS) according to the procedures in § 60.2730(m). (j) For waste-burning kilns, you must conduct an annual performance test for the pollutants (except mercury and particulate matter, and hydrogen chloride if no acid gas wet scrubber or dry scrubber is used) listed in table 8 of this subpart, unless you choose to demonstrate initial and continuous compliance using CEMS, as allowed in E:\FR\FM\16APR3.SGM 16APR3 15895 paragraph (u) of this section. If you do not use an acid gas wet scrubber or dry scrubber, you must determine compliance with the hydrogen chloride emissions limit using a HCl CEMS according to the requirements in paragraph (j)(1) of this section. You must determine compliance with the mercury emissions limit using a mercury CEMS or an integrated sorbent trap monitoring system according to paragraph (j)(2) of this section. You must determine compliance with particulate matter using CPMS. (1) If you monitor compliance with the HCl emissions limit by operating an HCl CEMS, you must do so in accordance with Performance Specification 15 (PS 15) of appendix B to 40 CFR part 60, or, PS 18 of appendix B to 40 CFR part 60. You must operate, maintain, and quality assure a HCl CEMS installed and certified under PS 15 according to the quality assurance requirements in Procedure 1 of appendix F to 40 CFR part 60 except that the Relative Accuracy Test Audit requirements of Procedure 1 must be replaced with the validation requirements and criteria of sections 11.1.1 and 12.0 of PS 15. You must operate, maintain and quality assure a HCl CEMS installed and certified under PS 18 according to the quality assurance requirements in Procedure 6 of appendix F to 40 CFR part 60. For any performance specification that you use, you must use Method 321 of appendix A to 40 CFR part 63 as the reference test method for conducting relative accuracy testing. The span value and calibration requirements in paragraphs (j)(1)(i) and (ii) of this section apply to all HCl CEMS used under this subpart: (i) You must use a measurement span value for any HCl CEMS of 0–10 ppmvw unless the monitor is installed on a kiln without an inline raw mill. Kilns without an inline raw mill may use a higher span value sufficient to quantify all expected emissions concentrations. The HCl CEMS data recorder output range must include the full range of expected HCl concentration values which would include those expected during ‘‘mill off’’ conditions. The corresponding data recorder range shall be documented in the site-specific monitoring plan and associated records; and (ii) In order to quality assure data measured above the span value, you must use one of the three options in paragraphs (j)(1)(ii)(A) through (C) of this section: (A) Include a second span that encompasses the HCl emission concentrations expected to be encountered during ‘‘mill off’’ conditions. This second span may be rounded to a multiple of 5 ppm of total HCl. The requirements of the appropriate HCl monitor performance specification shall be followed for this second span with the exception that a RATA with the mill off is not required; (B) Quality assure any data above the span value by proving instrument linearity beyond the span value established in paragraph (j)(1)(i) of this section using the following procedure. Conduct a weekly ‘‘above span linearity’’ calibration challenge of the monitoring system using a reference gas with a certified value greater than your highest expected hourly concentration or greater than 75% of the highest measured hourly concentration. The ‘‘above span’’ reference gas must meet the requirements of the applicable performance specification and must be introduced to the measurement system at the probe. Record and report the results of this procedure as you would for a daily calibration. The ‘‘above span linearity’’ challenge is successful if the value measured by the HCl CEMS falls within 10 percent of the certified value of the reference gas. If the value measured by the HCl CEMS during the above span linearity challenge exceeds 10 percent of the certified value of the reference gas, the monitoring system must be evaluated and repaired and a new ‘‘above span linearity’’ challenge met before returning the HCl CEMS to service, or data above span from the HCl CEMS must be subject to the quality assurance procedures established in (j)(1)(ii)(D) of this section. In this manner values measured by the HCl CEMS during the above span linearity challenge exceeding +/-20 percent of the certified value of the reference gas must be normalized using equation 6; (C) Quality assure any data above the span value established in paragraph (j)(1)(i) of this section using the following procedure. Any time two consecutive one-hour average measured concentration of HCl exceeds the span value you must, within 24 hours before or after, introduce a higher, ‘‘above span’’ HCl reference gas standard to the HCl CEMS. The ‘‘above span’’ reference gas must meet the requirements of the applicable performance specification and target a concentration level between 50 and 150 percent of the highest expected hourly concentration measured during the period of measurements above span, and must be introduced at the probe. While this target represents a desired concentration range that is not always achievable in practice, it is expected that the intent to meet this range is demonstrated by the value of the reference gas. Expected values may include above span calibrations done before or after the above-span measurement period. Record and report the results of this procedure as you would for a daily calibration. The ‘‘above span’’ calibration is successful if the value measured by the HCl CEMS is within 20 percent of the certified value of the reference gas. If the value measured by the HCl CEMS is not within 20 percent of the certified value of the reference gas, then you must normalize the stack gas values measured above span as described in paragraph (j)(1)(ii)(D) of this section. If the ‘‘above span’’ calibration is conducted during the period when measured emissions are above span and there is a failure to collect the one data point in an hour due to the calibration duration, then you must determine the emissions average for that missed hour as the average of hourly averages for the hour preceding the missed hour and the hour following the missed hour. In an hour where an ‘‘above span’’ calibration is being conducted and one or more data points are collected, the emissions average is represented by the average of all valid data points collected in that hour; and (D) In the event that the ‘‘above span’’ calibration is not successful (i.e., the HCl CEMS measured value is not within 20 percent of the certified value of the reference gas), then you must normalize the one-hour average stack gas values measured above the span during the 24hour period preceding or following the ‘‘above span’’ calibration for reporting based on the HCl CEMS response to the reference gas as shown in equation 6: Only one ‘‘above span’’ calibration is needed per 24-hour period. (2) Compliance with the mercury emissions limit must be determined using a mercury CEMS or integrated sorbent trap monitoring system according to the following requirements: VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 PO 00000 Frm 00051 Fmt 4701 Sfmt 4700 E:\FR\FM\16APR3.SGM 16APR3 ER16AP19.018</GPH> khammond on DSKBBV9HB2PROD with RULES3 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations khammond on DSKBBV9HB2PROD with RULES3 15896 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations (i) You must operate a mercury CEMS in accordance with performance specification 12A at 40 CFR part 60, appendix B or an integrated sorbent trap monitoring system in accordance with performance specification 12B at 40 CFR part 60, appendix B; these monitoring systems must be quality assured according to procedure 5 of 40 CFR 60, appendix F. For the purposes of emissions calculations when using an integrated sorbent trap monitoring system, the mercury concentration determined for each sampling period must be assigned to each hour during the sampling period. If you choose to comply with the production-rate based mercury limit for your waste-burning kiln, you must also monitor hourly clinker production and determine the hourly mercury emissions rate in pounds per million ton of clinker produced. You must demonstrate compliance with the mercury emissions limit using a 30-day rolling average of these 1-hour mercury concentrations or mass emissions rates, including CEMS data during startup and shutdown as defined in this subpart, calculated using equation 19–19 in section 12.4.1 of EPA Reference Method 19 at 40 CFR part 60, appendix A–7 of this part. CEMS data during startup and shutdown, as defined in this subpart, are not corrected to 7 percent oxygen, and are measured at stack oxygen content; (ii) Owners or operators using a mercury CEMS or integrated sorbent trap monitoring system to determine mass emission rate must install, operate, calibrate and maintain an instrument for continuously measuring and recording the mercury mass emissions rate to the atmosphere according to the requirements of performance specification 6 at 40 CFR part 60, appendix B and conducting an annual relative accuracy test of the continuous emission rate monitoring system according to section 8.2 of performance specification 6; and (iii) The owner or operator of a wasteburning kiln must demonstrate initial compliance by operating a mercury CEMS or integrated sorbent trap monitoring system while the raw mill of the in-line kiln/raw mill is operating under normal conditions and including at least one period when the raw mill is off. (k) If you use an air pollution control device to meet the emission limitations in this subpart, you must conduct an initial and annual inspection of the air pollution control device. The inspection must include, at a minimum, the following: (1) Inspect air pollution control device(s) for proper operation; and VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 (2) Develop a site-specific monitoring plan according to the requirements in paragraph (l) of this section. This requirement also applies to you if you petition the EPA Administrator for alternative monitoring parameters under § 60.13(i). (l) For each CMS required in this section, you must develop and submit to the EPA Administrator for approval a site-specific monitoring plan according to the requirements of this paragraph (l) that addresses paragraphs (l)(1)(i) through (vi) of this section: (1) You must submit this site-specific monitoring plan at least 60 days before your initial performance evaluation of your continuous monitoring system: (i) Installation of the continuous monitoring system sampling probe or other interface at a measurement location relative to each affected process unit such that the measurement is representative of control of the exhaust emissions (e.g., on or downstream of the last control device); (ii) Performance and equipment specifications for the sample interface, the pollutant concentration or parametric signal analyzer and the data collection and reduction systems; (iii) Performance evaluation procedures and acceptance criteria (e.g., calibrations); (iv) Ongoing operation and maintenance procedures in accordance with the general requirements of § 60.11(d); (v) Ongoing data quality assurance procedures in accordance with the general requirements of § 60.13; and (vi) Ongoing recordkeeping and reporting procedures in accordance with the general requirements of § 60.7(b), (c) introductory text, (c)(1) and (4), and (d) through (g). (2) You must conduct a performance evaluation of each continuous monitoring system in accordance with your site-specific monitoring plan. (3) You must operate and maintain the continuous monitoring system in continuous operation according to the site-specific monitoring plan. (m) If you have an operating limit that requires the use of a flow monitoring system, you must meet the requirements in paragraphs (l) and (m)(1) through (4) of this section: (1) Install the flow sensor and other necessary equipment in a position that provides a representative flow; (2) Use a flow sensor with a measurement sensitivity at full scale of no greater than 2 percent; (3) Minimize the effects of swirling flow or abnormal velocity distributions due to upstream and downstream disturbances; and PO 00000 Frm 00052 Fmt 4701 Sfmt 4700 (4) Conduct a flow monitoring system performance evaluation in accordance with your monitoring plan at the time of each performance test but no less frequently than annually. (n) If you have an operating limit that requires the use of a pressure monitoring system, you must meet the requirements in paragraphs (l) and (n)(1) through (6) of this section: (1) Install the pressure sensor(s) in a position that provides a representative measurement of the pressure (e.g., PM scrubber pressure drop); (2) Minimize or eliminate pulsating pressure, vibration, and internal and external corrosion; (3) Use a pressure sensor with a minimum tolerance of 1.27 centimeters of water or a minimum tolerance of 1 percent of the pressure monitoring system operating range, whichever is less; (4) Perform checks at the frequency outlined in your site-specific monitoring plan to ensure pressure measurements are not obstructed (e.g., check for pressure tap plugging daily); (5) Conduct a performance evaluation of the pressure monitoring system in accordance with your monitoring plan at the time of each performance test but no less frequently than annually; and (6) If at any time the measured pressure exceeds the manufacturer’s specified maximum operating pressure range, conduct a performance evaluation of the pressure monitoring system in accordance with your monitoring plan and confirm that the pressure monitoring system continues to meet the performance requirements in your monitoring plan. Alternatively, install and verify the operation of a new pressure sensor. (o) If you have an operating limit that requires a pH monitoring system, you must meet the requirements in paragraphs (l) and (o)(1) through (4) of this section: (1) Install the pH sensor in a position that provides a representative measurement of scrubber effluent pH; (2) Ensure the sample is properly mixed and representative of the fluid to be measured; (3) Conduct a performance evaluation of the pH monitoring system in accordance with your monitoring plan at least once each process operating day; and (4) Conduct a performance evaluation (including a two-point calibration with one of the two buffer solutions having a pH within 1 of the pH of the operating limit) of the pH monitoring system in accordance with your monitoring plan at the time of each performance test but no less frequently than quarterly. E:\FR\FM\16APR3.SGM 16APR3 khammond on DSKBBV9HB2PROD with RULES3 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations (p) If you have an operating limit that requires a secondary electric power monitoring system for an electrostatic precipitator, you must meet the requirements in paragraphs (l) and (p)(1) and (2) of this section: (1) Install sensors to measure (secondary) voltage and current to the precipitator collection plates; and (2) Conduct a performance evaluation of the electric power monitoring system in accordance with your monitoring plan at the time of each performance test but no less frequently than annually. (q) If you have an operating limit that requires the use of a monitoring system to measure sorbent injection rate (e.g., weigh belt, weigh hopper, or hopper flow measurement device), you must meet the requirements in paragraphs (l) and (q)(1) and (2) of this section: (1) Install the system in a position(s) that provides a representative measurement of the total sorbent injection rate; and (2) Conduct a performance evaluation of the sorbent injection rate monitoring system in accordance with your monitoring plan at the time of each performance test but no less frequently than annually. (r) If you elect to use a fabric filter bag leak detection system to comply with the requirements of this subpart, you must install, calibrate, maintain, and continuously operate a bag leak detection system as specified in paragraphs (l) and (r)(1) through (5) of this section: (1) Install a bag leak detection sensor(s) in a position(s) that will be representative of the relative or absolute particulate matter loadings for each exhaust stack, roof vent, or compartment (e.g., for a positive pressure fabric filter) of the fabric filter; (2) Use a bag leak detection system certified by the manufacturer to be capable of detecting particulate matter emissions at concentrations of 10 milligrams per actual cubic meter or less; (3) Conduct a performance evaluation of the bag leak detection system in accordance with your monitoring plan and consistent with the guidance provided in EPA–454/R–98–015 (incorporated by reference, see § 60.17); (4) Use a bag leak detection system equipped with a device to continuously record the output signal from the sensor; and (5) Use a bag leak detection system equipped with a system that will sound an alarm when an increase in relative particulate matter emissions over a preset level is detected. The alarm must VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 be located where it is observed readily by plant operating personnel. (s) For facilities using a CEMS to demonstrate initial and continuous compliance with the sulfur dioxide emission limit, compliance with the sulfur dioxide emission limit may be demonstrated by using the CEMS specified in § 60.2730(l) to measure sulfur dioxide. The sulfur dioxide CEMS must follow the procedures and methods specified in paragraph (s) of this section. For sources that have actual inlet emissions less than 100 parts per million dry volume, the relative accuracy criterion for inlet sulfur dioxide CEMS should be no greater than 20 percent of the mean value of the reference method test data in terms of the units of the emission standard, or 5 parts per million dry volume absolute value of the mean difference between the reference method and the CEMS, whichever is greater: (1) During each relative accuracy test run of the CEMS required by performance specification 2 in appendix B of this part, collect sulfur dioxide and oxygen (or carbon dioxide) data concurrently (or within a 30- to 60minute period) with both the CEMS and the test methods specified in paragraphs (s)(1)(i) and (ii) of this section: (i) For sulfur dioxide, EPA Reference Method 6 or 6C, or as an alternative ANSI/ASME PTC 19.10–1981 (incorporated by reference, see § 60.17) must be used; and (ii) For oxygen (or carbon dioxide), EPA Reference Method 3A or 3B, or as an alternative ANSI/ASME PTC 19.10– 1981 (incorporated by reference, see § 60.17), as applicable, must be used. (2) The span value of the CEMS at the inlet to the sulfur dioxide control device must be 125 percent of the maximum estimated hourly potential sulfur dioxide emissions of the unit subject to this subpart. The span value of the CEMS at the outlet of the sulfur dioxide control device must be 50 percent of the maximum estimated hourly potential sulfur dioxide emissions of the unit subject to this subpart. (3) Conduct accuracy determinations quarterly and calibration drift tests daily in accordance with procedure 1 in appendix F of this part. (t) For facilities using a CEMS to demonstrate initial and continuous compliance with the nitrogen oxides emission limit, compliance with the nitrogen oxides emission limit may be demonstrated by using the CEMS specified in § 60.2730 to measure nitrogen oxides. The nitrogen oxides CEMS must follow the procedures and methods specified in paragraphs (t)(1) through (4) of this section: PO 00000 Frm 00053 Fmt 4701 Sfmt 4700 15897 (1) During each relative accuracy test run of the CEMS required by performance specification 2 of appendix B of this part, collect nitrogen oxides and oxygen (or carbon dioxide) data concurrently (or within a 30- to 60minute period) with both the CEMS and the test methods specified in paragraphs (t)(1)(i) and (ii) of this section: (i) For nitrogen oxides, EPA Reference Method 7 or 7E at 40 CFR part 60, appendix A–4 must be used; and (ii) For oxygen (or carbon dioxide), EPA Reference Method 3A or 3B, or as an alternative ANSI/ASME PTC 19.10– 1981 (incorporated by reference, see § 60.17), as applicable, must be used. (2) The span value of the CEMS must be 125 percent of the maximum estimated hourly potential nitrogen oxide emissions of unit. (3) Conduct accuracy determinations quarterly and calibration drift tests daily in accordance with procedure 1 in appendix F of this part. (4) The owner or operator of an affected facility may request that compliance with the nitrogen oxides emission limit be determined using carbon dioxide measurements corrected to an equivalent of 7 percent oxygen. If carbon dioxide is selected for use in diluent corrections, the relationship between oxygen and carbon dioxide levels must be established during the initial performance test according to the procedures and methods specified in paragraphs (t)(4)(i) through (iv) of this section. This relationship may be reestablished during performance compliance tests: (i) The fuel factor equation in Method 3B must be used to determine the relationship between oxygen and carbon dioxide at a sampling location. Method 3A, 3B, or as an alternative ANSI/ASME PTC 19.10–1981 (incorporated by reference, see § 60.17), as applicable, must be used to determine the oxygen concentration at the same location as the carbon dioxide monitor; (ii) Samples must be taken for at least 30 minutes in each hour; (iii) Each sample must represent a 1hour average; and (iv) A minimum of 3 runs must be performed. (u) For facilities using a CEMS or an integrated sorbent trap monitoring system for mercury to demonstrate initial and continuous compliance with any of the emission limits of this subpart, you must complete the following: (1) Demonstrate compliance with the appropriate emission limit(s) using a 30day rolling average of 1-hour arithmetic average emission concentrations, including CEMS or an integrated E:\FR\FM\16APR3.SGM 16APR3 khammond on DSKBBV9HB2PROD with RULES3 15898 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations sorbent trap monitoring system data during startup and shutdown, as defined in this subpart, calculated using equation 19–19 in section 12.4.1 of EPA Reference Method 19 at appendix A–7 of this part. The 1-hour arithmetic averages for CEMS must be calculated using the data points required under § 60.13(e)(2). Except for CEMS or an integrated sorbent trap monitoring system data during startup and shutdown, the 1-hour arithmetic averages used to calculate the 30-day rolling average emission concentrations must be corrected to 7 percent oxygen (dry basis). Integrated sorbent trap monitoring system or CEMS data during startup and shutdown, as defined in this subpart, are not corrected to 7 percent oxygen, and are measured at stack oxygen content; and (2) Operate all CEMS and integrated sorbent trap monitoring systems in accordance with the applicable procedures under appendices B and F of this part. (v) Use of the bypass stack at any time is an emissions standards deviation for PM, HCl, lead, cadmium, mercury, nitrogen oxides, sulfur dioxide, and dioxin/furans. (w) For energy recovery units with a design heat input capacity of 100 MMBtu/hr or greater that do not use a carbon monoxide CEMS, you must install, operate, and maintain an oxygen analyzer system as defined in § 60.2875 according to the procedures in paragraphs (w)(1) through (4) of this section: (1) The oxygen analyzer system must be installed by the initial performance test date specified in § 60.2675; (2) You must operate the oxygen trim system within compliance with paragraph (w)(3) of this section at all times; (3) You must maintain the oxygen level such that the 30-day rolling average that is established as the operating limit for oxygen is not below the lowest hourly average oxygen concentration measured during the most recent CO performance test; and (4) You must calculate and record a 30-day rolling average oxygen concentration using equation 19–19 in section 12.4.1 of EPA Reference Method 19 of Appendix A–7 of this part. (x) For energy recovery units with annual average heat input rates greater than or equal to 250 MMBtu/hr and waste-burning kilns, you must install, calibrate, maintain, and operate a PM CPMS and record the output of the system as specified in paragraphs (x)(1) through (8) of this section. For other energy recovery units, you may elect to use PM CPMS operated in accordance VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 with this section. PM CPMS are suitable in lieu of using other CMS for monitoring PM compliance (e.g., bag leak detectors, ESP secondary power, PM scrubber pressure): (1) Install, calibrate, operate, and maintain your PM CPMS according to the procedures in your approved sitespecific monitoring plan developed in accordance with paragraphs (l) and (x)(1)(i) through (iii) of this section: (i) The operating principle of the PM CPMS must be based on in-stack or extractive light scatter, light scintillation, beta attenuation, or mass accumulation of the exhaust gas or representative sample. The reportable measurement output from the PM CPMS must be expressed as milliamps or the digital signal equivalent; (ii) The PM CPMS must have a cycle time (i.e., period required to complete sampling, measurement, and reporting for each measurement) no longer than 60 minutes; and (iii) The PM CPMS must be capable of detecting and responding to particulate matter concentrations increments no greater than 0.5 mg/actual cubic meter. (2) During the initial performance test or any such subsequent performance test that demonstrates compliance with the PM limit, you must adjust the sitespecific operating limit in accordance with the results of the performance test according to the procedures specified in § 60.2675. (3) Collect PM CPMS hourly average output data for all energy recovery unit or waste-burning kiln operating hours. Express the PM CPMS output as milliamps or the digital signal equivalent. (4) Calculate the arithmetic 30-day rolling average of all of the hourly average PM CPMS output collected during all energy recovery unit or wasteburning kiln operating hours data (milliamps or their digital equivalent). (5) You must collect data using the PM CPMS at all times the energy recovery unit or waste-burning kiln is operating and at the intervals specified in paragraph (x)(1)(ii) of this section, except for periods of monitoring system malfunctions, repairs associated with monitoring system malfunctions, required monitoring system quality assurance or quality control activities (including, as applicable, calibration checks and required zero and span adjustments), and any scheduled maintenance as defined in your sitespecific monitoring plan. (6) You must use all the data collected during all energy recovery unit or wasteburning kiln operating hours in assessing the compliance with your operating limit except: PO 00000 Frm 00054 Fmt 4701 Sfmt 4700 (i) Any data collected during monitoring system malfunctions, repairs associated with monitoring system malfunctions, or required monitoring system quality assurance or quality control activities conducted during monitoring system malfunctions are not used in calculations (report any such periods in your annual deviation report); (ii) Any data collected during periods when the monitoring system is out of control as specified in your site-specific monitoring plan, repairs associated with periods when the monitoring system is out of control, or required monitoring system quality assurance or quality control activities conducted during outof-control periods are not used in calculations (report emissions or operating levels and report any such periods in your annual deviation report); (iii) Any PM CPMS data recorded during periods of CEMS data during startup and shutdown, as defined in this subpart. (7) You must record and make available upon request results of PM CPMS system performance audits, as well as the dates and duration of periods from when the PM CPMS is out of control until completion of the corrective actions necessary to return the PM CPMS to operation consistent with your site-specific monitoring plan. (8) For any deviation of the 30-day rolling average PM CPMS average value from the established operating parameter limit, you must: (i) Within 48 hours of the deviation, visually inspect the air pollution control device; (ii) If inspection of the air pollution control device identifies the cause of the deviation, take corrective action as soon as possible and return the PM CPMS measurement to within the established value; (iii) Within 30 days of the deviation or at the time of the annual compliance test, whichever comes first, conduct a PM emissions compliance test to determine compliance with the PM emissions limit. Within 45 days of the deviation, you must re-establish the CPMS operating limit. You are not required to conduct additional testing for any deviations that occur between the time of the original deviation and the PM emissions compliance test required under paragraph (x) of this section; and (iv) PM CPMS deviations leading to more than four required performance tests in a 12-month process operating period (rolling monthly) constitute a violation of this subpart. E:\FR\FM\16APR3.SGM 16APR3 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations (y) When there is an alkali bypass and/or an in-line coal mill that exhaust emissions through a separate stack(s), the combined emissions are subject to the emission limits applicable to wasteburning kilns. To determine the kilnspecific emission limit for demonstrating compliance, you must: (1) Calculate a kiln-specific emission limit using equation 7: Where: Cks = Kiln stack concentration (ppmvd, mg/ dscm, ng/dscm, depending on pollutant. Each corrected to 7% O2.) Qab = Alkali bypass flow rate (volume/hr) Cab = Alkali bypass concentration (ppmvd, mg/dscm, ng/dscm, depending on pollutant. Each corrected to 7% O2.) Qcm = In-line coal mill flow rate (volume/hr) Ccm = In-line coal mill concentration (ppmvd, mg/dscm, ng/dscm, depending on pollutant. Each corrected to 7% O2.) Qks = Kiln stack flow rate (volume/hr) new values for the operating limits, as specified in § 60.2725. New operating limits become effective on the date that the performance test report is submitted to the EPA’s Central Data Exchange or postmarked, per the requirements of § 60.2795(b). The Administrator may request a repeat performance test at any time; (2) You must repeat the performance test within 60 days of a process change, as defined in § 60.2875; and (3) You can conduct performance tests less often if you meet the following conditions: Your performance tests for the pollutant for at least 2 consecutive performance tests demonstrates that the emission level for the pollutant is no greater than the emission level specified in paragraph (a)(3)(i) or (ii) of this section, as applicable; there are no changes in the operation of the affected source or air pollution control equipment that could increase emissions; and you are not required to conduct a performance test for the pollutant in response to a request by the Administrator in paragraph (a)(1) of this section or a process change in paragraph (a)(2) of this section. In this case, you do not have to conduct a performance test for that pollutant for the next 2 years. You must conduct a performance test for the pollutant no more than 37 months following the previous performance test for the pollutant. If the emission level for your CISWI continues to meet the emission level specified in paragraph (a)(3)(i) or (ii) of this section, as applicable, you may choose to conduct performance tests for the pollutant every third year, as long as there are no changes in the operation of the affected source or air pollution control equipment that could increase emissions. Each such performance test must be conducted no more than 37 months after the previous performance test. (i) For particulate matter, hydrogen chloride, mercury, carbon monoxide, nitrogen oxides, sulfur dioxide, cadmium, lead, and dioxins/furans, the emission level equal to 75 percent of the applicable emission limit in table 2 or tables 6 through 9 of this subpart, as applicable; and (ii) For fugitive emissions, visible emissions (of combustion ash from the ash conveying system) for 2 percent of the time during each of the three 1-hour observation periods. (4) If you are conducting less frequent testing for a pollutant as provided in paragraph (a)(3) of this section and a subsequent performance test for the pollutant indicates that your CISWI does not meet the emission level specified in paragraph (a)(3)(i) or (a)(3)(ii) of this section, as applicable, you must conduct annual performance tests for the pollutant according to the schedule specified in paragraph (a) of this section until you qualify for less frequent testing for the pollutant as specified in paragraph (a)(3) of this section. (b) [Reserved] § 60.2715 By what date must I conduct the annual performance test? You must conduct annual performance tests between 11 and 13 calendar months of the previous performance test. § 60.2716 By what date must I conduct the annual air pollution control device inspection? On an annual basis (no more than 12 months following the previous annual air pollution control device inspection), you must complete the air pollution control device inspection as described in § 60.2706. § 60.2720 May I conduct performance testing less often? (a) You must conduct annual performance tests according to the schedule specified in § 60.2715, with the following exceptions: (1) You may conduct a repeat performance test at any time to establish VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 PO 00000 Frm 00055 Fmt 4701 Sfmt 4700 § 60.2725 May I conduct a repeat performance test to establish new operating limits? (a) Yes. You may conduct a repeat performance test at any time to establish new values for the operating limits. The Administrator may request a repeat performance test at any time. (b) You must repeat the performance test if your feed stream is different than the feed streams used during any performance test used to demonstrate compliance. Model Rule—Monitoring § 60.2730 What monitoring equipment must I install and what parameters must I monitor? (a) If you are using a wet scrubber to comply with the emission limitation under § 60.2670, you must install, calibrate (to manufacturers’ specifications), maintain, and operate devices (or establish methods) for monitoring the value of the operating parameters used to determine compliance with the operating limits listed in table 3 of this subpart. These devices (or methods) must measure and record the values for these operating parameters at the frequencies indicated in table 3 of this subpart at all times except as specified in § 60.2735(a). (b) If you use a fabric filter to comply with the requirements of this subpart and you do not use a PM CPMS or PM CEMS for monitoring PM compliance, E:\FR\FM\16APR3.SGM 16APR3 ER16AP19.019</GPH> (2) Particulate matter concentration must be measured downstream of the in-line coal mill. All other pollutant concentrations must be measured either upstream or downstream of the in-line coal mill. (3) For purposes of determining the combined emissions from kilns equipped with an alkali bypass or that exhaust kiln gases to a coal mill that exhausts through a separate stack, instead of installing a CEMS or PM CPMS on the alkali bypass stack or inline coal mill stack, the results of the initial and subsequent performance test can be used to demonstrate compliance with the relevant emissions limit. A performance test must be conducted on an annual basis (between 11 and 13 calendar months following the previous performance test). khammond on DSKBBV9HB2PROD with RULES3 15899 khammond on DSKBBV9HB2PROD with RULES3 15900 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations you must install, calibrate, maintain, and continuously operate a bag leak detection system as specified in paragraphs (b)(1) through (8) of this section: (1) You must install and operate a bag leak detection system for each exhaust stack of the fabric filter; (2) Each bag leak detection system must be installed, operated, calibrated, and maintained in a manner consistent with the manufacturer’s written specifications and recommendations; (3) The bag leak detection system must be certified by the manufacturer to be capable of detecting particulate matter emissions at concentrations of 10 milligrams per actual cubic meter or less; (4) The bag leak detection system sensor must provide output of relative or absolute particulate matter loadings; (5) The bag leak detection system must be equipped with a device to continuously record the output signal from the sensor; (6) The bag leak detection system must be equipped with an alarm system that will alert automatically an operator when an increase in relative particulate matter emission over a preset level is detected. The alarm must be located where it is observed easily by plant operating personnel; (7) For positive pressure fabric filter systems, a bag leak detection system must be installed in each baghouse compartment or cell. For negative pressure or induced air fabric filters, the bag leak detector must be installed downstream of the fabric filter; and (8) Where multiple detectors are required, the system’s instrumentation and alarm may be shared among detectors. (c) If you are using something other than a wet scrubber, activated carbon, selective non-catalytic reduction, an electrostatic precipitator, or a dry scrubber to comply with the emission limitations under § 60.2670, you must install, calibrate (to the manufacturers’ specifications), maintain, and operate the equipment necessary to monitor compliance with the site-specific operating limits established using the procedures in § 60.2680. (d) If you use activated carbon injection to comply with the emission limitations in this subpart, you must measure the minimum sorbent flow rate once per hour. (e) If you use selective noncatalytic reduction to comply with the emission limitations, you must complete the following: (1) Following the date on which the initial performance test is completed or is required to be completed under VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 § 60.2690, whichever date comes first, ensure that the affected facility does not operate above the maximum charge rate, or below the minimum secondary chamber temperature (if applicable to your CISWI) or the minimum reagent flow rate measured as 3-hour block averages at all times; and (2) Operation of the affected facility above the maximum charge rate, below the minimum secondary chamber temperature and below the minimum reagent flow rate simultaneously constitute a violation of the nitrogen oxides emissions limit. (f) If you use an electrostatic precipitator to comply with the emission limits of this subpart and you do not use a PM CPMS for monitoring PM compliance, you must monitor the secondary power to the electrostatic precipitator collection plates and maintain the 3-hour block averages at or above the operating limits established during the mercury or particulate matter performance test. (g) For waste-burning kilns not equipped with a wet scrubber or dry scrubber, you must install, calibrate, maintain, and operate a CEMS for monitoring hydrogen chloride emissions discharged to the atmosphere, as specified in § 60.2710(j), and record the output of the system. You may substitute use of a HCl CEMS for conducting the HCl initial and annual testing with EPA Method 321 at 40 CFR part 63, appendix A. For units other than waste-burning kilns not equipped with a wet scrubber or dry scrubber, a facility may substitute use of a hydrogen chloride CEMS for conducting the hydrogen chloride initial and annual performance test. For units equipped with a hydrogen chloride CEMS, you are not required to monitor the minimum hydrogen chloride sorbent flow rate, monitoring the minimum scrubber liquor pH, and monitoring minimum injection rate. (h) To demonstrate continuous compliance with the particulate matter emissions limit, a facility may substitute use of either a particulate matter CEMS or a particulate matter CPMS for conducting the particulate matter annual performance test. For units equipped with a particulate matter CEMS, you are not required to use other CMS monitoring for PM compliance (e.g., bag leak detectors, ESP secondary power, PM scrubber pressure). A facility may also substitute use of a particulate matter CEMS for conducting the PM initial performance test. (i) To demonstrate initial and continuous compliance with the dioxin/ furan emissions limit, a facility may substitute use of a continuous PO 00000 Frm 00056 Fmt 4701 Sfmt 4700 automated sampling system for the dioxin/furan initial and annual performance test. You must record the output of the system and analyze the sample according to EPA Method 23 at 40 CFR part 60, appendix A–7. This option to use a continuous automated sampling system takes effect on the date a final performance specification applicable to dioxin/furan from continuous monitors is published in the Federal Register. The owner or operator who elects to continuously sample dioxin/furan emissions instead of sampling and testing using EPA Method 23 at 40 CFR part 60, appendix A–7 must install, calibrate, maintain and operate a continuous automated sampling system and must comply with the requirements specified in § 60.58b(p) and (q). A facility may substitute continuous dioxin/furan monitoring for the minimum sorbent flow rate, if activated carbon sorbent injection is used solely for compliance with the dioxin/furan emission limit. (j) To demonstrate initial and continuous compliance with the mercury emissions limit, a facility may substitute use of a mercury CEMS or and integrated sorbent trap monitoring system for the mercury initial and annual performance test. The owner or operator who elects to continuously measure mercury emissions instead of sampling and testing using EPA Method 29 or 30B at 40 CFR part 60, appendix A–8, ASTM D6784–02 (Reapproved 2008) (incorporated by reference, see § 60.17), or an approved alternative method for measuring mercury emissions, must install, calibrate, maintain and operate the mercury CEMS or integrated sorbent trap monitoringsystem and must comply with performance specification 12A or performance specification 12B, respectively, and quality assurance procedure 5. For the purposes of emissions calculations when using an integrated sorbent trap monitoring system, the mercury concentration determined for each sampling period must be assigned to each hour during the sampling period. For units equipped with a mercury CEMS or an integrated sorbent trap monitoring system, you are not required to monitor the minimum sorbent flow rate, if activated carbon sorbent injection is used solely for compliance with the mercury emission limit. Waste-burning kilns must install, calibrate, maintain, and operate a mercury CEMS or an integrated sorbent trap monitoring system as specified in § 60.2710(j). (k) To demonstrate initial and continuous compliance with the nitrogen oxides emissions limit, a E:\FR\FM\16APR3.SGM 16APR3 khammond on DSKBBV9HB2PROD with RULES3 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations facility may substitute use of a CEMS for the nitrogen oxides initial and annual performance test to demonstrate compliance with the nitrogen oxides emissions limits. For units equipped with a nitrogen xides CEMS, you are not required to monitor the charge rate, secondary chamber temperature and reagent flow for selective noncatalytic reduction, if applicable: (1) Install, calibrate, maintain and operate a CEMS for measuring nitrogen oxides emissions discharged to the atmosphere and record the output of the system. The requirements under performance specification 2 of appendix B of this part, the quality assurance procedure 1 of appendix F of this part and the procedures under § 60.13 must be followed for installation, evaluation and operation of the CEMS; and (2) Compliance with the emission limit for nitrogen oxides must be determined based on the 30-day rolling average of the hourly emission concentrations using CEMS outlet data, as outlined in § 60.2710(u). (l) To demonstrate initial and continuous compliance with the sulfur dioxide emissions limit, a facility may substitute use of a CEMS for the sulfur dioxide initial and annual performance test to demonstrate compliance with the sulfur dioxide emissions limits: (1) Install, calibrate, maintain and operate a CEMS for measuring sulfur dioxide emissions discharged to the atmosphere and record the output of the system. The requirements under performance specification 2 of appendix B of this part, the quality assurance requirements of procedure 1 of appendix F of this part and the procedures under § 60.13 must be followed for installation, evaluation and operation of the CEMS; and (2) Compliance with the sulfur dioxide emission limit shall be determined based on the 30-day rolling average of the hourly arithmetic average emission concentrations using CEMS outlet data, as outlined in § 60.2710(u). (m) For energy recovery units over 10 MMBtu/hr but less than 250 MMBtu/hr annual average heat input rates that do not use a wet scrubber, fabric filter with bag leak detection system, an electrostatic precipitator, particulate matter CEMS, or particulate matter CPMS, you must install, operate, certify and maintain a continuous opacity monitoring system according to the procedures in paragraphs (m)(1) through (5) of this section by the compliance date specified in § 60.2670. Energy recovery units that use a particulate matter CEMS to demonstrate initial and continuing compliance according to the procedures in § 60.2730(n) are not VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 required to install a continuous opacity monitoring system and must perform the annual performance tests for opacity consistent with § 60.2710(f): (1) Install, operate and maintain each continuous opacity monitoring system according to performance specification 1 at 40 CFR part 60, appendix B; (2) Conduct a performance evaluation of each continuous opacity monitoring system according to the requirements in § 60.13 and according to performance specification 1 at 40 CFR part 60, appendix B; (3) As specified in § 60.13(e)(1), each continuous opacity monitoring system must complete a minimum of one cycle of sampling and analyzing for each successive 10-second period and one cycle of data recording for each successive 6-minute period; (4) Reduce the continuous opacity monitoring system data as specified in § 60.13(h)(1); and (5) Determine and record all the 6minute averages (and 1-hour block averages as applicable) collected. (n) For coal and liquid/gas energy recovery units, incinerators, and small remote incinerators, an owner or operator may elect to install, calibrate, maintain and operate a CEMS for monitoring particulate matter emissions discharged to the atmosphere and record the output of the system. The owner or operator of an affected facility who continuously monitors particulate matter emissions instead of conducting performance testing using EPA Method 5 at 40 CFR part 60, appendix A–3 or monitoring with a particulate matter CPMS according to paragraph (r) of this section, must install, calibrate, maintain and operate a PM CEMS and must comply with the requirements specified in paragraphs (n)(1) through (10) of this section: (1) The PM CEMS must be installed, evaluated and operated in accordance with the requirements of performance specification 11 of appendix B of this part and quality assurance requirements of procedure 2 of appendix F of this part and § 60.13; (2) The initial performance evaluation must be completed no later than 180 days after the final compliance date for meeting the amended emission limitations, as specified under § 60.2690 or within 180 days of notification to the Administrator of use of the continuous monitoring system if the owner or operator was previously determining compliance by Method 5 at 40 CFR part 60, appendix A–3 performance tests, whichever is later; (3) The owner or operator of an affected facility may request that compliance with the particulate matter PO 00000 Frm 00057 Fmt 4701 Sfmt 4700 15901 emission limit be determined using carbon dioxide measurements corrected to an equivalent of 7 percent oxygen. The relationship between oxygen and carbon dioxide levels for the affected facility must be established according to the procedures and methods specified in § 60.2710(t)(4)(i) through (iv); (4) The owner or operator of an affected facility must conduct an initial performance test for particulate matter emissions. If PM CEMS are elected for demonstrating compliance, and the initial performance test has not yet been conducted, then initial compliance must be determined by using the CEMS specified in paragraph (n) of this section to measure particulate matter. You must calculate a 30-day rolling average of 1hour arithmetic average emission concentrations, including CEMS data during startup and shutdown, as defined in this subpart, using equation 19–19 in section 12.4.1 of EPA Reference Method 19 at 40 CFR part 60, appendix A–7 of this part; (5) Continuous compliance with the particulate matter emission limit must be determined based on the 30-day rolling average calculated using equation 19–19 in section 12.4.1 of EPA Reference Method 19 at 40 CFR part 60, Appendix A–7 of the part from the 1hour arithmetic average of the CEMS outlet data. (6) At a minimum, valid continuous monitoring system hourly averages must be obtained as specified § 60.2735; (7) The 1-hour arithmetic averages required under paragraph (n)(5) of this section must be expressed in milligrams per dry standard cubic meter corrected to 7 percent oxygen (or carbon dioxide)(dry basis) and must be used to calculate the 30-day rolling average emission concentrations. CEMS data during startup and shutdown, as defined in this subpart, are not corrected to 7 percent oxygen, and are measured at stack oxygen content. The 1-hour arithmetic averages must be calculated using the data points required under § 60.13(e)(2); (8) All valid CEMS data must be used in calculating average emission concentrations even if the minimum CEMS data requirements of paragraph (n)(6) of this section are not met; (9) The CEMS must be operated according to performance specification 11 in appendix B of this part; and, (10) Quarterly and yearly accuracy audits and daily drift, system optics, and sample volume checks must be performed in accordance with procedure 2 in appendix F of this part. (o) To demonstrate initial and continuous compliance with the carbon monoxide emissions limit, a facility E:\FR\FM\16APR3.SGM 16APR3 khammond on DSKBBV9HB2PROD with RULES3 15902 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations may substitute use of a CEMS for the carbon monoxide initial and annual performance test to demonstrate compliance with the carbon monoxide emissions limits: (1) Install, calibrate, maintain, and operate a CEMS for measuring carbon monoxide emissions discharged to the atmosphere and record the output of the system. The requirements under performance specification 4A or 4B of appendix B of this part, the quality assurance procedure 1 of appendix F of this part and the procedures under § 60.13 must be followed for installation, evaluation, and operation of the CEMS; and (2) Compliance with the carbon monoxide emission limit shall be determined based on the 30-day rolling average of the hourly arithmetic average emission concentrations, including CEMS data during startup and shutdown as defined in this subpart, using CEMS outlet data, as outlined in § 60.2710(u). (p) The owner/operator of an affected source with a bypass stack shall install, calibrate (to manufacturers’ specifications), maintain and operate a device or method for measuring the use of the bypass stack including date, time and duration. (q) For energy recovery units with a heat input capacity of 100 MMBtu/hr or greater that do not use a carbon monoxide CEMS, you must install, operate and maintain the continuous oxygen monitoring system as defined in § 60.2875 according to the procedures in paragraphs (q)(1) through (4) of this section: (1) The oxygen analyzer system must be installed by the initial performance test date specified in § 60.2675; (2) You must operate the oxygen trim system within compliance with paragraph (q)(3) of this section at all times; (3) You must maintain the oxygen level such that the 30-day rolling average that is established as the operating limit for oxygen according to paragraph (q)(4) of this section is not below the lowest hourly average oxygen concentration measured during the most recent CO performance test; and (4) You must calculate and record a 30-day rolling average oxygen concentration using equation 19–19 in section 12.4.1 of EPA Reference Method 19 of Appendix A–7 of this part. (r) For energy recovery units with annual average heat input rates greater than or equal to 250 MMBtu/hr and waste-burning kilns, you must install, calibrate, maintain, and operate a PM CPMS and record the output of the system as specified in paragraphs (r)(1) VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 through (8) of this section. For other energy recovery units, you may elect to use PM CPMS operated in accordance with this section. PM CPMS are suitable in lieu of using other CMS for monitoring PM compliance (e.g., bag leak detectors, ESP secondary power, PM scrubber pressure): (1) Install, calibrate, operate, and maintain your PM CPMS according to the procedures in your approved sitespecific monitoring plan developed in accordance with § 60.2710(l) and (r)(1)(i) through (iii) of this section: (i) The operating principle of the PM CPMS must be based on in-stack or extractive light scatter, light scintillation, beta attenuation, or mass accumulation of the exhaust gas or representative sample. The reportable measurement output from the PM CPMS must be expressed as milliamps or the digital signal equivalent; (ii) The PM CPMS must have a cycle time (i.e., period required to complete sampling, measurement, and reporting for each measurement) no longer than 60 minutes; and (iii) The PM CPMS must be capable of detecting and responding to particulate matter concentrations increments no greater than 0.5 mg/actual cubic meter. (2) During the initial performance test or any such subsequent performance test that demonstrates compliance with the PM limit, you must adjust the sitespecific operating limit in accordance with the results of the performance test according to the procedures specified in § 60.2675. (3) Collect PM CPMS hourly average output data for all energy recovery unit or waste-burning kiln operating hours. Express the PM CPMS output as milliamps or the digital signal equivalent. (4) Calculate the arithmetic 30-day rolling average of all of the hourly average PM CPMS output collected during all energy recovery unit or wasteburning kiln operating hours data (milliamps or digital bits). (5) You must collect data using the PM CPMS at all times the energy recovery unit or waste-burning kiln is operating and at the intervals specified in paragraph (r)(1)(ii) of this section, except for periods of monitoring system malfunctions, repairs associated with monitoring system malfunctions, required monitoring system quality assurance or quality control activities (including, as applicable, calibration checks and required zero and span adjustments), and any scheduled maintenance as defined in your sitespecific monitoring plan. (6) You must use all the data collected during all energy recovery unit or waste- PO 00000 Frm 00058 Fmt 4701 Sfmt 4700 burning kiln operating hours in assessing the compliance with your operating limit except: (i) Any data collected during monitoring system malfunctions, repairs associated with monitoring system malfunctions, or required monitoring system quality assurance or quality control activities conducted during monitoring system malfunctions are not used in calculations (report any such periods in your annual deviation report); (ii) Any data collected during periods when the monitoring system is out of control as specified in your site-specific monitoring plan, repairs associated with periods when the monitoring system is out of control, or required monitoring system quality assurance or quality control activities conducted during outof-control periods are not used in calculations (report emissions or operating levels and report any such periods in your annual deviation report); and (iii) Any PM CPMS data recorded during periods of CEMS data during startup and shutdown, as defined in this subpart. (7) You must record and make available upon request results of PM CPMS system performance audits, as well as the dates and duration of periods from when the PM CPMS is out of control until completion of the corrective actions necessary to return the PM CPMS to operation consistent with your site-specific monitoring plan. (8) For any deviation of the 30-day rolling average PM CPMS average value from the established operating parameter limit, you must: (i) Within 48 hours of the deviation, visually inspect the air pollution control device; (ii) If inspection of the air pollution control device identifies the cause of the deviation, take corrective action as soon as possible and return the PM CPMS measurement to within the established value; (iii) Within 30 days of the deviation or at the time of the annual compliance test, whichever comes first, conduct a PM emissions compliance test to determine compliance with the PM emissions limit and to verify the operation of the emissions control device(s). Within 45 days of the deviation, you must re-establish the CPMS operating limit. You are not required to conduct additional testing for any deviations that occur between the time of the original deviation and the PM emissions compliance test required under this paragraph; and (iv) PM CPMS deviations leading to more than four required performance E:\FR\FM\16APR3.SGM 16APR3 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations tests in a 12-month process operating period (rolling monthly) constitute a violation of this subpart. (s) If you use a dry scrubber to comply with the emission limits of this subpart, you must monitor the injection rate of each sorbent and maintain the 3-hour block averages at or above the operating limits established during the hydrogen chloride performance test. (t) If you are required to monitor clinker production because you comply with the production-rate based mercury limit for your waste-burning kiln, you must: (1) Determine hourly clinker production by one of two methods: (i) Install, calibrate, maintain, and operate a permanent weigh scale system to measure and record weight rates in tons-mass per hour of the amount of clinker produced. The system of measuring hourly clinker production must be maintained within ±5 percent accuracy, or (ii) Install, calibrate, maintain, and operate a permanent weigh scale system to measure and record weight rates in tons-mass per hour of the amount of feed to the kiln. The system of measuring feed must be maintained within ±5 percent accuracy. Calculate your hourly clinker production rate using a kiln-specific feed to clinker ratio based on reconciled clinker production determined for accounting purposes and recorded feed rates. Update this ratio monthly. Note that if this ratio changes at clinker reconciliation, you must use the new ratio going forward, but you do not have to retroactively change clinker production rates previously estimated. (2) Determine the accuracy of the system of measuring hourly clinker production (or feed mass flow if applicable) before the final compliance date of this rule and during each quarter of source operation. (3) Conduct accuracy checks in accordance with the procedures outlined in your site-specific monitoring plan under § 60.2710(l). khammond on DSKBBV9HB2PROD with RULES3 § 60.2735 Is there a minimum amount of monitoring data I must obtain? For each continuous monitoring system required or optionally allowed under § 60.2730, you must monitor and collect data according to this section: (a) You must operate the monitoring system and collect data at all required intervals at all times compliance is required except for periods of monitoring system malfunctions or outof-control periods, repairs associated with monitoring system malfunctions or out-of-control periods (as specified in § 60.2770(o)), and required monitoring system quality assurance or quality VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 control activities including, as applicable, calibration checks and required zero and span adjustments. A monitoring system malfunction is any sudden, infrequent, not reasonably preventable failure of the monitoring system to provide valid data. Monitoring system failures that are caused in part by poor maintenance or careless operation are not malfunctions. You are required to effect monitoring system repairs in response to monitoring system malfunctions or outof-control periods and to return the monitoring system to operation as expeditiously as practicable. (b) You may not use data recorded during the monitoring system malfunctions, repairs associated with monitoring system malfunctions or outof control periods, or required monitoring system quality assurance or control activities in calculations used to report emissions or operating levels. You must use all the data collected during all other periods, including data normalized for above scale readings, in assessing the operation of the control device and associated control system. (c) Except for periods of monitoring system malfunctions or out-of-control periods, repairs associated with monitoring system malfunctions or outof-control periods, and required monitoring system quality assurance or quality control activities including, as applicable, calibration checks and required zero and span adjustments, failure to collect required data is a deviation of the monitoring requirements. Model Rule—Recordkeeping and Reporting § 60.2740 What records must I keep? You must maintain the items (as applicable) as specified in paragraphs (a), (b), and (e) through (w) of this section for a period of at least 5 years: (a) Calendar date of each record; (b) Records of the data described in paragraphs (b)(1) through (7) of this section: (1) The CISWI charge dates, times, weights, and hourly charge rates; (2) Liquor flow rate to the wet scrubber inlet every 15 minutes of operation, as applicable; (3) Pressure drop across the wet scrubber system every 15 minutes of operation or amperage to the wet scrubber every 15 minutes of operation, as applicable; (4) Liquor pH as introduced to the wet scrubber every 15 minutes of operation, as applicable; (5) For affected CISWIs that establish operating limits for controls other than PO 00000 Frm 00059 Fmt 4701 Sfmt 4700 15903 wet scrubbers under § 60.2675(d) through (g) or § 60.2680, you must maintain data collected for all operating parameters used to determine compliance with the operating limits. For energy recovery units using activated carbon injection or a dry scrubber, you must also maintain records of the load fraction and corresponding sorbent injection rate records; and (6) If a fabric filter is used to comply with the emission limitations, you must record the date, time, and duration of each alarm and the time corrective action was initiated and completed, and a brief description of the cause of the alarm and the corrective action taken. You must also record the percent of operating time during each 6-month period that the alarm sounds, calculated as specified in § 60.2675(c). (7) If you monitor clinker production in accordance with § 60.2730(t): (i) Hourly clinker rate produced if clinker production is measured directly; (ii) Hourly measured kiln feed rates and calculated clinker production rates if clinker production is not measured directly; (iii) 30-day rolling averages for mercury in pounds per million tons of clinker produced; (iv) The initial and quarterly accuracy of the system of measruing hourly clinker production (or feed mass flow). (c)–(d) [Reserved] (e) Identification of calendar dates and times for which data show a deviation from the operating limits in table 3 of this subpart or a deviation from other operating limits established under § 60.2675(d) through (g) or § 60.2680 with a description of the deviations, reasons for such deviations, and a description of corrective actions taken. (f) The results of the initial, annual, and any subsequent performance tests conducted to determine compliance with the emission limits and/or to establish operating limits, as applicable. Retain a copy of the complete test report including calculations. (g) Records showing the names of CISWI operators who have completed review of the information in § 60.2660(a) as required by § 60.2660(b), including the date of the initial review and all subsequent annual reviews. (h) Records showing the names of the CISWI operators who have completed the operator training requirements under § 60.2635, met the criteria for qualification under § 60.2645, and maintained or renewed their qualification under § 60.2650 or § 60.2655. Records must include documentation of training, the dates of E:\FR\FM\16APR3.SGM 16APR3 khammond on DSKBBV9HB2PROD with RULES3 15904 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations the initial and refresher training, and the dates of their qualification and all subsequent renewals of such qualifications. (i) For each qualified operator, the phone and/or pager number at which they can be reached during operating hours. (j) Records of calibration of any monitoring devices as required under § 60.2730. (k) Equipment vendor specifications and related operation and maintenance requirements for the incinerator, emission controls, and monitoring equipment. (l) The information listed in § 60.2660(a). (m) On a daily basis, keep a log of the quantity of waste burned and the types of waste burned (always required). (n) Maintain records of the annual air pollution control device inspections that are required for each CISWI subject to the emissions limits in table 2 of this subpart or tables 6 through 9 of this subpart, any required maintenance and any repairs not completed within 10 days of an inspection or the timeframe established by the state regulatory agency. (o) For continuously monitored pollutants or parameters, you must document and keep a record of the following parameters measured using continuous monitoring systems. If you monitor emissions with a CEMS, you must indicate which data are CEMS data during startup and shutdown: (1) All 6-minute average levels of opacity; (2) All 1-hour average concentrations of sulfur dioxide emissions; (3) All 1-hour average concentrations of nitrogen oxides emissions; (4) All 1-hour average concentrations of carbon monoxide emissions; (5) All 1-hour average concentrations of particulate matter emissions; (6) All 1-hour average concentrations of mercury emissions; (7) All 1-hour average concentrations of HCl CEMS outputs; (8) All 1-hour average percent oxygen concentrations; and (9) All 1-hour average PM CPMS readings or particulate matter CEMS outputs. (p) Records indicating use of the bypass stack, including dates, times and durations. (q) If you choose to stack test less frequently than annually, consistent with § 60.2720(a) through (c), you must keep annual records that document that your emissions in the previous stack test(s) were less than 75 percent of the applicable emission limit and document that there was no change in source VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 operations including fuel composition and operation of air pollution control equipment that would cause emissions of the relevant pollutant to increase within the past year. (r) Records of the occurrence and duration of each malfunction of operation (i.e., process equipment) or the air pollution control and monitoring equipment. (s) Records of all required maintenance performed on the air pollution control and monitoring equipment. (t) Records of actions taken during periods of malfunction to minimize emissions in accordance with § 60.11(d), including corrective actions to restore malfunctioning process and air pollution control and monitoring equipment to its normal or usual manner of operation. (u) For operating units that combust non-hazardous secondary materials that have been determined not to be solid waste pursuant to § 241.3(b)(1) of this chapter, you must keep a record which documents how the secondary material meets each of the legitimacy criteria under § 241.3(d)(1). If you combust a fuel that has been processed from a discarded non-hazardous secondary material pursuant to § 241.3(b)(4), you must keep records as to how the operations that produced the fuel satisfies the definition of processing in § 241.2 and each of the legitimacy criteria in § 241.3(d)(1) of this chapter. If the fuel received a non-waste determination pursuant to the petition process submitted under § 241.3(c), you must keep a record that documents how the fuel satisfies the requirements of the petition process. For operating units that combust non-hazardous secondary materials as fuel per § 241.4, you must keep records documenting that the material is a listed non-waste under § 241.4(a). (v) Records of the criteria used to establish that the unit qualifies as a small power production facility under section 3(17)(C) of the Federal Power Act (16 U.S.C. 796(17)(C)) and that the waste material the unit is proposed to burn is homogeneous. (w) Records of the criteria used to establish that the unit qualifies as a cogeneration facility under section 3(18)(B) of the Federal Power Act (16 U.S.C. 796(18)(B)) and that the waste material the unit is proposed to burn is homogeneous. § 60.2745 Where and in what format must I keep my records? All records must be available onsite in either paper copy or computer-readable format that can be printed upon request, PO 00000 Frm 00060 Fmt 4701 Sfmt 4700 unless an alternative format is approved by the Administrator. § 60.2750 What reports must I submit? See table 5 of this subpart for a summary of the reporting requirements. § 60.2755 When must I submit my waste management plan? You must submit the waste management plan no later than the date specified in table 1 of this subpart for submittal of the final control plan. § 60.2760 What information must I submit following my initial performance test? You must submit the information specified in paragraphs (a) through (c) of this section no later than 60 days following the initial performance test. All reports must be signed by the facilities manager: (a) The complete test report for the initial performance test results obtained under § 60.2700, as applicable; (b) The values for the site-specific operating limits established in § 60.2675 or § 60.2680; and (c) If you are using a fabric filter to comply with the emission limitations, documentation that a bag leak detection system has been installed and is being operated, calibrated, and maintained as required by § 60.2730(b). § 60.2765 report? When must I submit my annual You must submit an annual report no later than 12 months following the submission of the information in § 60.2760. You must submit subsequent reports no more than 12 months following the previous report. (If the unit is subject to permitting requirements under title V of the Clean Air Act, you may be required by the permit to submit these reports more frequently.) § 60.2770 What information must I include in my annual report? The annual report required under § 60.2765 must include the items listed in paragraphs (a) through (p) of this section. If you have a deviation from the operating limits or the emission limitations, you must also submit deviation reports as specified in §§ 60.2775, 60.2780, and 60.2785: (a) Company name and address; (b) Statement by a responsible official, with that official’s name, title, and signature, certifying the accuracy of the content of the report; (c) Date of report and beginning and ending dates of the reporting period; (d) The values for the operating limits established pursuant to § 60.2675 or § 60.2680; (e) If no deviation from any emission limitation or operating limit that applies E:\FR\FM\16APR3.SGM 16APR3 khammond on DSKBBV9HB2PROD with RULES3 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations to you has been reported, a statement that there was no deviation from the emission limitations or operating limits during the reporting period; (f) The highest recorded 3-hour average and the lowest recorded 3-hour average (30-day average for energy recovery units), as applicable, for each operating parameter recorded for the calendar year being reported; (g) Information recorded under § 60.2740(b)(6) and (c) through (e) for the calendar year being reported; (h) For each performance test conducted during the reporting period, if any performance test is conducted, the process unit(s) tested, the pollutant(s) tested and the date that such performance test was conducted. Submit, following the procedure specified in § 60.2795(b)(1), the performance test report no later than the date that you submit the annual report; (i) If you met the requirements of § 60.2720(a) or (b), and did not conduct a performance test during the reporting period, you must state that you met the requirements of § 60.2720(a) or (b), and, therefore, you were not required to conduct a performance test during the reporting period; (j) Documentation of periods when all qualified CISWI operators were unavailable for more than 8 hours, but less than 2 weeks; (k) If you had a malfunction during the reporting period, the compliance report must include the number, duration, and a brief description for each type of malfunction that occurred during the reporting period and that caused or may have caused any applicable emission limitation to be exceeded. The report must also include a description of actions taken by an owner or operator during a malfunction of an affected source to minimize emissions in accordance with § 60.11(d), including actions taken to correct a malfunction; (l) For each deviation from an emission or operating limitation that occurs for a CISWI for which you are not using a CMS to comply with the emission or operating limitations in this subpart, the annual report must contain the following information: (1) The total operating time of the CISWI at which the deviation occurred during the reporting period; and (2) Information on the number, duration, and cause of deviations (including unknown cause, if applicable), as applicable, and the corrective action taken. (m) If there were periods during which the continuous monitoring system, including the CEMS, was out of control as specified in paragraph (o) of VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 this section, the annual report must contain the following information for each deviation from an emission or operating limitation occurring for a CISWI for which you are using a continuous monitoring system to comply with the emission and operating limitations in this subpart: (1) The date and time that each malfunction started and stopped; (2) The date, time, and duration that each CMS was inoperative, except for zero (low-level) and high-level checks; (3) The date, time, and duration that each continuous monitoring system was out-of-control, including start and end dates and hours and descriptions of corrective actions taken; (4) The date and time that each deviation started and stopped, and whether each deviation occurred during a period of malfunction or during another period; (5) A summary of the total duration of the deviation during the reporting period, and the total duration as a percent of the total source operating time during that reporting period; (6) A breakdown of the total duration of the deviations during the reporting period into those that are due to control equipment problems, process problems, other known causes, and other unknown causes; (7) A summary of the total duration of continuous monitoring system downtime during the reporting period, and the total duration of continuous monitoring system downtime as a percent of the total operating time of the CISWI at which the continuous monitoring system downtime occurred during that reporting period; (8) An identification of each parameter and pollutant that was monitored at the CISWI; (9) A brief description of the CISWI; (10) A brief description of the continuous monitoring system; (11) The date of the latest continuous monitoring system certification or audit; and (12) A description of any changes in continuous monitoring system, processes, or controls since the last reporting period. (n) If there were periods during which the continuous monitoring system, including the CEMS, was not out of control as specified in paragraph (o) of this section, a statement that there were not periods during which the continuous monitoring system was out of control during the reporting period. (o) A continuous monitoring system is out of control if any of the following occur: (1) The zero (low-level), mid-level (if applicable), or high-level calibration PO 00000 Frm 00061 Fmt 4701 Sfmt 4700 15905 drift exceeds two times the applicable calibration drift specification in the applicable performance specification or in the relevant standard; (2) The continuous monitoring system fails a performance test audit (e.g., cylinder gas audit), relative accuracy audit, relative accuracy test audit, or linearity test audit; and (3) The continuous opacity monitoring system calibration drift exceeds two times the limit in the applicable performance specification in the relevant standard. (p) For energy recovery units, include the annual heat input and average annual heat input rate of all fuels being burned in the unit to verify which subcategory of energy recovery unit applies. § 60.2775 What else must I report if I have a deviation from the operating limits or the emission limitations? (a) You must submit a deviation report if any recorded 3-hour average (30-day average for energy recovery units or for PM CPMS) parameter level is above the maximum operating limit or below the minimum operating limit established under this subpart, if the bag leak detection system alarm sounds for more than 5 percent of the operating time for the 6-month reporting period, if a performance test was conducted that deviated from any emission limitation, if a 30-day average measured using a CEMS deviated from any emission limitation. (b) The deviation report must be submitted by August 1 of that year for data collected during the first half of the calendar year (January 1 to June 30), and by February 1 of the following year for data you collected during the second half of the calendar year (July 1 to December 31). § 60.2780 What must I include in the deviation report? In each report required under § 60.2775, for any pollutant or parameter that deviated from the emission limitations or operating limits specified in this subpart, include the four items described in paragraphs (a) through (d) of this section: (a) The calendar dates and times your unit deviated from the emission limitations or operating limit requirements; (b) The averaged and recorded data for those dates; (c) Durations and causes of the following: (1) Each deviation from emission limitations or operating limits and your corrective actions; and (2) Bypass events and your corrective actions. E:\FR\FM\16APR3.SGM 16APR3 15906 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations (d) A copy of the operating limit monitoring data during each deviation and for any test report that documents the emission levels the process unit(s) tested, the pollutant(s) tested and the date that the performance test was conducted. Submit, following the procedure specified in § 60.2795(b)(1), the performance test report no later than the date that you submit the deviation report. § 60.2785 What else must I report if I have a deviation from the requirement to have a qualified operator accessible? (a) If all qualified operators are not accessible for 2 weeks or more, you must take the two actions in paragraphs (a)(1) and (2) of this section: (1) Submit a notification of the deviation within 10 days that includes the three items in paragraphs (a)(1)(i) through (iii) of this section: (i) A statement of what caused the deviation; (ii) A description of what you are doing to ensure that a qualified operator is accessible; and (iii) The date when you anticipate that a qualified operator will be available. (2) Submit a status report to the Administrator every 4 weeks that includes the three items in paragraphs (a)(2)(i) through (iii) of this section: (i) A description of what you are doing to ensure that a qualified operator is accessible; (ii) The date when you anticipate that a qualified operator will be accessible; and (iii) Request approval from the Administrator to continue operation of the CISWI. (b) If your unit was shut down by the Administrator, under the provisions of § 60.2665(b)(2), due to a failure to provide an accessible qualified operator, you must notify the Administrator that you are resuming operation once a qualified operator is accessible. khammond on DSKBBV9HB2PROD with RULES3 § 60.2790 Are there any other notifications or reports that I must submit? (a) Yes. You must submit notifications as provided by § 60.7. (b) If you cease combusting solid waste but continue to operate, you must provide 30 days prior notice of the effective date of the waste-to-fuel switch, consistent with § 60.2710(a). The notification must identify: (1) The name of the owner or operator of the CISWI, the location of the source, the emissions unit(s) that will cease burning solid waste, and the date of the notice; (2) The currently applicable subcategory under this subpart, and any 40 CFR part 63 subpart and subcategory VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 that will be applicable after you cease combusting solid waste; (3) The fuel(s), non-waste material(s) and solid waste(s) the CISWI is currently combusting and has combusted over the past 6 months, and the fuel(s) or non-waste materials the unit will commence combusting; (4) The date on which you became subject to the currently applicable emission limits; and (5) The date upon which you will cease combusting solid waste, and the date (if different) that you intend for any new requirements to become applicable (i.e., the effective date of the waste-tofuel switch), consistent with paragraphs (b)(2) and (3) of this section. § 60.2795 reports? In what form can I submit my (a) Submit initial, annual and deviation reports electronically or in paper format, postmarked on or before the submittal due dates. Beginning on April 16, 2021 or once the reporting form has been available in CEDRI for 1 year, whichever is later, you must submit subsequent reports on or before the submittal dates to the EPA via the Compliance and Emissions Data Reporting Interface (CEDRI), which CEDRI can be accessed through the EPA’s Central Data Exchange (CDX) (https://cdx.epa.gov/). Use the appropriate electronic report in CEDRI for this subpart or an alternate electronic file format consistent with the extensible markup language (XML) schema listed on the CEDRI website (https://www3.epa.gov/ttn/chief/cedri/ index.html). When the date forms become available in CEDRI will be listed on the CEDRI website. The reports must be submitted by the deadlines specified in this subpart, regardless of the method in which the report is submitted. (b) Submit results of each performance test and CEMS performance evaluation required by this subpart as follows: (1) Within 60 days after the date of completing each performance test (see § 60.8) required by this subpart, you must submit the results of the performance test following the procedure specified in either paragraph (b)(1)(i) or (b)(1)(ii) of this section: (i) For data collected using test methods supported by the EPA’s Electronic Reporting Tool (ERT) as listed on the EPA’s ERT website (https://www3.epa.gov/ttn/chief/ert/ert_ info.html) at the time of the test, you must submit the results of the performance test to the EPA via the CEDRI. (CEDRI can be accessed through the EPA’s CDX (https://cdx.epa.gov/).) Performance test data must be submitted PO 00000 Frm 00062 Fmt 4701 Sfmt 4700 in a file format generated through the use of the EPA’s ERT or an alternate electronic file format consistent with the XML schema listed on the EPA’s ERT website. If you claim that some of the performance test information being submitted is confidential business information (CBI), you must submit a complete file generated through the use of the EPA’s ERT or an alternate electronic file consistent with the XML schema listed on the EPA’s ERT website, including information claimed to be CBI, on a compact disc, flash drive, or other commonly used electronic storage media to the EPA. The electronic media must be clearly marked as CBI and mailed to U.S. EPA/OAQPS/ CORE CBI Office, Attention: Group Leader, Measurement Policy Group, MD C404–02, 4930 Old Page Rd., Durham, NC 27703. The same ERT or alternate file with the CBI omitted must be submitted to the EPA via the EPA’s CDX as described earlier in this paragraph; and (ii) For data collected using test methods that are not supported by the EPA’s ERT as listed on the EPA’s ERT website at the time of the test, you must submit the results of the performance test to the Administrator at the appropriate address listed in § 60.4. (2) Within 60 days after the date of completing each continuous emissions monitoring system performance evaluation you must submit the results of the performance evaluation following the procedure specified in either paragraph (b)(1) or (2) of this section: (i) For performance evaluations of continuous monitoring systems measuring relative accuracy test audit (RATA) pollutants that are supported by the EPA’s ERT as listed on the EPA’s ERT website at the time of the evaluation, you must submit the results of the performance evaluation to the EPA via the CEDRI. CEDRI can be accessed through the EPA’s CDX. Performance evaluation data must be submitted in a file format generated through the use of the EPA’s ERT or an alternate file format consistent with the XML schema listed on the EPA’s ERT website. If you claim that some of the performance evaluation information being submitted is CBI, you must submit a complete file generated through the use of the EPA’s ERT or an alternate electronic file consistent with the XML schema listed on the EPA’s ERT website, including information claimed to be CBI, on a compact disc, flash drive, or other commonly used electronic storage media to the EPA. The electronic storage media must be clearly marked as CBI and mailed to U.S. EPA/ OAQPS/CORE CBI Office, Attention: E:\FR\FM\16APR3.SGM 16APR3 khammond on DSKBBV9HB2PROD with RULES3 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations Group Leader, Measurement Policy Group, MD C404–02, 4930 Old Page Rd., Durham, NC 27703. The same ERT or alternate file with the CBI omitted must be submitted to the EPA via the EPA’s CDX as described earlier in this paragraph; and (ii) For any performance evaluations of continuous monitoring systems measuring RATA pollutants that are not supported by the EPA’s ERT as listed on the EPA’s ERT website at the time of the evaluation, you must submit the results of the performance evaluation to the Administrator at the appropriate address listed in § 60.4. (c) If you are required to electronically submit a report through the Compliance and Emissions Data Reporting Interface (CEDRI) in the EPA’s Central Data Exchange (CDX), and due to a planned or actual outage of either the EPA’s CEDRI or CDX systems within the period of time beginning 5 business days prior to the date that the submission is due, you will be or are precluded from accessing CEDRI or CDX and submitting a required report within the time prescribed, you may assert a claim of EPA system outage for failure to timely comply with the reporting requirement. You must submit notification to the Administrator in writing as soon as possible following the date you first knew, or through due diligence should have known, that the event may cause or caused a delay in reporting. You must provide to the Administrator a written description identifying the date, time and length of the outage; a rationale for attributing the delay in reporting beyond the regulatory deadline to the EPA system outage; describe the measures taken or to be taken to minimize the delay in reporting; and identify a date by which you propose to report, or if you have already met the reporting requirement at the time of the notification, the date you reported. In any circumstance, the report must be submitted electronically as soon as possible after the outage is resolved. The decision to accept the claim of EPA system outage and allow an extension to the reporting deadline is solely within the discretion of the Administrator. (d) If you are required to electronically submit a report through CEDRI in the EPA’s CDX and a force majeure event is about to occur, occurs, or has occurred or there are lingering effects from such an event within the period of time beginning 5 business days prior to the date the submission is due, the owner or operator may assert a claim of force majeure for failure to timely comply with the reporting requirement. For the purposes of this VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 section, a force majeure event is defined as an event that will be or has been caused by circumstances beyond the control of the affected facility, its contractors, or any entity controlled by the affected facility that prevents you from complying with the requirement to submit a report electronically within the time period prescribed. Examples of such events are acts of nature (e.g., hurricanes, earthquakes, or floods), acts of war or terrorism, or equipment failure or safety hazard beyond the control of the affected facility (e.g., large scale power outage). If you intend to assert a claim of force majeure, you must submit notification to the Administrator in writing as soon as possible following the date you first knew, or through due diligence should have known, that the event may cause or caused a delay in reporting. You must provide to the Administrator a written description of the force majeure event and a rationale for attributing the delay in reporting beyond the regulatory deadline to the force majeure event; describe the measures taken or to be taken to minimize the delay in reporting; and identify a date by which you propose to report, or if you have already met the reporting requirement at the time of the notification, the date you reported. In any circumstance, the reporting must occur as soon as possible after the force majeure event occurs. The decision to accept the claim of force majeure and allow an extension to the reporting deadline is solely within the discretion of the Administrator. 15907 walls and floor. Air curtain incinerators are not to be confused with conventional combustion devices with enclosed fireboxes and controlled air technology such as mass burn, modular, and fluidized bed combustors. (b) Air curtain incinerators that burn only the materials listed in paragraphs (b)(1) through (3) of this section are only required to meet the requirements under § 60.2805 and under ‘‘Air Curtain Incinerators’’ (§§ 60.2810 through 60.2870): (1) 100 percent wood waste; (2) 100 percent clean lumber; and (3) 100 percent mixture of only wood waste, clean lumber, and/or yard waste. § 60.2815 What are my requirements for meeting increments of progress and achieving final compliance? If you plan to achieve compliance more than 1 year following the effective date of state plan approval, you must meet the two increments of progress specified in paragraphs (a) and (b) of this section: (a) Submit a final control plan; and (b) Achieve final compliance. § 60.2820 When must I complete each increment of progress? Table 1 of this subpart specifies compliance dates for each of the increments of progress. § 60.2825 What must I include in the notifications of achievement of increments of progress? Model Rule—Title V Operating Permits Your notification of achievement of increments of progress must include the three items described in paragraphs (a) through (c) of this section: (a) Notification that the increment of progress has been achieved; (b) Any items required to be submitted with each increment of progress (see § 60.2840); and (c) Signature of the owner or operator of the incinerator. § 60.2805 Am I required to apply for and obtain a Title V operating permit for my unit? § 60.2830 When must I submit the notifications of achievement of increments of progress? § 60.2800 Can reporting dates be changed? If the Administrator agrees, you may change the semiannual or annual reporting dates. See § 60.19(c) for procedures to seek approval to change your reporting date. Yes. Each CISWI and ACI subject to standards under this subpart must operate pursuant to a permit issued under Clean Air Act sections 129(e) and Title V. Model Rule—Air Curtain Incinerators (ACIs) § 60.2810 What is an air curtain incinerator? (a) An ACI operates by forcefully projecting a curtain of air across an open chamber or open pit in which combustion occurs. Incinerators of this type can be constructed above or below ground and with or without refractory PO 00000 Frm 00063 Fmt 4701 Sfmt 4700 Notifications for achieving increments of progress must be postmarked no later than 10 business days after the compliance date for the increment. § 60.2835 What if I do not meet an increment of progress? If you fail to meet an increment of progress, you must submit a notification to the Administrator postmarked within 10 business days after the date for that increment of progress in table 1 of this subpart. You must inform the Administrator that you did not meet the increment, and you must continue to submit reports each subsequent E:\FR\FM\16APR3.SGM 16APR3 15908 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations calendar month until the increment of progress is met. § 60.2840 How do I comply with the increment of progress for submittal of a control plan? For your control plan increment of progress, you must satisfy the two requirements specified in paragraphs (a) and (b) of this section: (a) Submit the final control plan, including a description of any devices for air pollution control and any process changes that you will use to comply with the emission limitations and other requirements of this subpart; and (b) Maintain an onsite copy of the final control plan. § 60.2865 How must I monitor opacity for air curtain incinerators? § 60.2845 How do I comply with the increment of progress for achieving final compliance? § 60.2870 What are the recordkeeping and reporting requirements for air curtain incinerators? For the final compliance increment of progress, you must complete all process changes and retrofit construction of control devices, as specified in the final control plan, so that, if the affected incinerator is brought online, all necessary process changes and air pollution control devices would operate as designed. (a) Keep records of results of all initial and annual opacity tests onsite in either paper copy or electronic format, unless the Administrator approves another format, for at least 5 years. (b) Make all records available for submittal to the Administrator or for an inspector’s onsite review. (c) Submit an initial report no later than 60 days following the initial opacity test that includes the information specified in paragraphs (c)(1) and (2) of this section: (1) The types of materials you plan to combust in your ACI; and (2) The results (as determined by the average of three 1-hour blocks consisting of ten 6-minute average opacity values) of the initial opacity tests. (d) Submit annual opacity test results within 12 months following the previous report. (e) Submit initial and annual opacity test reports as electronic or paper copy on or before the applicable submittal date and keep a copy onsite for a period of 5 years. § 60.2850 What must I do if I close my air curtain incinerator and then restart it? (a) If you close your incinerator but will reopen it prior to the final compliance date in your state plan, you must meet the increments of progress specified in § 60.2815. (b) If you close your incinerator but will restart it after your final compliance date, you must complete emission control retrofits and meet the emission limitations on the date your incinerator restarts operation. § 60.2855 What must I do if I plan to permanently close my air curtain incinerator and not restart it? If you plan to close your incinerator rather than comply with the state plan, submit a closure notification, including the date of closure, to the Administrator by the date your final control plan is due. § 60.2860 What are the emission limitations for air curtain incinerators? khammond on DSKBBV9HB2PROD with RULES3 determined by the average of three 1hour blocks consisting of ten 6-minute average opacity values) during the startup period that is within the first 30 minutes of operation. After the date the initial stack test is required or completed (whichever is earlier), you must meet the limitations in paragraphs (a) and (b) of this section: (a) Maintain opacity to less than or equal to 10 percent opacity (as determined by the average of three 1hour blocks consisting of ten 6-minute average opacity values), except as described in paragraph (b) of this section; and (b) Maintain opacity to less than or equal to 35 percent opacity (as VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 (a) Use Method 9 of appendix A of this part to determine compliance with the opacity limitation. (b) Conduct an initial test for opacity as specified in § 60.8 no later than 180 days after your final compliance date. (c) After the initial test for opacity, conduct annual tests no more than 12 calendar months following the date of your previous test. Model Rule—Definitions § 60.2875 What definitions must I know? Terms used but not defined in this subpart are defined in the Clean Air Act and subparts A and B of this part. 30-day rolling average means the arithmetic mean of the previous 720 hours of valid operating data. Valid data excludes periods when this unit is not operating. The 720 hours should be consecutive, but not necessarily continuous if operations are intermittent. Administrator means the Administrator of the U.S. Environmental Protection Agency or his/her authorized representative or Administrator of a State Air Pollution Control Agency. PO 00000 Frm 00064 Fmt 4701 Sfmt 4700 Agricultural waste means vegetative agricultural materials such as nut and grain hulls and chaff (e.g., almond, walnut, peanut, rice, and wheat), bagasse, orchard prunings, corn stalks, coffee bean hulls and grounds, and other vegetative waste materials generated as a result of agricultural operations. Air curtain incinerator (ACI) means an incinerator that operates by forcefully projecting a curtain of air across an open chamber or pit in which combustion occurs. Incinerators of this type can be constructed above or below ground and with or without refractory walls and floor. Air curtain incinerators are not to be confused with conventional combustion devices with enclosed fireboxes and controlled air technology such as mass burn, modular, and fluidized bed combustors. Annual heat input means the heat input for the 12 months preceding the compliance demonstration. Auxiliary fuel means natural gas, liquified petroleum gas, fuel oil, or diesel fuel. Average annual heat input rate means annual heat input divided by the hours of operation for the 12 months preceding the compliance demonstration. Bag leak detection system means an instrument that is capable of monitoring particulate matter loadings in the exhaust of a fabric filter (i.e., baghouse) in order to detect bag failures. A bag leak detection system includes, but is not limited to, an instrument that operates on triboelectric, light scattering, light transmittance, or other principle to monitor relative particulate matter loadings. Burn-off oven means any rack reclamation unit, part reclamation unit, or drum reclamation unit. A burn-off oven is not an incinerator, wasteburning kiln, an energy recovery unit or a small, remote incinerator under this subpart. Bypass stack means a device used for discharging combustion gases to avoid severe damage to the air pollution control device or other equipment. Calendar quarter means three consecutive months (nonoverlapping) beginning on: January 1, April 1, July 1, or October 1. Calendar year means 365 consecutive days starting on January 1 and ending on December 31. CEMS data during startup and shutdown means the following: (1) For incinerators and small remote incinerators: CEMS data collected during the first hours of operation of a CISWI startup from a cold start until waste is fed into the unit and the hours E:\FR\FM\16APR3.SGM 16APR3 khammond on DSKBBV9HB2PROD with RULES3 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations of operation following the cessation of waste material being fed to the CISWI during a unit shutdown. For each startup event, the length of time that CEMS data may be claimed as being CEMS data during startup must be 48 operating hours or less. For each shutdown event, the length of time that CEMS data may be claimed as being CEMS data during shutdown must be 24 operating hours or less; (2) For energy recovery units: CEMS data collected during the startup or shutdown periods of operation. Startup begins with either the first-ever firing of fuel in a boiler or process heater for the purpose of supplying useful thermal energy (such as steam or heat) for heating, cooling or process purposes, or producing electricity, or the firing of fuel in a boiler or process heater for any purpose after a shutdown event. Startup ends four hours after when the boiler or process heater makes useful thermal energy (such as heat or steam) for heating, cooling, or process purposes, or generates electricity, whichever is earlier. Shutdown begins when the boiler or process heater no longer makes useful thermal energy (such as heat or steam) for heating, cooling, or process purposes and/or generates electricity or when no fuel is being fed to the boiler or process heater, whichever is earlier. Shutdown ends when the boiler or process heater no longer makes useful thermal energy (such as steam or heat) for heating, cooling, or process purposes and/or generates electricity, and no fuel is being combusted in the boiler or process heater; and (3) For waste-burning kilns: CEMS data collected during the periods of kiln operation that do not include normal operations. Startup means the time from when a shutdown kiln first begins firing fuel until it begins producing clinker. Startup begins when a shutdown kiln turns on the induced draft fan and begins firing fuel in the main burner. Startup ends when feed is being continuously introduced into the kiln for at least 120 minutes or when the feed rate exceeds 60 percent of the kiln design limitation rate, whichever occurs first. Shutdown means the cessation of kiln operation. Shutdown begins when feed to the kiln is halted and ends when continuous kiln rotation ceases. Chemical recovery unit means combustion units burning materials to recover chemical constituents or to produce chemical compounds where there is an existing commercial market for such recovered chemical constituents or compounds. A chemical recovery unit is not an incinerator, a waste-burning kiln, an energy recovery unit or a small, remote incinerator VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 under this subpart. The following seven types of units are considered chemical recovery units: (1) Units burning only pulping liquors (i.e., black liquor) that are reclaimed in a pulping liquor recovery process and reused in the pulping process; (2) Units burning only spent sulfuric acid used to produce virgin sulfuric acid; (3) Units burning only wood or coal feedstock for the production of charcoal; (4) Units burning only manufacturing byproduct streams/residue containing catalyst metals that are reclaimed and reused as catalysts or used to produce commercial grade catalysts; (5) Units burning only coke to produce purified carbon monoxide that is used as an intermediate in the production of other chemical compounds; (6) Units burning only hydrocarbon liquids or solids to produce hydrogen, carbon monoxide, synthesis gas, or other gases for use in other manufacturing processes; and (7) Units burning only photographic film to recover silver. Chemotherapeutic waste means waste material resulting from the production or use of antineoplastic agents used for the purpose of stopping or reversing the growth of malignant cells. Clean lumber means wood or wood products that have been cut or shaped and include wet, air-dried, and kilndried wood products. Clean lumber does not include wood products that have been painted, pigment-stained, or pressure-treated by compounds such as chromate copper arsenate, pentachlorophenol, and creosote. Commercial and industrial solid waste incineration unit (CISWI) means any distinct operating unit of any commercial or industrial facility that combusts, or has combusted in the preceding 6 months, any solid waste as that term is defined in 40 CFR part 241. If the operating unit burns materials other than traditional fuels as defined in § 241.2 that have been discarded, and you do not keep and produce records as required by § 60.2740(u), the operating unit is a CISWI. While not all CISWIs will include all of the following components, a CISWI includes, but is not limited to, the solid waste feed system, grate system, flue gas system, waste heat recovery equipment, if any, and bottom ash system. The CISWI does not include air pollution control equipment or the stack. The CISWI boundary starts at the solid waste hopper (if applicable) and extends through two areas: The combustion unit flue gas system, which ends immediately after the last combustion PO 00000 Frm 00065 Fmt 4701 Sfmt 4700 15909 chamber or after the waste heat recovery equipment, if any; and the combustion unit bottom ash system, which ends at the truck loading station or similar equipment that transfers the ash to final disposal. The CISWI includes all ash handling systems connected to the bottom ash handling system. Contained gaseous material means gases that are in a container when that container is combusted. Continuous emission monitoring system (CEMS) means the total equipment that may be required to meet the data acquisition and availability requirements of this subpart, used to sample, condition (if applicable), analyze, and provide a record of emissions. Continuous monitoring system (CMS) means the total equipment, required under the emission monitoring sections in applicable subparts, used to sample and condition (if applicable), to analyze, and to provide a permanent record of emissions or process parameters. A particulate matter continuous parameter monitoring system (PM CPMS) is a type of CMS. Cyclonic burn barrel means a combustion device for waste materials that is attached to a 55 gallon, openhead drum. The device consists of a lid, which fits onto and encloses the drum, and a blower that forces combustion air into the drum in a cyclonic manner to enhance the mixing of waste material and air. A cyclonic burn barrel is not an incinerator, a waste-burning kiln, an energy recovery unit or a small, remote incinerator under this subpart. Deviation means any instance in which an affected source subject to this subpart, or an owner or operator of such a source: (1) Fails to meet any requirement or obligation established by this subpart, including but not limited to any emission limitation, operating limit, or operator qualification and accessibility requirements; and (2) Fails to meet any term or condition that is adopted to implement an applicable requirement in this subpart and that is included in the operating permit for any affected source required to obtain such a permit. Dioxins/furans means tetra-through octachlorinated dibenzo-p-dioxins and dibenzofurans. Discard means, for purposes of this subpart and 40 CFR part 60, subpart DDDD, only, burned in an incineration unit without energy recovery. Drum reclamation unit means a unit that burns residues out of drums (e.g., 55 gallon drums) so that the drums can be reused. E:\FR\FM\16APR3.SGM 16APR3 khammond on DSKBBV9HB2PROD with RULES3 15910 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations Dry scrubber means an add-on air pollution control system that injects dry alkaline sorbent (dry injection) or sprays an alkaline sorbent (spray dryer) to react with and neutralize acid gas in the exhaust stream forming a dry powder material. Sorbent injection systems in fluidized bed boilers and process heaters are included in this definition. A dry scrubber is a dry control system. Energy recovery means the process of recovering thermal energy from combustion for useful purposes such as steam generation or process heating. Energy recovery unit means a combustion unit combusting solid waste (as that term is defined by the Administrator in 40 CFR part 241) for energy recovery. Energy recovery units include units that would be considered boilers and process heaters if they did not combust solid waste. Energy recovery unit designed to burn biomass (Biomass) means an energy recovery unit that burns solid waste, biomass, and non-coal solid materials but less than 10 percent coal, on a heat input basis on an annual average, either alone or in combination with liquid waste, liquid fuel or gaseous fuels. Energy recovery unit designed to burn coal (Coal) means an energy recovery unit that burns solid waste and at least 10 percent coal on a heat input basis on an annual average, either alone or in combination with liquid waste, liquid fuel or gaseous fuels. Energy recovery unit designed to burn liquid waste materials and gas (Liquid/ gas) means an energy recovery unit that burns a liquid waste with liquid or gaseous fuels not combined with any solid fuel or waste materials. Energy recovery unit designed to burn solid materials (Solids) includes energy recovery units designed to burn coal and energy recovery units designed to burn biomass. Fabric filter means an add-on air pollution control device used to capture particulate matter by filtering gas streams through filter media, also known as a baghouse. Foundry sand thermal reclamation unit means a type of part reclamation unit that removes coatings that are on foundry sand. A foundry sand thermal reclamation unit is not an incinerator, a waste-burning kiln, an energy recovery unit or a small, remote incinerator under this subpart. Incinerator means any furnace used in the process of combusting solid waste (as that term is defined by the Administrator in 40 CFR part 241) for the purpose of reducing the volume of the waste by removing combustible matter. Incinerator designs include single chamber and two-chamber. VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 In-line coal mill means those coal mills using kiln exhaust gases in their process. Coal mills with a heat source other than the kiln or coal mills using exhaust gases from the clinker cooler alone are not an in-line coal mill. In-line kiln/raw mill means a system in a Portland Cement production process where a dry kiln system is integrated with the raw mill so that all or a portion of the kiln exhaust gases are used to perform the drying operation of the raw mill, with no auxiliary heat source used. In this system the kiln is capable of operating without the raw mill operating, but the raw mill cannot operate without the kiln gases, and consequently, the raw mill does not generate a separate exhaust gas stream. Kiln means an oven or furnace, including any associated preheater or precalciner devices, in-line raw mills, in-line coal mills or alkali bypasses used for processing a substance by burning, firing or drying. Kilns include cement kilns that produce clinker by heating limestone and other materials for subsequent production of Portland Cement. Because the alkali bypass, inline raw mill and in-line coal mill are considered an integral part of the kiln, the kiln emissions limits also apply to the exhaust of the alkali bypass, in-line raw mill and in-line coal mill. Laboratory analysis unit means units that burn samples of materials for the purpose of chemical or physical analysis. A laboratory analysis unit is not an incinerator, waste-burning kiln, an energy recovery unit or a small, remote incinerator under this subpart. Load fraction means the actual heat input of an energy recovery unit divided by heat input during the performance test that established the minimum sorbent injection rate or minimum activated carbon injection rate, expressed as a fraction (e.g., for 50 percent load the load fraction is 0.5). Low-level radioactive waste means waste material which contains radioactive nuclides emitting primarily beta or gamma radiation, or both, in concentrations or quantities that exceed applicable federal or state standards for unrestricted release. Low-level radioactive waste is not high-level radioactive waste, spent nuclear fuel, or by-product material as defined by the Atomic Energy Act of 1954 (42 U.S.C. 2014(e)(2)). Malfunction means any sudden, infrequent, and not reasonably preventable failure of air pollution control equipment, process equipment, or a process to operate in a normal or usual manner. Failures that are caused, in part, by poor maintenance or careless operation are not malfunctions. PO 00000 Frm 00066 Fmt 4701 Sfmt 4700 Minimum voltage or amperage means 90 percent of the lowest test-run average voltage or amperage to the electrostatic precipitator measured during the most recent particulate matter or mercury performance test demonstrating compliance with the applicable emission limits. Modification or modified CISWI means a CISWI that has been changed later than August 7, 2013, and that meets one of two criteria: (1) The cumulative cost of the changes over the life of the unit exceeds 50 percent of the original cost of building and installing the CISWI (not including the cost of land) updated to current costs (current dollars). To determine what systems are within the boundary of the CISWI used to calculate these costs, see the definition of CISWI; and (2) Any physical change in the CISWI or change in the method of operating it that increases the amount of any air pollutant emitted for which section 129 or section 111 of the Clean Air Act has established standards. Municipal solid waste or municipaltype solid waste means household, commercial/retail, or institutional waste. Household waste includes material discarded by residential dwellings, hotels, motels, and other similar permanent or temporary housing. Commercial/retail waste includes material discarded by stores, offices, restaurants, warehouses, nonmanufacturing activities at industrial facilities, and other similar establishments or facilities. Institutional waste includes materials discarded by schools, by hospitals (nonmedical), by nonmanufacturing activities at prisons and government facilities, and other similar establishments or facilities. Household, commercial/retail, and institutional waste does include yard waste and refuse-derived fuel. Household, commercial/retail, and institutional waste does not include used oil; sewage sludge; wood pallets; construction, renovation, and demolition wastes (which include railroad ties and telephone poles); clean wood; industrial process or manufacturing wastes; medical waste; or motor vehicles (including motor vehicle parts or vehicle fluff). Opacity means the degree to which emissions reduce the transmission of light and obscure the view of an object in the background. Operating day means a 24-hour period between 12:00 midnight and the following midnight during which any amount of solid waste is combusted at any time in the CISWI. Oxygen analyzer system means all equipment required to determine the E:\FR\FM\16APR3.SGM 16APR3 khammond on DSKBBV9HB2PROD with RULES3 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations oxygen content of a gas stream and used to monitor oxygen in the boiler or process heater flue gas, boiler/process heater, firebox, or other appropriate location. This definition includes oxygen trim systems and certified oxygen CEMS. The source owner or operator is responsible to install, calibrate, maintain, and operate the oxygen analyzer system in accordance with the manufacturer’s recommendations. Oxygen trim system means a system of monitors that is used to maintain excess air at the desired level in a combustion device over its operating range. A typical system consists of a flue gas oxygen and/or carbon monoxide monitor that automatically provides a feedback signal to the combustion air controller or draft controller. Part reclamation unit means a unit that burns coatings off parts (e.g., tools, equipment) so that the parts can be reconditioned and reused. Particulate matter means total particulate matter emitted from CISWIs as measured by Method 5 or Method 29 of appendix A of this part. Pathological waste means waste material consisting of only human or animal remains, anatomical parts, and/ or tissue, the bags/containers used to collect and transport the waste material, and animal bedding (if applicable). Performance evaluation means the conduct of relative accuracy testing, calibration error testing, and other measurements used in validating the continuous monitoring system data. Performance test means the collection of data resulting from the execution of a test method (usually three emission test runs) used to demonstrate compliance with a relevant emission standard as specified in the performance test section of the relevant standard. Process change means any of the following physical or operational changes: (1) A physical change (maintenance activities excluded) to the CISWI which may increase the emission rate of any air pollutant to which a standard applies; (2) An operational change to the CISWI where a new type of nonhazardous secondary material is being combusted; (3) A physical change (maintenance activities excluded) to the air pollution control devices used to comply with the emission limits for the CISWI (e.g., replacing an electrostatic precipitator with a fabric filter); and (4) An operational change to the air pollution control devices used to comply with the emission limits for the affected CISWI (e.g., change in the VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 sorbent injection rate used for activated carbon injection). Rack reclamation unit means a unit that burns the coatings off racks used to hold small items for application of a coating. The unit burns the coating overspray off the rack so the rack can be reused. Raw mill means a ball or tube mill, vertical roller mill or other size reduction equipment, that is not part of an in-line kiln/raw mill, used to grind feed to the appropriate size. Moisture may be added or removed from the feed during the grinding operation. If the raw mill is used to remove moisture from feed materials, it is also, by definition, a raw material dryer. The raw mill also includes the air separator associated with the raw mill. Reconstruction means rebuilding a CISWI and meeting two criteria: (1) The reconstruction begins on or after August 7, 2013; and (2) The cumulative cost of the construction over the life of the incineration unit exceeds 50 percent of the original cost of building and installing the CISWI (not including land) updated to current costs (current dollars). To determine what systems are within the boundary of the CISWI used to calculate these costs, see the definition of CISWI. Refuse-derived fuel means a type of municipal solid waste produced by processing municipal solid waste through shredding and size classification. This includes all classes of refuse-derived fuel including two fuels: (1) Low-density fluff refuse-derived fuel through densified refuse-derived fuel; and (2) Pelletized refuse-derived fuel. Responsible official means one of the following: (1) For a corporation: A president, secretary, treasurer, or vice-president of the corporation in charge of a principal business function, or any other person who performs similar policy or decision-making functions for the corporation, or a duly authorized representative of such person if the representative is responsible for the overall operation of one or more manufacturing, production, or operating facilities applying for or subject to a permit and either: (i) The facilities employ more than 250 persons or have gross annual sales or expenditures exceeding $25 million (in second quarter 1980 dollars); or (ii) The delegation of authority to such representatives is approved in advance by the permitting authority; PO 00000 Frm 00067 Fmt 4701 Sfmt 4700 15911 (2) For a partnership or sole proprietorship: a general partner or the proprietor, respectively; (3) For a municipality, state, federal, or other public agency: Either a principal executive officer or ranking elected official. For the purposes of this part, a principal executive officer of a Federal agency includes the chief executive officer having responsibility for the overall operations of a principal geographic unit of the agency (e.g., a Regional Administrator of EPA); or (4) For affected facilities: (i) The designated representative in so far as actions, standards, requirements, or prohibitions under Title IV of the Clean Air Act or the regulations promulgated thereunder are concerned; or (ii) The designated representative for any other purposes under part 60. Shutdown means, for incinerators and small, remote incinerators, the period of time after all waste has been combusted in the primary chamber. Small, remote incinerator means an incinerator that combusts solid waste (as that term is defined by the Administrator in 40 CFR part 241) and combusts 3 tons per day or less solid waste and is more than 25 miles driving distance to the nearest municipal solid waste landfill. Soil treatment unit means a unit that thermally treats petroleumcontaminated soils for the sole purpose of site remediation. A soil treatment unit may be direct-fired or indirect fired. A soil treatment unit is not an incinerator, a waste-burning kiln, an energy recovery unit or a small, remote incinerator under this subpart. Solid waste means the term solid waste as defined in 40 CFR 241.2. Solid waste incineration unit means a distinct operating unit of any facility which combusts any solid waste (as that term is defined by the Administrator in 40 CFR part 241) material from commercial or industrial establishments or the general public (including single and multiple residences, hotels and motels). Such term does not include incinerators or other units required to have a permit under section 3005 of the Solid Waste Disposal Act. The term ‘‘solid waste incineration unit’’ does not include: (1) Materials recovery facilities (including primary or secondary smelters) which combust waste for the primary purpose of recovering metals; (2) Qualifying small power production facilities, as defined in section 3(17)(C) of the Federal Power Act (16 U.S.C. 769(17)(C)), or qualifying cogeneration facilities, as defined in section 3(18)(B) of the Federal Power E:\FR\FM\16APR3.SGM 16APR3 15912 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations Act (16 U.S.C. 796(18)(B)), which burn homogeneous waste (such as units which burn tires or used oil, but not including refuse-derived fuel) for the production of electric energy or in the case of qualifying cogeneration facilities which burn homogeneous waste for the production of electric energy and steam or forms of useful energy (such as heat) which are used for industrial, commercial, heating or cooling purposes; or (3) Air curtain incinerators provided that such incinerators only burn wood wastes, yard wastes and clean lumber and that such air curtain incinerators comply with opacity limitations to be established by the Administrator by rule. Space heater means a unit that meets the requirements of 40 CFR 279.23. A space heater is not an incinerator, a waste-burning kiln, an energy recovery unit or a small, remote incinerator under this subpart. Standard conditions, when referring to units of measure, means a temperature of 68 °F (20 °C) and a pressure of 1 atmosphere (101.3 kilopascals). Startup period means, for incinerators and small, remote incinerators, the period of time between the activation of the system and the first charge to the unit. Useful thermal energy means energy (i.e., steam, hot water, or process heat) that meets the minimum operating temperature and/or pressure required by any energy use system that uses energy provided by the affected energy recovery unit. Waste-burning kiln means a kiln that is heated, in whole or in part, by combusting solid waste (as the term is defined by the Administrator in 40 CFR part 241). Secondary materials used in Portland cement kilns shall not be deemed to be combusted unless they are introduced into the flame zone in the hot end of the kiln or mixed with the precalciner fuel. Wet scrubber means an add-on air pollution control device that uses an aqueous or alkaline scrubbing liquor to collect particulate matter (including nonvaporous metals and condensed organics) and/or to absorb and neutralize acid gases. Wood waste means untreated wood and untreated wood products, including tree stumps (whole or chipped), trees, tree limbs (whole or chipped), bark, sawdust, chips, scraps, slabs, millings, and shavings. Wood waste does not include: (1) Grass, grass clippings, bushes, shrubs, and clippings from bushes and shrubs from residential, commercial/ retail, institutional, or industrial sources as part of maintaining yards or other private or public lands; (2) Construction, renovation, or demolition wastes; or (3) Clean lumber. TABLE 1 TO SUBPART DDDD OF PART 60—MODEL RULE—INCREMENTS OF PROGRESS AND COMPLIANCE SCHEDULES By these dates 1 Comply with these increments of progress Increment 1-Submit final control plan ...................................................... Increment 2-Final compliance .................................................................. (Dates to be specified in state plan). (Dates to be specified in state plan).2 1 Site-specific schedules can be used at the discretion of the state. date can be no later than 3 years after the effective date of state plan approval or December 1, 2005 for CISWIs that commenced construction on or before November 30, 1999. The date can be no later than 3 years after the effective date of approval of a revised state plan or February 7, 2018, for CISWIs that commenced construction on or before June 4, 2010. 2 The TABLE 2 TO SUBPART DDDD OF PART 60—MODEL RULE—EMISSION LIMITATIONS THAT APPLY TO INCINERATORS BEFORE [DATE TO BE SPECIFIED IN STATE PLAN] 1 For the air pollutant You must meet this emission limitation 2 Cadmium ........................................ 0.004 milligrams per dry standard cubic meter. 157 parts per million by dry volume. 3-run average (1 sample time per 3-run average (1 sample time per Dioxins/furans (toxic equivalency basis). Hydrogen chloride .......................... 0.41 nanograms per dry standard cubic meter. 62 parts per million by dry volume Lead ............................................... 0.04 milligrams per dry standard cubic meter. 0.47 milligrams per dry standard cubic meter. 3-run average (1 hour minimum sample time per run). 3-run average (For Method 26, collect a minimum volume of 120 liters per run. For Method 26A, collect a minimum volume of 1 dry standard cubic meter per run). 3-run average (1 hour minimum sample time per run). 3-run average (1 hour minimum sample time per run). Carbon monoxide .......................... khammond on DSKBBV9HB2PROD with RULES3 Mercury .......................................... And determining compliance using this method 3 Using this averaging time 3 hour minimum run). hour minimum run). Opacity ........................................... 10 percent ..................................... Nitrogen oxides .............................. 388 parts per million by dry volume. Three 1-hour blocks consisting of ten 6-minute average opacity values. 3-run average (1 hour minimum sample time per run). Particulate matter ........................... 70 milligrams per dry standard cubic meter. 3-run average (1 hour minimum sample time per run). VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 PO 00000 Frm 00068 Fmt 4701 Sfmt 4700 E:\FR\FM\16APR3.SGM Performance test (Method 29 of appendix A of this part). Performance test (Method 10, 10A, or 10B, of appendix A of this part). Performance test (Method 23 of appendix A of this part). Performance test (Method 26 or 26A at 40 CFR part 60, appendix A–8). Performance test (Method 29 of appendix A of this part). Performance test (Method 29 or 30B at 40 CFR part 60, appendix A–8) or ASTM D6784–02 (Reapproved 2008).4 Performance test (Method 9 at 40 CFR part 60, appendix A–4). Performance test (Methods 7 or 7E at 40 CFR part 60, appendix A–4). Performance test (Method 5 or 29 of appendix A of this part). 16APR3 15913 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations TABLE 2 TO SUBPART DDDD OF PART 60—MODEL RULE—EMISSION LIMITATIONS THAT APPLY TO INCINERATORS BEFORE [DATE TO BE SPECIFIED IN STATE PLAN] 1—Continued For the air pollutant You must meet this emission limitation 2 Using this averaging time 3 And determining compliance using this method 3 Sulfur dioxide ................................. 20 parts per million by dry volume 3-run average (1 hour minimum sample time per run). Performance test (Method 6 or 6c of appendix A of this part). 1 Applies only to incinerators subject to the CISWI standards through a state plan or the Federal plan prior to June 4, 2010. The date specified in the state plan can be no later than 3 years after the effective date of approval of a revised state plan or February 7, 2018. 2 All emission limitations (except for opacity) are measured at 7 percent oxygen, dry basis at standard conditions. 3 In lieu of performance testing, you may use a CEMS or, for mercury, an integrated sorbent trap monitoring system, to demonstrate initial and continuing compliance with an emissions limit, as long as you comply with the CEMS or integrated sorbent trap monitoring system requirements applicable to the specific pollutant in §§ 60.2710 and 60.2730. As prescribed in § 60.2710(u), if you use a CEMS or integrated sorbent trap monitoring system to demonstrate compliance with an emissions limit, your averaging time is a 30-day rolling average of 1-hour arithmetic average emission concentrations. 4 Incorporated by reference, see § 60.17. TABLE 3 TO SUBPART DDDD OF PART 60—MODEL RULE—OPERATING LIMITS FOR WET SCRUBBERS And monitor using these minimum frequencies For these operating parameters You must establish these operating limits Charge rate ....................... Pressure drop across the wet scrubber or amperage to wet scrubber. Scrubber liquor flow rate ... Scrubber liquor pH ............ 1 Calculated Data measurement Data recording Averaging time Maximum charge rate ....... Continuous ........................ Every hour ......................... Minimum pressure drop or amperage. Continuous ........................ Every 15 minutes .............. Daily (batch units). 3-hour rolling (continuous and intermittent units).1 3-hour rolling.1 Minimum flow rate ............. Minimum pH ...................... Continuous ........................ Continuous ........................ Every 15 minutes .............. Every 15 minutes .............. 3-hour rolling.1 3-hour rolling.1 each hour as the average of the previous 3 operating hours. TABLE 4 TO SUBPART DDDD OF PART 60—MODEL RULE—TOXIC EQUIVALENCY FACTORS Toxic equivalency factor Dioxin/furan isomer 2,3,7,8-tetrachlorinated dibenzo-p-dioxin .................................................................................................................................... 1,2,3,7,8-pentachlorinated dibenzo-p-dioxin ................................................................................................................................ 1,2,3,4,7,8-hexachlorinated dibenzo-p-dioxin .............................................................................................................................. 1,2,3,7,8,9-hexachlorinated dibenzo-p-dioxin .............................................................................................................................. 1,2,3,6,7,8-hexachlorinated dibenzo-p-dioxin .............................................................................................................................. 1,2,3,4,6,7,8-heptachlorinated dibenzo-p-dioxin .......................................................................................................................... octachlorinated dibenzo-p-dioxin ................................................................................................................................................. 2,3,7,8-tetrachlorinated dibenzofuran .......................................................................................................................................... 2,3,4,7,8-pentachlorinated dibenzofuran ..................................................................................................................................... 1,2,3,7,8-pentachlorinated dibenzofuran ..................................................................................................................................... 1,2,3,4,7,8-hexachlorinated dibenzofuran ................................................................................................................................... 1,2,3,6,7,8-hexachlorinated dibenzofuran ................................................................................................................................... 1,2,3,7,8,9-hexachlorinated dibenzofuran ................................................................................................................................... 2,3,4,6,7,8-hexachlorinated dibenzofuran ................................................................................................................................... 1,2,3,4,6,7,8-heptachlorinated dibenzofuran ............................................................................................................................... 1,2,3,4,7,8,9-heptachlorinated dibenzofuran ............................................................................................................................... octachlorinated dibenzofuran ....................................................................................................................................................... 1 0.5 0.1 0.1 0.1 0.01 0.001 0.1 0.5 0.05 0.1 0.1 0.1 0.1 0.01 0.01 0.001 khammond on DSKBBV9HB2PROD with RULES3 TABLE 5 TO SUBPART DDDD OF PART 60—MODEL RULE—SUMMARY OF REPORTING REQUIREMENTS 1 Report Due date Contents Waste Management Plan .... No later than the date specified in table 1 for submittal of the final control plan. No later than 60 days following the initial performance test. • Waste management plan ........................................... § 60.2755. • Complete test report for the initial performance test • The values for the site-specific operating limits ........ • Installation of bag leak detection systems for fabric filters. § 60.2760. Initial Test Report ................ VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 PO 00000 Frm 00069 Fmt 4701 Sfmt 4700 E:\FR\FM\16APR3.SGM Reference 16APR3 15914 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations TABLE 5 TO SUBPART DDDD OF PART 60—MODEL RULE—SUMMARY OF REPORTING REQUIREMENTS 1—Continued Report Due date Contents Annual report ....................... No later than 12 months following the submission of the initial test report. Subsequent reports are to be submitted no more than 12 months following the previous report. • • • • • • • • • • • Emission limitation or operating limit deviation report. Qualified Operator Deviation Notification. By August 1 of that year for data collected during the first half of the calendar year. By February 1 of the following year for data collected during the second half of the calendar year. Within 10 days of deviation Qualified Operator Deviation Status Report. Every 4 weeks following deviation. Qualified Operator Deviation Notification of Resumed Operation. Prior to resuming operation 1 This • • • • • • • • • • • • Reference Name and address .................................................... Statement and signature by responsible official ....... Date of report ............................................................. Values for the operating limits ................................... Highest recorded 3-hour average and the lowest 3hour average, as applicable, (or 30-day average, if applicable) for each operating parameter recorded for the calendar year being reported. If a performance test was conducted during the reporting period, the results of the test. If a performance test was not conducted during the reporting period, a statement that the requirements of § 60.2720(a) were met. Documentation of periods when all qualified CISWI operators were unavailable for more than 8 hours but less than 2 weeks. If you are conducting performance tests once every 3 years consistent with § 60.2720(a), the date of the last 2 performance tests, a comparison of the emission level you achieved in the last 2 performance tests to the 75 percent emission limit threshold required in § 60.2720(a) and a statement as to whether there have been any operational changes since the last performance test that could increase emissions. Any malfunction, deviation, or continuous monitoring system out of control periods information as specified in § 60.2770(k) through (o). Fuel input information for energy recovery unit subcategory verification as specified in § 60.2770(p). Dates and times of deviation ..................................... Averaged and recorded data for those dates ........... Duration and causes of each deviation and the corrective actions taken. Copy of operating limit monitoring data and any test reports. Dates, times and causes for monitor downtime incidents. Statement of cause of deviation ................................ Description of efforts to have an accessible qualified operator. The date a qualified operator will be accessible ....... Description of efforts to have an accessible qualified operator. The date a qualified operator will be accessible ....... Request for approval to continue operation .............. Notification that you are resuming operation ............ §§ 60.2765 and 60.2770. § 60.2775 and 60.2780. § 60.2785(a)(1). § 60.2785(a)(2). § 60.2785(b). table is only a summary, see the referenced sections of the rule for the complete requirements. khammond on DSKBBV9HB2PROD with RULES3 TABLE 6 TO SUBPART DDDD OF PART 60—MODEL RULE—EMISSION LIMITATIONS THAT APPLY TO INCINERATORS ON AND AFTER [DATE TO BE SPECIFIED IN STATE PLAN] 1 For the air pollutant You must meet this emission limitation 2 Using this averaging time 3 And determining compliance using this method 3 Cadmium ........................................ 0.0026 milligrams per dry standard cubic meter. 3-run average (collect a minimum volume of 2 dry standard cubic meters). Carbon monoxide .......................... 17 parts per million dry volume .... Dioxins/furans (total mass basis) ... 4.6 nanograms per dry standard cubic meter. Dioxins/furans (toxic equivalency basis). 0.13 nanograms per dry standard cubic meter. 3-run average (1 hour minimum sample time per run). 3-run average (collect a minimum volume of 2 dry standard cubic meters). 3-run average (collect a minimum volume of 2 dry standard cubic meters). Performance test (Method 29 at 40 CFR part 60, appendix A–8). Use ICPMS for the analytical finish. Performance test (Method 10 at 40 CFR part 60, appendix A–4). Performance test (Method 23 at 40 CFR part 60, appendix A–7). VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 PO 00000 Frm 00070 Fmt 4701 Sfmt 4700 E:\FR\FM\16APR3.SGM Performance test (Method 23 at 40 CFR part 60, appendix A–7). 16APR3 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations 15915 TABLE 6 TO SUBPART DDDD OF PART 60—MODEL RULE—EMISSION LIMITATIONS THAT APPLY TO INCINERATORS ON AND AFTER [DATE TO BE SPECIFIED IN STATE PLAN] 1—Continued For the air pollutant You must meet this emission limitation 2 Using this averaging time 3 And determining compliance using this method 3 Hydrogen chloride .......................... 29 parts per million dry volume .... Performance test (Method 26 or 26A at 40 CFR part 60, appendix A–8). Lead ............................................... 0.015 milligrams per dry standard cubic meter. 3-run average (For Method 26, collect a minimum volume of 60 liters per run. For Method 26A, collect a minimum volume of 1 dry standard cubic meter per run). 3-run average (collect a minimum volume of 2 dry standard cubic meters). Mercury .......................................... 0.0048 milligrams per dry standard cubic meter. Nitrogen oxides .............................. 53 parts per million dry volume .... Particulate matter filterable ............ 34 milligrams per dry standard cubic meter. Sulfur dioxide ................................. 11 parts per million dry volume .... Fugitive ash ................................... Visible emissions for no more than 5% of the hourly observation period. 3-run average (For Method 29 an ASTM D6784–02 (Reapproved 2008),4 collect a minimum volume of 2 dry standard cubic meters per run. For Method 30B, collect a minimum sample as specified in Method 30B at 40 CFR part 60, appendix A). 3-run average (for Method 7E, 1 hour minimum sample time per run). 3-run average (collect a minimum volume of 1 dry standard cubic meter). 3-run average (1 hour minimum sample time per run). Three 1-hour observation periods Performance test (Method 29 at 40 CFR part 60, appendix A–8). Use ICPMS for the analytical finish. Performance test (Method 29 or 30B at 40 CFR part 60, appendix A–8) or ASTM D6784–02 (Reapproved 2008).4 Performance test (Method 7 or 7E at 40 CFR part 60, appendix A– 4). Performance test (Method 5 or 29 at 40 CFR part 60, appendix A– 3 or appendix A–8). Performance test (Method 6 or 6c at 40 CFR part 60, appendix A– 4). Visible emission test (Method 22 at 40 CFR part 60, appendix A– 7). 1 The date specified in the state plan can be no later than 3 years after the effective date of approval of a revised state plan or February 7, 2018. 2 All emission limitations are measured at 7 percent oxygen, dry basis at standard conditions. For dioxins/furans, you must meet either the total mass basis limit or the toxic equivalency basis limit. 3 In lieu of performance testing, you may use a CEMS or, for mercury, an integrated sorbent trap monitoring system, to demonstrate initial and continuing compliance with an emissions limit, as long as you comply with the CEMS or integrated sorbent trap monitoring system requirements applicable to the specific pollutant in §§ 60.2710 and 60.2730. As prescribed in § 60.2710(u), if you use a CEMS or integrated sorbent trap monitoring system to demonstrate compliance with an emissions limit, your averaging time is a 30-day rolling average of 1-hour arithmetic average emission concentrations. 4 Incorporated by reference, see § 60.17. TABLE 7 TO SUBPART DDDD OF PART 60—MODEL RULE—EMISSION LIMITATIONS THAT APPLY TO ENERGY RECOVERY UNITS AFTER MAY 20, 2011 [DATE TO BE SPECIFIED IN STATE PLAN] 1 You must meet this emission limitation 2 Using this averaging time 3 For the air pollutant khammond on DSKBBV9HB2PROD with RULES3 Liquid/gas Solids Cadmium ........................... 0.023 milligrams per dry standard cubic meter. Carbon monoxide .............. 35 parts per million dry volume. Dioxins/furans (total mass basis). 2.9 nanograms per dry standard cubic meter. Dioxins/furans (toxic equivalency basis). 0.32 nanograms per dry standard cubic meter. VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 PO 00000 Biomass-0.0014 milligrams per dry standard cubic meter. Coal-0.0017 milligrams per dry standard cubic meter. Biomass-260 parts per million dry volume. Coal-95 parts per million dry volume. Biomass-0.52 nanograms per dry standard cubic meter. Coal-5.1 nanograms per dry standard cubic meter. Biomass-0.12 nanograms per dry standard cubic meter. Coal-0.075 nanograms per dry standard cubic meter. Frm 00071 Fmt 4701 Sfmt 4700 3-run average (collect a minimum volume of 2 dry standard cubic meters). 3-run average (1 hour minimum sample time per run). And determining compliance using this method 3 Performance test (Method 29 at 40 CFR part 60, appendix A–8). Use ICPMS for the analytical finish. Performance test (Method 10 at 40 CFR part 60, appendix A–4). 3-run average (collect a minimum volume of 4 dry standard cubic meter). Performance test (Method 23 at 40 CFR part 60, appendix A–7). 3-run average (collect a minimum volume of 4 dry standard cubic meters). Performance test (Method 23 at 40 CFR part 60, appendix A–7). E:\FR\FM\16APR3.SGM 16APR3 15916 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations TABLE 7 TO SUBPART DDDD OF PART 60—MODEL RULE—EMISSION LIMITATIONS THAT APPLY TO ENERGY RECOVERY UNITS AFTER MAY 20, 2011 [DATE TO BE SPECIFIED IN STATE PLAN] 1—Continued You must meet this emission limitation 2 For the air pollutant Liquid/gas Using this averaging time 3 And determining compliance using this method 3 3-run average (for Method 26, collect a minimum of 120 liters; for Method 26A, collect a minimum volume of 1 dry standard cubic meter). 3-run average (collect a minimum volume of 2 dry standard cubic meters). Performance test (Method 26 or 26A at 40 CFR part 60, appendix A–8). Solids Hydrogen chloride ............. 14 parts per million dry volume. Biomass-0.20 parts per million dry volume. Coal-58 parts per million dry volume. Lead ................................... 0.096 milligrams per dry standard cubic meter. Mercury .............................. 0.0024 milligrams per dry standard cubic meter. Nitrogen oxides ................. 76 parts per million dry volume. Particulate matter filterable 110 milligrams per dry standard cubic meter. Biomass-0.014 milligrams per dry standard cubic meter. Coal-0.057 milligrams per dry standard cubic meter. Biomass-0.0022 milligrams 3-run average (For Method per dry standard cubic 29 and ASTM D6784–02 meter. (Reapproved 2008),4 Coal-0.013 milligrams per collect a minimum voldry standard cubic meter. ume of 2 dry standard cubic meters per run. For Method 30B, collect a minimum sample as specified in Method 30B at 40 CFR part 60, appendix A). Biomass-290 parts per mil- 3-run average (for Method lion dry volume. 7E, 1 hour minimum Coal-460 parts per million sample time per run). dry volume. Biomass-11 milligrams per 3-run average (collect a dry standard cubic meter. minimum volume of 1 Coal-130 milligrams per dry standard cubic dry standard cubic meter. meter). Sulfur dioxide ..................... 720 parts per million dry volume. Fugitive ash ....................... Visible emissions for no more than 5 percent of the hourly observation period. Biomass-7.3 parts per million dry volume. Coal-850 parts per million dry volume. Visible emissions for no more than 5 percent of the hourly observation period. 3-run average (1 hour minimum sample time per run). Three 1-hour observation periods. Performance test (Method 29 at 40 CFR part 60, appendix A–8). Use ICPMS for the analytical finish. Performance test (Method 29 or 30B at 40 CFR part 60, appendix A–8) or ASTM D6784–02 (Reapproved 2008).4 Performance test (Method 7 or 7E at 40 CFR part 60, appendix A–4). Performance test (Method 5 or 29 at 40 CFR part 60, appendix A–3 or appendix A–8) if the unit has an annual average heat input rate less than or equal to 250 MMBtu/ hr; or PM CPMS (as specified in § 60.2710(x)) if the unit has an annual average heat input rate greater than 250 MMBtu/hr. Performance test (Method 6 or 6c at 40 CFR part 60, appendix A–4). Visible emission test (Method 22 at 40 CFR part 60, appendix A–7). khammond on DSKBBV9HB2PROD with RULES3 1 The date specified in the state plan can be no later than 3 years after the effective date of approval of a revised state plan or February 7, 2018. 2 All emission limitations (except for opacity) are measured at 7 percent oxygen, dry basis at standard conditions. For dioxins/furans, you must meet either the total mass basis limit or the toxic equivalency basis limit. 3 In lieu of performance testing, you may use a CEMS or, for mercury, an integrated sorbent trap monitoring system, to demonstrate initial and continuing compliance with an emissions limit, as long as you comply with the CEMS or integrated sorbent trap monitoring system requirements applicable to the specific pollutant in §§ 60.2710 and 60.2730. As prescribed in § 60.2710(u), if you use a CEMS or integrated sorbent trap monitoring system to demonstrate compliance with an emissions limit, your averaging time is a 30-day rolling average of 1-hour arithmetic average emission concentrations. 4 Incorporated by reference, see § 60.17. TABLE 8 TO SUBPART DDDD OF PART 60—MODEL RULE—EMISSION LIMITATIONS THAT APPLY TO WASTE-BURNING KILNS AFTER MAY 20, 2011 [DATE TO BE SPECIFIED IN STATE PLAN] 1 For the air pollutant You must meet this emission limitation 2 Using this averaging time 3 And determining compliance using this method 3 4 Cadmium ........................................ 0.0014 milligrams per dry standard cubic meter. 3-run average (collect a minimum volume of 2 dry standard cubic meters). Performance test (Method 29 at 40 CFR part 60, appendix A–8). VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 PO 00000 Frm 00072 Fmt 4701 Sfmt 4700 E:\FR\FM\16APR3.SGM 16APR3 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations 15917 TABLE 8 TO SUBPART DDDD OF PART 60—MODEL RULE—EMISSION LIMITATIONS THAT APPLY TO WASTE-BURNING KILNS AFTER MAY 20, 2011 [DATE TO BE SPECIFIED IN STATE PLAN] 1—Continued For the air pollutant You must meet this emission limitation 2 Using this averaging time 3 And determining compliance using this method 3 4 Carbon monoxide .......................... 110 (long kilns)/790 (preheater/ precalciner) parts per million dry volume. 1.3 nanograms per dry standard cubic meter. 3-run average (1 hour minimum sample time per run). Performance test (Method 10 at 40 CFR part 60, appendix A–4). 3-run average (collect a minimum volume of 4 dry standard cubic meters). 3-run average (collect a minimum volume of 4 dry standard cubic meters). 3-run average (collect a minimum volume of 1 dry standard cubic meter), or 30-day rolling average if HCl CEMS is being used. Performance test (Method 23 at 40 CFR part 60, appendix A–7). Dioxins/furans (total mass basis) ... Dioxins/furans (toxic equivalency basis). 0.075 nanograms per dry standard cubic meter. Hydrogen chloride .......................... 3.0 parts per million dry volume ... Lead ............................................... 0.014 milligrams per dry standard cubic meter. Mercury .......................................... 0.011 milligrams per dry standard cubic meter. Or .................................................. 58 pounds/million tons of clinker .. Nitrogen oxides .............................. 630 parts per million dry volume .. Particulate matter filterable ............ 13.5 milligrams per dry standard cubic meter. 600 parts per million dry volume .. Sulfur dioxide ................................. 3-run average (collect a minimum volume of 2 dry standard cubic meters). 30-day rolling average .................. 3-run average (for Method 7E, 1 hour minimum sample time per run). 30-day rolling average .................. 3-run average (for Method 6, collect a minimum of 20 liters; for Method 6C, 1 hour minimum sample time per run). Performance test (Method 23 at 40 CFR part 60, appendix A–7). If a wet scrubber or dry scrubber is used, performance test (Method 321 at 40 CFR part 63, appendix A of this part). If a wet scrubber or dry scrubber is not used, HCl CEMS as specified in § 60.2710(j). Performance test (Method 29 at 40 CFR part 60, appendix A–8). Mercury CEMS or integrated sorbent trap monitoring system (performance specification 12A or 12B, respectively, of appendix B and procedure 5 of appendix F of this part), as specified in § 60.2710(j). Performance test (Method 7 or 7E at 40 CFR part 60, appendix A– 4). PM CPMS (as specified in § 60.2710(x)). Performance test (Method 6 or 6c at 40 CFR part 60, appendix A– 4). 1 The date specified in the state plan can be no later than 3 years after the effective date of approval of a revised state plan or February 7, 2018. 2 All emission limitations are measured at 7 percent oxygen (except for CEMS and integrated sorbent trap monitoring system data during startup and shutdown), dry basis at standard conditions. For dioxins/furans, you must meet either the total mass basis limit or the toxic equivalency basis limit. 3 In lieu of performance testing, you may use a CEMS or, for mercury, an integrated sorbent trap monitoring system, to demonstrate initial and continuing compliance with an emissions limit, as long as you comply with the CEMS or integrated sorbent trap monitoring system requirements applicable to the specific pollutant in §§ 60.2710 and 60.2730. As prescribed in § 60.2710(u), if you use a CEMS or integrated sorbent trap monitoring system to demonstrate compliance with an emissions limit, your averaging time is a 30-day rolling average of 1-hour arithmetic average emission concentrations. 4 Alkali bypass and in-line coal mill stacks are subject to performance testing only, as specified in 60.2710(y)(3). They are not subject to the CEMS, integrated sorbent trap monitoring system, or CPMS requirements that otherwise may apply to the main kiln exhaust. khammond on DSKBBV9HB2PROD with RULES3 TABLE 9 TO SUBPART DDDD OF PART 60—MODEL RULE—EMISSION LIMITATIONS THAT APPLY TO SMALL, REMOTE INCINERATORS AFTER MAY 20, 2011 [DATE TO BE SPECIFIED IN STATE PLAN] 1 For the air pollutant You must meet this emission limitation 2 Using this averaging time 3 And determining compliance using this method 3 Cadmium ........................................ 0.95 milligrams per dry standard cubic meter. Performance test (Method 29 at 40 CFR part 60, appendix A–8). Carbon monoxide .......................... 64 parts per million dry volume .... Dioxins/furans (total mass basis) ... 4,400 nanograms per dry standard cubic meter. Dioxins/furans (toxic equivalency basis). 180 nanograms per dry standard cubic meter. Fugitive ash ................................... Visible emissions for no more than 5 percent of the hourly observation period. 3-run average (collect a minimum volume of 1 dry standard cubic meters per run). 3-run average (1 hour minimum sample time per run). 3-run average (collect a minimum volume of 1 dry standard cubic meters per run). 3-run average (collect a minimum volume of 1 dry standard cubic meters). Three 1-hour observation periods VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 PO 00000 Frm 00073 Fmt 4701 Sfmt 4700 E:\FR\FM\16APR3.SGM Performance test (Method 10 at 40 CFR part 60, appendix A–4). Performance test (Method 23 at 40 CFR part 60, appendix A–7). Performance test (Method 23 at 40 CFR part 60, appendix A–7). Visible emissions test (Method 22 at 40 CFR part 60, appendix A– 7). 16APR3 15918 Federal Register / Vol. 84, No. 73 / Tuesday, April 16, 2019 / Rules and Regulations TABLE 9 TO SUBPART DDDD OF PART 60—MODEL RULE—EMISSION LIMITATIONS THAT APPLY TO SMALL, REMOTE INCINERATORS AFTER MAY 20, 2011 [DATE TO BE SPECIFIED IN STATE PLAN] 1—Continued For the air pollutant You must meet this emission limitation 2 Using this averaging time 3 And determining compliance using this method 3 Hydrogen chloride .......................... 300 parts per million dry volume .. Performance test (Method 26 or 26A at 40 CFR part 60, appendix A–8). Lead ............................................... 2.1 milligrams per dry standard cubic meter. 3-run average (For Method 26, collect a minimum volume of 120 liters per run. For Method 26A, collect a minimum volume of 1 dry standard cubic meter per run). 3-run average (collect a minimum volume of 1 dry standard cubic meters). Mercury .......................................... 0.0053 milligrams per dry standard cubic meter. Nitrogen oxides .............................. 190 parts per million dry volume .. Particulate matter (filterable) .......... 270 milligrams per dry standard cubic meter. Sulfur dioxide ................................. 150 parts per million dry volume .. 3-run average (For Method 29 and ASTM D6784–02 (Reapproved 2008),3 collect a minimum volume of 2 dry standard cubic meters per run. For Method 30B, collect a minimum sample as specified in Method 30B at 40 CFR part 60, appendix A). 3-run average (for Method 7E, 1 hour minimum sample time per run). 3-run average (collect a minimum volume of 1 dry standard cubic meters). 3-run average (for Method 6, collect a minimum of 20 liters per run; for Method 6C, 1 hour minimum sample time per run). Performance test (Method 29 at 40 CFR part 60, appendix A–8). Use ICPMS for the analytical finish. Performance test (Method 29 or 30B at 40 CFR part 60, appendix A–8) or ASTM D6784–02 (Reapproved 2008).4 Performance test (Method 7 or 7E at 40 CFR part 60, appendix A– 4). Performance test (Method 5 or 29 at 40 CFR part 60, appendix A– 3 or appendix A–8). Performance test (Method 6 or 6c at 40 CFR part 60, appendix A– 4). 1 The date specified in the state plan can be no later than 3 years after the effective date of approval of a revised state plan or February 7, 2018. 2 All emission limitations (except for opacity) are measured at 7 percent oxygen, dry basis at standard conditions. For dioxins/furans, you must meet either the total mass basis limit or the toxic equivalency basis limit. 3 In lieu of performance testing, you may use a CEMS or, for mercury, an integrated sorbent trap monitoring system, to demonstrate initial and continuing compliance with an emissions limit, as long as you comply with the CEMS or integrated sorbent trap monitoring system requirements applicable to the specific pollutant in §§ 60.2710 and 60.2730. As prescribed in § 60.2710(u), if you use a CEMS or integrated sorbent trap monitoring system to demonstrate compliance with an emissions limit, your averaging time is a 30-day rolling average of 1-hour arithmetic average emission concentrations. 4 Incorporated by reference, see § 60.17. [FR Doc. 2019–05529 Filed 4–15–19; 8:45 am] khammond on DSKBBV9HB2PROD with RULES3 BILLING CODE 6560–50–P VerDate Sep<11>2014 18:25 Apr 15, 2019 Jkt 247001 PO 00000 Frm 00074 Fmt 4701 Sfmt 9990 E:\FR\FM\16APR3.SGM 16APR3

Agencies

ENVIRONMENTAL PROTECTION AGENCY

[Federal Register Volume 84, Number 73 (Tuesday, April 16, 2019)]
[Rules and Regulations]
[Pages 15846-15918]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2019-05529]



[[Page 15845]]

Vol. 84

Tuesday,

No. 73

April 16, 2019

Part III





Environmental Protection Agency





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40 CFR Part 60





Standards of Performance for New Stationary Sources and Emission 
Guidelines for Existing Sources: Commercial and Industrial Solid Waste 
Incineration Units; Technical Amendments; Final Rule

Federal Register / Vol. 84 , No. 73 / Tuesday, April 16, 2019 / Rules 
and Regulations

[[Page 15846]]


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ENVIRONMENTAL PROTECTION AGENCY

40 CFR Part 60

[EPA-HQ-OAR-2003-0119; FRL-9991-32-OAR]
RIN 2060-AT84


Standards of Performance for New Stationary Sources and Emission 
Guidelines for Existing Sources: Commercial and Industrial Solid Waste 
Incineration Units; Technical Amendments

AGENCY: Environmental Protection Agency (EPA).

ACTION: Final rule.

-----------------------------------------------------------------------

SUMMARY: Following requests for clarification of its June 2016 final 
action, the Environmental Protection Agency (EPA) published proposed 
amendments to several provisions of the 2016 New Source Performance 
Standards (NSPS) and Emission Guidelines (EG) for Commercial and 
Industrial Solid Waste Incineration (CISWI). This action finalizes the 
proposed amendments, which provide clarity and address implementation 
issues in the final CISWI NSPS and EG, as well as correcting 
inconsistencies and errors in these provisions.

DATES: This final rule is effective on April 16, 2019. The 
incorporation by reference of certain publications listed in the rule 
is approved by the Director of the Federal Register as of February 7, 
2013.

ADDRESSES: The EPA has established a docket for this action under 
Docket ID No. EPA-HQ-OAR-2003-0119. All documents in the docket are 
listed on the https://www.regulations.gov website. Although listed, 
some information is not publicly available, e.g., confidential business 
information or other information whose disclosure is restricted by 
statute. Certain other material, such as copyrighted material, is not 
placed on the internet and will be publicly available only in hard copy 
form. Publicly available docket materials are available electronically 
through https://www.regulations.gov, or in hard copy at the EPA Docket 
Center, WJC West Building, Room Number 3334, 1301 Constitution Ave. NW, 
Washington, DC. The Public Reading Room hours of operation are 8:30 
a.m. to 4:30 p.m. Eastern Standard Time (EST), Monday through Friday. 
The telephone number for the Public Reading Room is (202) 566-1744, and 
the telephone number for the Docket Center is (202) 566-1742.

FOR FURTHER INFORMATION CONTACT: Dr. Nabanita Modak Fischer, Fuels and 
Incineration Group, Sector Policies and Programs Division (E143-05), 
Environmental Protection Agency, Research Triangle Park, North Carolina 
27711; telephone number: (919) 541-5572; fax number: (919) 541-0516; 
email address: [email protected].

SUPPLEMENTARY INFORMATION: Acronyms and Abbreviations. A number of 
acronyms and abbreviations are used in this preamble. While this may 
not be an exhaustive list, to ease the reading of this preamble and for 
reference purposes, the following terms and acronyms are defined:

ACI air curtain incinerator
CAA Clean Air Act
CEDRI Compliance and Emissions Data Reporting Interface
CEMS Continuous Emissions Monitoring System
CFR Code of Federal Regulations
CISWI Commercial and Industrial Solid Waste Incineration
CO carbon monoxide
COMS Continuous Opacity Monitoring System
CPMS Continuous Parameter Monitoring System
EG Emission Guidelines
EPA U.S. Environmental Protection Agency
ESP electrostatic precipitator
HCl hydrogen chloride
Hg mercury
mg/dscm milligrams per dry standard cubic meter
NAICS North American Industry Classification System
NESHAP National Emission Standards for Hazardous Air Pollutants
NHSM Non-Hazardous Secondary Material(s)
NSPS New Source Performance Standards
NTTAA National Technology Transfer and Advancement Act
OAQPS Office of Air Quality Planning and Standards
OMB Office of Management and Budget
PC Portland Cement
ppmv parts per million by volume
ppmvd parts per million by dry volume
RIN Regulatory Information Number
UMRA Unfunded Mandates Reform Act
U.S.C. United States Code

    Organization of this Document. The following outline is provided to 
aid in locating information in this preamble.

I. General Information
    A. Does this action apply to me?
    B. Where can I get a copy of this document and other related 
information?
    C. Judicial Review
II. Background
    A. What is the statutory authority for taking this action?
    B. Background Information
III. Summary of Final Action
    A. EG 30-Day Rolling Average Provisions
    B. Clarification of Operating Parameter Monitoring for a 
Pollutant's Control When CEMS Are Being Used for Continuous 
Compliance Demonstration for the Pollutant
IV. Public Comments
V. Rationale for Final Amendments to 2016 CISWI Rule
    A. Discussion of Final Technical Amendments
    B. Typographical Errors and Corrections
    C. Environmental, Energy, and Economic Impacts
VI. Statutory and Executive Order Reviews
    A. Executive Order 12866: Regulatory Planning and Review and 
Executive Order 13563: Improving Regulation and Regulatory Review
    B. Executive Order 13771: Reducing Regulations and Controlling 
Regulatory Costs
    C. Paperwork Reduction Act (PRA)
    D. Regulatory Flexibility Act (RFA)
    E. Unfunded Mandates Reform Act (UMRA)
    F. Executive Order 13132: Federalism
    G. Executive Order 13175: Consultation and Coordination With 
Indian Tribal Governments
    H. Executive Order 13045: Protection of Children From 
Environmental Health Risks and Safety Risks
    I. Executive Order 13211: Actions Concerning Regulations That 
Significantly Affect Energy Supply, Distribution, or Use
    J. National Technology Transfer and Advancement Act (NTTAA)
    K. Executive Order 12898: Federal Actions To Address 
Environmental Justice in Minority Populations and Low-Income 
Populations
    L. Congressional Review Act (CRA)

I. General Information

A. Does this action apply to me?

    Categories and entities affected by the final action are those that 
operate CISWI units. The NSPS and EG, herein after referred to as 
``standards,'' for CISWI affect the following categories of sources:

----------------------------------------------------------------------------------------------------------------
                                                                                     Examples of potentially
                Category                             NAICS \1\ code                    regulated entities
----------------------------------------------------------------------------------------------------------------
Any industrial or commercial facility     211, 212, 486.......................  Oil and gas exploration
 using a solid waste incinerator.                                                operations; Mining, pipeline
                                                                                 operators.
                                          221.................................  Utility providers.

[[Page 15847]]

 
                                          321, 322, 337.......................  Manufacturers of wood products;
                                                                                 Manufacturers of pulp, paper,
                                                                                 and paperboard; Manufacturers
                                                                                 of furniture and related
                                                                                 products.
                                          325, 326............................  Manufacturers of chemicals and
                                                                                 allied products; Manufacturers
                                                                                 of plastics and rubber
                                                                                 products.
                                          327.................................  Manufacturers of cement;
                                                                                 Nonmetallic mineral product
                                                                                 manufacturing.
                                          333, 336............................  Manufacturers of machinery;
                                                                                 Manufacturers of transportation
                                                                                 equipment.
                                          423, 44.............................  Merchant wholesalers, durable
                                                                                 goods; Retail trade.
----------------------------------------------------------------------------------------------------------------
\1\ North American Industry Classification System.

    This table is not intended to be exhaustive, but rather provides a 
guide for readers regarding entities likely to be affected by the final 
action. To determine whether your facility will be affected by this 
action, you should examine the applicability criteria in 40 Code of 
Federal Regulations (CFR) 60.2010 of subpart CCCC, 40 CFR 60.2505 of 
subpart DDDD, and 40 CFR 241. If you have any questions regarding the 
applicability of the final action to a particular entity, contact the 
person listed in the preceding FOR FURTHER INFORMATION CONTACT section.

B. Where can I get a copy of this document and other related 
information?

    The docket number for this final action regarding the CISWI 
Technical Amendments is Docket ID No. EPA-HQ-OAR-2003-0119.
    In addition to being available in the docket, an electronic copy of 
this action is available on the internet. Following signature by the 
Administrator, the EPA will post a copy of this final action at https://www.epa.gov/stationary-sources-air-pollution/commercial-and-industrial-solid-waste-incineration-units-ciswi-new. Following 
publication in the Federal Register, the EPA will post the Federal 
Register version and key technical documents at the same website.

C. Judicial Review

    Under Clean Air Act (CAA) section 307(b)(1), judicial review of 
this final rule is available only by filing a petition for review in 
the United States Court of Appeals for the District of Columbia Circuit 
(D.C. Circuit) by June 17, 2019. Under CAA section 307(d)(7)(B), only 
an objection to this final rule that was raised with reasonable 
specificity during the period for public comment can be raised during 
judicial review. Any person who believes the final rule contains 
provisions that were not reasonably forseeable based on the proposed 
rule should submit a Petition for Reconsideration to the Office of the 
Administrator, Environmental Protection Agency, Room 3000, EPA WJC 
South Building, 1200 Pennsylvania Ave. NW, Washington, DC 20460, with a 
copy to the persons listed in the preceding FOR FURTHER INFORMATION 
CONTACT section, and the Associate General Counsel for the Air and 
Radiation Law Office, Office of General Counsel (Mail Code 2344A), 
Environmental Protection Agency, 1200 Pennsylvania Ave. NW, Washington, 
DC 20460. Note, under CAA section 307(b)(2), the requirements 
established by this final rule may not be challenged separately in any 
civil or criminal proceedings brought by the EPA to enforce these 
requirements.

II. Background

A. What is the statutory authority for taking this action?

    Section 129 of the CAA requires the EPA to establish NSPS and EG 
pursuant to sections 111 and 129 of the CAA for new and existing solid 
waste incineration units located at commercial and industrial 
facilities. This action amends standards developed under these 
authorities.

B. Background Information

    On March 21, 2011, the EPA promulgated revised NSPS and EG for 
CISWI units (i.e., solid waste incineration units located at commercial 
or industrial facilities). Following that action, the Administrator 
received petitions for reconsideration that identified certain issues 
that warranted further opportunity for public comment. In response to 
the petitions, the EPA reconsidered, proposed revisions to, and 
requested comment on several provisions of the March 2011 final NSPS 
and EG for CISWI units. These proposed revisions were published on 
December 23, 2011 (76 FR 80452).
    On February 7, 2013, the EPA finalized revisions to the CISWI NSPS 
and EG (78 FR 9112). In that final action, the EPA made additional 
revisions in response to comments that had not been proposed in the 
December 23, 2011, Federal Register document. Subsequently, the EPA 
received petitions for reconsideration of the final 2013 action. These 
petitions assert that the public did not have sufficient opportunity to 
comment on some of the provisions contained in that final rule. In 
response, the EPA proposed to reconsider four provisions of the 2013 
final revisions to the NSPS and EG for CISWI units (80 FR 3018, January 
21, 2015). The EPA took final action on that proposal on June 23, 2016 
(81 FR 40956). We will refer to this final CISWI rule, as revised 
through June 2016, as the 2016 CISWI rule.
    Following promulgation of the 2016 CISWI rule, the EPA received 
requests from industry stakeholders and implementing agencies to 
clarify various issues with implementation of the standards. In 
addition, the EPA identified certain testing and monitoring issues and 
inconsistencies within the rules that required further clarification or 
correction. On June 15, 2018, the EPA proposed amendments to several 
provisions of the 2016 CISWI rule to address these issues (83 FR 
28068). In addition, the EPA identified additional regulatory 
provisions, beyond those raised by the requests from industry 
stakeholders and implementing agencies, that require clarification and 
editorial correction to address inconsistencies and errors in the final 
rules. In this document, the EPA is taking final action on the June 
2018 proposal by promulgating clarifying changes and corrections to the 
2016 CISWI rule.
    For more detailed background and additional information on how this 
rule is related to other CAA combustion rules issued under CAA section 
112 and the Resource Conservation and Recovery Act definition of solid 
waste, refer to the prior final actions discussed above (76 FR 15704, 
March 21, 2011; 78 FR 9112, February 7, 2013).

III. Summary of Final Action

    In this final rule, we are amending the 2016 CISWI rule to address 
certain

[[Page 15848]]

issues raised by industry stakeholders and implementing agencies, as 
well as to address other issues identified during implementation of the 
CISWI rule. Provisions affected by the amendments are: (1) Alternative 
equivalent emission limit for mercury (Hg) for the waste-burning kiln 
subcategory; (2) timing of initial test and initial performance 
evaluation; (3) extension of the date by which electronic data 
reporting requirements must be met; (4) clarification of non-delegated 
authorities; (5) demonstration of initial and continuous compliance 
when using a continuous emissions monitoring system (CEMS); (6) 
continuous opacity monitoring requirements; (7) other CEMS 
requirements; (8) clarification of skip testing requirements; (9) 
deviation reporting requirements for continuous monitoring data; and 
(10) clarification of air curtain incinerator (ACI) requirements. In 
addition to these provisions, we are also correcting minor 
typographical errors identified in the rule as noted in section V.B of 
this preamble.
    This final rule provides meaningful burden reduction by providing 
regulated facilities additional time to complete initial compliance 
demonstrations and by allowing facilities to comply with production-
based emission limits in lieu of the concentration-based limits in the 
2016 CISWI rule. Specifically, cement kilns would be allowed to report 
mercury emissions on a mass-based production basis (pounds per million 
(lb/MM) ton of clinker) in lieu of reporting on a concentration based 
limit (milligrams per dry standard cubic meter (mg/dscm)). This 
alternative provision may result in lower costs for the cement industry 
by making the format of the mercury emission limits consistent with the 
Portland Cement NESHAP (PC NESHAP). Further, the rule adds 
flexibilities in the compliance demonstration process by extending the 
timeline for performance evaluation tests from 60 days to 180 days and 
allows facilities to use CEMS for demonstrating initial compliance. 
These provisions may lower compliance testing costs as stack testing 
could be avoided if the facilities use CEMS. Moreover, facilities with 
CEMS will not be required to retest in the event of original stack 
testing failure.
    The EPA is taking final action on all the amendments discussed in 
the June 15, 2018 (83 FR 28068), proposed rule and also making two 
additional changes to clarify provisions of the 2016 CISWI rule. A more 
detailed discussion of the rationale behind the technical amendments is 
located in section V.A of this preamble.

A. EG 30-Day Rolling Average Provisions

    A commenter noted that the 30-day rolling average language found in 
40 CFR 60.2710(c) was inconsistent with how the averaging period is 
defined elsewhere in the rule because it contained the additional 
qualifier ``over the previous 30 days of operation.'' The EPA realizes 
that units may not necessarily operate continuously, and that valid 
operating data exclude periods when a unit is not operating. The EPA 
has removed the phrase ``over the previous 30 days of operation'' from 
40 CFR 60.2710(c) to be consistent with similar provisions elsewhere in 
the EG and in the NSPS.

B. Clarification of Operating Parameter Monitoring for a Pollutant's 
Control When CEMS are Being Used for Continuous Compliance 
Demonstration for the Pollutant

    The EPA is clarifying that continuous operating parameter 
monitoring is not required when CEMS are used for direct and continuous 
compliance demonstrations for the pollutant. See section V.A.5 of this 
preamble for further discussion.

IV. Public Comments

    Public comments on the proposed rule and the EPA's responses to 
these comments are addressed in a separate response to comment 
document, available in the docket for this action at Docket ID No. EPA-
HQ-OAR-2003-0119.

V. Rationale for Final Amendments to 2016 CISWI Rule

A. Discussion of Final Technical Amendments

    This section of the preamble explains the basis for the changes in 
this final rule.
1. Alternative Equivalent Emission Limit for Hg for the Waste-Burning 
Kiln Subcategory
    The December 23, 2011, proposed CISWI reconsideration rule preamble 
discussed and presented equivalent emission limits for waste-burning 
kilns expressed on a production basis (76 FR 80458). In the February 
2013 CISWI final reconsideration rule preamble, the EPA again included 
these equivalent production-based limits, but at that time the EPA 
decided not to codify these within the rule text. In the process of 
approving state plans to implement the CISWI EG, the EPA has recognized 
that there is a benefit to some affected sources and implementing 
agencies in codifying the emission limit for Hg for waste-burning kilns 
expressed as a production-based limit (i.e., lb/MM ton clinker) as an 
alternative equivalent standard to the existing concentration-based 
standard (i.e., mg/dscm), because this is the format of the Hg 
standards found in the PC NESHAP. The EPA strives to make compliance 
with both CISWI standards and the PC NESHAP as streamlined and 
consistent as possible to facilitate compliance with both standards 
because these sources (and energy recovery units) must comply with the 
CISWI standard when they are combusting solid waste and must comply 
with the PC NESHAP or Boiler Maximum Achievable Control Technology 
standards, as applicable, when combusting nonwaste materials. Having an 
equivalent emission limit in the same units as the PC NESHAP will, 
thus, aid affected sources in demonstrating compliance with both 
standards, and will aid implementing agencies in enforcing the 
standards.
    As discussed in 2011 and repeated in 2013 (78 FR 9122-3, February 
7, 2013), the Hg emission limit of 58 lb/MM ton clinker and 21 lb/MM 
ton clinker for existing and new sources, respectively, are equivalent 
to the concentration-based Hg standards of 0.011 mg/dscm and 0.0037 mg/
dscm within the currently published 2016 CISWI rule. To facilitate use 
of the equivalent production-based emission limits, the EPA is adding 
these emission limits to the emission limitation tables, and including 
recordkeeping, calculation, and reporting requirements for clinker 
production rate as necessary. The regulatory provisions and 
calculations being made final are consistent with those found in the PC 
NESHAP, see 40 CFR 63, subpart LLL.
2. Timing of Initial Test and Initial Performance Evaluation
    The current CISWI NSPS and EG (2016 CISWI Rule) require affected 
sources to conduct a performance evaluation of each continuous 
monitoring system within 60 days of installation of the monitoring 
system (see 40 CFR 60.2135 and 60.2700). The rule also allows up to 180 
days from the final compliance date for affected sources to conduct an 
initial performance test. The EPA received questions from implementing 
agencies asking whether these requirements can be synchronized to 
prevent duplicate testing requirements because the continuous 
monitoring system performance evaluation would require an emissions 
test being conducted at the same time regardless. We recognize that

[[Page 15849]]

the requirement to conduct a performance evaluation within 60 days of 
installation could present a situation for sources where the deadline 
for conducting the performance evaluation would precede the deadline 
for conducting the initial performance test. The EPA did not intend to 
require sources to conduct duplicative initial performance tests, and 
we see a benefit to sources and implementing agencies to be able to 
schedule and conduct both of these demonstrations at the same time. 
Therefore, the EPA is adjusting the timing of the continuous monitoring 
system initial performance evaluation to allow 180 days from 
installation to match the schedule which is allowed for conducting the 
initial performance test. The EPA has determined that making these 
timelines consistent (i.e., 180 days from installation) will streamline 
compliance demonstrations and prevent possible duplicative testing 
requirements.
3. Extension of Electronic Data Reporting Requirement
    In this action, the EPA is extending the electronic reporting 
requirement dates found in 40 CFR 60.2235(a) and 60.2795(a). The 
electronic reporting provisions promulgated in CISWI require submittal 
of initial, annual, and deviation reports electronically through the 
EPA's Compliance and Emissions Data Reporting Interface (CEDRI), which 
is accessed through the EPA's Central Data Exchange. The existing rule 
provides that the requirement for electronic submittal will take effect 
once the relevant forms have been available in CEDRI for 90 calendar 
days. As stated in the CISWI reconsideration (81 FR 40956), the EPA 
intended to make the requirements of the CISWI rule consistent with the 
Electronic Reporting and Recordkeeping Requirements for New Source 
Performance Standards, which was proposed on March 20, 2015 (80 FR 
15100).\1\ However, the CISWI reconsideration final rule was published 
on June 23, 2016 (81 FR 40956), before the Electronic Reporting and 
Recordkeeping Requirements for New Source Performance Standards rule 
\2\ was finalized and did not take into account comments received on 
that rule.
---------------------------------------------------------------------------

    \1\ Originally, the Electronic Reporting and Recordkeeping 
Requirements for New Source Performance Standards rule included 
CISWI as one of the affected subparts. However, because the CISWI 
reconsideration package was proposed at nearly the same time as that 
rule, CISWI was removed as an affected subpart, and the language 
associated with the Electronic Reporting and Recordkeeping 
Requirements for New Source Performance Standards rule was inserted 
into the CISWI reconsideration proposal.
    \2\ This final rule was signed on December 21, 2016, but was 
withdrawn from the Office of the Federal Register prior to 
publication.
---------------------------------------------------------------------------

    The extension for CISWI units in this action is consistent with the 
EPA's approach to electronic reporting outlined in the Electronic 
Reporting and Recordkeeping Requirements for New Source Performance 
Standards final rule.\3\ This approach has also been used in recent EPA 
rulemakings (e.g., National Emissions Standards for Hazardous Air 
Pollutants for Chemical Recovery Combustion Sources at Kraft, Soda, 
Sulfite, and Stand-Alone Semi Chemical Pulp Mills, 82 FR 47328 (October 
11, 2017); National Emissions Standards for Hazardous Air Pollutants: 
Publicly Owned Treatment Works Residual Risk and Technology Review, 82 
FR 49513, October 26, 2017). The extension requires electronic 
submission of initial, annual, and deviation reports 2 years from 
publication of the final rule or 1 year after the reporting form 
becomes available in CEDRI, whichever date is later. This extension is 
necessary to allow the EPA time to develop and adequately test the new 
forms and for regulated entities to become familiar with the forms and 
reprogram systems that collect data for periodic reports once the forms 
are available. The extension also allows state, local, and tribal 
agencies more time to implement electronic reporting and to make any 
needed permit revisions to accommodate electronic reporting and allows 
for development of third-party software to populate the reporting 
forms.
---------------------------------------------------------------------------

    \3\ The prepublication version of the final rule is available at 
https://www.epa.gov/sites/production/files/2017-04/documents/e-reporting-nsps-final-rule-pre-publication.pdf. Accessed November 15, 
2018.
---------------------------------------------------------------------------

4. Clarification of Non-Delegated Authorities
    In this action, the EPA is making final corrections to the 
authorities listed in 40 CFR 60.2030(c). Specifically, the reference to 
40 CFR 60.2125(j) is an outdated reference to previously proposed, but 
never promulgated, performance test waiver provisions. These provisions 
were included in the June 4, 2010, CISWI proposed rule (see 75 FR 
31975), but were not made final in the March 21, 2011, final rule (see 
76 FR 15752-3). This reference was inadvertently not included in the 
final rule to reflect that the proposed 40 CFR 60.2125(j) was not 
finalized. Another correction relates to the provisions of 40 CFR 
60.2030(c)(10) that require obtaining a determination from the EPA of 
whether a qualifying small power facility or cogeneration facility is 
combusting homogeneous waste. We intended to remove these provisions in 
the 2013 CISWI final rule as part of the removal of the definition of 
homogeneous waste (see 78 FR 9124, February 7, 2013). As discussed in 
the preamble to the February 7, 2013, final revision action, the EPA 
determined that the proposed ``definition and provisions could be 
interpreted in a manner that would be unduly restrictive.'' Therefore, 
the EPA did not include a definition of ``homogeneous waste'' in the 
final CISWI rule and the Agency stated it was (without actually 
amending the CFR text to reflect its intent) ``removing the requirement 
that qualifying small power producers and qualifying cogeneration 
facilities that combust solid waste obtain a determination from the EPA 
that such waste is homogeneous.'' Id. Accordingly, the EPA is removing 
paragraph 40 CFR 60.2030(c)(10). While no other authorities have been 
added or removed from this list, the EPA is making minor revisions to 
streamline the section by removing the reserved subparagraphs (i.e., 
(5) and (10)) and renumbering the subparagraphs sequentially.
    In this action, we are also clarifying, with respect to the EG, 
which authorities will not be delegated. Language in 40 CFR 60.2542 
simply contains a reference to the analogous paragraph (40 CFR 
60.2030(c)) within the CISWI NSPS. However, since the CISWI NSPS 
applies to new sources, applicability of these non-delegated 
authorities to state plans implementing the emission guidelines for 
existing sources was unclear to implementing agencies. To remove this 
confusion, we have eliminated the cross reference to 40 CFR 60.2030(c) 
and have instead provided the specific details on which authorities 
will not be delegated within the text of 40 CFR 60.2542. The final list 
of authorities in 40 CFR 60.2542 matches the updated list found in 40 
CFR 60.2030(c), with the appropriate adjustments made to subpart 
section cross references.
5. Demonstrating Initial Compliance When Using CEMS
    As the EPA noted at proposal, (see 83 FR 28072, June 15, 2018), the 
provisions regarding CEMS monitoring for demonstrating initial 
compliance are inconsistent and somewhat unclear. The final CISWI rules 
require some sources to demonstrate compliance using CEMS, and allow 
the option for any source to use CEMS to demonstrate compliance ``with 
any of the emission limits of this subpart'' (see 40 CFR 60.2145(u) and 
60.2710(u)). However, for most of the

[[Page 15850]]

paragraphs containing the pollutant-specific CEMS requirements, the 
language was unclear on whether these demonstrations were applicable to 
demonstrating initial compliance, with the exception of carbon monoxide 
(CO). The EPA's intent was to allow CEMS for demonstrating initial 
compliance for any pollutant (i.e., with any of the emission limits of 
this subpart). To express the EPA's intent of providing this 
flexibility for compliance demonstration more clearly, we have revised 
several sections of the rule in this final action. For example, the 
initial compliance requirements in 40 CFR 60.2135 and 60.2700 have been 
revised to also reflect use of CEMS data as an initial compliance 
demonstration alternative to an emissions test, provided that the 
initial CEMS performance evaluation has been conducted prior to 
collecting CEMS data used for the initial performance test. Likewise, 
language surrounding the CEMS requirements found in 40 CFR 60.2145, 
60.2165, 60.2710, and 60.2730, and the emission limitation tables, has 
been revised and streamlined to clarify that CEMS data may be used to 
demonstrate compliance (i.e., initial and continuing) with the 
standards.
    In addition to clarifying initial compliance demonstrations using 
CEMS, commenters suggested a similar issue occurs with continuous 
parametric monitoring requirements for sources that use CEMS to 
demonstrate compliance for a pollutant. It was not the EPA's intent to 
require duplicative operating parameter monitoring for pollutants if 
emissions for the pollutants are directly and continuously monitored 
using CEMS. Therefore, the EPA has clarified the CEMS requirements in 
40 CFR 60.2165 and 40 CFR 60.2730 to indicate that sources using CEMS 
to monitor for a pollutant are not required to monitor the associated 
operating parameters unless it is necessary for compliance with the 
monitoring requirements of another regulated pollutant. This 
clarification is not removing any monitoring requirements, but only 
acknowledging that direct pollutant emission measurement with CEMS is a 
suitable, if not even preferential, alternative to continuous parameter 
monitoring.
6. Clarification of Continuous Opacity Monitoring System (COMS) 
Requirements
    In addition to the clarifications to CEMS provisions, we are also 
revising 40 CFR 60.2145(i) and 60.2710(i) to clarify our intent 
regarding the types of units required to install COMS and to make it 
consistent with the COMS monitoring requirement language found in 40 
CFR 60.2165(m) and 60.2730(m), respectively. We are adding language 
clarifying that energy recovery units between 10 and 250 million 
British thermal units/hour design heat input that are equipped with 
electrostatic precipitators (ESP), particulate matter CEMS, or 
particulate matter continuous parameter monitoring systems (CPMS) are 
not required to additionally install and operate COMS because these 
units have an air pollution control device that has continuous 
parameter monitoring requirements or are using continuous particulate 
matter monitoring compliant with provisions within the rule already 
(see 40 CFR 60.2145(q), for example). The rule currently excludes the 
COMS requirement for energy recovery units using other types of 
particulate matter control devices or that use particulate matter CEMS 
for continuous particulate matter monitoring, but inadvertently omitted 
ESPs and particulate matter CPMS from the list. Therefore, we are 
adding ``electrostatic precipitator'' and ``particulate matter CPMS'' 
to the list (that currently includes CO wet scrubbers and fabric 
filters) found in 40 CFR 60.2165(m) and 60.2730(m) as types of units 
that do not require COMS. As a further clarification, we are also 
amending the text to 40 CFR 60.2145(i) and 60.2710(i) to clearly 
specify that the COMS requirement is applicable to units within the 
specified size range ``that do not use a wet scrubber, fabric filter 
with bag leak detection system, an electrostatic precipitator, 
particulate matter CEMS, or particulate matter CPMS.''
7. Clarification of Other CEMS Requirements
    In addition to the CEMS-related requirements discussed above, the 
EPA is making two other CEMS-related clarifications in this final rule: 
(1) To not require CO CEMS for new waste-burning kilns; and (2) to 
remove outdated notification requirements when particulate matter CEMS 
are being used. For the CO CEMS issue, the rule as finalized in 
February 7, 2013, erroneously includes a requirement at 40 CFR 
60.2145(j) for new waste-burning kilns to demonstrate compliance with 
CO emission limits using CEMS. This issue was not corrected in the 2016 
final rules and is inconsistent with the requirements found in Table 7 
to 40 CFR 60, subpart CCCC, and with the EPA's intent to remove CO CEMS 
requirements for new CISWI sources, as stated in the February 7, 2013, 
final CISWI rules (see 78 FR 9120). Carbon monoxide CEMS are allowed as 
an alternative compliance demonstration, but sources who adopt this 
alternative are not required to conduct annual testing using EPA Method 
10. To make this clarification, the EPA is revising 40 CFR 60.2145(j) 
to reflect that CO is one of the pollutants for which an annual test is 
required and removing CO from the list of pollutants requiring CEMS for 
demonstrating compliance.
    Regarding the removal of outdated notification requirements when 
particulate matter CEMS are used, the EPA is removing the outdated 
requirements to notify the Administrator prior to beginning and 
stopping use of an optional particulate matter CEMS. These provisions 
are 40 CFR 60.2165(n)(1) and (2), and 40 CFR 60.2730(n)(1) and (2). 
These provisions are an inadvertent holdover from model provisions from 
a prior rule. CEMS technology and application has progressed to an 
extent that these notifications are no longer needed or desired by the 
EPA. Furthermore, these notifications do not appear in the reporting 
requirements outlined in the reporting requirement tables (Table 4 to 
40 CFR part 60, subpart CCCC and Table 3 to 40 CFR part 60, subpart 
DDDD), nor the other notification requirements, so they introduced an 
unintended inconsistency within the rule. To resolve this, we are 
deleting the current subparagraphs (1) and (2) of these sections and 
renumbering the remaining subparagraphs sequentially to streamline 
these requirements.
8. Clarification of Reduced Testing Requirements
    It has come to the EPA's attention that there is confusion 
regarding how reduced testing is applied after a source has 
demonstrated good performance and has skipped testing for 2 years (see 
40 CFR 60.2155 and 60.2720). Stakeholders suggest that the current 
CISWI rule language would have a good-performing source return to an 
annual testing schedule after being able to skip testing for 2 years, 
with no opportunity for additional reduced testing. It was not the 
EPA's intent to only offer this allowance once when developing these 
provisions. To the contrary, the EPA intended this allowance to be 
available for as long as good performance could be reaffirmed with 
testing every 3 years instead of annually (see 76 FR 15714, March 21, 
2011). The intended sequence of testing consisted of two consecutive 
annual tests showing 75 percent or less of the applicable standard is 
achieved; followed by 2 years of testing being skipped; followed by an 
annual test showing that 75 percent of the standard is achieved; 
followed by 2 years of

[[Page 15851]]

testing being skipped; etc. In other words, starting with the initial 
compliance test (first year), for the first and second years, a source 
would perform compliance testing; for the third and fourth years, the 
source could skip testing (if both the first and second-year results 
showed that the source achieves 75 percent or less of the applicable 
standard); for the fifth year a source would perform compliance 
testing; for the sixth and seventh years, the source could skip testing 
(if the fifth-year results showed that the source achieves 75 percent 
or less of the applicable standard); for the eighth year, a source 
would perform compliance testing, and so on. Since the promulgation of 
these standards, these skip testing provisions have been refined and 
promulgated during regulatory development efforts in the CAA section 
129 rulemakings for sewage sludge incinerators (40 CFR part 60, 
subparts LLLL and MMMM). In this action, the EPA is clarifying the 
ongoing allowance for reduced testing provisions we intended, based 
largely on language used in the recent sewage sludge incinerator rule 
(see 81 FR 26039, April 29, 2016).
9. Clarification of Deviation Reporting Requirements for Continuous 
Monitoring Data
    The EPA has become aware of some unclear requirements in the 
deviation reporting requirements of 40 CFR 60.2215(a) and 60.2775(a). 
In particular, the requirements for continuously measured parameters or 
emissions using CEMS are not clearly outlined within these sections. 
While these provisions are clear for 3-hour average parameters and 
performance testing, the EPA recognizes that 30-day averages allowed 
for energy recovery units and particulate matter CEMS were 
inadvertently omitted, as well as requirements for any other 30-day 
average measured using CEMS that deviated from an emission limit. The 
EPA is adding language to these paragraphs to clarify that deviations 
for these other operating parameters or CEMS measurements that deviate 
from an operating limit or emissions limitation must be included in a 
deviation report.
10. Clarification of ACI Requirements
    Since promulgation of the 2016 CISWI final rule, the EPA has 
received various questions from implementing agencies regarding the 
applicability of CISWI to ACI. While the limited requirements of ACIs 
burning only wood waste, clean lumber, or a mixture of wood waste, 
clean lumber, and/or yard waste are defined within the rule, ACIs' 
status as a CISWI-affected source is unclear to some implementing 
agencies as they work to prepare state plans and negative declarations 
because of confusing language in the 2016 CISWI Rule. See 40 CFR 
60.2550. Specifically, the section of the EG addressing the units 
subject to the final CISWI rule includes a reference to ACI in 40 CFR 
60.2550(a)(1), but 40 CFR 60.2550(a)(2) further states that only units 
that meet the definition of a CISWI unit are subject to the final rule, 
and ACIs do not meet the regulatory definition of a CISWI unit.\4\
---------------------------------------------------------------------------

    \4\ The phrasing of the regulations at 40 CFR 60.2010 and 
60.2015 of the NSPS similarly confuse the applicability of the final 
CISWI rule to new ACIs located at commercial and industrial 
facilities.
---------------------------------------------------------------------------

    Notwithstanding that provision, the record demonstrates that the 
EPA considers ACIs located at commercial and industrial facilities and 
otherwise meeting the definition of an ACI as being CISWI-affected 
sources. See CAA section 129(g)(1)(C) (defining ACIs) and 40 CFR 
60.2245-2260 of the NSPS and 60.2810-2870 of the EG (setting forth the 
CISWI EG requirements applicable to ACI). Facilities can have CISWI-
affected ACIs even if they do not have CISWI units located at the 
facility. If an ACI begins burning solid waste as defined in the Non 
Hazardous Secondary Materials rule (see 40 CFR part 241) in addition 
to, or instead of, wood waste, clean lumber, or a mixture of wood 
waste, clean lumber, and/or yard waste, it is a solid waste 
incineration unit that is subject to the applicable numerical emission 
standards contained in CISWI or another CAA section 129 standard, 
depending on the type of waste combusted (e.g., such as a unit burning 
more than 30-percent municipal solid waste would be a municipal solid 
waste incineration unit instead of a CISWI unit).
    The EPA's intent is further demonstrated in a response to comment 
on title V permitting requirements for ACIs in the preamble to the 
March 21, 2011, final CISWI rule (76 FR 15741):
    Commenters are correct that ACIs are not solid waste incineration 
units pursuant to CAA section 129(g)(1)(C), but that is only correct if 
the units ``only burn wood wastes, yard wastes and clean lumber and 
[they] * * * comply with opacity limitations to be established by the 
Administrator by rule.'' The EPA has established opacity limitations 
for ACIs pursuant to CAA sections 111 and 129.
    Pursuant to CAA section 502(a), sources subject to standards or 
regulations under CAA section 111 must obtain a title V permit; 
therefore, ACIs are required to obtain a title V permit. As commenters 
note, the EPA may exempt minor and area sources from the requirement to 
obtain a title V permit, but the EPA must first determine that 
compliance with title V requirements is ``impracticable, infeasible, or 
unnecessarily burdensome'' for the sources before exempting them (CAA 
section 502(a)). The EPA has not made the necessary finding pursuant to 
CAA section 502(a) for ACIs in any of the CAA section 129 rulemakings, 
and we believe that ACIs exist at CAA section 129 facilities other than 
at the commercial and industrial facilities subject to this final rule. 
Because we think it is important to treat all ACIs in the same manner, 
we decline to consider a title V exemption for minor and area source 
ACIs at commercial and industrial facilities.
    As the record demonstrates, the EPA determined that ACIs located at 
commercial and industrial facilities are CISWI-affected sources that 
must be included in state plans and regulated consistent with the final 
CISWI standards applicable to such units. To address the uncertainty 
created by the CISWI rule, the EPA is clarifying the affected source 
status of ACIs by revising the regulations to make clear that ``air 
curtain incinerators'' do not need to meet the definition of a ``CISWI 
unit'' to be subject to the CISWI rule (40 CFR 60.2010 of the NSPS and 
40 CFR 60.2500 and 60.2550 of the EG).

B. Typographical Errors and Corrections

    In this action, we are also revising the final rule to correct 
minor typographical errors and clarify provisions that are unclear. The 
list of these changes is included in the Typographical Errors and 
Corrections for Final Technical Amendments memorandum in Docket ID No. 
EPA-OAR-HQ-2003-0119.

C. Environmental, Energy, and Economic Impacts

    This action makes technical and clarifying corrections to aid in 
implementation and compliance, but does not make substantive changes to 
the February 7, 2013, final CISWI rule (78 FR 9112).\5\ As such, there 
are no environmental, energy, or economic impacts associated with this 
final action. The impacts associated with the CISWI rule were discussed 
in detail in

[[Page 15852]]

the February 7, 2013, final CISWI rule document.
---------------------------------------------------------------------------

    \5\ The June 23, 2016, final CISWI rule amendments (81 FR 40956) 
also did not entail any environmental, energy or economic impacts, 
and therefore the February 7, 2013, final CISWI rule presents the 
impacts associated with the CISWI rule.
---------------------------------------------------------------------------

VI. Statutory and Executive Order Reviews

    Additional information about these statutes and Executive Orders 
can be found at https://www.epa.gov/laws-regulations/laws-and-executive-orders.

A. Executive Order 12866: Regulatory Planning and Review and Executive 
Order 13563: Improving Regulation and Regulatory Review

    This action is not a significant regulatory action and was 
therefore not submitted to the Office of Management and Budget (OMB) 
for review.

B. Executive Order 13771: Reducing Regulations and Controlling 
Regulatory Costs

    This action is considered an Executive Order 13771 deregulatory 
action. This final rule provides meaningful burden reduction by 
providing additional regulatory flexibilities that address several 
implementation issues raised by the stakeholders.

C. Paperwork Reduction Act (PRA)

    This action does not impose any new information collection burden 
under the PRA. OMB has previously approved the information collection 
activities contained in the existing regulations and has assigned OMB 
Control number 2060-0662 for 40 CFR part 60, subpart CCCC, and OMB 
Control number 2060-0664 for 40 CFR part 60, subpart DDDD. This action 
is believed to result in no changes to the information collection 
requirements of the 2016 CISWI rule, so that the information collection 
estimate of project cost and hour burden from the 2016 CISWI Rule have 
not been revised.

D. Regulatory Flexibility Act (RFA)

    I certify that this action will not have a significant economic 
impact on a substantial number of small entities under the RFA. In 
making this determination, the impact of concern is any significant 
adverse economic impact on small entities. An agency may certify that a 
rule will not have a significant economic impact on a substantial 
number of small entities if the rule relieves regulatory burden, has no 
net burden, or otherwise has a positive economic effect on the small 
entities subject to the rule. This final rule will not impose any new 
requirements on any entities because it does not impose any additional 
regulatory requirements relative to those specified in the 2016 CISWI 
rule, which also did not impose any additional regulatory requirements 
beyond those specified in the February 2013 final CISWI rule. The 
February 2013 final CISWI rule was certified as not having a 
significant economic impact on a substantial number of small entities. 
We have, therefore, concluded that this action will have no net 
regulatory burden for all directly regulated small entities.

E. Unfunded Mandates Reform Act (UMRA)

    This action does not contain any unfunded mandate as described in 
UMRA, 2 U.S.C. 1531-1538, and does not significantly or uniquely affect 
small governments. The action imposes no enforceable duty on any state, 
local, or tribal governments, or the private sector.

F. Executive Order 13132: Federalism

    This action does not have federalism implications. It will not have 
substantial direct effects on the states, on the relationship between 
the national government and the states, or on the distribution of power 
and responsibilities among the various levels of government.

G. Executive Order 13175: Consultation and Coordination With Indian 
Tribal Governments

    This action does not have tribal implications as specified in 
Executive Order 13175. The EPA is not aware of any CISWI in Indian 
country or owned or operated by Indian tribal governments. The CISWI 
aspects of this rule may, however, invoke minor indirect tribal 
implications to the extent that entities generating solid wastes on 
tribal lands could be affected. Thus, Executive Order 13175 does not 
apply to this action.

H. Executive Order 13045: Protection of Children From Environmental 
Health Risks and Safety Risks

    The EPA interprets Executive Order 13045 as applying to those 
regulatory actions that concern environmental health or safety risks 
that the EPA has reason to believe may disproportionately affect 
children, per the definition of ``covered regulatory action'' in 
section 2-202 of the Executive Order. This action is not subject to 
Executive Order 13045 because it does not concern an environmental 
health risk or safety risk.

I. Executive Order 13211: Actions Concerning Regulations That 
Significantly Affect Energy Supply, Distribution, or Use

    This action is not subject to Executive Order 13211 because it is 
not a significant regulatory action under Executive Order 12866.

J. National Technology Transfer and Advancement Act (NTTAA)

    This rulemaking does not involve technical standards.

K. Executive Order 12898: Federal Actions To Address Environmental 
Justice in Minority Populations and Low-Income Populations

    The EPA believes that this action does not have disproportionately 
high and adverse human health or environmental effects on minority 
populations, low-income populations, and/or indigenous peoples, as 
specified in Executive Order 12898 (58 FR 7629, February 16, 1994).
    It does not affect the level of protection provided to human health 
or the environment. The final corrections do not relax the control 
measures on sources regulated by the 2016 CISWI rule, which also did 
not relax any control measures on sources regulated by the February 
2013 final CISWI rule. Therefore, this final action will not cause 
emissions increases from these sources. The February 2013 final CISWI 
rule reduced emissions of all the listed toxics emitted from this 
source, thereby helping to further ensure against any 
disproportionately high and adverse human health or environmental 
effects on minority or low-income populations.

L. Congressional Review Act (CRA)

    This action is subject to the CRA, and the EPA will submit a rule 
report to each House of the Congress and to the Comptroller General of 
the United States. This action is not a ``major rule'' as defined by 5 
U.S.C. 804(2).

List of Subjects in 40 CFR Part 60

    Environmental protection, Administrative practice and procedure, 
Air pollution control, Hazardous substances, Incorporation by 
reference.

    Dated: March 18, 2019.
Andrew R. Wheeler,
Administrator.
    For the reasons stated in the preamble, the Environmental 
Protection Agency is amending title 40, chapter I, of the Code of 
Federal Regulations as follows:

PART 60--STANDARDS OF PERFORMANCE FOR NEW STATIONARY SOURCES

0
1. The authority citation for part 60 continues to read as follows:

    Authority:  42 U.S.C. 7401, et seq.


Sec.  60.17   [Amended]

0
2. Amend Sec.  60.17 by:

[[Page 15853]]

0
a. In paragraph (g)(14), by removing ``60.2710(s), (t), and (w),''and 
adding, it its place, ``60.2710(s) and (t),''; and
0
b. In paragraph (h)(190), by removing ``tables 1, 5,'' and adding, in 
its place, ``tables 5,''.

0
3. Revise subpart CCCC to read as follows:
Sec.
Subpart CCCC--Standards of Performance for Commercial and Industrial 
Solid Waste Incineration Units

Introduction

60.2000 What does this subpart do?
60.2005 When did this subpart become effective?

Applicability

60.2010 Does this subpart apply to my incineration unit?
60.2015 What is a new incineration unit?
60.2020 What combustion units are exempt from this subpart?
60.2030 Who implements and enforces this subpart?
60.2035 How are these new source performance standards structured?
60.2040 Do all eleven components of these new source performance 
standards apply at the same time?

Preconstruction Siting Analysis

60.2045 Who must prepare a siting analysis?
60.2050 What is a siting analysis?

Waste Management Plan

60.2055 What is a waste management plan?
60.2060 When must I submit my waste management plan?
60.2065 What should I include in my waste management plan?

Operator Training and Qualification

60.2070 What are the operator training and qualification 
requirements?
60.2075 When must the operator training course be completed?
60.2080 How do I obtain my operator qualification?
60.2085 How do I maintain my operator qualification?
60.2090 How do I renew my lapsed operator qualification?
60.2095 What site-specific documentation is required?
60.2100 What if all the qualified operators are temporarily not 
accessible?

Emission Limitations and Operating Limits

60.2105 What emission limitations must I meet and by when?
60.2110 What operating limits must I meet and by when?
60.2115 What if I do not use a wet scrubber, fabric filter, 
activated carbon injection, selective noncatalytic reduction, an 
electrostatic precipitator, or a dry scrubber to comply with the 
emission limitations?

Performance Testing

60.2125 How do I conduct the initial and annual performance test?
60.2130 How are the performance test data used?

Initial Compliance Requirements

60.2135 How do I demonstrate initial compliance with the emission 
limitations and establish the operating limits?
60.2140 By what date must I conduct the initial performance test?
60.2141 By what date must I conduct the initial air pollution 
control device inspection?

Continuous Compliance Requirements

60.2145 How do I demonstrate continuous compliance with the emission 
limitations and the operating limits?
60.2150 By what date must I conduct the annual performance test?
60.2151 By what date must I conduct the annual air pollution control 
device inspection?
60.2155 May I conduct performance testing less often?
60.2160 May I conduct a repeat performance test to establish new 
operating limits?

Monitoring

60.2165 What monitoring equipment must I install and what parameters 
must I monitor?
60.2170 Is there a minimum amount of monitoring data I must obtain?

Recordkeeping and Reporting

60.2175 What records must I keep?
60.2180 Where and in what format must I keep my records?
60.2185 What reports must I submit?
60.2190 What must I submit prior to commencing construction?
60.2195 What information must I submit prior to initial startup?
60.2200 What information must I submit following my initial 
performance test?
60.2205 When must I submit my annual report?
60.2210 What information must I include in my annual report?
60.2215 What else must I report if I have a deviation from the 
operating limits or the emission limitations?
60.2220 What must I include in the deviation report?
60.2225 What else must I report if I have a deviation from the 
requirement to have a qualified operator accessible?
60.2230 Are there any other notifications or reports that I must 
submit?
60.2235 In what form can I submit my reports?
60.2240 Can reporting dates be changed?

Title V Operating Permits

60.2242 Am I required to apply for and obtain a Title V operating 
permit for my unit?

Air Curtain Incinerators (ACIs)

60.2245 What is an air curtain incinerator?
60.2250 What are the emission limitations for air curtain 
incinerators?
60.2255 How must I monitor opacity for air curtain incinerators?
60.2260 What are the recordkeeping and reporting requirements for 
air curtain incinerators?

Definitions

60.2265 What definitions must I know?

Tables to Subpart CCCC

    Table 1 to Subpart CCCC of Part 60--Emission Limitations for 
Incinerators for Which Construction is Commenced After November 30, 
1999, But no Later Than June 4, 2010, or for Which Modification or 
Reconstruction is Commenced on or After June 1, 2001, But no Later Than 
August 7, 2013
    Table 2 to Subpart CCCC of Part 60--Operating Limits for Wet 
Scrubbers
    Table 3 to Subpart CCCC of Part 60--Toxic Equivalency Factors
    Table 4 to Subpart CCCC of Part 60--Summary of Reporting 
Requirements
    Table 5 to Subpart CCCC of Part 60--Emission Limitations for 
Incinerators That Commenced Construction After June 4, 2010, or That 
Commenced Reconstruction or Modification After August 7, 2013
    Table 6 to Subpart CCCC of Part 60--Emission Limitations for Energy 
Recovery Units That Commenced Construction After June 4, 2010, or That 
Commenced Reconstruction or Modification After August 7, 2013
    Table 7 to Subpart CCCC of Part 60--Emission Limitations for Waste-
burning Kilns That Commenced Construction After June 4, 2010, or 
Reconstruction or Modification After August 7, 2013
    Table 8 to Subpart CCCC of Part 60--Emission Limitations for Small, 
Remote Incinerators That Commenced Construction After June 4, 2010, Or 
That Commenced Reconstruction or Modification After August 7, 2013

Subpart CCCC--Standards of Performance for Commercial and 
Industrial Solid Waste Incineration Units

Introduction


Sec.  60.2000  What does this subpart do?

    This subpart establishes new source performance standards for 
commercial and industrial solid waste incineration units (CISWIs) and 
air curtain incinerators (ACIs).


Sec.  60.2005  When did this subpart become effective?

    This subpart became effective on August 7, 2013. Some of the 
requirements in this subpart apply to planning the CISWI or ACI (i.e., 
the preconstruction requirements in

[[Page 15854]]

Sec. Sec.  60.2045 and 60.2050). Other requirements such as the 
emission limitations and operating limits apply after the CISWI or ACI 
begins operation.

Applicability


Sec.  60.2010  Does this subpart apply to my incineration unit?

    Yes, this subpart applies if your incineration unit meets all the 
requirements specified in paragraphs (a) through (c) of this section:
    (a) Your incineration unit is a new incineration unit as defined in 
Sec.  60.2015;
    (b) Your incineration unit is a CISWI as defined in Sec.  60.2265, 
or an ACI as defined in Sec.  60.2265; and
    (c) Your incineration unit is not exempt under Sec.  60.2020.


Sec.  60.2015   What is a new incineration unit?

    (a) A new incineration unit is an incineration unit that meets any 
of the criteria specified in paragraphs (a)(1) through (3) of this 
section:
    (1) A CISWI or ACI that commenced construction after June 4, 2010;
    (2) A CISWI or ACI that commenced reconstruction or modification 
after August 7, 2013; and
    (3) Incinerators and ACIs, as defined in this subpart, that 
commenced construction after November 30, 1999, but no later than June 
4, 2010, or that commenced reconstruction or modification on or after 
June 1, 2001, but no later than August 7, 2013, are considered new 
incineration units and remain subject to the applicable requirements of 
this subpart until the units become subject to the requirements of an 
approved state plan or federal plan that implements subpart DDDD of 
this part (Emission Guidelines and Compliance Times for Commercial and 
Industrial Solid Waste Incineration Units).
    (b) This subpart does not affect your CISWI or ACI if you make 
physical or operational changes to your incineration unit primarily to 
comply with subpart DDDD of this part (Emission Guidelines and 
Compliance Times for Commercial and Industrial Solid Waste Incineration 
Units). Such changes do not qualify as reconstruction or modification 
under this subpart.


Sec.  60.2020   What combustion units are exempt from this subpart?

    This subpart exempts the types of units described in paragraphs (a) 
through (j) of this section, but some units are required to provide 
notifications.
    (a) Pathological waste incineration units. Incineration units 
burning 90 percent or more by weight (on a calendar quarter basis and 
excluding the weight of auxiliary fuel and combustion air) of 
pathological waste, low-level radioactive waste, and/or 
chemotherapeutic waste as defined in Sec.  60.2265 are not subject to 
this subpart if you meet the two requirements specified in paragraphs 
(a)(1) and (2) of this section:
    (1) Notify the Administrator that the unit meets these criteria; 
and
    (2) Keep records on a calendar quarter basis of the weight of 
pathological waste, low-level radioactive waste, and/or 
chemotherapeutic waste burned, and the weight of all other fuels and 
wastes burned in the unit.
    (b) Municipal waste combustion units. Incineration units that are 
subject to subpart Ea of this part (Standards of Performance for 
Municipal Waste Combustors); subpart Eb of this part (Standards of 
Performance for Large Municipal Waste Combustors); subpart Cb of this 
part (Emission Guidelines and Compliance Time for Large Municipal 
Combustors); subpart AAAA of this part (Standards of Performance for 
Small Municipal Waste Combustion Units); or subpart BBBB of this part 
(Emission Guidelines for Small Municipal Waste Combustion Units).
    (c) Medical waste incineration units. Incineration units regulated 
under subpart Ec of this part (Standards of Performance for Hospital/
Medical/Infectious Waste Incinerators for Which Construction is 
Commenced After June 20, 1996) or subpart Ce of this part (Emission 
Guidelines and Compliance Times for Hospital/Medical/Infectious Waste 
Incinerators).
    (d) Small power production facilities. Units that meet the four 
requirements specified in paragraphs (d)(1) through (4) of this 
section:
    (1) The unit qualifies as a small power-production facility under 
section 3(17)(C) of the Federal Power Act (16 U.S.C. 796(17)(C));
    (2) The unit burns homogeneous waste (not including refuse-derived 
fuel) to produce electricity;
    (3) You submit documentation to the Administrator notifying the EPA 
that the qualifying small power production facility is combusting 
homogenous waste; and
    (4) You maintain the records specified in Sec.  60.2175(w).
    (e) Cogeneration facilities. Units that meet the four requirements 
specified in paragraphs (e)(1) through (4) of this section:
    (1) The unit qualifies as a cogeneration facility under section 
3(18)(B) of the Federal Power Act (16 U.S.C. 796(18)(B));
    (2) The unit burns homogeneous waste (not including refuse-derived 
fuel) to produce electricity and steam or other forms of energy used 
for industrial, commercial, heating, or cooling purposes;
    (3) You submit documentation to the Administrator notifying the 
Agency that the qualifying cogeneration facility is combusting 
homogenous waste; and
    (4) You maintain the records specified in Sec.  60.2175(x).
    (f) Hazardous waste combustion units. Units for which you are 
required to get a permit under section 3005 of the Solid Waste Disposal 
Act.
    (g) Materials recovery units. Units that combust waste for the 
primary purpose of recovering metals, such as primary and secondary 
smelters.
    (h) Sewage treatment plants. Incineration units regulated under 
subpart O of this part (Standards of Performance for Sewage Treatment 
Plants).
    (i) Sewage sludge incineration units. Incineration units combusting 
sewage sludge for the purpose of reducing the volume of the sewage 
sludge by removing combustible matter that are subject to subpart LLLL 
of this part (Standards of Performance for New Sewage Sludge 
Incineration Units) or subpart MMMM of this part (Emission Guidelines 
and Compliance Times for Existing Sewage Sludge Incineration Units).
    (j) Other solid waste incineration units. Incineration units that 
are subject to subpart EEEE of this part (Standards of Performance for 
Other Solid Waste Incineration Units for Which Construction is 
Commenced After December 9, 2004, or for Which Modification or 
Reconstruction is Commenced on or After June 16, 2006) or subpart FFFF 
of this part (Emission Guidelines and Compliance Times for Other Solid 
Waste Incineration Units That Commenced Construction On or Before 
December 9, 2004).


Sec.  60.2030   Who implements and enforces this subpart?

    (a) This subpart can be implemented and enforced by the U.S. 
Environmental Protection Agency (EPA), or a delegated authority such as 
your state, local, or tribal agency. If the EPA Administrator has 
delegated authority to your state, local, or tribal agency, then that 
agency (as well as EPA) has the authority to implement and enforce this 
subpart. You should contact your EPA Regional Office to find out if 
this subpart is delegated to your state, local, or tribal agency.
    (b) In delegating implementation and enforcement authority of this 
subpart to

[[Page 15855]]

a state, local, or tribal agency, the authorities contained in 
paragraph (c) of this section are retained by the EPA Administrator and 
are not transferred to the state, local, or tribal agency.
    (c) The authorities that will not be delegated to state, local, or 
tribal agencies are specified in paragraphs (c)(1) through (9) of this 
section:
    (1) Approval of alternatives to the emission limitations in tables 
1, 5, 6, 7, and 8 of this subpart and operating limits established 
under Sec.  60.2110;
    (2) Approval of major alternatives to test methods;
    (3) Approval of major alternatives to monitoring;
    (4) Approval of major alternatives to recordkeeping and reporting;
    (5) The requirements in Sec.  60.2115;
    (6) The requirements in Sec.  60.2100(b)(2);
    (7) Approval of alternative opacity emission limits in Sec.  
60.2105 under Sec.  60.11(e)(6) through (8);
    (8) Performance test and data reduction waivers under Sec.  
60.8(b)(4) and (5);
    (9) Approval of an alternative to any electronic reporting to the 
EPA required by this subpart.


Sec.  60.2035   How are these new source performance standards 
structured?

    These new source performance standards contain the eleven major 
components listed in paragraphs (a) through (k) of this section:
    (a) Preconstruction siting analysis;
    (b) Waste management plan;
    (c) Operator training and qualification;
    (d) Emission limitations and operating limits;
    (e) Performance testing;
    (f) Initial compliance requirements;
    (g) Continuous compliance requirements;
    (h) Monitoring;
    (i) Recordkeeping and reporting;
    (j) Definitions; and
    (k) Tables.


Sec.  60.2040   Do all eleven components of these new source 
performance standards apply at the same time?

    No. You must meet the preconstruction siting analysis and waste 
management plan requirements before you commence construction of the 
CISWI. The operator training and qualification, emission limitations, 
operating limits, performance testing and compliance, monitoring, and 
most recordkeeping and reporting requirements are met after the CISWI 
begins operation.

Preconstruction Siting Analysis


Sec.  60.2045   Who must prepare a siting analysis?

    (a) You must prepare a siting analysis if you plan to commence 
construction of an incinerator after December 1, 2000.
    (b) You must prepare a siting analysis for CISWIs that commenced 
construction after June 4, 2010, or that commenced reconstruction or 
modification after August 7, 2013.
    (c) You must prepare a siting analysis if you are required to 
submit an initial application for a construction permit under 40 CFR 
part 51, subpart I, or 40 CFR part 52, as applicable, for the 
reconstruction or modification of your CISWI.


Sec.  60.2050   What is a siting analysis?

    (a) The siting analysis must consider air pollution control 
alternatives that minimize, on a site-specific basis, to the maximum 
extent practicable, potential risks to public health or the 
environment. In considering such alternatives, the analysis may 
consider costs, energy impacts, nonair environmental impacts, or any 
other factors related to the practicability of the alternatives.
    (b) Analyses of your CISWI's impacts that are prepared to comply 
with state, local, or other federal regulatory requirements may be used 
to satisfy the requirements of this section, provided they include the 
consideration of air pollution control alternatives specified in 
paragraph (a) of this section.
    (c) You must complete and submit the siting requirements of this 
section as required under Sec.  60.2190(c) prior to commencing 
construction.

Waste Management Plan


Sec.  60.2055   What is a waste management plan?

    A waste management plan is a written plan that identifies both the 
feasibility and the methods used to reduce or separate certain 
components of solid waste from the waste stream in order to reduce or 
eliminate toxic emissions from incinerated waste.


Sec.  60.2060   When must I submit my waste management plan?

    (a) You must submit a waste management plan prior to commencing 
construction.
    (b) For CISWIs that commence reconstruction or modification after 
August 7, 2013, you must submit a waste management plan prior to the 
commencement of modification or reconstruction.


Sec.  60.2065   What should I include in my waste management plan?

    A waste management plan must include consideration of the reduction 
or separation of waste-stream elements such as paper, cardboard, 
plastics, glass, batteries, or metals; or the use of recyclable 
materials. The plan must identify any additional waste management 
measures and implement those measures the source considers practical 
and feasible, considering the effectiveness of waste management 
measures already in place, the costs of additional measures, the 
emissions reductions expected to be achieved, and any other 
environmental or energy impacts they might have.

Operator Training and Qualification


Sec.  60.2070   What are the operator training and qualification 
requirements?

    (a) No CISWI can be operated unless a fully trained and qualified 
CISWI operator is accessible, either at the facility or can be at the 
facility within 1 hour. The trained and qualified CISWI operator may 
operate the CISWI directly or be the direct supervisor of one or more 
other plant personnel who operate the unit. If all qualified CISWI 
operators are temporarily not accessible, you must follow the 
procedures in Sec.  60.2100.
    (b) Operator training and qualification must be obtained through a 
state-approved program or by completing the requirements included in 
paragraph (c) of this section.
    (c) Training must be obtained by completing an incinerator operator 
training course that includes, at a minimum, the three elements 
described in paragraphs (c)(1) through (3) of this section:
    (1) Training on the eleven subjects listed in paragraphs (c)(1)(i) 
through (xi) of this section;
    (i) Environmental concerns, including types of emissions;
    (ii) Basic combustion principles, including products of combustion;
    (iii) Operation of the specific type of incinerator to be used by 
the operator, including proper startup, waste charging, and shutdown 
procedures;
    (iv) Combustion controls and monitoring;
    (v) Operation of air pollution control equipment and factors 
affecting performance (if applicable);
    (vi) Inspection and maintenance of the incinerator and air 
pollution control devices;
    (vii) Actions to prevent and correct malfunctions or to prevent 
conditions that may lead to malfunctions;
    (viii) Bottom and fly ash characteristics and handling procedures;

[[Page 15856]]

    (ix) Applicable federal, state, and local regulations, including 
Occupational Safety and Health Administration workplace standards;
    (x) Pollution prevention; and
    (xi) Waste management practices.
    (2) An examination designed and administered by the instructor.
    (3) Written material covering the training course topics that may 
serve as reference material following completion of the course.


Sec.  60.2075   When must the operator training course be completed?

    The operator training course must be completed by the later of the 
three dates specified in paragraphs (a) through (c) of this section:
    (a) Six months after your CISWI startup;
    (b) December 3, 2001; and
    (c) The date before an employee assumes responsibility for 
operating the CISWI or assumes responsibility for supervising the 
operation of the CISWI.


Sec.  60.2080   How do I obtain my operator qualification?

    (a) You must obtain operator qualification by completing a training 
course that satisfies the criteria under Sec.  60.2070(b).
    (b) Qualification is valid from the date on which the training 
course is completed and the operator successfully passes the 
examination required under Sec.  60.2070(c)(2).


Sec.  60.2085   How do I maintain my operator qualification?

    To maintain qualification, you must complete an annual review or 
refresher course covering, at a minimum, the five topics described in 
paragraphs (a) through (e) of this section:
    (a) Update of regulations;
    (b) Incinerator operation, including startup and shutdown 
procedures, waste charging, and ash handling;
    (c) Inspection and maintenance;
    (d) Prevention and correction of malfunctions or conditions that 
may lead to malfunction; and
    (e) Discussion of operating problems encountered by attendees.


Sec.  60.2090   How do I renew my lapsed operator qualification?

    You must renew a lapsed operator qualification by one of the two 
methods specified in paragraphs (a) and (b) of this section:
    (a) For a lapse of less than 3 years, you must complete a standard 
annual refresher course described in Sec.  60.2085; and
    (b) For a lapse of 3 years or more, you must repeat the initial 
qualification requirements in Sec.  60.2080(a).


Sec.  60.2095   What site-specific documentation is required?

    (a) Documentation must be available at the facility and readily 
accessible for all CISWI operators that addresses the ten topics 
described in paragraphs (a)(1) through (10) of this section. You must 
maintain this information and the training records required by 
paragraph (c) of this section in a manner that they can be readily 
accessed and are suitable for inspection upon request:
    (1) Summary of the applicable standards under this subpart;
    (2) Procedures for receiving, handling, and charging waste;
    (3) Incinerator startup, shutdown, and malfunction procedures;
    (4) Procedures for maintaining proper combustion air supply levels;
    (5) Procedures for operating the incinerator and associated air 
pollution control systems within the standards established under this 
subpart;
    (6) Monitoring procedures for demonstrating compliance with the 
incinerator operating limits;
    (7) Reporting and recordkeeping procedures;
    (8) The waste management plan required under Sec. Sec.  60.2055 
through 60.2065;
    (9) Procedures for handling ash; and
    (10) A list of the wastes burned during the performance test.
    (b) You must establish a program for reviewing the information 
listed in paragraph (a) of this section with each incinerator operator:
    (1) The initial review of the information listed in paragraph (a) 
of this section must be conducted within 6 months after the effective 
date of this subpart or prior to an employee's assumption of 
responsibilities for operation of the CISWI, whichever date is later; 
and
    (2) Subsequent annual reviews of the information listed in 
paragraph (a) of this section must be conducted no later than 12 months 
following the previous review.
    (c) You must also maintain the information specified in paragraphs 
(c)(1) through (3) of this section:
    (1) Records showing the names of CISWI operators who have completed 
review of the information in Sec.  60.2095(a) as required by Sec.  
60.2095(b), including the date of the initial review and all subsequent 
annual reviews;
    (2) Records showing the names of the CISWI operators who have 
completed the operator training requirements under Sec.  60.2070, met 
the criteria for qualification under Sec.  60.2080, and maintained or 
renewed their qualification under Sec.  60.2085 or Sec.  60.2090. 
Records must include documentation of training, the dates of the 
initial and refresher training, and the dates of their qualification 
and all subsequent renewals of such qualifications; and
    (3) For each qualified operator, the phone and/or pager number at 
which they can be reached during operating hours.


Sec.  60.2100   What if all the qualified operators are temporarily not 
accessible?

    If all qualified operators are temporarily not accessible (i.e., 
not at the facility and not able to be at the facility within 1 hour), 
you must meet one of the two criteria specified in paragraphs (a) and 
(b) of this section, depending on the length of time that a qualified 
operator is not accessible:
    (a) When all qualified operators are not accessible for more than 8 
hours, but less than 2 weeks, the CISWI may be operated by other plant 
personnel familiar with the operation of the CISWI who have completed a 
review of the information specified in Sec.  60.2095(a) within the past 
12 months. However, you must record the period when all qualified 
operators were not accessible and include this deviation in the annual 
report as specified under Sec.  60.2210; and
    (b) When all qualified operators are not accessible for 2 weeks or 
more, you must take the two actions that are described in paragraphs 
(b)(1) and (2) of this section:
    (1) Notify the Administrator of this deviation in writing within 10 
days. In the notice, state what caused this deviation, what you are 
doing to ensure that a qualified operator is accessible, and when you 
anticipate that a qualified operator will be accessible; and
    (2) Submit a status report to the Administrator every 4 weeks 
outlining what you are doing to ensure that a qualified operator is 
accessible, stating when you anticipate that a qualified operator will 
be accessible and requesting approval from the Administrator to 
continue operation of the CISWI. You must submit the first status 
report 4 weeks after you notify the Administrator of the deviation 
under paragraph (b)(1) of this section. If the Administrator notifies 
you that your request to continue operation of the CISWI is 
disapproved, the CISWI may continue operation for 90 days, then must 
cease operation. Operation of the unit may resume if you meet the two 
requirements in paragraphs (b)(2)(i) and (ii) of this section:
    (i) A qualified operator is accessible as required under Sec.  
60.2070(a); and
    (ii) You notify the Administrator that a qualified operator is 
accessible and that you are resuming operation.

[[Page 15857]]

Emission Limitations and Operating Limits


Sec.  60.2105   What emission limitations must I meet and by when?

    (a) You must meet the emission limitations for each CISWI, 
including bypass stack or vent, specified in table 1 of this subpart or 
tables 5 through 8 of this subpart by the applicable date in Sec.  
60.2140. You must be in compliance with the emission limitations of 
this subpart that apply to you at all times.
    (b) A CISWI or ACI that commenced construction after November 30, 
1999, but no later than June 4, 2010, or that commenced reconstruction 
or modification on or after June 1, 2001 but no later than August 7, 
2013, must continue to meet the emission limits in table 1 of this 
subpart for units in the incinerator subcategory and Sec.  60.2250 for 
ACIs until the units become subject to the requirements of an approved 
state plan or federal plan that implements subpart DDDD of this part 
(Emission Guidelines and Compliance Times for Commercial and Industrial 
Solid Waste Incineration Units).


Sec.  60.2110   What operating limits must I meet and by when?

    (a) If you use a wet scrubber(s) to comply with the emission 
limitations, you must establish operating limits for up to four 
operating parameters (as specified in table 2 of this subpart) as 
described in paragraphs (a)(1) through (4) of this section during the 
initial performance test:
    (1) Maximum charge rate, calculated using one of the two different 
procedures in paragraph (a)(1)(i) or (ii) of this section, as 
appropriate:
    (i) For continuous and intermittent units, maximum charge rate is 
110 percent of the average charge rate measured during the most recent 
performance test demonstrating compliance with all applicable emission 
limitations; and
    (ii) For batch units, maximum charge rate is 110 percent of the 
daily charge rate measured during the most recent performance test 
demonstrating compliance with all applicable emission limitations.
    (2) Minimum pressure drop across the wet particulate matter 
scrubber, which is calculated as the lowest 1-hour average pressure 
drop across the wet scrubber measured during the most recent 
performance test demonstrating compliance with the particulate matter 
emission limitations; or minimum amperage to the wet scrubber, which is 
calculated as the lowest 1-hour average amperage to the wet scrubber 
measured during the most recent performance test demonstrating 
compliance with the particulate matter emission limitations;
    (3) Minimum scrubber liquid flow rate, which is calculated as the 
lowest 1-hour average liquid flow rate at the inlet to the wet acid gas 
or particulate matter scrubber measured during the most recent 
performance test demonstrating compliance with all applicable emission 
limitations; and
    (4) Minimum scrubber liquor pH, which is calculated as the lowest 
1-hour average liquor pH at the inlet to the wet acid gas scrubber 
measured during the most recent performance test demonstrating 
compliance with the hydrogen chloride (HCl) emission limitation.
    (b) You must meet the operating limits established during the 
initial performance test 60 days after your CISWI reaches the charge 
rate at which it will operate, but no later than 180 days after its 
initial startup.
    (c) If you use a fabric filter to comply with the emission 
limitations and you do not use a particulate matter (PM) continuous 
parameter monitoring system (CPMS) for monitoring PM compliance, you 
must operate each fabric filter system such that the bag leak detection 
system alarm does not sound more than 5 percent of the operating time 
during a 6-month period. In calculating this operating time percentage, 
if inspection of the fabric filter demonstrates that no corrective 
action is required, no alarm time is counted. If corrective action is 
required, each alarm shall be counted as a minimum of 1 hour. If you 
take longer than 1 hour to initiate corrective action, the alarm time 
shall be counted as the actual amount of time taken by you to initiate 
corrective action.
    (d) If you use an electrostatic precipitator to comply with the 
emission limitations and you do not use a PM CPMS for monitoring PM 
compliance, you must measure the (secondary) voltage and amperage of 
the electrostatic precipitator collection plates during the particulate 
matter performance test. Calculate the average electric power value 
(secondary voltage x secondary current = secondary electric power) for 
each test run. The operating limit for the electrostatic precipitator 
is calculated as the lowest 1-hour average secondary electric power 
measured during the most recent performance test demonstrating 
compliance with the particulate matter emission limitations.
    (e) If you use activated carbon sorbent injection to comply with 
the emission limitations, you must measure the sorbent flow rate during 
the performance testing. The operating limit for the carbon sorbent 
injection is calculated as the lowest 1-hour average sorbent flow rate 
measured during the most recent performance test demonstrating 
compliance with the mercury emission limitations. For energy recovery 
units, when your unit operates at lower loads, multiply your sorbent 
injection rate by the load fraction, as defined in this subpart, to 
determine the required injection rate (e.g., for 50 percent load, 
multiply the injection rate operating limit by 0.5).
    (f) If you use selective noncatalytic reduction to comply with the 
emission limitations, you must measure the charge rate, the secondary 
chamber temperature (if applicable to your CISWI), and the reagent flow 
rate during the nitrogen oxides performance testing. The operating 
limits for the selective noncatalytic reduction are calculated as the 
highest 1-hour average charge rate, lower secondary chamber 
temperature, and lowest reagent flow rate measured during the most 
recent performance test demonstrating compliance with the nitrogen 
oxides emission limitations.
    (g) If you use a dry scrubber to comply with the emission 
limitations, you must measure the injection rate of each sorbent during 
the performance testing. The operating limit for the injection rate of 
each sorbent is calculated as the lowest 1-hour average injection rate 
for each sorbent measured during the most recent performance test 
demonstrating compliance with the hydrogen chloride emission 
limitations. For energy recovery units, when your unit operates at 
lower loads, multiply your sorbent injection rate by the load fraction, 
as defined in this subpart, to determine the required injection rate 
(e.g., for 50 percent load, multiply the injection rate operating limit 
by 0.5).
    (h) If you do not use a wet scrubber, electrostatic precipitator, 
or fabric filter to comply with the emission limitations, and if you do 
not determine compliance with your particulate matter emission 
limitation with either a particulate matter CEMS or a particulate 
matter CPMS, you must maintain opacity to less than or equal to 10 
percent opacity (1-hour block average).
    (i) If you use a PM CPMS to demonstrate compliance, you must 
establish your PM CPMS operating limit and determine compliance with it 
according to paragraphs (i)(1) through (5) of this section:
    (1) Determine your operating limit as the average PM CPMS output 
value recorded during the performance test or at a PM CPMS output value 
corresponding to 75 percent of the emission limit if your PM 
performance test demonstrates compliance below 75 percent of the 
emission limit. You must

[[Page 15858]]

verify an existing or establish a new operating limit after each 
repeated performance test. You must repeat the performance test 
annually and reassess and adjust the site-specific operating limit in 
accordance with the results of the performance test:
    (i) Your PM CPMS must provide a 4-20 milliamp output, or digital 
equivalent, and the establishment of its relationship to manual 
reference method measurements must be determined in units of milliamps;
    (ii) Your PM CPMS operating range must be capable of reading PM 
concentrations from zero to a level equivalent to at least two times 
your allowable emission limit. If your PM CPMS is an auto-ranging 
instrument capable of multiple scales, the primary range of the 
instrument must be capable of reading PM concentration from zero to a 
level equivalent to two times your allowable emission limit; and
    (iii) During the initial performance test or any such subsequent 
performance test that demonstrates compliance with the PM limit, record 
and average all milliamp output values, or their digital equivalent, 
from the PM CPMS for the periods corresponding to the compliance test 
runs (e.g., average all your PM CPMS output values for three 
corresponding 2-hour Method 5I test runs).
    (2) If the average of your three PM performance test runs are below 
75 percent of your PM emission limit, you must calculate an operating 
limit by establishing a relationship of PM CPMS signal to PM 
concentration using the PM CPMS instrument zero, the average PM CPMS 
output values corresponding to the three compliance test runs, and the 
average PM concentration from the Method 5 or performance test with the 
procedures in (i)(1) through (5) of this section:
    (i) Determine your instrument zero output with one of the following 
procedures:
    (A) Zero point data for in-situ instruments should be obtained by 
removing the instrument from the stack and monitoring ambient air on a 
test bench;
    (B) Zero point data for extractive instruments should be obtained 
by removing the extractive probe from the stack and drawing in clean 
ambient air;
    (C) The zero point can also can be established obtained by 
performing manual reference method measurements when the flue gas is 
free of PM emissions or contains very low PM concentrations (e.g., when 
your process is not operating, but the fans are operating or your 
source is combusting only natural gas) and plotting these with the 
compliance data to find the zero intercept; and
    (D) If none of the steps in paragraphs (i)(2)(i)(A) through (C) of 
this section are possible, you must use a zero output value provided by 
the manufacturer.
    (ii) Determine your PM CPMS instrument average in milliamps, or the 
digital equivalent, and the average of your corresponding three PM 
compliance test runs, using equation 1:
[GRAPHIC] [TIFF OMITTED] TR16AP19.006


Where:

    X1 = the PM CPMS output data points for the three 
runs constituting the performance test,
    Y1 = the PM concentration value for the three runs 
constituting the performance test, and
    n = the number of data points.

    (iii) With your instrument zero expressed in milliamps, or the 
digital equivalent, your three run average PM CPMS milliamp value, or 
its digital equivalent, and your three run average PM concentration 
from your three compliance tests, determine a relationship of mg/dscm 
per milliamp or digital signal equivalent with equation 2:
[GRAPHIC] [TIFF OMITTED] TR16AP19.007

Where:

R = the relative mg/dscm per milliamp or digital equivalent for your 
PM CPMS,
Y1 = the three run average mg/dscm PM concentration,
X1 = the three run average milliamp or digital signal 
output from you PM CPMS, and
z = the milliamp or digital signal equivalent of your instrument 
zero determined from paragraph (2)(i) of this section.

    (iv) Determine your source specific 30-day rolling average 
operating limit using the mg/dscm per milliamp or digital value from 
equation 2 in equation 3, below. This sets your operating limit at the 
PM CPMS output value corresponding to 75 percent of your emission 
limit:
[GRAPHIC] [TIFF OMITTED] TR16AP19.008

Where:

Ol = the operating limit for your PM CPMS on a 30-day 
rolling average, in milliamps or their digital signal equivalent,
L = your source emission limit expressed in mg/dscm,
z = your instrument zero in milliamps or the digital equivalent, 
determined from paragraph (2)(i) of this secction, and

[[Page 15859]]

R = the relative mg/dscm per milliamp or digital signal output 
equivalent for your PM CPMS, from equation 2.

    (3) If the average of your three PM compliance test runs is at or 
above 75 percent of your PM emission limit you must determine your 
operating limit by averaging the PM CPMS milliamp or digital signal 
output corresponding to your three PM performance test runs that 
demonstrate compliance with the emission limit using equation 4 and you 
must submit all compliance test and PM CPMS data according to the 
reporting requirements in paragraph (i)(5) of this section:
[GRAPHIC] [TIFF OMITTED] TR16AP19.009

Where:

X1 = the PM CPMS data points for all runs i,
n = the number of data points, and
Oh = your site specific operating limit, in milliamps or 
digital signal equivalent.

    (4) To determine continuous compliance, you must record the PM CPMS 
output data for all periods when the process is operating and the PM 
CPMS is not out-of-control. You must demonstrate continuous compliance 
by using all quality-assured hourly average data collected by the PM 
CPMS for all operating hours to calculate the arithmetic average 
operating parameter in units of the operating limit (e.g., milliamps or 
digital signal bits, PM concentration, raw data signal) on a 30-day 
rolling average basis.
    (5) For PM performance test reports used to set a PM CPMS operating 
limit, the electronic submission of the test report must also include 
the make and model of the PM CPMS instrument, serial number of the 
instrument, analytical principle of the instrument (e.g., beta 
attenuation), span of the instruments primary analytical range, 
milliamp or digital signal value equivalent to the instrument zero 
output, technique by which this zero value was determined, and the 
average milliamp or digital signals corresponding to each PM compliance 
test run.


Sec.  60.2115   What if I do not use a wet scrubber, fabric filter, 
activated carbon injection, selective noncatalytic reduction, an 
electrostatic precipitator, or a dry scrubber to comply with the 
emission limitations?

    If you use an air pollution control device other than a wet 
scrubber, activated carbon injection, selective noncatalytic reduction, 
fabric filter, an electrostatic precipitator, or a dry scrubber or 
limit emissions in some other manner, including material balances, to 
comply with the emission limitations under Sec.  60.2105, you must 
petition the EPA Administrator for specific operating limits to be 
established during the initial performance test and continuously 
monitored thereafter. You must submit the petition at least sixty days 
before the performance test is scheduled to begin. Your petition must 
include the five items listed in paragraphs (a) through (e) of this 
section:
    (a) Identification of the specific parameters you propose to use as 
additional operating limits;
    (b) A discussion of the relationship between these parameters and 
emissions of regulated pollutants, identifying how emissions of 
regulated pollutants change with changes in these parameters and how 
limits on these parameters will serve to limit emissions of regulated 
pollutants;
    (c) A discussion of how you will establish the upper and/or lower 
values for these parameters which will establish the operating limits 
on these parameters;
    (d) A discussion identifying the methods you will use to measure 
and the instruments you will use to monitor these parameters, as well 
as the relative accuracy and precision of these methods and 
instruments; and
    (e) A discussion identifying the frequency and methods for 
recalibrating the instruments you will use for monitoring these 
parameters.

Performance Testing


Sec.  60.2125   How do I conduct the initial and annual performance 
test?

    (a) All performance tests must consist of a minimum of three test 
runs conducted under conditions representative of normal operations.
    (b) You must document that the waste burned during the performance 
test is representative of the waste burned under normal operating 
conditions by maintaining a log of the quantity of waste burned (as 
required in Sec.  60.2175(b)(1)) and the types of waste burned during 
the performance test.
    (c) All performance tests must be conducted using the minimum run 
duration specified in table 1 of this subpart or tables 5 through 8 of 
this subpart.
    (d) Method 1 of appendix A of this part must be used to select the 
sampling location and number of traverse points.
    (e) Method 3A or 3B of appendix A of this part must be used for gas 
composition analysis, including measurement of oxygen concentration. 
Method 3A or 3B of appendix A of this part must be used simultaneously 
with each method (except when using Method 9 and Method 22).
    (f) All pollutant concentrations, except for opacity, must be 
adjusted to 7 percent oxygen using equation 5 of this section:
[GRAPHIC] [TIFF OMITTED] TR16AP19.010

Where:

Cadj = pollutant concentration adjusted to 7 percent 
oxygen;
Cmeas = pollutant concentration measured on a dry basis;
(20.9-7) = 20.9 percent oxygen-7 percent oxygen (defined oxygen 
correction basis);

[[Page 15860]]

20.9 = oxygen concentration in air, percent; and
%O2 = oxygen concentration measured on a dry basis, 
percent.

    (g) You must determine dioxins/furans toxic equivalency by 
following the procedures in paragraphs (g)(1) through (4) of this 
section:
    (1) Measure the concentration of each dioxin/furan tetra-through 
octa-chlorinated isomer emitted using EPA Method 23 at 40 CFR part 60, 
appendix A-7;
    (2) Quantify isomers meeting identification criteria 2, 3, 4, and 5 
in Section 5.3.2.5 of Method 23, regardless of whether the isomers meet 
identification criteria 1 and 7. You must quantify the isomers per 
Section 9.0 of Method 23. (Note: You may reanalyze the sample aliquot 
or split to reduce the number of isomers not meeting identification 
criteria 1 or 7 of Section 5.3.2.5.);
    (3) For each dioxin/furan (tetra-through octa-chlorinated) isomer 
measured in accordance with paragraphs (g)(1) and (2) of this section, 
multiply the isomer concentration by its corresponding toxic 
equivalency factor specified in table 3 of this subpart; and
    (4) Sum the products calculated in accordance with paragraph (g)(3) 
of this section to obtain the total concentration of dioxins/furans 
emitted in terms of toxic equivalency.
    (h) Method 22 at 40 CFR part 60, appendix A-7 of this part must be 
used to determine compliance with the fugitive ash emission limit in 
table 1 of this subpart or tables 5 through 8 of this subpart.
    (i) If you have an applicable opacity operating limit, you must 
determine compliance with the opacity limit using Method 9 at 40 CFR 
part 60, appendix A-4, based on three 1-hour blocks consisting of ten 
6-minute average opacity values, unless you are required to install a 
continuous opacity monitoring system, consistent with Sec. Sec.  
60.2145 and 60.2165.
    (j) You must determine dioxins/furans total mass basis by following 
the procedures in paragraphs (j)(1) through (3) of this section:
    (1) Measure the concentration of each dioxin/furan tetra-through 
octa-chlorinated isomer emitted using EPA Method 23 at 40 CFR part 60, 
appendix A-7;
    (2) Quantify isomers meeting identification criteria 2, 3, 4, and 5 
in Section 5.3.2.5 of Method 23, regardless of whether the isomers meet 
identification criteria 1 and 7. You must quantify the isomers per 
Section 9.0 of Method 23. (Note: You may reanalyze the sample aliquot 
or split to reduce the number of isomers not meeting identification 
criteria 1 or 7 of Section 5.3.2.5.); and
    (3) Sum the quantities measured in accordance with paragraphs 
(j)(1) and (2) of this section to obtain the total concentration of 
dioxins/furans emitted in terms of total mass basis.


Sec.  60.2130   How are the performance test data used?

    You use results of performance tests to demonstrate compliance with 
the emission limitations in table 1 of this subpart or tables 5 through 
8 of this subpart.

Initial Compliance Requirements


Sec.  60.2135   How do I demonstrate initial compliance with the 
emission limitations and establish the operating limits?

    (a) You must conduct a performance test, as required under 
Sec. Sec.  60.2125 and 60.2105to determine compliance with the emission 
limitations in table 1 of this subpart or tables 5 through 8 of this 
subpart, to establish compliance with any opacity operating limit in 
Sec.  60.2110, to establish the kiln-specific emission limit in Sec.  
60.2145(y), as applicable, and to establish operating limits using the 
procedures in Sec.  60.2110 or Sec.  60.2115. The performance test must 
be conducted using the test methods listed in table 1 of this subpart 
or tables 5 through 8 of this subpart and the procedures in Sec.  
60.2125. The use of the bypass stack during a performance test shall 
invalidate the performance test.
    (b) As an alternative to conducting a performance test, as required 
under Sec. Sec.  60.2125 and 60.2105, you may use a 30-day rolling 
average of the 1-hour arithmetic average CEMS data, including CEMS data 
during startup and shutdown as defined in this subpart, to determine 
compliance with the emission limitations in Table 1 of this subpart or 
tables 5 through 8 of this subpart. You must conduct a performance 
evaluation of each continuous monitoring system within 180 days of 
installation of the monitoring system. The initial performance 
evaluation must be conducted prior to collecting CEMS data that will be 
used for the initial compliance demonstration.


Sec.  60.2140   By what date must I conduct the initial performance 
test?

    (a) The initial performance test must be conducted within 60 days 
after your CISWI reaches the charge rate at which it will operate, but 
no later than 180 days after its initial startup.
    (b) If you commence or recommence combusting a solid waste at an 
existing combustion unit at any commercial or industrial facility, and 
you conducted a test consistent with the provisions of this subpart 
while combusting the solid waste within the 6 months preceding the 
reintroduction of that solid waste in the combustion chamber, you do 
not need to retest until 6 months from the date you reintroduce that 
solid waste.
    (c) If you commence or recommence combusting a solid waste at an 
existing combustion unit at any commercial or industrial facility and 
you have not conducted a performance test consistent with the 
provisions of this subpart while combusting the solid waste within the 
6 months preceding the reintroduction of that solid waste in the 
combustion chamber, you must conduct a performance test within 60 days 
from the date you reintroduce that solid waste.


Sec.  60.2141   By what date must I conduct the initial air pollution 
control device inspection?

    (a) The initial air pollution control device inspection must be 
conducted within 60 days after installation of the control device and 
the associated CISWI reaches the charge rate at which it will operate, 
but no later than 180 days after the device's initial startup.
    (b) Within 10 operating days following an air pollution control 
device inspection, all necessary repairs must be completed unless the 
owner or operator obtains written approval from the state agency 
establishing a date whereby all necessary repairs of the designated 
facility must be completed.

Continuous Compliance Requirements


Sec.  60.2145   How do I demonstrate continuous compliance with the 
emission limitations and the operating limits?

    (a) General compliance with standards, considering some units may 
be able to switch between solid waste and non-waste fuel combustion, is 
specified in paragraph (a)(1) through (6) of this section.
    (1) The emission standards and operating requirements set forth in 
this subpart apply at all times;
    (2) If you cease combusting solid waste, you may opt to remain 
subject to the provisions of this subpart. Consistent with the 
definition of CISWI, you are subject to the requirements of this 
subpart at least 6 months following the last date of solid waste 
combustion. Solid waste combustion is ceased when solid waste is not in 
the combustion chamber (i.e., the solid waste feed to the combustor has 
been cut off for a period of time not less than the solid waste 
residence time);
    (3) If you cease combusting solid waste, you must be in compliance 
with

[[Page 15861]]

any newly applicable standards on the effective date of the waste-to-
fuel switch. The effective date of the waste-to-fuel switch is a date 
selected by you, that must be at least 6 months from the date that you 
ceased combusting solid waste, consistent with Sec.  60.2145(a)(2). 
Your source must remain in compliance with this subpart until the 
effective date of the waste-to-fuel switch;
    (4) If you own or operate an existing commercial or industrial 
combustion unit that combusted a fuel or non-waste material, and you 
commence or recommence combustion of solid waste, you are subject to 
the provisions of this subpart as of the first day you introduce or 
reintroduce solid waste to the combustion chamber, and this date 
constitutes the effective date of the fuel-to-waste switch. You must 
complete all initial compliance demonstrations for any section 112 
standards that are applicable to your facility before you commence or 
recommence combustion of solid waste. You must provide 30 days prior 
notice of the effective date of the waste-to-fuel switch. The 
notification must identify:
    (i) The name of the owner or operator of the CISWI, the location of 
the source, the emissions unit(s) that will cease burning solid waste, 
and the date of the notice;
    (ii) The currently applicable subcategory under this subpart, and 
any 40 CFR part 63 subpart and subcategory that will be applicable 
after you cease combusting solid waste;
    (iii) The fuel(s), non-waste material(s) and solid waste(s) the 
CISWI is currently combusting and has combusted over the past 6 months, 
and the fuel(s) or non-waste materials the unit will commence 
combusting;
    (iv) The date on which you became subject to the currently 
applicable emission limits; and
    (v) The date upon which you will cease combusting solid waste, and 
the date (if different) that you intend for any new requirements to 
become applicable (i.e., the effective date of the waste-to-fuel 
switch), consistent with paragraphs (a)(2) and (3) of this section.
    (5) All air pollution control equipment necessary for compliance 
with any newly applicable emissions limits which apply as a result of 
the cessation or commencement or recommencement of combusting solid 
waste must be installed and operational as of the effective date of the 
waste-to-fuel, or fuel-to-waste switch.
    (6) All monitoring systems necessary for compliance with any newly 
applicable monitoring requirements which apply as a result of the 
cessation or commencement or recommencement of combusting solid waste 
must be installed and operational as of the effective date of the 
waste-to-fuel, or fuel-to-waste switch. All calibration and drift 
checks must be performed as of the effective date of the waste-to-fuel, 
or fuel-to-waste switch. Relative accuracy tests must be performed as 
of the performance test deadline for PM CEMS (if PM CEMS are elected to 
demonstrate continuous compliance with the particulate matter emission 
limits). Relative accuracy testing for other CEMS need not be repeated 
if that testing was previously performed consistent with Clean Air Act 
section 112 monitoring requirements or monitoring requirements under 
this subpart.
    (b) You must conduct an annual performance test for the pollutants 
listed in table 1 of this subpart or tables 5 through 8 of this subpart 
and opacity for each CISWI as required under Sec.  60.2125. The annual 
performance test must be conducted using the test methods listed in 
table 1 of this subpart or tables 5 through 8 of this subpart and the 
procedures in Sec.  60.2125. Annual performance tests are not required 
if you use CEMS or continuous opacity monitoring systems to determine 
compliance.
    (c) You must continuously monitor the operating parameters 
specified in Sec.  60.2110 or established under Sec.  60.2115 and as 
specified in Sec.  60.2170. Use 3-hour block average values to 
determine compliance (except for baghouse leak detection system alarms) 
unless a different averaging period is established under Sec.  60.2115 
or, for energy recovery units, where the averaging time for each 
operating parameter is a 30-day rolling, calculated each hour as the 
average of the previous 720 operating hours. Operation above the 
established maximum, below the established minimum, or outside the 
allowable range of operating limits specified in paragraph (a) of this 
section constitutes a deviation from your operating limits established 
under this subpart, except during performance tests conducted to 
determine compliance with the emission and operating limits or to 
establish new operating limits. Operating limits are confirmed or 
reestablished during performance tests.
    (d) You must burn only the same types of waste and fuels used to 
establish subcategory applicability (for energy recovery units) and 
operating limits during the performance test.
    (e) For energy recovery units, incinerators, and small remote 
units, you must perform an annual visual emissions test for ash 
handling.
    (f) For energy recovery units, you must conduct an annual 
performance test for opacity (except where particulate matter CEMS or 
continuous opacity monitoring systems are used are used) and the 
pollutants listed in table 6 of this subpart.
    (g) You may elect to demonstrate initial and continuous compliance 
with the carbon monoxide emission limit using a carbon monoxide CEMS, 
as described in Sec.  60.2165(o).
    (h) Coal and liquid/gas energy recovery units with average annual 
heat input rates greater than or equal to 250 million British thermal 
units/hour (MMBtu/hr) may elect to demonstrate initial and continuous 
compliance with the particulate matter emissions limit using a 
particulate matter CEMS according to the procedures in Sec.  60.2165(n) 
instead of the PM CPMS specified in Sec.  60.2145. Coal and liquid/gas 
energy recovery units with annual average heat input rates less than 
250 MMBtu/hr, incinerators, and small remote incinerators may also 
elect to demonstrate initial and continuous compliance using a 
particulate matter CEMS according to the procedures in Sec.  60.2165(n) 
instead of particulate matter testing with EPA Method 5 at 40 CFR part 
60, appendix A-3 and, if applicable, the continuous opacity monitoring 
requirements in paragraph (i) of this section.
    (i) For energy recovery units with annual average heat input rates 
greater than or equal to 10 MMBtu/hr and less than 250 MMBtu/hr that do 
not use a wet scrubber, fabric filter with bag leak detection system, 
an electrostatic precipitator, particulate matter CEMS, or particulate 
matter CPMS, you must install, operate, certify and maintain a 
continuous opacity monitoring system (COMS) according to the procedures 
in Sec.  60.2165(m).
    (j) For waste-burning kilns, you must conduct an annual performance 
test for cadmium, lead, carbon monoxide, dioxins/furans and hydrogen 
chloride as listed in Table 7 of this subpart, unless you choose to 
demonstrate initial and continuous compliance using CEMS, as allowed in 
paragraph (u) of this section. If you do not use an acid gas wet 
scrubber or dry scrubber, you must determine compliance with the 
hydrogen chloride emissions limit using a HCl CEMS according to the 
requirements in paragraph (j)(1) of this section. You must determine 
compliance with the mercury emissions limit using a mercury CEMS or an 
integrated sorbent trap monitoring system according to paragraph (j)(2) 
of this section. You must determine compliance with nitrogen oxides and

[[Page 15862]]

sulfur dioxide using CEMS. You must determine compliance with 
particulate matter using CPMS.
    (1) If you monitor compliance with the HCl emissions limit by 
operating an HCl CEMS, you must do so in accordance with Performance 
Specification 15 (PS 15) of appendix B to 40 CFR part 60 or PS 18 of 
appendix B to 40 CFR part 60. You must operate, maintain, and quality 
assure a HCl CEMS installed and certified under PS 15 according to the 
quality assurance requirements in Procedure 1 of appendix F to 40 CFR 
part 60 except that the Relative Accuracy Test Audit requirements of 
Procedure 1 must be replaced with the validation requirements and 
criteria of sections 11.1.1 and 12.0 of PS 15. You must operate, 
maintain and quality assure a HCl CEMS installed and certified under PS 
18 according to the quality assurance requirements in Procedure 6 of 
appendix F to 40 CFR part 60. For any performance specification that 
you use, you must use Method 321 of appendix A to 40 CFR part 63 as the 
reference test method for conducting relative accuracy testing. The 
span value and calibration requirements in paragraphs (j)(1)(i) and 
(ii) of this section apply to all HCl CEMS used under this subpart:
    (i) You must use a measurement span value for any HCl CEMS of 0-10 
ppmvw unless the monitor is installed on a kiln without an inline raw 
mill. Kilns without an inline raw mill may use a higher span value 
sufficient to quantify all expected emissions concentrations. The HCl 
CEMS data recorder output range must include the full range of expected 
HCl concentration values which would include those expected during 
``mill off'' conditions. The corresponding data recorder range shall be 
documented in the site-specific monitoring plan and associated records;
    (ii) In order to quality assure data measured above the span value, 
you must use one of the three options in paragraphs (j)(1)(ii)(A) 
through (C) of this section:
    (A) Include a second span that encompasses the HCl emission 
concentrations expected to be encountered during ``mill off'' 
conditions. This second span may be rounded to a multiple of 5 ppm of 
total HCl. The requirements of the appropriate HCl monitor performance 
specification shall be followed for this second span with the exception 
that a RATA with the mill off is not required;
    (B) Quality assure any data above the span value by proving 
instrument linearity beyond the span value established in paragraph 
(j)(1)(i) of this section using the following procedure. Conduct a 
weekly ``above span linearity'' calibration challenge of the monitoring 
system using a reference gas with a certified value greater than your 
highest expected hourly concentration or greater than 75% of the 
highest measured hourly concentration. The ``above span'' reference gas 
must meet the requirements of the applicable performance specification 
and must be introduced to the measurement system at the probe. Record 
and report the results of this procedure as you would for a daily 
calibration. The ``above span linearity'' challenge is successful if 
the value measured by the HCl CEMS falls within 10 percent of the 
certified value of the reference gas. If the value measured by the HCl 
CEMS during the above span linearity challenge exceeds 10 percent of 
the certified value of the reference gas, the monitoring system must be 
evaluated and repaired and a new ``above span linearity'' challenge met 
before returning the HCl CEMS to service, or data above span from the 
HCl CEMS must be subject to the quality assurance procedures 
established in (j)(1)(ii)(D) of this section. In this manner values 
measured by the HCl CEMS during the above span linearity challenge 
exceeding +/-20 percent of the certified value of the reference gas 
must be normalized using equation 6;
    (C) Quality assure any data above the span value established in 
paragraph (j)(1)(i) of this section using the following procedure. Any 
time two consecutive one-hour average measured concentration of HCl 
exceeds the span value you must, within 24 hours before or after, 
introduce a higher, ``above span'' HCl reference gas standard to the 
HCl CEMS. The ``above span'' reference gas must meet the requirements 
of the applicable performance specification and target a concentration 
level between 50 and 150 percent of the highest expected hourly 
concentration measured during the period of measurements above span, 
and must be introduced at the probe. While this target represents a 
desired concentration range that is not always achievable in practice, 
it is expected that the intent to meet this range is demonstrated by 
the value of the reference gas. Expected values may include above span 
calibrations done before or after the above-span measurement period. 
Record and report the results of this procedure as you would for a 
daily calibration. The ``above span'' calibration is successful if the 
value measured by the HCl CEMS is within 20 percent of the certified 
value of the reference gas. If the value measured by the HCl CEMS is 
not within 20 percent of the certified value of the reference gas, then 
you must normalize the stack gas values measured above span as 
described in paragraph (j)(1)(ii)(D) of this section. If the ``above 
span'' calibration is conducted during the period when measured 
emissions are above span and there is a failure to collect the one data 
point in an hour due to the calibration duration, then you must 
determine the emissions average for that missed hour as the average of 
hourly averages for the hour preceding the missed hour and the hour 
following the missed hour. In an hour where an ``above span'' 
calibration is being conducted and one or more data points are 
collected, the emissions average is represented by the average of all 
valid data points collected in that hour;
    (D) In the event that the ``above span'' calibration is not 
successful (i.e., the HCl CEMS measured value is not within 20 percent 
of the certified value of the reference gas), then you must normalize 
the one-hour average stack gas values measured above the span during 
the 24-hour period preceding or following the ``above span'' 
calibration for reporting based on the HCl CEMS response to the 
reference gas as shown in equation 6:
[GRAPHIC] [TIFF OMITTED] TR16AP19.011

    Only one ``above span'' calibration is needed per 24-hour period.
    (2) Compliance with the mercury emissions limit must be determined 
using a mercury CEMS or integrated sorbent trap monitoring system 
according to the following requirements:
    (i) You must operate a mercury CEMS system in accordance with 
performance specification 12A of 40 CFR part 60, appendix B or an 
integrated sorbent trap monitoring system in accordance with 
performance specification 12B of 40 CFR part 60, appendix B; these 
monitoring systems must be quality assured according to procedure 5 of 
40

[[Page 15863]]

CFR 60, appendix F. For the purposes of emissions calculations when 
using an integrated sorbent trap monitoring system, the mercury 
concentration determined for each sampling period must be assigned to 
each hour during the sampling period. If you choose to comply with the 
production-rate based mercury limit for your waste-burning kiln, you 
must also monitor hourly clinker production and determine the hourly 
mercury emissions rate in pounds per million ton of clinker produced. 
You must demonstrate compliance with the mercury emissions limit using 
a 30-day rolling average of these 1-hour mercury concentrations or mass 
emissions rates, including CEMS and integerated sorbent trap monitoring 
system data during startup and shutdown as defined in this subpart, 
calculated using equation 19-19 in section 12.4.1 of EPA Reference 
Method 19 at 40 CFR part 60, appendix A-7 of this part. Integerated 
sorbent trap monitoring system and CEMS data during startup and 
shutdown, as defined in this subpart, are not corrected to 7 percent 
oxygen, and are measured at stack oxygen content;
    (ii) Owners or operators using a mercury CEMS or integrated sorbent 
trap monitoring system to determine mass emission rate must install, 
operate, calibrate, and maintain an instrument for continuously 
measuring and recording the mercury mass emissions rate to the 
atmosphere according to the requirements of performance specification 6 
of 40 CFR part 60, appendix B, and conducting an annual relative 
accuracy test of the continuous emission rate monitoring system 
according to section 8.2 of performance specification 6; and
    (iii) The owner or operator of a waste-burning kiln must 
demonstrate initial compliance by operating a mercury CEMS or 
integrated sorbent trap monitoring system while the raw mill of the in-
line kiln/raw mill is operating under normal conditions and including 
at least one period when the raw mill is off.
    (k) If you use an air pollution control device to meet the emission 
limitations in this subpart, you must conduct an initial and annual 
inspection of the air pollution control device. The inspection must 
include, at a minimum, the following:
    (1) Inspect air pollution control device(s) for proper operation; 
and
    (2) Develop a site-specific monitoring plan according to the 
requirements in paragraph (l) of this section. This requirement also 
applies to you if you petition the EPA Administrator for alternative 
monitoring parameters under Sec.  60.13(i).
    (l) For each continuous monitoring system required in this section, 
you must develop and submit to the EPA Administrator for approval a 
site-specific monitoring plan according to the requirements of this 
paragraph (l) that addresses paragraphs (l)(1)(i) through (vi) of this 
section:
    (1) You must submit this site-specific monitoring plan at least 60 
days before your initial performance evaluation of your continuous 
monitoring system:
    (i) Installation of the continuous monitoring system sampling probe 
or other interface at a measurement location relative to each affected 
process unit such that the measurement is representative of control of 
the exhaust emissions (e.g., on or downstream of the last control 
device);
    (ii) Performance and equipment specifications for the sample 
interface, the pollutant concentration or parametric signal analyzer 
and the data collection and reduction systems.
    (iii) Performance evaluation procedures and acceptance criteria 
(e.g., calibrations);
    (iv) Ongoing operation and maintenance procedures in accordance 
with the general requirements of Sec.  60.11(d);
    (v) Ongoing data quality assurance procedures in accordance with 
the general requirements of Sec.  60.13; and
    (vi) Ongoing recordkeeping and reporting procedures in accordance 
with the general requirements of Sec.  60.7(b), (c) introductory text, 
(c)(1) and (4), and (d) through (g).
    (2) You must conduct a performance evaluation of each continuous 
monitoring system in accordance with your site-specific monitoring 
plan.
    (3) You must operate and maintain the continuous monitoring system 
in continuous operation according to the site-specific monitoring plan.
    (m) If you have an operating limit that requires the use of a flow 
monitoring system, you must meet the requirements in paragraphs (l) and 
(m)(1) through (4) of this section:
    (1) Install the flow sensor and other necessary equipment in a 
position that provides a representative flow;
    (2) Use a flow sensor with a measurement sensitivity at full scale 
of no greater than 2 percent;
    (3) Minimize the effects of swirling flow or abnormal velocity 
distributions due to upstream and downstream disturbances; and
    (4) Conduct a flow monitoring system performance evaluation in 
accordance with your monitoring plan at the time of each performance 
test but no less frequently than annually.
    (n) If you have an operating limit that requires the use of a 
pressure monitoring system, you must meet the requirements in 
paragraphs (l) and (n)(1) through (6) of this section:
    (1) Install the pressure sensor(s) in a position that provides a 
representative measurement of the pressure (e.g., PM scrubber pressure 
drop);
    (2) Minimize or eliminate pulsating pressure, vibration, and 
internal and external corrosion;
    (3) Use a pressure sensor with a minimum tolerance of 1.27 
centimeters of water or a minimum tolerance of 1 percent of the 
pressure monitoring system operating range, whichever is less;
    (4) Perform checks at the frequency outlined in your site-specific 
monitoring plan to ensure pressure measurements are not obstructed 
(e.g., check for pressure tap plugging daily);
    (5) Conduct a performance evaluation of the pressure monitoring 
system in accordance with your monitoring plan at the time of each 
performance test but no less frequently than annually; and
    (6) If at any time the measured pressure exceeds the manufacturer's 
specified maximum operating pressure range, conduct a performance 
evaluation of the pressure monitoring system in accordance with your 
monitoring plan and confirm that the pressure monitoring system 
continues to meet the performance requirements in your monitoring plan. 
Alternatively, install and verify the operation of a new pressure 
sensor.
    (o) If you have an operating limit that requires a pH monitoring 
system, you must meet the requirements in paragraphs (l) and (o)(1) 
through (4) of this section:
    (1) Install the pH sensor in a position that provides a 
representative measurement of scrubber effluent pH;
    (2) Ensure the sample is properly mixed and representative of the 
fluid to be measured;
    (3) Conduct a performance evaluation of the pH monitoring system in 
accordance with your monitoring plan at least once each process 
operating day; and
    (4) Conduct a performance evaluation (including a two-point 
calibration with one of the two buffer solutions having a pH within 1 
of the pH of the operating limit) of the pH monitoring system in 
accordance with your monitoring plan at the time of each performance 
test but no less frequently than quarterly.
    (p) If you have an operating limit that requires a secondary 
electric power monitoring system for an electrostatic

[[Page 15864]]

precipitator, you must meet the requirements in paragraphs (l) and 
(p)(1) and (2) of this section:
    (1) Install sensors to measure (secondary) voltage and current to 
the precipitator collection plates; and
    (2) Conduct a performance evaluation of the electric power 
monitoring system in accordance with your monitoring plan at the time 
of each performance test but no less frequently than annually.
    (q) If you have an operating limit that requires the use of a 
monitoring system to measure sorbent injection rate (e.g., weigh belt, 
weigh hopper, or hopper flow measurement device), you must meet the 
requirements in paragraphs (l) and (q)(1) and (2) of this section:
    (1) Install the system in a position(s) that provides a 
representative measurement of the total sorbent injection rate; and
    (2) Conduct a performance evaluation of the sorbent injection rate 
monitoring system in accordance with your monitoring plan at the time 
of each performance test but no less frequently than annually.
    (r) If you elect to use a fabric filter bag leak detection system 
to comply with the requirements of this subpart, you must install, 
calibrate, maintain, and continuously operate a bag leak detection 
system as specified in paragraphs (l) and (r)(1) through (5) of this 
section:
    (1) Install a bag leak detection sensor(s) in a position(s) that 
will be representative of the relative or absolute particulate matter 
loadings for each exhaust stack, roof vent, or compartment (e.g., for a 
positive pressure fabric filter) of the fabric filter;
    (2) Use a bag leak detection system certified by the manufacturer 
to be capable of detecting particulate matter emissions at 
concentrations of 10 milligrams per actual cubic meter or less;
    (3) Conduct a performance evaluation of the bag leak detection 
system in accordance with your monitoring plan and consistent with the 
guidance provided in EPA-454/R-98-015 (incorporated by reference, see 
Sec.  60.17);
    (4) Use a bag leak detection system equipped with a device to 
continuously record the output signal from the sensor; and
    (5) Use a bag leak detection system equipped with a system that 
will sound an alarm when an increase in relative particulate matter 
emissions over a preset level is detected. The alarm must be located 
where it is observed readily by plant operating personnel.
    (s) For facilities using a CEMS to demonstrate initial and 
continuous compliance with the sulfur dioxide emission limit, 
compliance with the sulfur dioxide emission limit may be demonstrated 
by using the CEMS specified in Sec.  60.2165(l) to measure sulfur 
dioxide. The sulfur dioxide CEMS must follow the procedures and methods 
specified in paragraph (s) of this section. For sources that have 
actual inlet emissions less than 100 parts per million dry volume, the 
relative accuracy criterion for inlet sulfur dioxide CEMS should be no 
greater than 20 percent of the mean value of the reference method test 
data in terms of the units of the emission standard, or 5 parts per 
million dry volume absolute value of the mean difference between the 
reference method and the CEMS, whichever is greater:
    (1) During each relative accuracy test run of the CEMS required by 
performance specification 2 in appendix B of this part, collect sulfur 
dioxide and oxygen (or carbon dioxide) data concurrently (or within a 
30- to 60-minute period) with both the CEMS and the test methods 
specified in paragraphs (s)(1)(i) and (ii) of this section:
    (i) For sulfur dioxide, EPA Reference Method 6 or 6C, or as an 
alternative ANSI/ASME PTC 19.10-1981 (incorporated by reference, see 
Sec.  60.17) must be used; and
    (ii) For oxygen (or carbon dioxide), EPA Reference Method 3A or 3B, 
or as an alternative ANSI/ASME PTC 19.10-1981 (incorporated by 
reference, see Sec.  60.17), must be used.
    (2) The span value of the CEMS at the inlet to the sulfur dioxide 
control device must be 125 percent of the maximum estimated hourly 
potential sulfur dioxide emissions of the unit subject to this subpart. 
The span value of the CEMS at the outlet of the sulfur dioxide control 
device must be 50 percent of the maximum estimated hourly potential 
sulfur dioxide emissions of the unit subject to this subpart.
    (3) Conduct accuracy determinations quarterly and calibration drift 
tests daily in accordance with procedure 1 in appendix F of this part.
    (t) For facilities using a CEMS to demonstrate initial and 
continuous compliance with the nitrogen oxides emission limit, 
compliance with the nitrogen oxides emission limit may be demonstrated 
by using the CEMS specified in Sec.  60.2165 to measure nitrogen 
oxides. The nitrogen oxides CEMS must follow the procedures and methods 
specified in paragraphs (t)(1) through (4) of this section:
    (1) During each relative accuracy test run of the CEMS required by 
performance specification 2 of appendix B of this part, collect 
nitrogen oxides and oxygen (or carbon dioxide) data concurrently (or 
within a 30- to 60-minute period) with both the CEMS and the test 
methods specified in paragraphs (t)(1)(i) and (ii) of this section:
    (i) For nitrogen oxides, EPA Reference Method 7 or 7E at 40 CFR 
part 60, appendix A-4 must be used; and
    (ii) For oxygen (or carbon dioxide), EPA Reference Method 3A or 3B 
at 40 CFR part 60, appendix A-3, or as an alternative ANSI/ASME PTC 19-
10.1981 (incorporated by reference, see Sec.  60.17), as applicable, 
must be used.
    (2) The span value of the continuous emission monitoring system 
must be 125 percent of the maximum estimated hourly potential nitrogen 
oxide emissions of the unit.
    (3) Conduct accuracy determinations quarterly and calibration drift 
tests daily in accordance with procedure 1 in appendix F of this part.
    (4) The owner or operator of an affected facility may request that 
compliance with the nitrogen oxides emission limit be determined using 
carbon dioxide measurements corrected to an equivalent of 7 percent 
oxygen. If carbon dioxide is selected for use in diluent corrections, 
the relationship between oxygen and carbon dioxide levels must be 
established during the initial performance test according to the 
procedures and methods specified in paragraphs (t)(4)(i) through (iv) 
of this section. This relationship may be re-established during 
performance compliance tests:
    (i) The fuel factor equation in Method 3B must be used to determine 
the relationship between oxygen and carbon dioxide at a sampling 
location. Method 3A or 3B, or as an alternative ANSI/ASME PTC 19.10-
1981 (incorporated by reference, see Sec.  60.17), as applicable, must 
be used to determine the oxygen concentration at the same location as 
the carbon dioxide monitor;
    (ii) Samples must be taken for at least 30 minutes in each hour;
    (iii) Each sample must represent a 1-hour average; and
    (iv) A minimum of three runs must be performed.
    (u) For facilities using a CEMS or an integrated sorbent trap 
monitoring system for mercury to demonstrate initial and 
continuouscompliance with any of the emission limits of this subpart, 
you must complete the following:
    (1) Demonstrate compliance with the appropriate emission limit(s) 
using a 30-day rolling average of 1-hour arithmetic average emission 
concentrations, including CEMS or integrated sorbent trap monitoring 
systems data during startup and shutdown as defined in this

[[Page 15865]]

subpart, calculated using equation 19-19 in section 12.4.1 of EPA 
Reference Method 19 at appendix A-7 of this part. The 1-hour arithmetic 
averages for CEMS must be calculated using the data points required 
under Sec.  60.13(e)(2). Except for CEMS or integrated sorbent trap 
monitoring systems data during startup and shutdown, the 1-hour 
arithmetic averages used to calculate the 30-day rolling average 
emission concentrations must be corrected to 7 percent oxygen (dry 
basis). Integrated sorbent trap monitoring systems or CEMS data during 
startup and shutdown, as defined in the subpart, are not corrected to 7 
percent oxygen, and are measured at stack oxygen content; and
    (2) Operate all CEMS and integrated sorbent trap monitoring systems 
in accordance with the applicable procedures under appendices B and F 
of this part.
    (v) Use of the bypass stack at any time is an emissions standards 
deviation for PM, HCl, lead, cadmium, mercury, nitrogen oxides, sulfur 
dioxide, and dioxin/furans.
    (w) For energy recovery units with a design heat input capacity of 
100 MMBtu/hr or greater that do not use a carbon monoxide CEMS, you 
must install, operate, and maintain a oxygen analyzer system as defined 
in Sec.  60.2265 according to the procedures in paragraphs (w)(1) 
through (4) of this section:
    (1) The oxygen analyzer system must be installed by the initial 
performance test date specified in Sec.  60.2140;
    (2) You must operate the oxygen trim system within compliance with 
paragraph (w)(3) of this section at all times;
    (3) You must maintain the oxygen level such that the 30-day rolling 
average that is established as the operating limit for oxygen is not 
below the lowest hourly average oxygen concentration measured during 
the most recent CO performance test; and
    (4) You must calculate and record a 30-day rolling average oxygen 
concentration using equation 19-19 in section 12.4.1 of EPA Reference 
Method 19 of Appendix A-7 of this part.
    (x) For energy recovery units with annual average heat input rates 
greater than or equal to 250 MMBtu/hr and waste-burning kilns, you must 
install, calibrate, maintain, and operate a PM CPMS and record the 
output of the system as specified in paragraphs (x)(1) through (8) of 
this section. For other energy recovery units, you may elect to use PM 
CPMS operated in accordance with this section. PM CPMS are suitable in 
lieu of using other CMS for monitoring PM compliance (e.g., bag leak 
detectors, ESP secondary power, PM scrubber pressure):
    (1) Install, calibrate, operate, and maintain your PM CPMS 
according to the procedures in your approved site-specific monitoring 
plan developed in accordance with paragraphs (l) and (x)(1)(i) through 
(iii) of this section:
    (i) The operating principle of the PM CPMS must be based on in-
stack or extractive light scatter, light scintillation, beta 
attenuation, or mass accumulation detection of the exhaust gas or 
representative sample. The reportable measurement output from the PM 
CPMS must be expressed as milliamps or the digital signal equivalent;
    (ii) The PM CPMS must have a cycle time (i.e., period required to 
complete sampling, measurement, and reporting for each measurement) no 
longer than 60 minutes; and
    (iii) The PM CPMS must be capable of detecting and responding to 
particulate matter concentrations increments no greater than 0.5 mg/
actual cubic meter.
    (2) During the initial performance test or any such subsequent 
performance test that demonstrates compliance with the PM limit, you 
must adjust the site-specific operating limit in accordance with the 
results of the performance test according to the procedures specified 
in Sec.  60.2110.
    (3) Collect PM CPMS hourly average output data for all energy 
recovery unit or waste-burning kiln operating hours. Express the PM 
CPMS output as milliamps.
    (4) Calculate the arithmetic 30-day rolling average of all of the 
hourly average PM CPMS output collected during all energy recovery unit 
or waste-burning kiln operating hours data (milliamps or their digital 
equivalent).
    (5) You must collect data using the PM CPMS at all times the energy 
recovery unit or waste-burning kiln is operating and at the intervals 
specified in paragraph (x)(1)(ii) of this section, except for periods 
of monitoring system malfunctions, repairs associated with monitoring 
system malfunctions, required monitoring system quality assurance or 
quality control activities (including, as applicable, calibration 
checks and required zero and span adjustments), and any scheduled 
maintenance as defined in your site-specific monitoring plan.
    (6) You must use all the data collected during all energy recovery 
unit or waste-burning kiln operating hours in assessing the compliance 
with your operating limit except:
    (i) Any data collected during monitoring system malfunctions, 
repairs associated with monitoring system malfunctions, or required 
monitoring system quality assurance or quality control activities 
conducted during monitoring system malfunctions are not used in 
calculations (report any such periods in your annual deviation report);
    (ii) Any data collected during periods when the monitoring system 
is out of control as specified in your site-specific monitoring plan, 
repairs associated with periods when the monitoring system is out of 
control, or required monitoring system quality assurance or quality 
control activities conducted during out-of-control periods are not used 
in calculations (report emissions or operating levels and report any 
such periods in your annual deviation report);
    (iii) Any PM CPMS data recorded during periods of CEMS data during 
startup and shutdown, as defined in this subpart.
    (7) You must record and make available upon request results of PM 
CPMS system performance audits, as well as the dates and duration of 
periods from when the PM CPMS is out of control until completion of the 
corrective actions necessary to return the PM CPMS to operation 
consistent with your site-specific monitoring plan.
    (8) For any deviation of the 30-day rolling average PM CPMS average 
value from the established operating parameter limit, you must:
    (i) Within 48 hours of the deviation, visually inspect the air 
pollution control device;
    (ii) If inspection of the air pollution control device identifies 
the cause of the deviation, take corrective action as soon as possible 
and return the PM CPMS measurement to within the established value;
    (iii) Within 30 days of the deviation or at the time of the annual 
compliance test, whichever comes first, conduct a PM emissions 
compliance test to determine compliance with the PM emissions limit. 
Within 45 days of the deviation, you must re-establish the CPMS 
operating limit. You are not required to conduct additional testing for 
any deviations that occur between the time of the original deviation 
and the PM emissions compliance test required under paragraph (x) of 
this section; and
    (iv) PM CPMS deviations leading to more than four required 
performance tests in a 12-month process operating period (rolling 
monthly) constitute a violation of this subpart.
    (y) When there is an alkali bypass and/or an in-line coal mill that 
exhaust emissions through a separate stack(s),

[[Page 15866]]

the combined emissions are subject to the emission limits applicable to 
waste-burning kilns. To determine the kiln-specific emission limit for 
demonstrating compliance, you must:
    (1) Calculate a kiln-specific emission limit using equation 7:
    [GRAPHIC] [TIFF OMITTED] TR16AP19.012
    
Where:

Cks = Kiln stack concentration (ppmvd, mg/dscm, ng/dscm, 
depending on pollutant. Each corrected to 7% O2.)
Qab = Alkali bypass flow rate (volume/hr)
Cab = Alkali bypass concentration (ppmvd, mg/dscm, ng/
dscm, depending on pollutant. Each corrected to 7% O2.)
Qcm = In-line coal mill flow rate (volume/hr)
Ccm = In-line coal mill concentration (ppmvd, mg/dscm, 
ng/dscm, depending on pollutant. Each corrected to 7% 
O2.)
Qks = Kiln stack flow rate (volume/hr)

    (2) Particulate matter concentration must be measured downstream of 
the in-line coal mill. All other pollutant concentrations must be 
measured either upstream or downstream of the in-line coal mill; and
    (3) For purposes of determining the combined emissions from kilns 
equipped with an alkali bypass or that exhaust kiln gases to a coal 
mill that exhausts through a separate stack, instead of installing a 
CEMS or PM CPMS on the alkali bypass stack or in-line coal mill stack, 
the results of the initial and subsequent performance test can be used 
to demonstrate compliance with the relevant emissions limit. A 
performance test must be conducted on an annual basis (between 11 and 
13 calendar months following the previous performance test).


Sec.  60.2150   By what date must I conduct the annual performance 
test?

    You must conduct annual performance tests between 11 and 13 months 
of the previous performance test.


Sec.  60.2151   By what date must I conduct the annual air pollution 
control device inspection?

    On an annual basis (no more than 12 months following the previous 
annual air pollution control device inspection), you must complete the 
air pollution control device inspection as described in Sec.  60.2141.


Sec.  60.2155   May I conduct performance testing less often?

    (a) You must conduct annual performance tests according to the 
schedule specified in Sec.  60.2150, with the following exceptions:
    (1) You may conduct a repeat performance test at any time to 
establish new values for the operating limits, as specified in Sec.  
60.2160. New operating limits become effective on the date that the 
performance test report is submitted to the EPA's Central Data Exchange 
or postmarked, per the requirements of Sec.  60.2235(b). The 
Administrator may request a repeat performance test at any time;
    (2) You must repeat the performance test within 60 days of a 
process change, as defined in Sec.  60.2265;
    (3) You can conduct performance tests less often if you meet the 
following conditions: your performance tests for the pollutant for at 
least 2 consecutive performance tests demonstrates that the emission 
level for the pollutant is no greater than the emission level specified 
in paragraph (a)(3)(i) or (ii) of this section, as applicable; there 
are no changes in the operation of the affected source or air pollution 
control equipment that could increase emissions; and you are not 
required to conduct a performance test for the pollutant in response to 
a request by the Administrator in paragraph (a)(1) of this section or a 
process change in paragraph (a)(2) of this section. In this case, you 
do not have to conduct a performance test for that pollutant for the 
next 2 years. You must conduct a performance test for the pollutant no 
more than 37 months following the previous performance test for the 
pollutant. If the emission level for your CISWI continues to meet the 
emission level specified in paragraph (a)(3)(i) or (ii) of this 
section, as applicable, you may choose to conduct performance tests for 
the pollutant every third year, as long as there are no changes in the 
operation of the affected source or air pollution control equipment 
that could increase emissions. Each such performance test must be 
conducted no more than 37 months after the previous performance test.
    (i) For particulate matter, hydrogen chloride, mercury, nitrogen 
oxides, sulfur dioxide, cadmium, lead and dioxins/furans, the emission 
level equal to 75 percent of the applicable emission limit in table 1 
or tables 5 through 8 of this subpart, as applicable; and
    (ii) For fugitive emissions, visible emissions (of combustion ash 
from the ash conveying system) for 2 percent of the time during each of 
the three 1-hour observations periods.
    (4) If you are conducting less frequent testing for a pollutant as 
provided in paragraph (a)(3) of this section and a subsequent 
performance test for the pollutant indicates that your CISWI does not 
meet the emission level specified in paragraph (a)(3)(i) or (ii) of 
this section, as applicable, you must conduct annual performance tests 
for the pollutant according to the schedule specified in paragraph (a) 
of this section until you qualify for less frequent testing for the 
pollutant as specified in paragraph (a)(3) of this section.
    (b) [Reserved]


Sec.  60.2160  May I conduct a repeat performance test to establish new 
operating limits?

    (a) Yes. You may conduct a repeat performance test at any time to 
establish new values for the operating limits. The Administrator may 
request a repeat performance test at any time.
    (b) You must repeat the performance test if your feed stream is 
different than the feed streams used during any performance test used 
to demonstrate compliance.

Monitoring


Sec.  60.2165   What monitoring equipment must I install and what 
parameters must I monitor?

    (a) If you are using a wet scrubber to comply with the emission 
limitation under Sec.  60.2105, you must install, calibrate (to 
manufacturers' specifications), maintain, and operate devices (or 
establish methods) for monitoring the value of the operating parameters 
used to determine compliance with the operating limits listed in table 
2 of this subpart. These devices (or methods) must measure and record 
the values for these operating parameters at the frequencies indicated 
in table 2 of this subpart at all times except as specified in Sec.  
60.2170(a).
    (b) If you use a fabric filter to comply with the requirements of 
this subpart and you do not use a PM CPMS or PM CEMS for monitoring PM 
compliance, you must install, calibrate, maintain, and continuously 
operate a bag leak detection system as specified in paragraphs (b)(1) 
through (8) of this section:

[[Page 15867]]

    (1) You must install and operate a bag leak detection system for 
each exhaust stack of the fabric filter;
    (2) Each bag leak detection system must be installed, operated, 
calibrated, and maintained in a manner consistent with the 
manufacturer's written specifications and recommendations;
    (3) The bag leak detection system must be certified by the 
manufacturer to be capable of detecting particulate matter emissions at 
concentrations of 10 milligrams per actual cubic meter or less;
    (4) The bag leak detection system sensor must provide output of 
relative or absolute particulate matter loadings;
    (5) The bag leak detection system must be equipped with a device to 
continuously record the output signal from the sensor;
    (6) The bag leak detection system must be equipped with an alarm 
system that will alert automatically an operator when an increase in 
relative particulate matter emissions over a preset level is detected. 
The alarm must be located where it is observed easily by plant 
operating personnel;
    (7) For positive pressure fabric filter systems, a bag leak 
detection system must be installed in each baghouse compartment or 
cell. For negative pressure or induced air fabric filters, the bag leak 
detector must be installed downstream of the fabric filter; and
    (8) Where multiple detectors are required, the system's 
instrumentation and alarm may be shared among detectors.
    (c) If you are using something other than a wet scrubber, activated 
carbon, selective non-catalytic reduction, an electrostatic 
precipitator, or a dry scrubber to comply with the emission limitations 
under Sec.  60.2105, you must install, calibrate (to the manufacturers' 
specifications), maintain, and operate the equipment necessary to 
monitor compliance with the site-specific operating limits established 
using the procedures in Sec.  60.2115.
    (d) If you use activated carbon injection to comply with the 
emission limitations in this subpart, you must measure the minimum 
mercury sorbent flow rate once per hour.
    (e) If you use selective noncatalytic reduction to comply with the 
emission limitations, you must complete the following:
    (1) Following the date on which the initial performance test is 
completed or is required to be completed under Sec.  60.2125, whichever 
date comes first, ensure that the affected facility does not operate 
above the maximum charge rate, or below the minimum secondary chamber 
temperature (if applicable to your CISWI) or the minimum reagent flow 
rate measured as 3-hour block averages at all times; and
    (2) Operation of the affected facility above the maximum charge 
rate, below the minimum secondary chamber temperature and below the 
minimum reagent flow rate simultaneously constitute a violation of the 
nitrogen oxides emissions limit.
    (f) If you use an electrostatic precipitator to comply with the 
emission limits of this subpart and you do not use a PM CPMS for 
monitoring PM compliance, you must monitor the secondary power to the 
electrostatic precipitator collection plates and maintain the 3-hour 
block averages at or above the operating limits established during the 
mercury or particulate matter performance test.
    (g) For waste-burning kilns not equipped with a wet scrubber or dry 
scrubber, you must install, calibrate, maintain, and operate a CEMS for 
monitoring hydrogen chloride emissions discharged to the atmosphere, as 
specified in Sec.  60.2145(j), and record the output of the system. You 
may substitute use of a HCl CEMS for conducting the HCl initial and 
annual testing with EPA Method 321 at 40 CFR part 63, appendix A. For 
units other than waste-burning kilns not equipped with a wet scrubber 
or dry scrubber, a facility may substitute use of a hydrogen chloride 
CEMS for conducting the hydrogen chloride initial and annual 
performance test. For units equipped with a hydrogen chloride CEMS, you 
are not required to monitor the minimum hydrogen chloride sorbent flow 
rate, the minimum scrubber liquor pH, or the monitoring minimum 
injection rate.
    (h) To demonstrate compliance with the particulate matter emissions 
limit, a facility may substitute use of a particulate matter CEMS for 
conducting the PM initial and annual performance test. For units 
equipped with a particulate matter CEMS, you are not required to use 
other CMS for monitoring PM compliance (e.g., bag leak detectors, ESP 
secondary power, PM scrubber pressure).
    (i) To demonstrate initial and continuous compliance with the 
dioxin/furan emissions limit, a facility may substitute use of a 
continuous automated sampling system for the dioxin/furan initial and 
annual performance tests. You must record the output of the system and 
analyze the sample according to EPA Method 23 at 40 CFR part 60, 
Appendix A-7 of this part. This option to use a continuous automated 
sampling system takes effect on the date a final performance 
specification applicable to dioxin/furan from continuous monitors is 
published in the Federal Register. The owner or operator who elects to 
continuously sample dioxin/furan emissions instead of sampling and 
testing using EPA Method 23 at 40 CFR part 60, appendix A-7 must 
install, calibrate, maintain, and operate a continuous automated 
sampling system and must comply with the requirements specified in 
Sec.  60.58b(p) and (q). A facility may substitute continuous dioxin/
furan monitoring for the minimum sorbent flow rate, if activated carbon 
sorbent injection is used solely for compliance with the dioxin/furan 
emission limit.
    (j) To demonstrate initial and continuous compliance with the 
mercury emissions limit, a facility may substitute use of a mercury 
CEMS or an integrated sorbent trap monitoring system for the mercury 
initial and annual performance test. The owner or operator who elects 
to continuously measure mercury emissions instead of sampling and 
testing using EPA Reference Method 29 or 30B at 40 CFR part 60, 
appendix A-8, ASTM D6784-02 (Reapproved 2008) (incorporated by 
reference, see Sec.  60.17), or an approved alternative method for 
measuring mercury emissions, must install, calibrate, maintain, and 
operate the mercury CEMS or integrated sorbent trap monitoring system 
and must comply with performance specification 12A or performance 
specification 12B, respectively, and quality assurance procedure 5. For 
the purposes of emissions calculations when using an integrated sorbent 
trap monitoring system, the mercury concentration determined for each 
sampling period must be assigned to each hour during the sampling 
period. Waste-burning kilns must install, calibrate, maintain, and 
operate a mercury CEMS or an integrated sorbent trap monitoring system 
as specified in Sec.  60.2145(j). For units equipped with a mercury 
CEMS or an integrated sorbent trap monitoring system, you are not 
required to monitor the minimum sorbent flow rate, if activated carbon 
sorbent injection is used solely for compliance with the mercury 
emission limit.
    (k) To demonstrate initial and continuous compliance with the 
nitrogen oxides emissions limit, a facility may substitute use of a 
CEMS for the nitrogen oxides initial and annual performance test to 
demonstrate compliance with the nitrogen oxides emissions limits. For 
units equipped with a nitrogen oxides CEMS, you are not required to 
monitor the charge rate, secondary chamber temperature, and reagent 
flow for selective noncatalytic reduction, if applicable:

[[Page 15868]]

    (1) Install, calibrate, maintain, and operate a CEMS for measuring 
nitrogen oxides emissions discharged to the atmosphere and record the 
output of the system. The requirements under performance specification 
2 of appendix B of this part, the quality assurance procedure 1 of 
appendix F of this part and the procedures under Sec.  60.13 must be 
followed for installation, evaluation, and operation of the CEMS; and
    (2) Compliance with the emission limit for nitrogen oxides must be 
determined based on the 30-day rolling average of the hourly emission 
concentrations using CEMS outlet data, as outlined in Sec.  60.2145(u).
    (l) To demonstrate initial and continuous compliance with the 
sulfur dioxide emissions limit, a facility may substitute use of a CEMS 
for the sulfur dioxide initial and annual performance test to 
demonstrate compliance with the sulfur dioxide emissions limits:
    (1) Install, calibrate, maintain, and operate a CEMS for measuring 
sulfur dioxide emissions discharged to the atmosphere and record the 
output of the system. The requirements under performance specification 
2 of appendix B of this part, the quality assurance requirements of 
procedure one of appendix F of this part and procedures under Sec.  
60.13 must be followed for installation, evaluation, and operation of 
the CEMS; and
    (2) Compliance with the sulfur dioxide emission limit shall be 
determined based on the 30-day rolling average of the hourly arithmetic 
average emission concentrations using CEMS outlet data, as outlined in 
Sec.  60.2145(u).
    (m) For energy recovery units over 10 MMBtu/hr but less than 250 
MMBtu/hr annual average heat input rates that do not use a wet 
scrubber, fabric filter with bag leak detection system, an 
electrostatic precipitator, particulate matter CEMS, or particulate 
matter CPMS you must install, operate, certify, and maintain a 
continuous opacity monitoring system according to the procedures in 
paragraphs (m)(1) through (5) of this section by the compliance date 
specified in Sec.  60.2105. Energy recovery units that use a CEMS to 
demonstrate initial and continuing compliance according to the 
procedures in Sec.  60.2165(n) are not required to install a continuous 
opacity monitoring system and must perform the annual performance tests 
for the opacity consistent with Sec.  60.2145(f):
    (1) Install, operate, and maintain each continuous opacity 
monitoring system according to performance specification 1 of 40 CFR 
part 60, appendix B;
    (2) Conduct a performance evaluation of each continuous opacity 
monitoring system according to the requirements in Sec.  60.13 and 
according to PS-1 of 40 CFR part 60, appendix B;
    (3) As specified in Sec.  60.13(e)(1), each continuous opacity 
monitoring system must complete a minimum of one cycle of sampling and 
analyzing for each successive 10-second period and one cycle of data 
recording for each successive 6-minute period;
    (4) Reduce the continuous opacity monitoring system data as 
specified in Sec.  60.13(h)(1); and
    (5) Determine and record all the 6-minute averages (and 1-hour 
block averages as applicable) collected.
    (n) For coal and liquid/gas energy recovery units, incinerators, 
and small remote incinerators, an owner or operator may elect to 
install, calibrate, maintain, and operate a CEMS for monitoring 
particulate matter emissions discharged to the atmosphere and record 
the output of the system. The owner or operator of an affected facility 
who continuously monitors particulate matter emissions instead of 
conducting performance testing using EPA Method 5 at 40 CFR part 60, 
appendix A-3 or monitoring with a particulate matter CPMS according to 
paragraph (r) of this section, must install, calibrate, maintain, and 
operate a PM CEMS and must comply with the requirements specified in 
paragraphs (n)(1) through (10) of this section:
    (1) The PM CEMS must be installed, evaluated, and operated in 
accordance with the requirements of performance specification 11 of 
appendix B of this part and quality assurance requirements of procedure 
2 of appendix F of this part and Sec.  60.13. Use Method 5 or Method 5I 
of appendix A of this part for the PM CEMS correlation testing;
    (2) The initial performance evaluation must be completed no later 
than 180 days after the date of initial startup of the affected 
facility, as specified under Sec.  60.2125 or within 180 days of 
notification to the Administrator of use of the continuous monitoring 
system if the owner or operator was previously determining compliance 
by Method 5 performance tests, whichever is later;
    (3) The owner or operator of an affected facility may request that 
compliance with the particulate matter emission limit be determined 
using carbon dioxide measurements corrected to an equivalent of 7 
percent oxygen. The relationship between oxygen and carbon dioxide 
levels for the affected facility must be established according to the 
procedures and methods specified in Sec.  60.2145(t)(4)(i) through 
(iv);
    (4) The owner or operator of an affected facility must conduct an 
initial performance test for particulate matter emissions. If PM CEMS 
are elected for demonstrating compliance, and the initial performance 
test has not yet been conducted, then initial compliance must be 
determined by using the CEMS specified in paragraph (n) of this section 
to measure particulate matter. You must calculate a 30-day rolling 
average of 1-hour arithmetic average emission concentrations, including 
CEMS data during startup and shutdown, as defined in this subpart, 
using equation 19-19 in section 12.4.1 of EPA Reference Method 19 at 40 
CFR part 60, appendix A-7;
    (5) Continuous compliance with the particulate matter emission 
limit must be determined based on the 30-day rolling average calculated 
using equation 19-19 in section 12.4.1 of EPA Reference Method 19 at 40 
CFR part 60, appendix A-7 from the 1-hour arithmetic average CEMS 
outlet data;
    (6) At a minimum, valid continuous monitoring system hourly 
averages must be obtained as specified in Sec.  60.2170(e);
    (7) The 1-hour arithmetic averages required under paragraph (n)(5) 
of this section must be expressed in milligrams per dry standard cubic 
meter corrected to 7 percent oxygen (dry basis) and must be used to 
calculate the 30-day rolling average emission concentrations. CEMS data 
during startup and shutdown, as defined in this subpart, are not 
corrected to 7 percent oxygen, and are measured at stack oxygen 
content. The 1-hour arithmetic averages must be calculated using the 
data points required under Sec.  60.13(e)(2);
    (8) All valid CEMS data must be used in calculating average 
emission concentrations even if the minimum CEMS data requirements of 
paragraph (n)(6) of this section are not met.
    (9) The CEMS must be operated according to performance 
specification 11 in appendix B of this part; and,
    (10) Quarterly and yearly accuracy audits and daily drift, system 
optics, and sample volume checks must be performed in accordance with 
procedure 2 in appendix F of this part.
    (o) To demonstrate initial and continuous compliance with the 
carbon monoxide emissions limit, you may substitute use of a CEMS for 
the carbon monoxide initial and annual performance test:
    (1) Install, calibrate, maintain, and operate a CEMS for measuring 
carbon monoxide emissions discharged to the atmosphere and record the 
output of the system. The requirements under performance specification 
4A or 4B of appendix B of this part, the quality assurance procedure 1 
of appendix F of this part and the procedures under Sec.  60.13 must be 
followed for

[[Page 15869]]

installation, evaluation, and operation of the CEMS; and
    (2) Compliance with the carbon monoxide emission limit shall be 
determined based on the 30-day rolling average of the hourly arithmetic 
average emission concentrations, including CEMS data during startup and 
shutdown as defined in this subpart, using CEMS outlet data, as 
outlined in Sec.  60.2145(u).
    (p) The owner/operator of an affected source with a bypass stack 
shall install, calibrate (to manufacturers' specifications), maintain, 
and operate a device or method for measuring the use of the bypass 
stack including date, time and duration.
    (q) For energy recovery units with a design heat input capacity of 
100 MMBtu/hr or greater that do not use a carbon monoxide CEMS, you 
must install, operate, and maintain a oxygen analyzer system as defined 
in Sec.  60.2265 according to the procedures in paragraphs (q)(1) 
through (4) of this section:
    (1) The oxygen analyzer system must be installed by the initial 
performance test date specified in Sec.  60.2140;
    (2) You must operate the oxygen trim system within compliance with 
paragraph (q)(3) of this section at all times;
    (3) You must maintain the oxygen level such that the 30-day rolling 
average that is established as the operating limit for oxygen according 
to paragraph (q)(4) of this section is not below the lowest hourly 
average oxygen concentration measured during the most recent CO 
performance test; and
    (4) You must calculate and record a 30-day rolling average oxygen 
concentration using equation 19-19 in section 12.4.1 of EPA Reference 
Method 19 of Appendix A-7 of this part.
    (r) For energy recovery units with annual average heat input rates 
greater than or equal to 250 MMBtu/hr and waste-burning kilns, you must 
install, calibrate, maintain, and operate a PM CPMS and record the 
output of the system as specified in paragraphs (r)(1) through (8) of 
this section. If you elect to use a particulate matter CEMS as 
specified in paragraph (n) of this section, you are not required to use 
a PM CPMS to monitor particulate matter emissions. For other energy 
recovery units, you may elect to use PM CPMS operated in accordance 
with this section. PM CPMS are suitable in lieu of using other CMS for 
monitoring PM compliance (e.g., bag leak detectors, ESP secondary 
power, PM scrubber pressure):
    (1) Install, calibrate, operate, and maintain your PM CPMS 
according to the procedures in your approved site-specific monitoring 
plan developed in accordance with Sec.  60.2145(l) and paragraphs 
(r)(1)(i) through (iii) of this section:
    (i) The operating principle of the PM CPMS must be based on in-
stack or extractive light scatter, light scintillation, beta 
attenuation, or mass accumulation detection of PM in the exhaust gas or 
representative sample. The reportable measurement output from the PM 
CPMS must be expressed as milliamps or a digital signal equivalent;
    (ii) The PM CPMS must have a cycle time (i.e., period required to 
complete sampling, measurement, and reporting for each measurement) no 
longer than 60 minutes; and
    (iii) The PM CPMS must be capable of detecting and responding to 
particulate matter concentration increments no greater than 0.5 mg/
actual cubic meter.
    (2) During the initial performance test or any such subsequent 
performance test that demonstrates compliance with the PM limit, you 
must adjust the site-specific operating limit in accordance with the 
results of the performance test according to the procedures specified 
in Sec.  60.2110.
    (3) Collect PM CPMS hourly average output data for all energy 
recovery unit or waste-burning kiln operating hours. Express the PM 
CPMS output as milliamps or the digital signal equivalent.
    (4) Calculate the arithmetic 30-day rolling average of all of the 
hourly average PM CPMS output collected during all energy recovery unit 
or waste-burning kiln operating hours data (milliamps or digital bits).
    (5) You must collect data using the PM CPMS at all times the energy 
recovery unit or waste-burning kiln is operating and at the intervals 
specified in paragraph (r)(1)(ii) of this section, except for periods 
of monitoring system malfunctions, repairs associated with monitoring 
system malfunctions, required monitoring system quality assurance or 
quality control activities (including, as applicable, calibration 
checks and required zero and span adjustments), and any scheduled 
maintenance as defined in your site-specific monitoring plan.
    (6) You must use all the data collected during all energy recovery 
unit or waste-burning kiln operating hours in assessing the compliance 
with your operating limit except:
    (i) Any data collected during monitoring system malfunctions, 
repairs associated with monitoring system malfunctions, or required 
monitoring system quality assurance or quality control activities 
conducted during monitoring system malfunctions are not used in 
calculations (report any such periods in your annual deviation report);
    (ii) Any data collected during periods when the monitoring system 
is out of control as specified in your site-specific monitoring plan, 
repairs associated with periods when the monitoring system is out of 
control, or required monitoring system quality assurance or quality 
control activities conducted during out-of-control periods are not used 
in calculations (report emissions or operating levels and report any 
such periods in your annual deviation report); and
    (iii) Any PM CPMS data recorded during periods of CEMS data during 
startup and shutdown, as defined in this subpart.
    (7) You must record and make available upon request results of PM 
CPMS system performance audits, as well as the dates and duration of 
periods from when the PM CPMS is out of control until completion of the 
corrective actions necessary to return the PM CPMS to operation 
consistent with your site-specific monitoring plan.
    (8) For any deviation of the 30-day rolling average PM CPMS average 
value from the established operating parameter limit, you must:
    (i) Within 48 hours of the deviation, visually inspect the air 
pollution control device;
    (ii) If inspection of the air pollution control device identifies 
the cause of the deviation, take corrective action as soon as possible 
and return the PM CPMS measurement to within the established value;
    (iii) Within 30 days of the deviation or at the time of the annual 
compliance test, whichever comes first, conduct a PM emissions 
compliance test to determine compliance with the PM emissions limit and 
to verify the operation of the emissions control device(s). Within 45 
days of the deviation, you must re-establish the CPMS operating limit. 
You are not required to conduct additional testing for any deviations 
that occur between the time of the original deviation and the PM 
emissions compliance test required under this paragraph; and
    (iv) PM CPMS deviations leading to more than four required 
performance tests in a 12-month process operating period (rolling 
monthly) constitute a violation of this subpart.
    (s) If you use a dry scrubber to comply with the emission limits of 
this subpart, you must monitor the injection rate of each sorbent and 
maintain the 3-hour block averages at or above the operating

[[Page 15870]]

limits established during the hydrogen chloride performance test.
    (t) If you are required to monitor clinker production because you 
comply with the production-rate based mercury limit for your waste-
burning kiln, you must:
    (1) Determine hourly clinker production by one of two methods:
    (i) Install, calibrate, maintain, and operate a permanent weigh 
scale system to measure and record weight rates in tons-mass per hour 
of the amount of clinker produced. The system of measuring hourly 
clinker production must be maintained within 5 percent 
accuracy, or
    (ii) Install, calibrate, maintain, and operate a permanent weigh 
scale system to measure and record weight rates in tons-mass per hour 
of the amount of feed to the kiln. The system of measuring feed must be 
maintained within 5 percent accuracy. Calculate your hourly 
clinker production rate using a kiln-specific feed to clinker ratio 
based on reconciled clinker production determined for accounting 
purposes and recorded feed rates. Update this ratio monthly. Note that 
if this ratio changes at clinker reconciliation, you must use the new 
ratio going forward, but you do not have to retroactively change 
clinker production rates previously estimated.
    (2) Determine the accuracy of the system of measuring hourly 
clinker production (or feed mass flow if applicable) before the 
effective date and during each quarter of source operation.
    (3) Conduct accuracy checks in accordance with the procedures 
outlined in your site-specific monitoring plan under Sec.  60.2145(l).


Sec.  60.2170   Is there a minimum amount of monitoring data I must 
obtain?

    For each continuous monitoring system required or optionally 
allowed under Sec.  60.2165, you must collect data according to this 
section:
    (a) You must operate the monitoring system and collect data at all 
required intervals at all times compliance is required except for 
periods of monitoring system malfunctions or out-of-control periods, 
repairs associated with monitoring system malfunctions or out-of-
control periods (as specified in 60.2210(o)), and required monitoring 
system quality assurance or quality control activities (including, as 
applicable, calibration checks and required zero and span adjustments). 
A monitoring system malfunction is any sudden, infrequent, not 
reasonably preventable failure of the monitoring system to provide 
valid data. Monitoring system failures that are caused in part by poor 
maintenance or careless operation are not malfunctions. You are 
required to effect monitoring system repairs in response to monitoring 
system malfunctions or out-of-control periods and to return the 
monitoring system to operation as expeditiously as practicable;
    (b) You may not use data recorded during monitoring system 
malfunctions or out-of-control periods, repairs associated with 
monitoring system malfunctions or out-of-control periods, or required 
monitoring system quality assurance or control activities in 
calculations used to report emissions or operating levels. You must use 
all the data collected during all other periods, including data 
normalized for above scale readings, in assessing the operation of the 
control device and associated control system; and
    (c) Except for periods of monitoring system malfunctions or out-of-
control periods, repairs associated with monitoring system malfunctions 
or out-of-control periods, and required monitoring system quality 
assurance or quality control activities including, as applicable, 
calibration checks and required zero and span adjustments, failure to 
collect required data is a deviation of the monitoring requirements.

Recordkeeping and Reporting


Sec.  60.2175   What records must I keep?

    You must maintain the items (as applicable) as specified in 
paragraphs (a), (b), and (e) through (x) of this section for a period 
of at least 5 years:
    (a) Calendar date of each record; and
    (b) Records of the data described in paragraphs (b)(1) through (7) 
of this section:
    (1) The CISWI charge dates, times, weights, and hourly charge 
rates;
    (2) Liquor flow rate to the wet scrubber inlet every 15 minutes of 
operation, as applicable;
    (3) Pressure drop across the wet scrubber system every 15 minutes 
of operation or amperage to the wet scrubber every 15 minutes of 
operation, as applicable;
    (4) Liquor pH as introduced to the wet scrubber every 15 minutes of 
operation, as applicable;
    (5) For affected CISWIs that establish operating limits for 
controls other than wet scrubbers under Sec.  60.2110(d) through (g) or 
Sec.  60.2115, you must maintain data collected for all operating 
parameters used to determine compliance with the operating limits. For 
energy recovery units using activated carbon injection or a dry 
scrubber, you must also maintain records of the load fraction and 
corresponding sorbent injection rate records;
    (6) If a fabric filter is used to comply with the emission 
limitations, you must record the date, time, and duration of each alarm 
and the time corrective action was initiated and completed, and a brief 
description of the cause of the alarm and the corrective action taken. 
You must also record the percent of operating time during each 6-month 
period that the alarm sounds, calculated as specified in Sec.  
60.2110(c);
    (7) If you monitor clinker production in accordance with Sec.  
60.2165(t):
    (i) Hourly clinker rate produced if clinker production is measured 
directly;
    (ii) Hourly measured kiln feed rates and calculated clinker 
production rates if clinker production is not measured directly;
    (iii) 30-day rolling averages for mercury in pounds per million 
tons of clinker produced;
    (iv) The initial and quarterly accuracy of the system of measruing 
hourly clinker production (or feed mass flow).
    (c)-(d) [Reserved]
    (e) Identification of calendar dates and times for which data show 
a deviation from the operating limits in table 2 of this subpart or a 
deviation from other operating limits established under Sec.  
60.2110(d) through (g) or Sec.  60.2115 with a description of the 
deviations, reasons for such deviations, and a description of 
corrective actions taken;
    (f) The results of the initial, annual, and any subsequent 
performance tests conducted to determine compliance with the emission 
limits and/or to establish operating limits, as applicable. Retain a 
copy of the complete test report including calculations;
    (g) All documentation produced as a result of the siting 
requirements of Sec. Sec.  60.2045 and 60.2050;
    (h) Records showing the names of CISWI operators who have completed 
review of the information in Sec.  60.2095(a) as required by Sec.  
60.2095(b), including the date of the initial review and all subsequent 
annual reviews;
    (i) Records showing the names of the CISWI operators who have 
completed the operator training requirements under Sec.  60.2070, met 
the criteria for qualification under Sec.  60.2080, and maintained or 
renewed their qualification under Sec.  60.2085 or Sec.  60.2090. 
Records must include documentation of training, the dates of the 
initial and refresher training, and the dates of their qualification 
and all subsequent renewals of such qualifications;
    (j) For each qualified operator, the phone and/or pager number at 
which

[[Page 15871]]

they can be reached during operating hours;
    (k) Records of calibration of any monitoring devices as required 
under Sec.  60.2165;
    (l) Equipment vendor specifications and related operation and 
maintenance requirements for the incinerator, emission controls, and 
monitoring equipment;
    (m) The information listed in Sec.  60.2095(a);
    (n) On a daily basis, keep a log of the quantity of waste burned 
and the types of waste burned (always required);
    (o) Maintain records of the annual air pollution control device 
inspections that are required for each CISWI subject to the emissions 
limits in table 1 of this subpart or tables 5 through 8 of this 
subpart, any required maintenance, and any repairs not completed within 
10 days of an inspection or the timeframe established by the state 
regulatory agency;
    (p) For continuously monitored pollutants or parameters, you must 
document and keep a record of the following parameters measured using 
continuous monitoring systems. If you monitor emissions with a CEMS, 
you must indicate which data are CEMS data during startup and shutdown:
    (1) All 6-minute average levels of opacity;
    (2) All 1-hour average concentrations of sulfur dioxide emissions;
    (3) All 1-hour average concentrations of nitrogen oxides emissions;
    (4) All 1-hour average concentrations of carbon monoxide emissions;
    (5) All 1-hour average concentrations of particulate matter 
emissions;
    (6) All 1-hour average concentrations of mercury emissions;
    (7) All 1-hour average concentrations of HCl CEMS outputs;
    (8) All 1-hour average percent oxygen concentrations; and
    (9) All 1-hour average PM CPMS readings or particulate matter CEMS 
outputs;
    (q) Records indicating use of the bypass stack, including dates, 
times, and durations.
    (r) If you choose to stack test less frequently than annually, 
consistent with Sec.  60.2155(a) through (c), you must keep annual 
records that document that your emissions in the previous stack test(s) 
were less than 75 percent of the applicable emission limit and document 
that there was no change in source operations including fuel 
composition and operation of air pollution control equipment that would 
cause emissions of the relevant pollutant to increase within the past 
year.
    (s) Records of the occurrence and duration of each malfunction of 
operation (i.e., process equipment) or the air pollution control and 
monitoring equipment.
    (t) Records of all required maintenance performed on the air 
pollution control and monitoring equipment.
    (u) Records of actions taken during periods of malfunction to 
minimize emissions in accordance with Sec.  60.11(d), including 
corrective actions to restore malfunctioning process and air pollution 
control and monitoring equipment to its normal or usual manner of 
operation.
    (v) For operating units that combust non-hazardous secondary 
materials that have been determined not to be solid waste pursuant to 
Sec.  241.3(b)(1) of this chapter, you must keep a record which 
documents how the secondary material meets each of the legitimacy 
criteria under Sec.  241.3(d)(1). If you combust a fuel that has been 
processed from a discarded non-hazardous secondary material pursuant to 
Sec.  241.3(b)(4) of this chapter, you must keep records as to how the 
operations that produced the fuel satisfies the definition of 
processing in Sec.  241.2 and each of the legitimacy criteria of Sec.  
241.3(d)(1) of this chapter. If the fuel received a non-waste 
determination pursuant to the petition process submitted under Sec.  
241.3(c) of this chapter, you must keep a record that documents how the 
fuel satisfies the requirements of the petition process. For operating 
units that combust non-hazardous secondary materials as fuel per Sec.  
241.4, you must keep records documenting that the material is a listed 
non-waste under Sec.  241.4(a).
    (w) Records of the criteria used to establish that the unit 
qualifies as a small power production facility under section 3(17)(C) 
of the Federal Power Act (16 U.S.C. 796(17)(C)) and that the waste 
material the unit is proposed to burn is homogeneous.
    (x) Records of the criteria used to establish that the unit 
qualifies as a cogeneration facility under section 3(18)(B) of the 
Federal Power Act (16 U.S.C. 796(18)(B)) and that the waste material 
the unit is proposed to burn is homogeneous.


Sec.  60.2180   Where and in what format must I keep my records?

    All records must be available onsite in either paper copy or 
computer-readable format that can be printed upon request, unless an 
alternative format is approved by the Administrator.


Sec.  60.2185   What reports must I submit?

    See table 4 of this subpart for a summary of the reporting 
requirements.


Sec.  60.2190   What must I submit prior to commencing construction?

    You must submit a notification prior to commencing construction 
that includes the five items listed in paragraphs (a) through (e) of 
this section:
    (a) A statement of intent to construct;
    (b) The anticipated date of commencement of construction;
    (c) All documentation produced as a result of the siting 
requirements of Sec.  60.2050;
    (d) The waste management plan as specified in Sec. Sec.  60.2055 
through 60.2065; and
    (e) Anticipated date of initial startup.


Sec.  60.2195   What information must I submit prior to initial 
startup?

    You must submit the information specified in paragraphs (a) through 
(e) of this section prior to initial startup:
    (a) The type(s) of waste to be burned;
    (b) The maximum design waste burning capacity;
    (c) The anticipated maximum charge rate;
    (d) If applicable, the petition for site-specific operating limits 
under Sec.  60.2115; and
    (e) The anticipated date of initial startup.


Sec.  60.2200   What information must I submit following my initial 
performance test?

    You must submit the information specified in paragraphs (a) through 
(c) of this section no later than 60 days following the initial 
performance test. All reports must be signed by the facilities manager:
    (a) The complete test report for the initial performance test 
results obtained under Sec.  60.2135, as applicable;
    (b) The values for the site-specific operating limits established 
in Sec.  60.2110 or Sec.  60.2115; and
    (c) If you are using a fabric filter to comply with the emission 
limitations, documentation that a bag leak detection system has been 
installed and is being operated, calibrated, and maintained as required 
by Sec.  60.2165(b).


Sec.  60.2205   When must I submit my annual report?

    You must submit an annual report no later than 12 months following 
the submission of the information in Sec.  60.2200. You must submit 
subsequent reports no more than 12 months following the previous 
report. (If the unit is subject to permitting requirements under title 
V of the Clean Air Act, you may be required by the permit to submit 
these reports more frequently.)

[[Page 15872]]

Sec.  60.2210   What information must I include in my annual report?

    The annual report required under Sec.  60.2205 must include the 
items listed in paragraphs (a) through (o) of this section. If you have 
a deviation from the operating limits or the emission limitations, you 
must also submit deviation reports as specified in Sec. Sec.  60.2215, 
60.2220, and 60.2225:
    (a) Company name and address;
    (b) Statement by a responsible official, with that official's name, 
title, and signature, certifying the accuracy of the content of the 
report;
    (c) Date of report and beginning and ending dates of the reporting 
period;
    (d) The values for the operating limits established pursuant to 
Sec.  60.2110 or Sec.  60.2115;
    (e) If no deviation from any emission limitation or operating limit 
that applies to you has been reported, a statement that there was no 
deviation from the emission limitations or operating limits during the 
reporting period;
    (f) The highest recorded 3-hour average and the lowest recorded 3-
hour average (30-day average for energy recovery units), as applicable, 
for each operating parameter recorded for the calendar year being 
reported;
    (g) Information recorded under Sec.  60.2175(b)(6) and (c) through 
(e) for the calendar year being reported;
    (h) For each performance test conducted during the reporting 
period, if any performance test is conducted, the process unit(s) 
tested, the pollutant(s) tested and the date that such performance test 
was conducted. Submit, following the procedure specified in Sec.  
60.2235(b)(1), the performance test report no later than the date that 
you submit the annual report;
    (i) If you met the requirements of Sec.  60.2155(a) or (b), and did 
not conduct a performance test during the reporting period, you must 
state that you met the requirements of Sec.  60.2155(a) or (b), and, 
therefore, you were not required to conduct a performance test during 
the reporting period;
    (j) Documentation of periods when all qualified CISWI operators 
were unavailable for more than 8 hours, but less than 2 weeks;
    (k) If you had a malfunction during the reporting period, the 
compliance report must include the number, duration, and a brief 
description for each type of malfunction that occurred during the 
reporting period and that caused or may have caused any applicable 
emission limitation to be exceeded. The report must also include a 
description of actions taken by an owner or operator during a 
malfunction of an affected source to minimize emissions in accordance 
with Sec.  60.11(d), including actions taken to correct a malfunction;
    (l) For each deviation from an emission or operating limitation 
that occurs for a CISWI for which you are not using a continuous 
monitoring system to comply with the emission or operating limitations 
in this subpart, the annual report must contain the following 
information:
    (1) The total operating time of the CISWI at which the deviation 
occurred during the reporting period; and
    (2) Information on the number, duration, and cause of deviations 
(including unknown cause, if applicable), as applicable, and the 
corrective action taken.
    (m) If there were periods during which the continuous monitoring 
system, including the CEMS, was out of control as specified in 
paragraph (o) of this section, the annual report must contain the 
following information for each deviation from an emission or operating 
limitation occurring for a CISWI for which you are using a continuous 
monitoring system to comply with the emission and operating limitations 
in this subpart:
    (1) The date and time that each malfunction started and stopped;
    (2) The date, time, and duration that each CMS was inoperative, 
except for zero (low-level) and high-level checks;
    (3) The date, time, and duration that each continuous monitoring 
system was out-of-control, including start and end dates and hours and 
descriptions of corrective actions taken;
    (4) The date and time that each deviation started and stopped, and 
whether each deviation occurred during a period of malfunction or 
during another period;
    (5) A summary of the total duration of the deviation during the 
reporting period, and the total duration as a percent of the total 
source operating time during that reporting period;
    (6) A breakdown of the total duration of the deviations during the 
reporting period into those that are due to control equipment problems, 
process problems, other known causes, and other unknown causes;
    (7) A summary of the total duration of continuous monitoring system 
downtime during the reporting period, and the total duration of 
continuous monitoring system downtime as a percent of the total 
operating time of the CISWI at which the continuous monitoring system 
downtime occurred during that reporting period;
    (8) An identification of each parameter and pollutant that was 
monitored at the CISWI;
    (9) A brief description of the CISWI;
    (10) A brief description of the continuous monitoring system;
    (11) The date of the latest continuous monitoring system 
certification or audit; and
    (12) A description of any changes in continuous monitoring system, 
processes, or controls since the last reporting period.
    (n) If there were periods during which the continuous monitoring 
system, including the CEMS, was not out of control as specified in 
paragraph (o) of this section, a statement that there were not periods 
during which the continuous monitoring system was out of control during 
the reporting period.
    (o) A continuous monitoring system is out of control in accordance 
with the procedure in 40 CFR part 60, appendix F of this part, as if 
any of the following occur:
    (1) The zero (low-level), mid-level (if applicable), or high-level 
calibration drift exceeds two times the applicable calibration drift 
specification in the applicable performance specification or in the 
relevant standard;
    (2) The continuous monitoring system fails a performance test audit 
(e.g., cylinder gas audit), relative accuracy audit, relative accuracy 
test audit, or linearity test audit; and
    (3) The continuous opacity monitoring system calibration drift 
exceeds two times the limit in the applicable performance specification 
in the relevant standard.


Sec.  60.2215   What else must I report if I have a deviation from the 
operating limits or the emission limitations?

    (a) You must submit a deviation report if any recorded 3-hour 
average (30-day average for energy recovery units or for PM CPMS) 
parameter level is above the maximum operating limit or below the 
minimum operating limit established under this subpart, if the bag leak 
detection system alarm sounds for more than 5 percent of the operating 
time for the 6-month reporting period, if a performance test was 
conducted that deviated from any emission limitation, if a 30-day 
average measured using CEMS deviated from any emission limitation.
    (b) The deviation report must be submitted by August 1 of that year 
for data collected during the first half of the calendar year (January 
1 to June 30), and by February 1 of the following year for data you 
collected during the second half of the calendar year (July 1 to 
December 31).

[[Page 15873]]

Sec.  60.2220   What must I include in the deviation report?

    In each report required under Sec.  60.2215, for any pollutant or 
parameter that deviated from the emission limitations or operating 
limits specified in this subpart, include the six items described in 
paragraphs (a) through (d) of this section:
    (a) The calendar dates and times your unit deviated from the 
emission limitations or operating limit requirements;
    (b) The averaged and recorded data for those dates;
    (c) Durations and causes of the following:
    (1) Each deviation from emission limitations or operating limits 
and your corrective actions;
    (2) Bypass events and your corrective actions; and
    (d) A copy of the operating limit monitoring data during each 
deviation and for any test report that documents the emission levels 
the process unit(s) tested, the pollutant(s) tested and the date that 
the performance test was conducted. Submit, following the procedure 
specified in Sec.  60.2235(b)(1), the performance test report no later 
than the date that you submit the deviation report.


Sec.  60.2225   What else must I report if I have a deviation from the 
requirement to have a qualified operator accessible?

    (a) If all qualified operators are not accessible for 2 weeks or 
more, you must take the two actions in paragraphs (a)(1) and (2) of 
this section:
    (1) Submit a notification of the deviation within 10 days that 
includes the three items in paragraphs (a)(1)(i) through (iii) of this 
section:
    (i) A statement of what caused the deviation;
    (ii) A description of what you are doing to ensure that a qualified 
operator is accessible; and
    (iii) The date when you anticipate that a qualified operator will 
be available.
    (2) Submit a status report to the Administrator every 4 weeks that 
includes the three items in paragraphs (a)(2)(i) through (iii) of this 
section:
    (i) A description of what you are doing to ensure that a qualified 
operator is accessible;
    (ii) The date when you anticipate that a qualified operator will be 
accessible; and
    (iii) Request approval from the Administrator to continue operation 
of the CISWI.
    (b) If your unit was shut down by the Administrator, under the 
provisions of Sec.  60.2100(b)(2), due to a failure to provide an 
accessible qualified operator, you must notify the Administrator that 
you are resuming operation once a qualified operator is accessible.


Sec.  60.2230   Are there any other notifications or reports that I 
must submit?

    (a) Yes. You must submit notifications as provided by Sec.  60.7.
    (b) If you cease combusting solid waste but continue to operate, 
you must provide 30 days prior notice of the effective date of the 
waste-to-fuel switch, consistent with 60.2145(a). The notification must 
identify:
    (1) The name of the owner or operator of the CISWI, the location of 
the source, the emissions unit(s) that will cease burning solid waste, 
and the date of the notice;
    (2) The currently applicable subcategory under this subpart, and 
any 40 CFR part 63 subpart and subcategory that will be applicable 
after you cease combusting solid waste;
    (3) The fuel(s), non-waste material(s) and solid waste(s) the CISWI 
is currently combusting and has combusted over the past 6 months, and 
the fuel(s) or non-waste materials the unit will commence combusting;
    (4) The date on which you became subject to the currently 
applicable emission limits; and
    (5) The date upon which you will cease combusting solid waste, and 
the date (if different) that you intend for any new requirements to 
become applicable (i.e., the effective date of the waste-to-fuel 
switch), consistent with paragraphs (b)(2) and (3) of this section.


Sec.  60.2235   In what form can I submit my reports?

    (a) Submit initial, annual and deviation reports electronically or 
in paper format, postmarked on or before the submittal due dates. 
Beginning on April 16, 2021 or once the reporting form has been 
available in CEDRI for 1 year, whichever is later, you must submit 
subsequent reports on or before the submittal dates to the EPA via the 
Compliance and Emissions Data Reporting Interface (CEDRI),which can be 
accessed through the EPA's Central Data Exchange (CDX) (https://cdx.epa.gov/). Use the appropriate electronic report in CEDRI for this 
subpart or an alternate electronic file format consistent with the 
extensible markup language (XML) schema listed on the CEDRI website 
(https://www3.epa.gov/ttn/chief/cedri/). The date forms 
become available in CEDRI will be listed on the CEDRI website. The 
reports must be submitted by the deadlines specified in this subpart, 
regardless of the method in which the report is submitted.
    (b) Submit results of each performance test and CEMS performance 
evaluation required by this subpart as follows:
    (1) Within 60 days after the date of completing each performance 
test (see Sec.  60.8) required by this subpart, you must submit the 
results of the performance test following the procedure specified in 
either paragraph (b)(1)(i) or (b)(1)(ii) of this section:
    (i) For data collected using test methods supported by the EPA's 
Electronic Reporting Tool (ERT) as listed on the EPA's ERT website 
(https://www3.epa.gov/ttn/chief/ert/ert_info.html) at the time of the 
test, you must submit the results of the performance test to the EPA 
via the CEDRI. (CEDRI can be accessed through the EPA's CDX (https://cdx.epa.gov/).) Performance test data must be submitted in a file 
format generated through the use of the EPA's ERT or an alternate 
electronic file format consistent with the XML schema listed on the 
EPA's ERT website. If you claim that some of the performance test 
information being submitted is confidential business information (CBI), 
you must submit a complete file generated through the use of the EPA's 
ERT or an alternate electronic file consistent with the XML schema 
listed on the EPA's ERT website, including information claimed to be 
CBI, on a compact disc, flash drive, or other commonly used electronic 
storage media to the EPA. The electronic media must be clearly marked 
as CBI and mailed to U.S. EPA/OAQPS/CORE CBI Office, Attention: Group 
Leader, Measurement Policy Group, MD C404-02, 4930 Old Page Rd., 
Durham, NC 27703. The same ERT or alternate file with the CBI omitted 
must be submitted to the EPA via the EPA's CDX as described earlier in 
this paragraph; and
    (ii) For data collected using test methods that are not supported 
by the EPA's ERT as listed on the EPA's ERT website at the time of the 
test, you must submit the results of the performance test to the 
Administrator at the appropriate address listed in Sec.  60.4.
    (2) Within 60 days after the date of completing each continuous 
emissions monitoring system performance evaluation you must submit the 
results of the performance evaluation following the procedure specified 
in either paragraph (b)(2)(i) or (b)(2)(ii) of this section:
    (i) For performance evaluations of continuous monitoring systems 
measuring relative accuracy test audit (RATA) pollutants that are 
supported by the EPA's ERT as listed on the EPA's ERT website at the 
time of the

[[Page 15874]]

evaluation, you must submit the results of the performance evaluation 
to the EPA via the CEDRI. (CEDRI can be accessed through the EPA's 
CDX.) Performance evaluation data must be submitted in a file format 
generated through the use of the EPA's ERT or an alternate file format 
consistent with the XML schema listed on the EPA's ERT website. If you 
claim that some of the performance evaluation information being 
submitted is CBI, you must submit a complete file generated through the 
use of the EPA's ERT or an alternate electronic file consistent with 
the XML schema listed on the EPA's ERT website, including information 
claimed to be CBI, on a compact disc, flash drive, or other commonly 
used electronic storage media to the EPA. The electronic storage media 
must be clearly marked as CBI and mailed to U.S. EPA/OAQPS/CORE CBI 
Office, Attention: Group Leader, Measurement Policy Group, MD C404-02, 
4930 Old Page Rd., Durham, NC 27703. The same ERT or alternate file 
with the CBI omitted must be submitted to the EPA via the EPA's CDX as 
described earlier in this paragraph; and
    (ii) For any performance evaluations of continuous monitoring 
systems measuring RATA pollutants that are not supported by the EPA's 
ERT as listed on the EPA's ERT website at the time of the evaluation, 
you must submit the results of the performance evaluation to the 
Administrator at the appropriate address listed in Sec.  60.4.
    (c) If you are required to electronically submit a report through 
the Compliance and Emissions Data Reporting Interface (CEDRI) in the 
EPA's Central Data Exchange (CDX), and due to a planned or actual 
outage of either the EPA's CEDRI or CDX systems within the period of 
time beginning 5 business days prior to the date that the submission is 
due, you will be or are precluded from accessing CEDRI or CDX and 
submitting a required report within the time prescribed, you may assert 
a claim of EPA system outage for failure to timely comply with the 
reporting requirement. You must submit notification to the 
Administrator in writing as soon as possible following the date you 
first knew, or through due diligence should have known, that the event 
may cause or caused a delay in reporting. You must provide to the 
Administrator a written description identifying the date, time and 
length of the outage; a rationale for attributing the delay in 
reporting beyond the regulatory deadline to the EPA system outage; 
describe the measures taken or to be taken to minimize the delay in 
reporting; and identify a date by which you propose to report, or if 
you have already met the reporting requirement at the time of the 
notification, the date you reported. In any circumstance, the report 
must be submitted electronically as soon as possible after the outage 
is resolved. The decision to accept the claim of EPA system outage and 
allow an extension to the reporting deadline is solely within the 
discretion of the Administrator.
    (d) If you are required to electronically submit a report through 
CEDRI in the EPA's CDX and a force majeure event is about to occur, 
occurs, or has occurred or there are lingering effects from such an 
event within the period of time beginning 5 business days prior to the 
date the submission is due, the owner or operator may assert a claim of 
force majeure for failure to timely comply with the reporting 
requirement. For the purposes of this section, a force majeure event is 
defined as an event that will be or has been caused by circumstances 
beyond the control of the affected facility, its contractors, or any 
entity controlled by the affected facility that prevents you from 
complying with the requirement to submit a report electronically within 
the time period prescribed. Examples of such events are acts of nature 
(e.g., hurricanes, earthquakes, or floods), acts of war or terrorism, 
or equipment failure or safety hazard beyond the control of the 
affected facility (e.g., large scale power outage). If you intend to 
assert a claim of force majeure, you must submit notification to the 
Administrator in writing as soon as possible following the date you 
first knew, or through due diligence should have known, that the event 
may cause or caused a delay in reporting. You must provide to the 
Administrator a written description of the force majeure event and a 
rationale for attributing the delay in reporting beyond the regulatory 
deadline to the force majeure event; describe the measures taken or to 
be taken to minimize the delay in reporting; and identify a date by 
which you propose to report, or if you have already met the reporting 
requirement at the time of the notification, the date you reported. In 
any circumstance, the reporting must occur as soon as possible after 
the force majeure event occurs. The decision to accept the claim of 
force majeure and allow an extension to the reporting deadline is 
solely within the discretion of the Administrator.


Sec.  60.2240   Can reporting dates be changed?

    If the Administrator agrees, you may change the semiannual or 
annual reporting dates. See Sec.  60.19(c) for procedures to seek 
approval to change your reporting date.

Title V Operating Permits


Sec.  60.2242   Am I required to apply for and obtain a Title V 
operating permit for my unit?

    Yes. Each CISWI and ACI subject to standards under this subpart 
must operate pursuant to a permit issued under Section 129(e) and Title 
V of the Clean Air Act.

Air Curtain Incinerators (ACIs)


Sec.  60.2245   What is an air curtain incinerator?

    (a) An ACI operates by forcefully projecting a curtain of air 
across an open chamber or open pit in which combustion occurs. 
Incinerators of this type can be constructed above or below ground and 
with or without refractory walls and floor. Air curtain incinerators 
are not to be confused with conventional combustion devices with 
enclosed fireboxes and controlled air technology such as mass burn, 
modular, and fluidized bed combustors.
    (b) Air curtain incinerators that burn only the materials listed in 
paragraphs (b)(1) through (3) of this section are only required to meet 
the requirements under Sec.  60.2242 and under ``Air Curtain 
Incinerators'' (Sec. Sec.  60.2245 through 60.2260):
    (1) 100 percent wood waste;
    (2) 100 percent clean lumber; and
    (3) 100 percent mixture of only wood waste, clean lumber, and/or 
yard waste.


Sec.  60.2250   What are the emission limitations for air curtain 
incinerators?

    Within 60 days after your ACI reaches the charge rate at which it 
will operate, but no later than 180 days after its initial startup, you 
must meet the two limitations specified in paragraphs (a) and (b) of 
this section:
    (a) Maintain opacity to less than or equal to 10 percent opacity 
(as determined by the average of three 1-hour blocks consisting of ten 
6-minute average opacity values), except as described in paragraph (b) 
of this section; and
    (b) Maintain opacity to less than or equal to 35 percent opacity 
(as determined by the average of three 1-hour blocks consisting of ten 
6-minute average opacity values) during the startup period that is 
within the first 30 minutes of operation.


Sec.  60.2255   How must I monitor opacity for air curtain 
incinerators?

    (a) Use Method 9 of appendix A of this part to determine compliance 
with the opacity limitation.

[[Page 15875]]

    (b) Conduct an initial test for opacity as specified in Sec.  60.8.
    (c) After the initial test for opacity, conduct annual tests no 
more than 12 calendar months following the date of your previous test.


Sec.  60.2260   What are the recordkeeping and reporting requirements 
for air curtain incinerators?

    (a) Prior to commencing construction on your ACI, submit the three 
items described in paragraphs (a)(1) through (3) of this section:
    (1) Notification of your intent to construct the ACI;
    (2) Your planned initial startup date; and
    (3) Types of materials you plan to burn in your ACI.
    (b) Keep records of results of all initial and annual opacity tests 
onsite in either paper copy or electronic format, unless the 
Administrator approves another format, for at least 5 years.
    (c) Make all records available for submittal to the Administrator 
or for an inspector's onsite review.
    (d) You must submit the results (as determined by the average of 
three 1-hour blocks consisting of ten 6-minute average opacity values) 
of the initial opacity tests no later than 60 days following the 
initial test. Submit annual opacity test results within 12 months 
following the previous report.
    (e) Submit initial and annual opacity test reports as electronic or 
paper copy on or before the applicable submittal date.
    (f) Keep a copy of the initial and annual reports onsite for a 
period of 5 years.

Definitions


Sec.  60.2265   What definitions must I know?

    Terms used but not defined in this subpart are defined in the Clean 
Air Act and subpart A (General Provisions) of this part.
    30-day rolling average means the arithmetic mean of the previous 
720 hours of valid operating data. Valid data excludes periods when 
this unit is not operating. The 720 hours should be consecutive, but 
not necessarily continuous if operations are intermittent.
    Administrator means the Administrator of the U.S. Environmental 
Protection Agency or his/her authorized representative or Administrator 
of a State Air Pollution Control Agency.
    Air curtain incinerator (ACI) means an incinerator that operates by 
forcefully projecting a curtain of air across an open chamber or pit in 
which combustion occurs. Incinerators of this type can be constructed 
above or below ground and with or without refractory walls and floor. 
Air curtain incinerators are not to be confused with conventional 
combustion devices with enclosed fireboxes and controlled air 
technology such as mass burn, modular, and fluidized bed combustors.
    Annual heat input means the heat input for the 12 months preceding 
the compliance demonstration.
    Auxiliary fuel means natural gas, liquified petroleum gas, fuel 
oil, or diesel fuel.
    Average annual heat input rate means annual heat input divided by 
the hours of operation for the 12 months preceding the compliance 
demonstration.
    Bag leak detection system means an instrument that is capable of 
monitoring particulate matter loadings in the exhaust of a fabric 
filter (i.e., baghouse) in order to detect bag failures. A bag leak 
detection system includes, but is not limited to, an instrument that 
operates on triboelectric, light scattering, light transmittance, or 
other principle to monitor relative particulate matter loadings.
    Burn-off oven means any rack reclamation unit, part reclamation 
unit, or drum reclamation unit. A burn-off oven is not an incinerator, 
waste-burning kiln, an energy recovery unit or a small, remote 
incinerator under this subpart.
    Bypass stack means a device used for discharging combustion gases 
to avoid severe damage to the air pollution control device or other 
equipment.
    Calendar quarter means three consecutive months (nonoverlapping) 
beginning on: January 1, April 1, July 1, or October 1.
    Calendar year means 365 consecutive days starting on January 1 and 
ending on December 31.
    CEMS data during startup and shutdown means the following:
    (1) For incinerators and small remote incinerators: CEMS data 
collected during the first hours of a CISWI startup from a cold start 
until waste is fed to the unit and the hours of operation following the 
cessation of waste material being fed to the CISWI during a unit 
shutdown. For each startup event, the length of time that CEMS data may 
be claimed as being CEMS data during startup must be 48 operating hours 
or less. For each shutdown event, the length of time that CEMS data may 
be claimed as being CEMS data during shutdown must be 24 operating 
hours or less;
    (2) For energy recovery units: CEMS data collected during the 
startup or shutdown periods of operation. Startup begins with either 
the first-ever firing of fuel in a boiler or process heater for the 
purpose of supplying useful thermal energy (such as steam or heat) for 
heating, cooling or process purposes, or producing electricity, or the 
firing of fuel in a boiler or process heater for any purpose after a 
shutdown event. Startup ends four hours after when the boiler or 
process heater makes useful thermal energy (such as heat or steam) for 
heating, cooling, or process purposes, or generates electricity, 
whichever is earlier. Shutdown begins when the boiler or process heater 
no longer makes useful thermal energy (such as heat or steam) for 
heating, cooling, or process purposes and/or generates electricity or 
when no fuel is being fed to the boiler or process heater, whichever is 
earlier. Shutdown ends when the boiler or process heater no longer 
makes useful thermal energy (such as steam or heat) for heating, 
cooling, or process purposes and/or generates electricity, and no fuel 
is being combusted in the boiler or process heater; and
    (3) For waste-burning kilns: CEMS data collected during the periods 
of kiln operation that do not include normal operations. Startup means 
the time from when a shutdown kiln first begins firing fuel until it 
begins producing clinker. Startup begins when a shutdown kiln turns on 
the induced draft fan and begins firing fuel in the main burner. 
Startup ends when feed is being continuously introduced into the kiln 
for at least 120 minutes or when the feed rate exceeds 60 percent of 
the kiln design limitation rate, whichever occurs first. Shutdown means 
the cessation of kiln operation. Shutdown begins when feed to the kiln 
is halted and ends when continuous kiln rotation ceases.
    Chemical recovery unit means combustion units burning materials to 
recover chemical constituents or to produce chemical compounds where 
there is an existing commercial market for such recovered chemical 
constituents or compounds. A chemical recovery unit is not an 
incinerator, a waste-burning kiln, an energy recovery unit or a small, 
remote incinerator under this subpart. The following seven types of 
units are considered chemical recovery units:
    (1) Units burning only pulping liquors (i.e., black liquor) that 
are reclaimed in a pulping liquor recovery process and reused in the 
pulping process;
    (2) Units burning only spent sulfuric acid used to produce virgin 
sulfuric acid;
    (3) Units burning only wood or coal feedstock for the production of 
charcoal;
    (4) Units burning only manufacturing byproduct streams/residue 
containing

[[Page 15876]]

catalyst metals that are reclaimed and reused as catalysts or used to 
produce commercial grade catalysts;
    (5) Units burning only coke to produce purified carbon monoxide 
that is used as an intermediate in the production of other chemical 
compounds;
    (6) Units burning only hydrocarbon liquids or solids to produce 
hydrogen, carbon monoxide, synthesis gas, or other gases for use in 
other manufacturing processes; and
    (7) Units burning only photographic film to recover silver.
    Chemotherapeutic waste means waste material resulting from the 
production or use of antineoplastic agents used for the purpose of 
stopping or reversing the growth of malignant cells.
    Clean lumber means wood or wood products that have been cut or 
shaped and include wet, air-dried, and kiln-dried wood products. Clean 
lumber does not include wood products that have been painted, pigment-
stained, or pressure-treated by compounds such as chromate copper 
arsenate, pentachlorophenol, and creosote.
    Commercial and industrial solid waste incineration unit (CISWI) 
means any distinct operating unit of any commercial or industrial 
facility that combusts, or has combusted in the preceding 6 months, any 
solid waste as that term is defined in 40 CFR part 241. If the 
operating unit burns materials other than traditional fuels as defined 
in Sec.  241.2 that have been discarded, and you do not keep and 
produce records as required by Sec.  60.2175(v), the operating unit is 
a CISWI. While not all CISWIs will include all of the following 
components, a CISWI includes, but is not limited to, the solid waste 
feed system, grate system, flue gas system, waste heat recovery 
equipment, if any, and bottom ash system. The CISWI does not include 
air pollution control equipment or the stack. The CISWI boundary starts 
at the solid waste hopper (if applicable) and extends through two 
areas: The combustion unit flue gas system, which ends immediately 
after the last combustion chamber or after the waste heat recovery 
equipment, if any; and the combustion unit bottom ash system, which 
ends at the truck loading station or similar equipment that transfers 
the ash to final disposal. The CISWI includes all ash handling systems 
connected to the bottom ash handling system.
    Contained gaseous material means gases that are in a container when 
that container is combusted.
    Continuous emission monitoring system (CEMS) means the total 
equipment that may be required to meet the data acquisition and 
availability requirements of this subpart, used to sample, condition 
(if applicable), analyze, and provide a record of emissions.
    Continuous monitoring system (CMS) means the total equipment, 
required under the emission monitoring sections in applicable subparts, 
used to sample and condition (if applicable), to analyze, and to 
provide a permanent record of emissions or process parameters. A 
particulate matter continuous parameter monitoring system (PM CPMS) is 
a type of CMS.
    Cyclonic burn barrel means a combustion device for waste materials 
that is attached to a 55 gallon, open-head drum. The device consists of 
a lid, which fits onto and encloses the drum, and a blower that forces 
combustion air into the drum in a cyclonic manner to enhance the mixing 
of waste material and air. A cyclonic burn barrel is not an 
incinerator, a waste-burning kiln, an energy recovery unit or a small, 
remote incinerator under this subpart.
    Deviation means any instance in which an affected source subject to 
this subpart, or an owner or operator of such a source:
    (1) Fails to meet any requirement or obligation established by this 
subpart, including but not limited to any emission limitation, 
operating limit, or operator qualification and accessibility 
requirements; and
    (2) Fails to meet any term or condition that is adopted to 
implement an applicable requirement in this subpart and that is 
included in the operating permit for any affected source required to 
obtain such a permit.
    Dioxins/furans means tetra- through octa-chlorinated dibenzo-p-
dioxins and dibenzofurans.
    Discard means, for purposes of this subpart and 40 CFR part 60, 
subpart DDDD, only, burned in an incineration unit without energy 
recovery.
    Drum reclamation unit means a unit that burns residues out of drums 
(e.g., 55 gallon drums) so that the drums can be reused.
    Dry scrubber means an add-on air pollution control system that 
injects dry alkaline sorbent (dry injection) or sprays an alkaline 
sorbent (spray dryer) to react with and neutralize acid gas in the 
exhaust stream forming a dry powder material. Sorbent injection systems 
in fluidized bed boilers and process heaters are included in this 
definition. A dry scrubber is a dry control system.
    Energy recovery means the process of recovering thermal energy from 
combustion for useful purposes such as steam generation or process 
heating.
    Energy recovery unit means a combustion unit combusting solid waste 
(as that term is defined by the Administrator in 40 CFR part 241) for 
energy recovery. Energy recovery units include units that would be 
considered boilers and process heaters if they did not combust solid 
waste.
    Energy recovery unit designed to burn biomass (Biomass) means an 
energy recovery unit that burns solid waste, biomass, and non-coal 
solid materials but less than 10 percent coal, on a heat input basis on 
an annual average, either alone or in combination with liquid waste, 
liquid fuel or gaseous fuels.
    Energy recovery unit designed to burn coal (Coal) means an energy 
recovery unit that burns solid waste and at least 10 percent coal on a 
heat input basis on an annual average, either alone or in combination 
with liquid waste, liquid fuel or gaseous fuels.
    Energy recovery unit designed to burn liquid waste materials and 
gas (Liquid/gas) means an energy recovery unit that burns a liquid 
waste with liquid or gaseous fuels not combined with any solid fuel or 
waste materials.
    Energy recovery unit designed to burn solid materials (Solids) 
includes energy recovery units designed to burn coal and energy 
recovery units designed to burn biomass.
    Fabric filter means an add-on air pollution control device used to 
capture particulate matter by filtering gas streams through filter 
media, also known as a baghouse.
    Foundry sand thermal reclamation unit means a type of part 
reclamation unit that removes coatings that are on foundry sand. A 
foundry sand thermal reclamation unit is not an incinerator, a waste-
burning kiln, an energy recovery unit or a small, remote incinerator 
under this subpart.
    Incinerator means any furnace used in the process of combusting 
solid waste (as that term is defined by the Administrator in 40 CFR 
part 241) for the purpose of reducing the volume of the waste by 
removing combustible matter. Incinerator designs include single chamber 
and two-chamber.
    In-line coal mill means those coal mills using kiln exhaust gases 
in their process. Coal mills with a heat source other than the kiln or 
coal mills using exhaust gases from the clinker cooler alone are not an 
in-line coal mill.
    In-line kiln/raw mill means a system in a Portland Cement 
production process where a dry kiln system is integrated with the raw 
mill so that all or a portion of the kiln exhaust gases are used to 
perform the drying operation of the raw mill, with no auxiliary heat 
source used. In this system the kiln is

[[Page 15877]]

capable of operating without the raw mill operating, but the raw mill 
cannot operate without the kiln gases, and consequently, the raw mill 
does not generate a separate exhaust gas stream.
    Kiln means an oven or furnace, including any associated preheater 
or precalciner devices, in-line raw mills, in-line coal mills or alkali 
bypasses used for processing a substance by burning, firing or drying. 
Kilns include cement kilns that produce clinker by heating limestone 
and other materials for subsequent production of Portland Cement. 
Because the alkali bypass, in-line raw mill and in-line coal mill are 
considered an integral part of the kiln, the kiln emissions limits also 
apply to the exhaust of the alkali bypass, in-line raw mill and in-line 
coal mill.
    Laboratory analysis unit means units that burn samples of materials 
for the purpose of chemical or physical analysis. A laboratory analysis 
unit is not an incinerator, waste-burning kiln, an energy recovery unit 
or a small, remote incinerator under this subpart.
    Load fraction means the actual heat input of an energy recovery 
unit divided by heat input during the performance test that established 
the minimum sorbent injection rate or minimum activated carbon 
injection rate, expressed as a fraction (e.g., for 50 percent load the 
load fraction is 0.5).
    Low-level radioactive waste means waste material which contains 
radioactive nuclides emitting primarily beta or gamma radiation, or 
both, in concentrations or quantities that exceed applicable federal or 
state standards for unrestricted release. Low-level radioactive waste 
is not high-level radioactive waste, spent nuclear fuel, or byproduct 
material as defined by the Atomic Energy Act of 1954 (42 U.S.C. 
2014(e)(2)).
    Malfunction means any sudden, infrequent, and not reasonably 
preventable failure of air pollution control equipment, process 
equipment, or a process to operate in a normal or usual manner. 
Failures that are caused, in part, by poor maintenance or careless 
operation are not malfunctions.
    Minimum voltage or amperage means 90 percent of the lowest test-run 
average voltage or amperage to the electrostatic precipitator measured 
during the most recent particulate matter or mercury performance test 
demonstrating compliance with the applicable emission limits.
    Modification or modified CISWI means a CISWI that has been changed 
later than August 7, 2013 and that meets one of two criteria:
    (1) The cumulative cost of the changes over the life of the unit 
exceeds 50 percent of the original cost of building and installing the 
CISWI (not including the cost of land) updated to current costs 
(current dollars). To determine what systems are within the boundary of 
the CISWI used to calculate these costs, see the definition of CISWI; 
and
    (2) Any physical change in the CISWI or change in the method of 
operating it that increases the amount of any air pollutant emitted for 
which section 129 or section 111 of the Clean Air Act has established 
standards.
    Municipal solid waste or municipal-type solid waste means 
household, commercial/retail, or institutional waste. Household waste 
includes material discarded by residential dwellings, hotels, motels, 
and other similar permanent or temporary housing. Commercial/retail 
waste includes material discarded by stores, offices, restaurants, 
warehouses, nonmanufacturing activities at industrial facilities, and 
other similar establishments or facilities. Institutional waste 
includes materials discarded by schools, by hospitals (nonmedical), by 
nonmanufacturing activities at prisons and government facilities, and 
other similar establishments or facilities. Household, commercial/
retail, and institutional waste does include yard waste and refuse-
derived fuel. Household, commercial/retail, and institutional waste 
does not include used oil; sewage sludge; wood pallets; construction, 
renovation, and demolition wastes (which include railroad ties and 
telephone poles); clean wood; industrial process or manufacturing 
wastes; medical waste; or motor vehicles (including motor vehicle parts 
or vehicle fluff).
    Opacity means the degree to which emissions reduce the transmission 
of light and obscure the view of an object in the background.
    Operating day means a 24-hour period between 12 midnight and the 
following midnight during which any amount of solid waste is combusted 
at any time in the CISWI.
    Oxygen analyzer system means all equipment required to determine 
the oxygen content of a gas stream and used to monitor oxygen in the 
boiler or process heater flue gas, boiler or process heater, firebox, 
or other appropriate location. This definition includes oxygen trim 
systems and certified oxygen CEMS. The source owner or operator is 
responsible to install, calibrate, maintain, and operate the oxygen 
analyzer system in accordance with the manufacturer's recommendations.
    Oxygen trim system means a system of monitors that is used to 
maintain excess air at the desired level in a combustion device over 
its operating range. A typical system consists of a flue gas oxygen 
and/or carbon monoxide monitor that automatically provides a feedback 
signal to the combustion air controller or draft controller.
    Part reclamation unit means a unit that burns coatings off parts 
(e.g., tools, equipment) so that the parts can be reconditioned and 
reused.
    Particulate matter means total particulate matter emitted from 
CISWIs as measured by Method 5 or Method 29 of appendix A of this part.
    Pathological waste means waste material consisting of only human or 
animal remains, anatomical parts, and/or tissue, the bags/containers 
used to collect and transport the waste material, and animal bedding 
(if applicable).
    Performance evaluation means the conduct of relative accuracy 
testing, calibration error testing, and other measurements used in 
validating the continuous monitoring system data.
    Performance test means the collection of data resulting from the 
execution of a test method (usually three emission test runs) used to 
demonstrate compliance with a relevant emission standard as specified 
in the performance test section of the relevant standard.
    Process change means any of the following physical or operational 
changes:
    (1) A physical change (maintenance activities excluded) to the 
CISWI which may increase the emission rate of any air pollutant to 
which a standard applies;
    (2) An operational change to the CISWI where a new type of non-
hazardous secondary material is being combusted;
    (3) A physical change (maintenance activities excluded) to the air 
pollution control devices used to comply with the emission limits for 
the CISWI (e.g., replacing an electrostatic precipitator with a fabric 
filter); and
    (4) An operational change to the air pollution control devices used 
to comply with the emission limits for the affected CISWI (e.g., change 
in the sorbent injection rate used for activated carbon injection).
    Rack reclamation unit means a unit that burns the coatings off 
racks used to hold small items for application of a coating. The unit 
burns the coating overspray off the rack so the rack can be reused.
    Raw mill means a ball or tube mill, vertical roller mill or other 
size reduction equipment, that is not part of an in-line kiln/raw mill, 
used to grind feed to the appropriate size. Moisture may be added or 
removed from the feed

[[Page 15878]]

during the grinding operation. If the raw mill is used to remove 
moisture from feed materials, it is also, by definition, a raw material 
dryer. The raw mill also includes the air separator associated with the 
raw mill.
    Reconstruction means rebuilding a CISWI and meeting two criteria:
    (1) The reconstruction begins on or after August 7, 2013; and
    (2) The cumulative cost of the construction over the life of the 
incineration unit exceeds 50 percent of the original cost of building 
and installing the CISWI (not including land) updated to current costs 
(current dollars). To determine what systems are within the boundary of 
the CISWI used to calculate these costs, see the definition of CISWI.
    Refuse-derived fuel means a type of municipal solid waste produced 
by processing municipal solid waste through shredding and size 
classification. This includes all classes of refuse-derived fuel 
including two fuels:
    (1) Low-density fluff refuse-derived fuel through densified refuse-
derived fuel; and
    (2) Pelletized refuse-derived fuel.
    Responsible official means one of the following:
    (1) For a corporation: A president, secretary, treasurer, or vice-
president of the corporation in charge of a principal business 
function, or any other person who performs similar policy or decision-
making functions for the corporation, or a duly authorized 
representative of such person if the representative is responsible for 
the overall operation of one or more manufacturing, production, or 
operating facilities applying for or subject to a permit and either:
    (i) The facilities employ more than 250 persons or have gross 
annual sales or expenditures exceeding $25 million (in second quarter 
1980 dollars); or
    (ii) The delegation of authority to such representatives is 
approved in advance by the permitting authority;
    (2) For a partnership or sole proprietorship: A general partner or 
the proprietor, respectively;
    (3) For a municipality, state, federal, or other public agency: 
Either a principal executive officer or ranking elected official. For 
the purposes of this part, a principal executive officer of a federal 
agency includes the chief executive officer having responsibility for 
the overall operations of a principal geographic unit of the agency 
(e.g., a Regional Administrator of EPA); or
    (4) For affected facilities:
    (i) The designated representative in so far as actions, standards, 
requirements, or prohibitions under Title IV of the Clean Air Act or 
the regulations promulgated thereunder are concerned; or
    (ii) The designated representative for any other purposes under 
part 60.
    Shutdown means, for incinerators and small, remote incinerators, 
the period of time after all waste has been combusted in the primary 
chamber.
    Small, remote incinerator means an incinerator that combusts solid 
waste (as that term is defined by the Administrator in 40 CFR part 241) 
and combusts 3 tons per day or less solid waste and is more than 25 
miles driving distance to the nearest municipal solid waste landfill.
    Soil treatment unit means a unit that thermally treats petroleum-
contaminated soils for the sole purpose of site remediation. A soil 
treatment unit may be direct-fired or indirect fired. A soil treatment 
unit is not an incinerator, a waste-burning kiln, an energy recovery 
unit or a small, remote incinerator under this subpart.
    Solid waste means the term solid waste as defined in 40 CFR 241.2.
    Solid waste incineration unit means a distinct operating unit of 
any facility which combusts any solid waste (as that term is defined by 
the Administrator in 40 CFR part 241) material from commercial or 
industrial establishments or the general public (including single and 
multiple residences, hotels and motels). Such term does not include 
incinerators or other units required to have a permit under section 
3005 of the Solid Waste Disposal Act. The term ``solid waste 
incineration unit'' does not include:
    (1) Materials recovery facilities (including primary or secondary 
smelters) which combust waste for the primary purpose of recovering 
metals;
    (2) Qualifying small power production facilities, as defined in 
section 3(17)(C) of the Federal Power Act (16 U.S.C. 769(17)(C)), or 
qualifying cogeneration facilities, as defined in section 3(18)(B) of 
the Federal Power Act (16 U.S.C. 796(18)(B)), which burn homogeneous 
waste (such as units which burn tires or used oil, but not including 
refuse-derived fuel) for the production of electric energy or in the 
case of qualifying cogeneration facilities which burn homogeneous waste 
for the production of electric energy and steam or forms of useful 
energy (such as heat) which are used for industrial, commercial, 
heating or cooling purposes; or
    (3) Air curtain incineratorsprovided that such incinerators only 
burn wood wastes, yard wastes, and clean lumber and that such ACIs 
comply with opacity limitations to be established by the Administrator 
by rule.
    Space heater means a unit that meets the requirements of 40 CFR 
279.23. A space heater is not an incinerator, a waste-burning kiln, an 
energy recovery unit or a small, remote incinerator under this subpart.
    Standard conditions, when referring to units of measure, means a 
temperature of 68 [deg]F (20 [deg]C) and a pressure of 1 atmosphere 
(101.3 kilopascals).
    Startup period means, for incinerators and small, remote 
incinerators, the period of time between the activation of the system 
and the first charge to the unit.
    Useful thermal energy means energy (i.e., steam, hot water, or 
process heat) that meets the minimum operating temperature and/or 
pressure required by any energy use system that uses energy provided by 
the affected energy recovery unit.
    Waste-burning kiln means a kiln that is heated, in whole or in 
part, by combusting solid waste (as that term is defined by the 
Administrator in 40 CFR part 241). Secondary materials used in Portland 
cement kilns shall not be deemed to be combusted unless they are 
introduced into the flame zone in the hot end of the kiln or mixed with 
the precalciner fuel.
    Wet scrubber means an add-on air pollution control device that uses 
an aqueous or alkaline scrubbing liquor to collect particulate matter 
(including nonvaporous metals and condensed organics) and/or to absorb 
and neutralize acid gases.
    Wood waste means untreated wood and untreated wood products, 
including tree stumps (whole or chipped), trees, tree limbs (whole or 
chipped), bark, sawdust, chips, scraps, slabs, millings, and shavings. 
Wood waste does not include:
    (1) Grass, grass clippings, bushes, shrubs, and clippings from 
bushes and shrubs from residential, commercial/retail, institutional, 
or industrial sources as part of maintaining yards or other private or 
public lands;
    (2) Construction, renovation, or demolition wastes; and
    (3) Clean lumber.

[[Page 15879]]



  Table 1 to Subpart CCCC of Part 60--Emission Limitations for Incinerators for Which Construction is Commenced
     After November 30, 1999, But no Later Than June 4, 2010, or for Which Modification or Reconstruction is
                      Commenced on or After June 1, 2001, But no Later Than August 7, 2013
----------------------------------------------------------------------------------------------------------------
                                       You must meet this                                     And determining
       For the air pollutant           emission limitation    Using this averaging time    compliance using this
                                               \1\                       \2\                    method \2\
----------------------------------------------------------------------------------------------------------------
Cadmium............................  0.004 milligrams per    3-run average (1 hour        Performance test
                                      dry standard cubic      minimum sample time per      (Method 29 of
                                      meter.                  run).                        appendix A of this
                                                                                           part).
Carbon monoxide....................  157 parts per million   3-run average (1 hour        Performance test
                                      by dry volume.          minimum sample time per      (Method 10 at 40 CFR
                                                              run).                        part 60, appendix A-
                                                                                           4).
Dioxin/Furan (toxic equivalency      0.41 nanograms per dry  3-run average (collect a     Performance test
 basis).                              standard cubic meter.   minimum volume of 4 dry      (Method 23 of
                                                              standard cubic meters per    appendix A-7 of this
                                                              run).                        part).
Hydrogen chloride..................  62 parts per million    3-run average (For Method    Performance test
                                      by dry volume.          26, collect a minimum        (Method 26 or 26A at
                                                              volume of 120 liters per     40 CFR part 60,
                                                              run. For Method 26A,         appendix A-8).
                                                              collect a minimum volume
                                                              of 1 dry standard cubic
                                                              meter per run).
Lead...............................  0.04 milligrams per     3-run average (1 hour        Performance test
                                      dry standard cubic      minimum sample time per      (Method 29 of
                                      meter.                  run).                        appendix A of this
                                                                                           part).
Mercury............................  0.47 milligrams per     3-run average (1 hour        Performance test
                                      dry standard cubic      minimum sample time per      (Method 29 of
                                      meter.                  run).                        appendix A of this
                                                                                           part).
Nitrogen oxides....................  388 parts per million   3-run average (for Method    Performance test
                                      by dry volume.          7E, 1 hour minimum sample    (Method 7 or 7E at 40
                                                              time per run).               CFR part 60, appendix
                                                                                           A-4).
Opacity............................  10 percent............  6-minute averages..........  Performance test
                                                                                           (Method 9 of appendix
                                                                                           A of this part).
Particulate matter.................  70 milligrams per dry   3-run average (1 hour        Performance test
                                      standard cubic meter.   minimum sample time per      (Method 5 or 29 of
                                                              run).                        appendix A of this
                                                                                           part).
Sulfur dioxide.....................  20 parts per million    3-run average (For Method    Performance test
                                      by dry volume.          6, collect a minimum         (Method 6 or 6C at 40
                                                              volume of 20 liters per      CFR part 60, appendix
                                                              run. For Method 6C,          A-4).
                                                              collect sample for a
                                                              minimum duration of 1 hour
                                                              per run).
----------------------------------------------------------------------------------------------------------------
\1\ All emission limitations (except for opacity) are measured at 7 percent oxygen, dry basis at standard
  conditions.
\2\ In lieu of performance testing, you may use a CEMS or, for mercury, an integrated sorbent trap monitoring
  system, to demonstrate initial and continuing compliance with an emissions limit, as long as you comply with
  the CEMS or integrated sorbent trap monitoring system requirements applicable to the specific pollutant in
  Sec.  Sec.   60.2145 and 60.2165. As prescribed in Sec.   60.2145(u), if you use a CEMS or an integrated
  sorbent trap monitoring system to demonstrate compliance with an emissions limit, your averaging time is a 30-
  day rolling average of 1-hour arithmetic average emission concentrations.


                                         Table 2 to Subpart CCCC of Part 60--Operating Limits for Wet Scrubbers
--------------------------------------------------------------------------------------------------------------------------------------------------------
                                                                                     And monitoring using these minimum frequencies
   For these operating parameters        You must establish   ------------------------------------------------------------------------------------------
                                       these operating limits           Data measurement                  Data recording              Averaging time
--------------------------------------------------------------------------------------------------------------------------------------------------------
Charge rate.........................  Maximum charge rate....  Continuous.......................  Every hour....................  Daily (batch units) 3-
                                                                                                                                   hour rolling
                                                                                                                                   (continuous and
                                                                                                                                   intermittent
                                                                                                                                   units).\1\
Pressure drop across the wet          Minimum pressure drop    Continuous.......................  Every 15 minutes..............  3-hour rolling.\1\
 scrubber or amperage to wet           or amperage.
 scrubber.
Scrubber liquor flow rate...........  Minimum flow rate......  Continuous.......................  Every 15 minutes..............  3-hour rolling.\1\
Scrubber liquor pH..................  Minimum pH.............  Continuous.......................  Every 15 minutes..............  3-hour rolling.\1\
--------------------------------------------------------------------------------------------------------------------------------------------------------
\1\ Calculated each hour as the average of the previous 3 operating hours.


      Table 3 to Subpart CCCC of Part 60--Toxic Equivalency Factors
------------------------------------------------------------------------
                                                               Toxic
                  Dioxin/furan congener                     equivalency
                                                              factor
------------------------------------------------------------------------
2,3,7,8-tetrachlorinated dibenzo-p-dioxin...............               1
1,2,3,7,8-pentachlorinated dibenzo-p-dioxin.............             0.5
1,2,3,4,7,8-hexachlorinated dibenzo-p-dioxin............             0.1
1,2,3,7,8,9-hexachlorinated dibenzo-p-dioxin............             0.1
1,2,3,6,7,8-hexachlorinated dibenzo-p-dioxin............             0.1
1,2,3,4,6,7,8-heptachlorinated dibenzo-p-dioxin.........            0.01
octachlorinated dibenzo-p-dioxin........................           0.001
2,3,7,8-tetrachlorinated dibenzofuran...................             0.1
2,3,4,7,8-pentachlorinated dibenzofuran.................             0.5
1,2,3,7,8-pentachlorinated dibenzofuran.................            0.05
1,2,3,4,7,8-hexachlorinated dibenzofuran................             0.1
1,2,3,6,7,8-hexachlorinated dibenzofuran................             0.1
1,2,3,7,8,9-hexachlorinated dibenzofuran................             0.1
2,3,4,6,7,8-hexachlorinated dibenzofuran................             0.1
1,2,3,4,6,7,8-heptachlorinated dibenzofuran.............            0.01
1,2,3,4,7,8,9-heptachlorinated dibenzofuran.............            0.01
octachlorinated dibenzofuran............................           0.001
------------------------------------------------------------------------


[[Page 15880]]


                    Table 4 to Subpart CCCC of Part 60--Summary of Reporting Requirements \1\
----------------------------------------------------------------------------------------------------------------
             Report                       Due date                  Contents                  Reference
----------------------------------------------------------------------------------------------------------------
Preconstruction report..........  Prior to commencing        Statement of    Sec.   60.2190.
                                   construction.             intent to construct.
                                                             Anticipated
                                                             date of commencement
                                                             of construction.
                                                             Documentation
                                                             for siting
                                                             requirements.
                                                             Waste
                                                             management plan.
                                                             Anticipated
                                                             date of initial
                                                             startup.
Startup notification............  Prior to initial startup   Type of waste   Sec.   60.2195.
                                                             to be burned.
                                                             Maximum design
                                                             waste burning capacity.
                                                             Anticipated
                                                             maximum charge rate.
                                                             If applicable,
                                                             the petition for site-
                                                             specific operating
                                                             limits.
Initial test report.............  No later than 60 days      Complete test   Sec.   60.2200.
                                   following the initial     report for the initial
                                   performance test.         performance test.
                                                             The values for
                                                             the site-specific
                                                             operating limits.
                                                             Installation    ...........................
                                                             of bag leak detection
                                                             system for fabric
                                                             filter.
Annual report...................  No later than 12 months    Name and        Sec.  Sec.   60.2205 and
                                   following the             address.                 60.2210.
                                   submission of the         Statement and
                                   initial test report.      signature by
                                   Subsequent reports are    responsible official.
                                   to be submitted no more   Date of report
                                   than 12 months            Values for the
                                   following the previous    operating limits.
                                   report.
                                                             Highest
                                                             recorded 3-hour
                                                             average and the lowest
                                                             3-hour average, as
                                                             applicable, (or 30-day
                                                             average, if
                                                             applicable) for each
                                                             operating parameter
                                                             recorded for the
                                                             calendar year being
                                                             reported.
                                                             For each
                                                             performance test
                                                             conducted during the
                                                             reporting period, if
                                                             any performance test
                                                             is conducted, the
                                                             process unit(s)
                                                             tested, the
                                                             pollutant(s) tested,
                                                             and the date that such
                                                             performance test was
                                                             conducted.
                                                             If a
                                                             performance test was
                                                             not conducted during
                                                             the reporting period,
                                                             a statement that the
                                                             requirements of Sec.
                                                             60.2155(a) were met.
                                                             Documentation
                                                             of periods when all
                                                             qualified CISWI
                                                             operators were
                                                             unavailable for more
                                                             than 8 hours but less
                                                             than 2 weeks.
                                                             If you are
                                                             conducting performance
                                                             tests once every 3
                                                             years consistent with
                                                             Sec.   60.2155(a), the
                                                             date of the last 2
                                                             performance tests, a
                                                             comparison of the
                                                             emission level you
                                                             achieved in the last 2
                                                             performance tests to
                                                             the 75 percent
                                                             emission limit
                                                             threshold required in
                                                             Sec.   60.2155(a) and
                                                             a statement as to
                                                             whether there have
                                                             been any operational
                                                             changes since the last
                                                             performance test that
                                                             could increase
                                                             emissions.
                                                             Any
                                                             malfunction,
                                                             deviation, or
                                                             continuous monitoring
                                                             system out of control
                                                             periods information as
                                                             specified in Sec.
                                                             60.2210(k) through (o).
Emission limitation or operating  By August 1 of that year   Dates and       Sec.   60.2215 and 60.2220.
 limit deviation report.           for data collected        times of deviation.
                                   during the first half     Averaged and
                                   of the calendar year.     recorded data for
                                   By February 1 of the      those dates.
                                   following year for data   Duration and
                                   collected during the      causes of each
                                   second half of the        deviation and the
                                   calendar year.            corrective actions
                                                             taken.
                                                             Copy of
                                                             operating limit
                                                             monitoring data and,
                                                             if any performance
                                                             test was conducted
                                                             that documents
                                                             emission levels, the
                                                             process unit(s)
                                                             tested, the
                                                             pollutant(s) tested,
                                                             and the date that such
                                                             performance test was
                                                             conducted.
                                                             Dates, times
                                                             and causes for monitor
                                                             downtime incidents.

[[Page 15881]]

 
Qualified operator deviation      Within 10 days of          Statement of    Sec.   60.2225(a)(1).
 notification.                     deviation.                cause of deviation.
                                                             Description of
                                                             efforts to have an
                                                             accessible qualified
                                                             operator.
                                                             The date a
                                                             qualified operator
                                                             will be accessible.
Qualified operator deviation      Every 4 weeks following    Description of  Sec.   60.2225(a)(2).
 status report.                    deviation.                efforts to have an
                                                             accessible qualified
                                                             operator.
                                                             The date a
                                                             qualified operator
                                                             will be accessible.
                                                             Request for
                                                             approval to continue
                                                             operation.
Qualified operator deviation      Prior to resuming          Notification    Sec.   60.2225(b).
 notification of resumed           operation.                that you are resuming
 operation.                                                  operation.
----------------------------------------------------------------------------------------------------------------
\1\ This table is only a summary, see the referenced sections of the rule for the complete requirements.


Table 5 to Subpart CCCC of Part 60--Emission Limitations for Incinerators That Commenced Construction After June
                 4, 2010, or That Commenced Reconstruction or Modification After August 7, 2013
----------------------------------------------------------------------------------------------------------------
                                      You must meet this                                    And determining
       For the air pollutant         emission limitation    Using this averaging time    compliance using this
                                             \1\                       \2\                     method \2\
----------------------------------------------------------------------------------------------------------------
Cadmium...........................  0.0023 milligrams per  3-run average (collect a    Performance test (Method
                                     dry standard cubic     minimum volume of 4 dry     29 at 40 CFR part 60,
                                     meter.                 standard cubic meter per    appendix A-8 of this
                                                            run).                       part). Use ICPMS for the
                                                                                        analytical finish.
Carbon monoxide...................  17 parts per million   3-run average (1 hour       Performance test (Method
                                     by dry volume.         minimum sample time per     10 at 40 CFR part 60,
                                                            run).                       appendix A-4).
Dioxin/furan (Total Mass Basis)...  0.58 nanograms per     3-run average (collect a    Performance test (Method
                                     dry standard cubic     minimum volume of 4 dry     23 at 40 CFR part 60,
                                     meter.                 standard cubic meters per   appendix A-7).
                                                            run).
Dioxin/furan (toxic equivalency     0.13 nanograms per     3-run average (collect a    Performance test (Method
 basis).                             dry standard cubic     minimum volume of 4 dry     23 at 40 CFR part 60,
                                     meter.                 standard cubic meter per    appendix A-7).
                                                            run).
Fugitive ash......................  Visible emissions for  Three 1-hour observation    Visible emission test
                                     no more than 5         periods.                    (Method 22 at 40 CFR
                                     percent of the                                     part 60, appendix A-7).
                                     hourly observation
                                     period.
Hydrogen chloride.................  0.091 parts per        3-run average (For Method   Performance test (Method
                                     million by dry         26, collect a minimum       26 or 26A at 40 CFR part
                                     volume.                volume of 360 liters per    60, appendix A-8).
                                                            run. For Method 26A,
                                                            collect a minimum volume
                                                            of 3 dry standard cubic
                                                            meters per run).
Lead..............................  0.015 milligrams per   3-run average (collect a    Performance test (Method
                                     dry standard cubic     minimum volume of 4 dry     29 of appendix A-8 at 40
                                     meter.                 standard cubic meters per   CFR part 60). Use ICPMS
                                                            run).                       for the analytical
                                                                                        finish.
Mercury...........................  0.00084 milligrams     3-run average (collect      Performance test (Method
                                     per dry standard       enough volume to meet a     29 or 30B at 40 CFR part
                                     cubic meter.           detection limit data        60, appendix A-8) or
                                                            quality objective of 0.03   ASTM D6784-02
                                                            ug/dry standard cubic       (Reapproved 2008).\3\
                                                            meter).
Nitrogen oxides...................  23 parts per million   3-run average (for Method   Performance test (Method
                                     dry volume.            7E, 1 hour minimum sample   7 or 7E at 40 CFR part
                                                            time per run).              60, appendix A-4).
Particulate matter (filterable)...  18 milligrams per dry  3-run average (collect a    Performance test (Method
                                     standard cubic meter.  minimum volume of 2 dry     5 or 29 at 40 CFR part
                                                            standard cubic meters per   60, appendix A-3 or
                                                            run).                       appendix A-8 at 40 CFR
                                                                                        part 60).
Sulfur dioxide....................  11 parts per million   3-run average (1 hour       Performance test (Method
                                     dry volume.            minimum sample time per     6 or 6C at 40 CFR part
                                                            run).                       60, appendix A-4).
----------------------------------------------------------------------------------------------------------------
\1\ All emission limitations are measured at 7 percent oxygen, dry basis at standard conditions. For dioxins/
  furans, you must meet either the Total Mass Limit or the toxic equivalency basis limit.
\2\ In lieu of performance testing, you may use a CEMS or, for mercury, an integrated sorbent trap monitoring
  system to demonstrate initial and continuing compliance with an emissions limit, as long as you comply with
  the CEMS or integrated sorbent trap monitoring system requirements applicable to the specific pollutant in
  Sec.  Sec.   60.2145 and 60.2165. As prescribed in Sec.   60.2145(u), if you use a CEMS or an integrated
  sorbent trap monitoring system to demonstrate compliance with an emissions limit, your averaging time is a 30-
  day rolling average of 1-hour arithmetic average emission concentrations.
\3\ Incorporated by reference, see Sec.   60.17.


[[Page 15882]]


 Table 6 to Subpart CCCC of Part 60--Emission Limitations for Energy Recovery Units That Commenced Construction
            After June 4, 2010, or That Commenced Reconstruction or Modification After August 7, 2013
----------------------------------------------------------------------------------------------------------------
                                      You must meet this emission
                                            limitation \1\                 Using this         And determining
     For the air pollutant      --------------------------------------   averaging time    compliance using this
                                     Liquid/gas           Solids              \2\               method \2\
----------------------------------------------------------------------------------------------------------------
Cadmium........................  0.023 milligrams   Biomass-0.0014     3-run average      Performance test
                                  per dry standard   milligrams per     (collect a         (Method 29 at 40 CFR
                                  cubic meter.       dry standard       minimum volume     part 60, appendix A-
                                                     cubic meter.       of 4 dry           8). Use ICPMS for the
                                                    Coal-0.0017         standard cubic     analytical finish.
                                                     milligrams per     meters per run).
                                                     dry standard
                                                     cubic meter.
Carbon monoxide................  35 parts per       Biomass-240 parts  3-run average (1   Performance test
                                  million dry        per million dry    hour minimum       (Method 10 at 40 CFR
                                  volume.            volume.            sample time per    part 60, appendix A-
                                                    Coal-95 parts per   run).              4).
                                                     million dry
                                                     volume.
Dioxin/furans (Total Mass        No Total Mass      Biomass-0.52       3-run average      Performance test
 Basis).                          Basis limit,       nanograms per      (collect a         (Method 23 at 40 CFR
                                  must meet the      dry standard       minimum volume     part 60, appendix A-
                                  toxic              cubic meter.       of 4 dry           7).
                                  equivalency       Coal-5.1            standard cubic
                                  basis limit        nanograms per      meters).
                                  below.             dry standard
                                                     cubic meter.
Dioxins/furans (toxic            0.093 nanograms    Biomass-0.076      3-run average      Performance test
 equivalency basis).              per dry standard   nanograms per      (collect a         (Method 23 of
                                  cubic meter.       dry standard       minimum volume     appendix A-7 of this
                                                     cubic meter \3\.   of 4 dry           part).
                                                    Coal-0.075          standard cubic
                                                     nanograms per      meters per run).
                                                     dry standard
                                                     cubic meter.
Fugitive ash...................  Visible emissions  Three 1-hour       Visible emission   Fugitive ash.
                                  for no more than   observation        test (Method 22
                                  5 percent of the   periods.           at 40 CFR part
                                  hourly                                60, appendix A-
                                  observation                           7).
                                  period.
Hydrogen chloride..............  14 parts per       Biomass-0.20       3-run average      Performance test
                                  million dry        parts per          (For Method 26,    (Method 26 or 26A at
                                  volume.            million dry        collect a          40 CFR part 60,
                                                     volume.            minimum volume     appendix A-8).
                                                    Coal-58 parts per   of 360 liters
                                                     million dry        per run. For
                                                     volume.            Method 26A,
                                                                        collect a
                                                                        minimum volume
                                                                        of 3 dry
                                                                        standard cubic
                                                                        meters per run).
Lead...........................  0.096 milligrams   Biomass-0.014      3-run average      Performance test
                                  per dry standard   milligrams per     (collect a         (Method 29 at 40 CFR
                                  cubic meter.       dry standard       minimum volume     part 60, appendix A-
                                                     cubic meter.       of 4 dry           8). Use ICPMS for the
                                                    Coal-0.057          standard cubic     analytical finish.
                                                     milligrams per     meters per run).
                                                     dry standard
                                                     cubic meter.
Mercury........................  0.00056            Biomass-0.0022     3-run average      Performance test
                                  milligrams per     milligrams per     (collect enough    (Method 29 or 30B at
                                  dry standard       dry standard       volume to meet     40 CFR part 60,
                                  cubic meter.       cubic meter.       an in-stack        appendix A-8) or ASTM
                                                    Coal-0.013          detection limit    D6784-02 (Reapproved
                                                     milligrams per     data quality       2008).\3\
                                                     dry standard       objective of
                                                     cubic meter.       0.03 ug/dscm).
Nitrogen oxides................  76 parts per       Biomass-290 parts  3-run average      Performance test
                                  million dry        per million dry    (for Method 7E,    (Method 7 or 7E at 40
                                  volume.            volume.            1 hour minimum     CFR part 60, appendix
                                                    Coal-460 parts      sample time per    A-4).
                                                     per million dry    run).
                                                     volume.
Particulate matter (filterable)  110 milligrams     Biomass-5.1        3-run average      Performance test
                                  per dry standard   milligrams per     (collect a         (Method 5 or 29 at 40
                                  cubic meter.       dry standard       minimum volume     CFR part 60, appendix
                                                     cubic meter.       of 1 dry           A-3 or appendix A-8)
                                                    Coal-130            standard cubic     if the unit has an
                                                     milligrams per     meter per run).    annual average heat
                                                     dry standard                          input rate less than
                                                     cubic meter.                          250 MMBtu/hr; or PM
                                                                                           CPMS (as specified in
                                                                                           Sec.   60.2145(x)) if
                                                                                           the unit has an
                                                                                           annual average heat
                                                                                           input rate equal to
                                                                                           or greater than 250
                                                                                           MMBtu/hr.
Sulfur dioxide.................  720 parts per      Biomass-7.3 parts  3-run average      Performance test
                                  million dry        per million dry    (for Method 6,     (Method 6 or 6C at 40
                                  volume.            volume.            collect a          CFR part 60, appendix
                                                    Coal-850 parts      minimum of 60      A-4).
                                                     per million dry    liters, for
                                                     volume.            Method 6C,1 hour
                                                                        minimum sample
                                                                        time per run).
----------------------------------------------------------------------------------------------------------------
\1\ All emission limitations are measured at 7 percent oxygen, dry basis at standard conditions. For dioxins/
  furans, you must meet either the Total Mass Basis limit or the toxic equivalency basis limit.
\2\ In lieu of performance testing, you may use a CEMS or, for mercury, an integrated sorbent trap monitoring
  system to demonstrate initial and continuing compliance with an emissions limit, as long as you comply with
  the CEMS or integrated sorbent trap monitoring system requirements applicable to the specific pollutant in
  Sec.  Sec.   60.2145 and 60.2165. As prescribed in Sec.   60.2145(u), if you use a CEMS or an integrated
  sorbent trap monitoring system to demonstrate compliance with an emissions limit, your averaging time is a 30-
  day rolling average of 1-hour arithmetic average emission concentrations.
\3\ Incorporated by reference, see Sec.   60.17.


  Table 7 to Subpart CCCC of Part 60--Emission Limitations for Waste-Burning Kilns That Commenced Construction
                   After June 4, 2010, or Reconstruction or Modification After August 7, 2013
----------------------------------------------------------------------------------------------------------------
                                       You must meet this                                     And determining
       For the air pollutant           emission limitation    Using this averaging time    compliance using this
                                               \1\                       \2\                  method \2\ \3\
----------------------------------------------------------------------------------------------------------------
Cadmium............................  0.0014 milligrams per   3-run average (collect a     Performance test
                                      dry standard cubic      minimum volume of 4 dry      (Method 29 at 40 CFR
                                      meter.                  standard cubic meters per    part 60, appendix A-
                                                              run).                        8). Use ICPMS for the
                                                                                           analytical finish.
Carbon monoxide....................  90 (long kilns)/190     3-run average (1 hour        Performance test
                                      (preheater/             minimum sample time per      (Method 10 at 40 CFR
                                      precalciner) parts      run).                        part 60, appendix A-
                                      per million dry                                      4).
                                      volume.
Dioxins/furans (total mass basis)..  0.51 nanograms per dry  3-run average (collect a     Performance test
                                      standard cubic meter.   minimum volume of 4 dry      (Method 23 at 40 CFR
                                                              standard cubic meters per    part 60, appendix A-
                                                              run).                        7).
Dioxins/furans (toxic equivalency    0.075 nanograms per     3-run average (collect a     Performance test
 basis).                              dry standard cubic      minimum volume of 4 dry      (Method 23 at 40 CFR
                                      meter.                  standard cubic meters).      part 60, appendix A-
                                                                                           7).

[[Page 15883]]

 
Hydrogen chloride..................  3.0 parts per million   3-run average (1 hour        If a wet scrubber or
                                      dry volume.             minimum sample time per      dry scrubber is used,
                                                              run) or 30-day rolling       performance test
                                                              average if HCl CEMS is       (Method 321 at 40 CFR
                                                              being used.                  part 63, appendix A).
                                                                                           If a wet scrubber or
                                                                                           dry scrubber is not
                                                                                           used, HCl CEMS as
                                                                                           specified in Sec.
                                                                                           60.2145(j).
Lead...............................  0.014 milligrams per    3-run average (collect a     Performance test
                                      dry standard cubic      minimum volume of 4 dry      (Method 29 at 40 CFR
                                      meter.                  standard cubic meters).      part 60, appendix A-
                                                                                           8). Use ICPMS for the
                                                                                           analytical finish.
Mercury............................  0.0037 milligrams per   30-day rolling average.....  Mercury CEMS or
                                      dry standard cubic                                   integrated sorbent
                                      meter.                                               trap monitoring
                                     Or....................                                system (performance
                                     21 pounds/million tons                                specification 12A or
                                      of clinker \3\.                                      12B, respectively, of
                                                                                           appendix B and
                                                                                           procedure 5 of
                                                                                           appendix F of this
                                                                                           part), as specified
                                                                                           in Sec.   60.2145(j).
Nitrogen oxides....................  200 parts per million   30-day rolling average.....  Nitrogen oxides CEMS
                                      dry volume.                                          (performance
                                                                                           specification 2 of
                                                                                           appendix B and
                                                                                           procedure 1 of
                                                                                           appendix F of this
                                                                                           part).
Particulate matter (filterable)....  4.9 milligrams per dry  30-day rolling average.....  PM CPMS (as specified
                                      standard cubic meter.                                in Sec.
                                                                                           60.2145(x)).
Sulfur dioxide.....................  28 parts per million    30-day rolling average.....  Sulfur dioxide CEMS
                                      dry volume.                                          (performance
                                                                                           specification 2 of
                                                                                           appendix B and
                                                                                           procedure 1 of
                                                                                           appendix F of this
                                                                                           part).
----------------------------------------------------------------------------------------------------------------
\1\ All emission limitations are measured at 7 percent oxygen (except for CEMS and integrated sorbent trap
  monitoring system data during startup and shutdown), dry basis at standard conditions. For dioxins/furans, you
  must meet either the Total Mass Basis limit or the toxic equivalency basis limit.
\2\ In lieu of performance testing, you may use a CEMS or, for mercury, an integrated sorbent trap monitoring
  system, to demonstrate initial and continuing compliance with an emissions limit, as long as you comply with
  the CEMS or integrated sorbent trap monitoring system requirements applicable to the specific pollutant in
  Sec.  Sec.   60.2145 and 60.2165. As prescribed in Sec.   60.2145(u), if you use a CEMS or integrated sorbent
  trap monitoring system to demonstrate compliance with an emissions limit, your averaging time is a 30-day
  rolling average of 1-hour arithmetic average emission concentrations.
\3\ Alkali bypass and in-line coal mill stacks are subject to performance testing only, as specified in Sec.
  60.2145(y)(3). They are not subject to the CEMS, integrated sorbent trap monitoring system, or CPMS
  requirements that otherwise may apply to the main kiln exhaust.


     Table 8 to Subpart CCCC of Part 60--Emission Limitations for Small, Remote Incinerators That Commenced
     Construction After June 4, 2010, or That Commenced Reconstruction or Modification After August 7, 2013
----------------------------------------------------------------------------------------------------------------
                                       You must meet this                                     And determining
       For the air pollutant           emission limitation    Using this averaging time    compliance using this
                                               \1\                       \2\                    method \2\
----------------------------------------------------------------------------------------------------------------
Cadmium............................  0.67 milligrams per     3-run average (collect a     Performance test
                                      dry standard cubic      minimum volume of 1 dry      (Method 29 at 40 CFR
                                      meter.                  standard cubic meters per    part 60, appendix A-
                                                              run).                        8).
Carbon monoxide....................  13 parts per million    3-run average (1 hour        Performance test
                                      dry volume.             minimum sample time per      (Method 10 at 40 CFR
                                                              run).                        part 60, appendix A-
                                                                                           4).
Dioxins/furans (total mass basis)..  1,800 nanograms per     3-run average (collect a     Performance test
                                      dry standard cubic      minimum volume of 1 dry      (Method 23 at 40 CFR
                                      meter.                  standard cubic meters per    part 60, appendix A-
                                                              run).                        7).
Dioxins/furans (toxic equivalency    31 nanograms per dry    3-run average (collect a     Performance test
 basis).                              standard cubic meter.   minimum volume of 1 dry      (Method 23 at 40 CFR
                                                              standard cubic meters).      part 60, appendix A-
                                                                                           7).
Fugitive ash.......................  Visible emissions for   Three 1-hour observation     Visible emissions test
                                      no more than 5          periods.                     (Method 22 at 40 CFR
                                      percent of the hourly                                part 60, appendix A-
                                      observation period.                                  7).
Hydrogen chloride..................  200 parts per million   3-run average (For Method    Performance test
                                      by dry volume.          26, collect a minimum        (Method 26 or 26A at
                                                              volume of 60 liters per      40 CFR part 60,
                                                              run. For Method 26A,         appendix A-8).
                                                              collect a minimum volume
                                                              of 1 dry standard cubic
                                                              meter per run).
Lead...............................  2.0 milligrams per dry  3-run average (collect a     Performance test
                                      standard cubic meter.   minimum volume of 1 dry      (Method 29 at 40 CFR
                                                              standard cubic meters).      part 60, appendix A-
                                                                                           8). Use ICPMS for the
                                                                                           analytical finish.
Mercury............................  0.0035 milligrams per   3-run average (For Method    Performance test
                                      dry standard cubic      29 and ASTM D6784-02         (Method 29 or 30B at
                                      meter.                  (Reapproved 2008) \2\,       40 CFR part 60,
                                                              collect a minimum volume     appendix A-8) or ASTM
                                                              of 2 dry standard cubic      D6784-02 (Reapproved
                                                              meters per run. For Method   2008).\3\
                                                              30B, collect a minimum
                                                              volume as specified in
                                                              Method 30B at 40 CFR part
                                                              60, appendix A).
Nitrogen oxides....................  170 parts per million   3-run average (for Method    Performance test
                                      dry volume.             7E, 1 hour minimum sample    (Method 7 or 7E at 40
                                                              time per run).               CFR part 60, appendix
                                                                                           A-4).
Particulate matter (filterable)....  270 milligrams per dry  3-run average (collect a     Performance test
                                      standard cubic meter.   minimum volume of 1 dry      (Method 5 or 29 at 40
                                                              standard cubic meters).      CFR part 60, appendix
                                                                                           A-3 or appendix A-8).
Sulfur dioxide.....................  1.2 parts per million   3-run average (1 hour        Performance test
                                      dry volume.             minimum sample time per      (Method 6 or 6c at 40
                                                              run).                        CFR part 60, appendix
                                                                                           A-4).
----------------------------------------------------------------------------------------------------------------
\1\ All emission limitations are measured at 7 percent oxygen, dry basis at standard conditions. For dioxins/
  furans, you must meet either the Total Mass Basis limit or the toxic equivalency basis limit.
\2\ In lieu of performance testing, you may use a CEMS or, for mercury, an integrated sorbent trap monitoring
  system to demonstrate initial and continuing compliance with an emissions limit, as long as you comply with
  the CEMS or integrated sorbent trap monitoring system requirements applicable to the specific pollutant in
  Sec.  Sec.   60.2145 and 60.2165. As prescribed in Sec.   60.2145(u), if you use a CEMS or an integrated
  sorbent trap monitoring system to demonstrate compliance with an emissions limit, your averaging time is a 30-
  day rolling average of 1-hour arithmetic average emission concentrations.
\3\ Incorporated by reference, see Sec.   60.17.


[[Page 15884]]


0
3. Revise subpart DDDD to read as follows:
Sec.
Subpart DDDD--Emissions Guidelines and Compliance Times for Commercial 
and Industrial Solid Waste Incineration Units

Introduction

60.2500 What is the purpose of this subpart?
60.2505 Am I affected by this subpart?
60.2510 Is a state plan required for all states?
60.2515 What must I include in my state plan?
60.2520 Is there an approval process for my state plan?
60.2525 What if my state plan is not approvable?
60.2530 Is there an approval process for a negative declaration 
letter?
60.2535 What compliance schedule must I include in my state plan?
60.2540 Are there any state plan requirements for this subpart that 
apply instead of the requirements specified in subpart B?
60.2541 In lieu of a state plan submittal, are there other 
acceptable option(s) for a state to meet its Clean Air Act section 
111(d)/129(b)(2) obligations?
60.2542 What authorities will not be delegated to state, local, or 
tribal agencies?
60.2545 Does this subpart directly affect CISWI owners and operators 
in my state?

Applicability of State Plans

60.2550 What CISWIs must I address in my state plan?
60.2555 What combustion units are exempt from my state plan?

Use of Model Rule

60.2560 What is the ``model rule'' in this subpart?
60.2565 How does the model rule relate to the required elements of 
my state plan?
60.2570 What are the principal components of the model rule?

Model Rule--Increments of Progress

60.2575 What are my requirements for meeting increments of progress 
and achieving final compliance?
60.2580 When must I complete each increment of progress?
60.2585 What must I include in the notifications of achievement of 
increments of progress?
60.2590 When must I submit the notifications of achievement of 
increments of progress?
60.2595 What if I do not meet an increment of progress?
60.2600 How do I comply with the increment of progress for submittal 
of a control plan?
60.2605 How do I comply with the increment of progress for achieving 
final compliance?
60.2610 What must I do if I close my CISWI and then restart it?
60.2615 What must I do if I plan to permanently close my CISWI and 
not restart it?

Model Rule--Waste Management Plan

60.2620 What is a waste management plan?
60.2625 When must I submit my waste management plan?
60.2630 What should I include in my waste management plan?

Model Rule--Operator Training and Qualification

60.2635 What are the operator training and qualification 
requirements?
60.2640 When must the operator training course be completed?
60.2645 How do I obtain my operator qualification?
60.2650 How do I maintain my operator qualification?
60.2655 How do I renew my lapsed operator qualification?
60.2660 What site-specific documentation is required?
60.2665 What if all the qualified operators are temporarily not 
accessible?

Model Rule--Emission Limitations and Operating Limits

60.2670 What emission limitations must I meet and by when?
60.2675 What operating limits must I meet and by when?
60.2680 What if I do not use a wet scrubber, fabric filter, 
activated carbon injection, selective noncatalytic reduction, an 
electrostatic precipitator, or a dry scrubber to comply with the 
emission limitations?

Model Rule--Performance Testing

60.2690 How do I conduct the initial and annual performance test?
60.2695 How are the performance test data used?

Model Rule--Initial Compliance Requirements

60.2700 How do I demonstrate initial compliance with the amended 
emission limitations and establish the operating limits?
60.2705 By what date must I conduct the initial performance test?
60.2706 By what date must I conduct the initial air pollution 
control device inspection?

Model Rule--Continuous Compliance Requirements

60.2710 How do I demonstrate continuous compliance with the amended 
emission limitations and the operating limits?
60.2715 By what date must I conduct the annual performance test?
60.2716 By what date must I conduct the annual air pollution control 
device inspection?
60.2720 May I conduct performance testing less often?
60.2725 May I conduct a repeat performance test to establish new 
operating limits?

Model Rule--Monitoring

60.2730 What monitoring equipment must I install and what parameters 
must I monitor?
60.2735 Is there a minimum amount of monitoring data I must obtain?

Model Rule--Recordkeeping and Reporting

60.2740 What records must I keep?
60.2745 Where and in what format must I keep my records?
60.2750 What reports must I submit?
60.2755 When must I submit my waste management plan?
60.2760 What information must I submit following my initial 
performance test?
60.2765 When must I submit my annual report?
60.2770 What information must I include in my annual report?
60.2775 What else must I report if I have a deviation from the 
operating limits or the emission limitations?
60.2780 What must I include in the deviation report?
60.2785 What else must I report if I have a deviation from the 
requirement to have a qualified operator accessible?
60.2790 Are there any other notifications or reports that I must 
submit?
60.2795 In what form can I submit my reports?
60.2800 Can reporting dates be changed?

Model Rule--Title V Operating Permits

60.2805 Am I required to apply for and obtain a Title V operating 
permit for my unit?

Model Rule--Air Curtain Incinerators (ACIs)

60.2810 What is an air curtain incinerator?
60.2815 What are my requirements for meeting increments of progress 
and achieving final compliance?
60.2820 When must I complete each increment of progress?
60.2825 What must I include in the notifications of achievement of 
increments of progress?
60.2830 When must I submit the notifications of achievement of 
increments of progress?
60.2835 What if I do not meet an increment of progress?
60.2840 How do I comply with the increment of progress for submittal 
of a control plan?
60.2845 How do I comply with the increment of progress for achieving 
final compliance?
60.2850 What must I do if I close my air curtain incinerator and 
then restart it?
60.2855 What must I do if I plan to permanently close my air curtain 
incinerator and not restart it?
60.2860 What are the emission limitations for air curtain 
incinerators?
60.2865 How must I monitor opacity for air curtain incinerators?
60.2870 What are the recordkeeping and reporting requirements for 
air curtain incinerators?

Model Rule--Definitions

60.2875 What definitions must I know?

Tables to Subpart DDDD

Table 1 to Subpart DDDD of Part 60--Model Rule--Increments of 
Progress and Compliance Schedules
Table 2 to Subpart DDDD of Part 60--Model Rule--Emission Limitations 
That Apply to Incinerators Before [Date to be specified in state 
plan]

[[Page 15885]]

Table 3 to Subpart DDDD of Part 60--Model Rule--Operating Limits for 
Wet Scrubbers
Table 4 to Subpart DDDD of Part 60--Model Rule--Toxic Equivalency 
Factors
Table 5 to Subpart DDDD of Part 60--Model Rule--Summary of Reporting 
Requirements
Table 6 to Subpart DDDD of Part 60--Model Rule--Emission Limitations 
That Apply to Incinerators on and After [Date to be specified in 
state plan]
Table 7 to Subpart DDDD of Part 60--Model Rule--Emission Limitations 
That Apply to Energy Recovery Units After May 20, 2011 [Date to be 
specified in state plan]
Table 8 to Subpart DDDD of Part 60--Model Rule--Emission Limitations 
That Apply to Waste-Burning Kilns After May 20, 2011 [Date to be 
specified in state plan.]
Table 9 to Subpart DDDD of Part 60--Model Rule--Emission Limitations 
That Apply to Small, Remote Incinerators After May 20, 2011 [Date to 
be specified in state plan]

Subpart DDDD--Emissions Guidelines and Compliance Times for 
Commercial and Industrial Solid Waste Incineration Units

Introduction


Sec.  60.2500   What is the purpose of this subpart?

    This subpart establishes emission guidelines and compliance 
schedules for the control of emissions from commercial and industrial 
solid waste incineration units (CISWIs) and air curtain incinerators 
(ACIs). The pollutants addressed by these emission guidelines are 
listed in table 2 of this subpart and tables 6 through 9 of this 
subpart. These emission guidelines are developed in accordance with 
sections 111(d) and 129 of the Clean Air Act and subpart B of this 
part.


Sec.  60.2505   Am I affected by this subpart?

    (a) If you are the Administrator of an air quality program in a 
state or United States protectorate with one or more existing CISWIs 
that meet the criteria in paragraphs (b) through (d) of this section, 
you must submit a state plan to U.S. Environmental Protection Agency 
(EPA) that implements the emission guidelines contained in this 
subpart.
    (b) You must submit a state plan to EPA by December 3, 2001 for 
incinerator units that commenced construction on or before November 30, 
1999 and that were not modified or reconstructed after June 1, 2001.
    (c) You must submit a state plan that meets the requirements of 
this subpart and contains the more stringent emission limit for the 
respective pollutant in table 6 of this subpart or table 1 of subpart 
CCCC of this part to EPA by February 7, 2014 for incinerators that 
commenced construction after November 30, 1999, but no later than June 
4, 2010, or commenced modification or reconstruction after June 1, 2001 
but no later than August 7, 2013.
    (d) You must submit a state plan to EPA that meets the requirements 
of this subpart and contains the emission limits in tables 7 through 9 
of this subpart by February 7, 2014, for CISWIs other than incinerator 
units that commenced construction on or before June 4, 2010, or 
commenced modification or reconstruction after June 4, 2010 but no 
later than August 7, 2013.


Sec.  60.2510   Is a state plan required for all states?

    No. You are not required to submit a state plan if there are no 
existing CISWIs in your state, and you submit a negative declaration 
letter in place of the state plan.


Sec.  60.2515   What must I include in my state plan?

    (a) You must include the nine items described in paragraphs (a)(1) 
through (9) of this section in your state plan:
    (1) Inventory of affected CISWIs, including those that have ceased 
operation but have not been dismantled;
    (2) Inventory of emissions from affected CISWIs in your state;
    (3) Compliance schedules for each affected CISWI;
    (4) Emission limitations, operator training and qualification 
requirements, a waste management plan, and operating limits for 
affected CISWIs that are at least as protective as the emission 
guidelines contained in this subpart;
    (5) Performance testing, recordkeeping, and reporting requirements;
    (6) Certification that the hearing on the state plan was held, a 
list of witnesses and their organizational affiliations, if any, 
appearing at the hearing, and a brief written summary of each 
presentation or written submission;
    (7) Provision for state progress reports to EPA;
    (8) Identification of enforceable state mechanisms that you 
selected for implementing the emission guidelines of this subpart; and
    (9) Demonstration of your state's legal authority to carry out the 
sections 111(d) and 129 state plan.
    (b) Your state plan may deviate from the format and content of the 
emission guidelines contained in this subpart. However, if your state 
plan does deviate in content, you must demonstrate that your state plan 
is at least as protective as the emission guidelines contained in this 
subpart. Your state plan must address regulatory applicability, 
increments of progress for retrofit, operator training and 
qualification, a waste management plan, emission limitations, 
performance testing, operating limits, monitoring, recordkeeping and 
reporting, and ACI requirements.
    (c) You must follow the requirements of subpart B of this part 
(Adoption and Submittal of State Plans for Designated Facilities) in 
your state plan.


Sec.  60.2520   Is there an approval process for my state plan?

    Yes. The EPA will review your state plan according to Sec.  60.27.


Sec.  60.2525   What if my state plan is not approvable?

    (a) If you do not submit an approvable state plan (or a negative 
declaration letter) by December 2, 2002, EPA will develop a federal 
plan according to Sec.  60.27 to implement the emission guidelines 
contained in this subpart. Owners and operators of CISWIs not covered 
by an approved state plan must comply with the federal plan. The 
federal plan is an interim action and will be automatically withdrawn 
when your state plan is approved.
    (b) If you do not submit an approvable state plan (or a negative 
declaration letter) to EPA that meets the requirements of this subpart 
and contains the emission limits in tables 6 through 9 of this subpart 
for CISWIs that commenced construction on or before June 4, 2010 and 
incinerator or ACIs that commenced reconstruction or modification on or 
after June 1, 2001 but no later than August 7, 2013, then EPA will 
develop a federal plan according to Sec.  60.27 to implement the 
emission guidelines contained in this subpart. Owners and operators of 
CISWIs not covered by an approved state plan must comply with the 
federal plan. The federal plan is an interim action and will be 
automatically withdrawn when your state plan is approved.


Sec.  60.2530   Is there an approval process for a negative declaration 
letter?

    No. The EPA has no formal review process for negative declaration 
letters. Once your negative declaration letter has been received, EPA 
will place a copy in the public docket and publish a document in the 
Federal Register. If, at a later date, an existing CISWI is found in 
your state, the federal plan implementing the emission guidelines 
contained in this subpart would automatically apply to that CISWI until 
your state plan is approved.

[[Page 15886]]

Sec.  60.2535   What compliance schedule must I include in my state 
plan?

    (a) For CISWIs in the incinerator subcategory and ACIs that 
commenced construction on or before November 30, 1999, your state plan 
must include compliance schedules that require CISWIs in the 
incinerator subcategory and ACIs to achieve final compliance as 
expeditiously as practicable after approval of the state plan but not 
later than the earlier of the two dates specified in paragraphs (a)(1) 
and (2) of this section:
    (1) December 1, 2005; and
    (2) Three years after the effective date of state plan approval.
    (b) For CISWIs in the incinerator subcategory and ACIs that 
commenced construction after November 30, 1999, but on or before June 
4, 2010 or that commenced reconstruction or modification on or after 
June 1, 2001 but no later than August 7, 2013, and for CISWIs in the 
small remote incinerator, energy recovery unit, and waste-burning kiln 
subcategories that commenced construction before June 4, 2010, your 
state plan must include compliance schedules that require CISWIs to 
achieve final compliance as expeditiously as practicable after approval 
of the state plan but not later than the earlier of the two dates 
specified in paragraphs (b)(1) and (2) of this section:
    (1) February 7, 2018; and
    (2) Three years after the effective date of State plan approval.
    (c) For compliance schedules more than 1 year following the 
effective date of State plan approval, State plans must include dates 
for enforceable increments of progress as specified in Sec.  60.2580.


Sec.  60.2540   Are there any state plan requirements for this subpart 
that apply instead of the requirements specified in subpart B?

    Yes. Subpart B establishes general requirements for developing and 
processing section 111(d) plans. This subpart applies instead of the 
requirements in subpart B of this part for paragraphs (a) and (b) of 
this section:
    (a) State plans developed to implement this subpart must be as 
protective as the emission guidelines contained in this subpart. State 
plans must require all CISWIs to comply by the dates specified in Sec.  
60.2535. This applies instead of the option for case-by-case less 
stringent emission standards and longer compliance schedules in Sec.  
60.24(f); and
    (b) State plans developed to implement this subpart are required to 
include two increments of progress for the affected CISWIs. These two 
minimum increments are the final control plan submittal date and final 
compliance date in Sec.  60.21(h)(1) and (5). This applies instead of 
the requirement of Sec.  60.24(e)(1) that would require a state plan to 
include all five increments of progress for all CISWIs.


Sec.  60.2541   In lieu of a state plan submittal, are there other 
acceptable option(s) for a state to meet its Clean Air Act section 
111(d)/129(b)(2) obligations?

    Yes, a state may meet its Clean Air Act section 111(d)/129 
obligations by submitting an acceptable written request for delegation 
of the federal plan that meets the requirements of this section. This 
is the only other option for a state to meet its Clean Air Act section 
111(d)/129 obligations.
    (a) An acceptable federal plan delegation request must include the 
following:
    (1) A demonstration of adequate resources and legal authority to 
administer and enforce the federal plan;
    (2) The items under Sec.  60.2515(a)(1), (2) and (7);
    (3) Certification that the hearing on the state delegation request, 
similar to the hearing for a state plan submittal, was held, a list of 
witnesses and their organizational affiliations, if any, appearing at 
the hearing, and a brief written summary of each presentation or 
written submission; and
    (4) A commitment to enter into a Memorandum of Agreement with the 
Regional Administrator who sets forth the terms, conditions, and 
effective date of the delegation and that serves as the mechanism for 
the transfer of authority. Additional guidance and information is given 
in EPA's Delegation Manual, Item 7-139, Implementation and Enforcement 
of 111(d)(2) and 111(d)/(2)/129(b)(3) federal plans.
    (b) A state with an already approved CISWI Clean Air Act section 
111(d)/129 state plan is not precluded from receiving EPA approval of a 
delegation request for the revised federal plan, providing the 
requirements of paragraph (a) of this section are met, and at the time 
of the delegation request, the state also requests withdrawal of EPA's 
previous state plan approval.
    (c) A state's Clean Air Act section 111(d)/129 obligations are 
separate from its obligations under Title V of the Clean Air Act.


Sec.  60.2542   What authorities will not be delegated to state, local, 
or tribal agencies?

    The authorities that will not be delegated to state, local, or 
tribal agencies are specified in paragraphs (a) through (i) of this 
section:
    (a) Approval of alternatives to the emission limitations in tables 
2, 6, 7, 8, and 9 of this subpart and operating limits established 
under Sec.  60.2675;
    (b) Approval of major alternatives to test methods;
    (c) Approval of major alternatives to monitoring;
    (d) Approval of major alternatives to recordkeeping and reporting;
    (e) The requirements in Sec.  60.2680;
    (f) The requirements in Sec.  60.2665(b)(2);
    (g) Approval of alternative opacity emission limits in Sec.  
60.2670 under Sec.  60.11(e)(6) through (8);
    (h) Performance test and data reduction waivers under Sec.  
60.8(b)(4) and (5); and
    (i) Approval of an alternative to any electronic reporting to the 
EPA required by this subpart.


Sec.  60.2545   Does this subpart directly affect CISWI owners and 
operators in my state?

    (a) No. This subpart does not directly affect CISWI owners and 
operators in your state. However, CISWI owners and operators must 
comply with the state plan you develop to implement the emission 
guidelines contained in this subpart. States may choose to incorporate 
the model rule text directly in their state plan.
    (b) If you do not submit an approvable plan to implement and 
enforce the guidelines contained in this subpart for CISWIs that 
commenced construction before November 30, 1999 by December 2, 2002, 
EPA will implement and enforce a federal plan, as provided in Sec.  
60.2525, to ensure that each unit within your state reaches compliance 
with all the provisions of this subpart by December 1, 2005.
    (c) If you do not submit an approvable plan to implement and 
enforce the guidelines contained in this subpart by February 7, 2014, 
for CISWIs that commenced construction on or before June 4, 2010, EPA 
will implement and enforce a federal plan, as provided in Sec.  
60.2525, to ensure that each unit within your state that commenced 
construction on or before June 4, 2010, reaches compliance with all the 
provisions of this subpart by February 7, 2018.

Applicability of State Plans


Sec.  60.2550   What CISWIs must I address in my state plan?

    (a) Your state plan must address incineration units that meet all 
three criteria described in paragraphs (a)(1) through (3) of this 
section:
    (1) Commercial and industrial solid waste incineration units and 
ACIs in your state that commenced construction on or before June 4, 
2010, or commenced modification or

[[Page 15887]]

reconstruction after June 4, 2010 but no later than August 7, 2013;
    (2) Incineration units that meet the definition of a CISWI as 
defined in Sec.  60.2875 or an ACI as defined in Sec.  60.2875; and
    (3) Incineration units not exempt under Sec.  60.2555.
    (b) If the owner or operator of a CISWI or ACI makes changes that 
meet the definition of modification or reconstruction after August 7, 
2013, the CISWI or ACI becomes subject to subpart CCCC of this part and 
the state plan no longer applies to that unit.
    (c) If the owner or operator of a CISWI or ACI makes physical or 
operational changes to an existing CISWI or ACI primarily to comply 
with your state plan, subpart CCCC of this part does not apply to that 
unit. Such changes do not qualify as modifications or reconstructions 
under subpart CCCC of this part.


Sec.  60.2555   What combustion units are exempt from my state plan?

    This subpart exempts the types of units described in paragraphs (a) 
through (j) of this section, but some units are required to provide 
notifications.
    (a) Pathological waste incineration units. Incineration units 
burning 90 percent or more by weight (on a calendar quarter basis and 
excluding the weight of auxiliary fuel and combustion air) of 
pathological waste, low-level radioactive waste, and/or 
chemotherapeutic waste as defined in Sec.  60.2875 are not subject to 
this subpart if you meet the two requirements specified in paragraphs 
(a)(1) and (2) of this section:
    (1) Notify the Administrator that the unit meets these criteria; 
and
    (2) Keep records on a calendar quarter basis of the weight of 
pathological waste, low-level radioactive waste, and/or 
chemotherapeutic waste burned, and the weight of all other fuels and 
wastes burned in the unit.
    (b) Municipal waste combustion units. Incineration units that are 
subject to subpart Ea of this part (Standards of Performance for 
Municipal Waste Combustors); subpart Eb of this part (Standards of 
Performance for Large Municipal Waste Combustors); subpart Cb of this 
part (Emission Guidelines and Compliance Time for Large Municipal 
Combustors); AAAA of this part (Standards of Performance for Small 
Municipal Waste Combustion Units); or subpart BBBB of this part 
(Emission Guidelines for Small Municipal Waste Combustion Units).
    (c) Medical waste incineration units. Incineration units regulated 
under subpart Ec of this part (Standards of Performance for Hospital/
Medical/Infectious Waste Incinerators for Which Construction is 
Commenced After June 20, 1996) or subpart Ca of this part (Emission 
Guidelines and Compliance Times for Hospital/Medical/Infectious Waste 
Incinerators).
    (d) Small power production facilities. Units that meet the four 
requirements specified in paragraphs (d)(1) through (4) of this 
section:
    (1) The unit qualifies as a small power-production facility under 
section 3(17)(C) of the Federal Power Act (16 U.S.C. 796(17)(C));
    (2) The unit burns homogeneous waste (not including refuse-derived 
fuel) to produce electricity;
    (3) You submit documentation to the Administrator notifying the 
Agency that the qualifying small power production facility is 
combusting homogenous waste; and
    (4) You maintain the records specified in Sec.  60.2740(v).
    (e) Cogeneration facilities. Units that meet the four requirements 
specified in paragraphs (e)(1) through (4) of this section:
    (1) The unit qualifies as a cogeneration facility under section 
3(18)(B) of the Federal Power Act (16 U.S.C. 796(18)(B));
    (2) The unit burns homogeneous waste (not including refuse-derived 
fuel) to produce electricity and steam or other forms of energy used 
for industrial, commercial, heating, or cooling purposes;
    (3) You submit documentation to the Administrator notifying the 
Agency that the qualifying cogeneration facility is combusting 
homogenous waste; and
    (4) You maintain the records specified in Sec.  60.2740(w).
    (f) Hazardous waste combustion units. Units for which you are 
required to get a permit under section 3005 of the Solid Waste Disposal 
Act.
    (g) Materials recovery units. Units that combust waste for the 
primary purpose of recovering metals, such as primary and secondary 
smelters.
    (h) Sewage treatment plants. Incineration units regulated under 
subpart O of this part (Standards of Performance for Sewage Treatment 
Plants).
    (i) Sewage sludge incineration units. Incineration units combusting 
sewage sludge for the purpose of reducing the volume of the sewage 
sludge by removing combustible matter that are subject to subpart LLLL 
of this part (Standards of Performance for New Sewage Sludge 
Incineration Units) or subpart MMMM of this part (Emission Guidelines 
and Compliance Times for Existing Sewage Sludge Incineration Units).
    (j) Other solid waste incineration units. Incineration units that 
are subject to subpart EEEE of this part (Standards of Performance for 
Other Solid Waste Incineration Units for Which Construction is 
Commenced After December 9, 2004, or for Which Modification or 
Reconstruction is Commenced on or After June 16, 2006) or subpart FFFF 
of this part (Emission Guidelines and Compliance Times for Other Solid 
Waste Incineration Units That Commenced Construction On or Before 
December 9, 2004).

Use of Model Rule


Sec.  60.2560   What is the ``model rule'' in this subpart?

    (a) The model rule is the portion of these emission guidelines 
(Sec. Sec.  60.2575 through 60.2875 of this part) that addresses the 
regulatory requirements applicable to CISWIs. The model rule provides 
these requirements in regulation format. You must develop a state plan 
that is at least as protective as the model rule. You may use the model 
rule language as part of your state plan. Alternative language may be 
used in your state plan if you demonstrate that the alternative 
language is at least as protective as the model rule contained in this 
subpart.
    (b) In the model rule of Sec. Sec.  60.2575 to 60.2875, ``you'' 
means the owner or operator of a CISWI.


Sec.  60.2565   How does the model rule relate to the required elements 
of my state plan?

    Use the model rule to satisfy the state plan requirements specified 
in Sec.  60.2515(a)(4) and (5) of this part.


Sec.  60.2570   What are the principal components of the model rule?

    The model rule contains the eleven major components listed in 
paragraphs (a) through (k) of this section:
    (a) Increments of progress toward compliance;
    (b) Waste management plan;
    (c) Operator training and qualification;
    (d) Emission limitations and operating limits;
    (e) Performance testing;
    (f) Initial compliance requirements;
    (g) Continuous compliance requirements;
    (h) Monitoring;
    (i) Recordkeeping and reporting;
    (j) Definitions; and
    (k) Tables.

[[Page 15888]]

Model Rule--Increments of Progress


Sec.  60.2575   What are my requirements for meeting increments of 
progress and achieving final compliance?

    If you plan to achieve compliance more than 1 year following the 
effective date of state plan approval, you must meet the two increments 
of progress specified in paragraphs (a) and (b) of this section:
    (a) Submit a final control plan; and
    (b) Achieve final compliance.


Sec.  60.2580   When must I complete each increment of progress?

    Table 1 of this subpart specifies compliance dates for each of the 
increments of progress.


Sec.  60.2585   What must I include in the notifications of achievement 
of increments of progress?

    Your notification of achievement of increments of progress must 
include the three items specified in paragraphs (a) through (c) of this 
section:
    (a) Notification that the increment of progress has been achieved;
    (b) Any items required to be submitted with each increment of 
progress; and
    (c) Signature of the owner or operator of the CISWI.


Sec.  60.2590   When must I submit the notifications of achievement of 
increments of progress?

    Notifications for achieving increments of progress must be 
postmarked no later than 10 business days after the compliance date for 
the increment.


Sec.  60.2595   What if I do not meet an increment of progress?

    If you fail to meet an increment of progress, you must submit a 
notification to the Administrator postmarked within 10 business days 
after the date for that increment of progress in table 1 of this 
subpart. You must inform the Administrator that you did not meet the 
increment, and you must continue to submit reports each subsequent 
calendar month until the increment of progress is met.


Sec.  60.2600   How do I comply with the increment of progress for 
submittal of a control plan?

    For your control plan increment of progress, you must satisfy the 
two requirements specified in paragraphs (a) and (b) of this section:
    (a) Submit the final control plan that includes the five items 
described in paragraphs (a)(1) through (5) of this section:
    (1) A description of the devices for air pollution control and 
process changes that you will use to comply with the emission 
limitations and other requirements of this subpart;
    (2) The type(s) of waste to be burned;
    (3) The maximum design waste burning capacity;
    (4) The anticipated maximum charge rate; and
    (5) If applicable, the petition for site-specific operating limits 
under Sec.  60.2680.
    (b) Maintain an onsite copy of the final control plan.


Sec.  60.2605  How do I comply with the increment of progress for 
achieving final compliance?

    For the final compliance increment of progress, you must complete 
all process changes and retrofit construction of control devices, as 
specified in the final control plan, so that, if the affected CISWI is 
brought online, all necessary process changes and air pollution control 
devices would operate as designed.


Sec.  60.2610   What must I do if I close my CISWI and then restart it?

    (a) If you close your CISWI but will restart it prior to the final 
compliance date in your state plan, you must meet the increments of 
progress specified in Sec.  60.2575.
    (b) If you close your CISWI but will restart it after your final 
compliance date, you must complete emission control retrofits and meet 
the emission limitations and operating limits on the date your unit 
restarts operation.


Sec.  60.2615   What must I do if I plan to permanently close my CISWI 
and not restart it?

    If you plan to close your CISWI rather than comply with the state 
plan, submit a closure notification, including the date of closure, to 
the Administrator by the date your final control plan is due.

Model Rule--Waste Management Plan


Sec.  60.2620   What is a waste management plan?

    A waste management plan is a written plan that identifies both the 
feasibility and the methods used to reduce or separate certain 
components of solid waste from the waste stream in order to reduce or 
eliminate toxic emissions from incinerated waste.


Sec.  60.2625   When must I submit my waste management plan?

    You must submit a waste management plan no later than the date 
specified in table 1 of this subpart for submittal of the final control 
plan.


Sec.  60.2630   What should I include in my waste management plan?

    A waste management plan must include consideration of the reduction 
or separation of waste-stream elements such as paper, cardboard, 
plastics, glass, batteries, or metals; or the use of recyclable 
materials. The plan must identify any additional waste management 
measures, and the source must implement those measures considered 
practical and feasible, based on the effectiveness of waste management 
measures already in place, the costs of additional measures, the 
emissions reductions expected to be achieved, and any other 
environmental or energy impacts they might have.

Model Rule--Operator Training and Qualification


Sec.  60.2635   What are the operator training and qualification 
requirements?

    (a) No CISWI can be operated unless a fully trained and qualified 
CISWI operator is accessible, either at the facility or can be at the 
facility within 1 hour. The trained and qualified CISWI operator may 
operate the CISWI directly or be the direct supervisor of one or more 
other plant personnel who operate the unit. If all qualified CISWI 
operators are temporarily not accessible, you must follow the 
procedures in Sec.  60.2665.
    (b) Operator training and qualification must be obtained through a 
state-approved program or by completing the requirements included in 
paragraph (c) of this section.
    (c) Training must be obtained by completing an incinerator operator 
training course that includes, at a minimum, the three elements 
described in paragraphs (c)(1) through (3) of this section:
    (1) Training on the eleven subjects listed in paragraphs (c)(1)(i) 
through (xi) of this section:
    (i) Environmental concerns, including types of emissions;
    (ii) Basic combustion principles, including products of combustion;
    (iii) Operation of the specific type of incinerator to be used by 
the operator, including proper startup, waste charging, and shutdown 
procedures;
    (iv) Combustion controls and monitoring;
    (v) Operation of air pollution control equipment and factors 
affecting performance (if applicable);
    (vi) Inspection and maintenance of the incinerator and air 
pollution control devices;
    (vii) Actions to prevent and correct malfunctions or to prevent 
conditions that may lead to malfunctions;
    (viii) Bottom and fly ash characteristics and handling procedures;
    (ix) Applicable federal, state, and local regulations, including 
Occupational Safety and Health Administration workplace standards;

[[Page 15889]]

    (x) Pollution prevention; and
    (xi) Waste management practices.
    (2) An examination designed and administered by the instructor.
    (3) Written material covering the training course topics that can 
serve as reference material following completion of the course.


Sec.  60.2640   When must the operator training course be completed?

    The operator training course must be completed by the later of the 
three dates specified in paragraphs (a) through (c) of this section:
    (a) The final compliance date (Increment 2);
    (b) Six months after CISWI startup; and
    (c) Six months after an employee assumes responsibility for 
operating the CISWI or assumes responsibility for supervising the 
operation of the CISWI.


Sec.  60.2645   How do I obtain my operator qualification?

    (a) You must obtain operator qualification by completing a training 
course that satisfies the criteria under Sec.  60.2635(b).
    (b) Qualification is valid from the date on which the training 
course is completed and the operator successfully passes the 
examination required under Sec.  60.2635(c)(2).


Sec.  60.2650   How do I maintain my operator qualification?

    To maintain qualification, you must complete an annual review or 
refresher course covering, at a minimum, the five topics described in 
paragraphs (a) through (e) of this section:
    (a) Update of regulations;
    (b) Incinerator operation, including startup and shutdown 
procedures, waste charging, and ash handling;
    (c) Inspection and maintenance;
    (d) Prevention and correction of malfunctions or conditions that 
may lead to malfunction; and
    (e) Discussion of operating problems encountered by attendees.


Sec.  60.2655   How do I renew my lapsed operator qualification?

    You must renew a lapsed operator qualification by one of the two 
methods specified in paragraphs (a) and (b) of this section:
    (a) For a lapse of less than 3 years, you must complete a standard 
annual refresher course described in Sec.  60.2650; and
    (b) For a lapse of 3 years or more, you must repeat the initial 
qualification requirements in Sec.  60.2645(a).


Sec.  60.2660   What site-specific documentation is required?

    (a) Documentation must be available at the facility and readily 
accessible for all CISWI operators that addresses the ten topics 
described in paragraphs (a)(1) through (10) of this section. You must 
maintain this information and the training records required by 
paragraph (c) of this section in a manner that they can be readily 
accessed and are suitable for inspection upon request:
    (1) Summary of the applicable standards under this subpart;
    (2) Procedures for receiving, handling, and charging waste;
    (3) Incinerator startup, shutdown, and malfunction procedures;
    (4) Procedures for maintaining proper combustion air supply levels;
    (5) Procedures for operating the incinerator and associated air 
pollution control systems within the standards established under this 
subpart;
    (6) Monitoring procedures for demonstrating compliance with the 
incinerator operating limits;
    (7) Reporting and recordkeeping procedures;
    (8) The waste management plan required under Sec. Sec.  60.2620 
through 60.2630;
    (9) Procedures for handling ash; and
    (10) A list of the wastes burned during the performance test.
    (b) You must establish a program for reviewing the information 
listed in paragraph (a) of this section with each incinerator operator:
    (1) The initial review of the information listed in paragraph (a) 
of this section must be conducted by the later of the three dates 
specified in paragraphs (b)(1)(i) through (iii) of this section:
    (i) The final compliance date (Increment 2);
    (ii) Six months after CISWI startup; and
    (iii) Six months after being assigned to operate the CISWI.
    (2) Subsequent annual reviews of the information listed in 
paragraph (a) of this section must be conducted no later than 12 months 
following the previous review.
    (c) You must also maintain the information specified in paragraphs 
(c)(1) through (3) of this section:
    (1) Records showing the names of CISWI operators who have completed 
review of the information in Sec.  60.2660(a) as required by Sec.  
60.2660(b), including the date of the initial review and all subsequent 
annual reviews;
    (2) Records showing the names of the CISWI operators who have 
completed the operator training requirements under Sec.  60.2635, met 
the criteria for qualification under Sec.  60.2645, and maintained or 
renewed their qualification under Sec.  60.2650 or Sec.  60.2655. 
Records must include documentation of training, the dates of the 
initial refresher training, and the dates of their qualification and 
all subsequent renewals of such qualifications; and
    (3) For each qualified operator, the phone and/or pager number at 
which they can be reached during operating hours.


Sec.  60.2665   What if all the qualified operators are temporarily not 
accessible?

    If all qualified operators are temporarily not accessible (i.e., 
not at the facility and not able to be at the facility within 1 hour), 
you must meet one of the two criteria specified in paragraphs (a) and 
(b) of this section, depending on the length of time that a qualified 
operator is not accessible:
    (a) When all qualified operators are not accessible for more than 8 
hours, but less than 2 weeks, the CISWI may be operated by other plant 
personnel familiar with the operation of the CISWI who have completed a 
review of the information specified in Sec.  60.2660(a) within the past 
12 months. However, you must record the period when all qualified 
operators were not accessible and include this deviation in the annual 
report as specified under Sec.  60.2770;
    (b) When all qualified operators are not accessible for 2 weeks or 
more, you must take the two actions that are described in paragraphs 
(b)(1) and (2) of this section:
    (1) Notify the Administrator of this deviation in writing within 10 
days. In the notice, state what caused this deviation, what you are 
doing to ensure that a qualified operator is accessible, and when you 
anticipate that a qualified operator will be accessible; and
    (2) Submit a status report to the Administrator every 4 weeks 
outlining what you are doing to ensure that a qualified operator is 
accessible, stating when you anticipate that a qualified operator will 
be accessible and requesting approval from the Administrator to 
continue operation of the CISWI. You must submit the first status 
report 4 weeks after you notify the Administrator of the deviation 
under paragraph (b)(1) of this section. If the Administrator notifies 
you that your request to continue operation of the CISWI is 
disapproved, the CISWI may continue operation for 90 days, then must 
cease operation. Operation of the unit may resume if you meet the two 
requirements in paragraphs (b)(2)(i) and (ii) of this section:

[[Page 15890]]

    (i) A qualified operator is accessible as required under Sec.  
60.2635(a); and
    (ii) You notify the Administrator that a qualified operator is 
accessible and that you are resuming operation.

Model Rule--Emission Limitations and Operating Limits


Sec.  60.2670   What emission limitations must I meet and by when?

    (a) You must meet the emission limitations for each CISWI, 
including bypass stack or vent, specified in table 2 of this subpart or 
tables 6 through 9 of this subpart by the final compliance date under 
the approved state plan, federal plan, or delegation, as applicable. 
The emission limitations apply at all times the unit is operating 
including and not limited to startup, shutdown, or malfunction.
    (b) Units that do not use wet scrubbers must maintain opacity to 
less than or equal to the percent opacity (three 1-hour blocks 
consisting of ten 6-minute average opacity values) specified in table 2 
of this subpart, as applicable.


Sec.  60.2675   What operating limits must I meet and by when?

    (a) If you use a wet scrubber(s) to comply with the emission 
limitations, you must establish operating limits for up to four 
operating parameters (as specified in table 3 of this subpart) as 
described in paragraphs (a)(1) through (4) of this section during the 
initial performance test:
    (1) Maximum charge rate, calculated using one of the two different 
procedures in paragraph (a)(1)(i) or (ii) of this section, as 
appropriate:
    (i) For continuous and intermittent units, maximum charge rate is 
110 percent of the average charge rate measured during the most recent 
performance test demonstrating compliance with all applicable emission 
limitations; and
    (ii) For batch units, maximum charge rate is 110 percent of the 
daily charge rate measured during the most recent performance test 
demonstrating compliance with all applicable emission limitations.
    (2) Minimum pressure drop across the wet particulate matter 
scrubber, which is calculated as the lowest 1-hour average pressure 
drop across the wet scrubber measured during the most recent 
performance test demonstrating compliance with the particulate matter 
emission limitations; or minimum amperage to the wet scrubber, which is 
calculated as the lowest 1-hour average amperage to the wet scrubber 
measured during the most recent performance test demonstrating 
compliance with the particulate matter emission limitations.
    (3) Minimum scrubber liquid flow rate, which is calculated as the 
lowest 1-hour average liquid flow rate at the inlet to the wet acid gas 
or particulate matter scrubber measured during the most recent 
performance test demonstrating compliance with all applicable emission 
limitations.
    (4) Minimum scrubber liquor pH, which is calculated as the lowest 
1-hour average liquor pH at the inlet to the wet acid gas scrubber 
measured during the most recent performance test demonstrating 
compliance with the hydrogen chloride (HCl) emission limitation.
    (b) You must meet the operating limits established on the date that 
the performance test report is submitted to the EPA's Central Data 
Exchange or postmarked, per the requirements of Sec.  60.2795(b).
    (c) If you use a fabric filter to comply with the emission 
limitations and you do not use a particulate matter (PM) continuous 
parameter monitoring system (CPMS) for monitoring PM compliance, you 
must operate each fabric filter system such that the bag leak detection 
system alarm does not sound more than 5 percent of the operating time 
during a 6-month period. In calculating this operating time percentage, 
if inspection of the fabric filter demonstrates that no corrective 
action is required, no alarm time is counted. If corrective action is 
required, each alarm shall be counted as a minimum of 1 hour. If you 
take longer than 1 hour to initiate corrective action, the alarm time 
shall be counted as the actual amount of time taken by you to initiate 
corrective action.
    (d) If you use an electrostatic precipitator to comply with the 
emission limitations and you do not use a PM CPMS for monitoring PM 
compliance, you must measure the (secondary) voltage and amperage of 
the electrostatic precipitator collection plates during the particulate 
matter performance test. Calculate the average electric power value 
(secondary voltage x secondary current = secondary electric power) for 
each test run. The operating limit for the electrostatic precipitator 
is calculated as the lowest 1-hour average secondary electric power 
measured during the most recent performance test demonstrating 
compliance with the particulate matter emission limitations.
    (e) If you use activated carbon sorbent injection to comply with 
the emission limitations, you must measure the sorbent flow rate during 
the performance testing. The operating limit for the carbon sorbent 
injection is calculated as the lowest 1-hour average sorbent flow rate 
measured during the most recent performance test demonstrating 
compliance with the mercury emission limitations. For energy recovery 
units, when your unit operates at lower loads, multiply your sorbent 
injection rate by the load fraction, as defined in this subpart, to 
determine the required injection rate (e.g., for 50 percent load, 
multiply the injection rate operating limit by 0.5).
    (f) If you use selective noncatalytic reduction to comply with the 
emission limitations, you must measure the charge rate, the secondary 
chamber temperature (if applicable to your CISWI), and the reagent flow 
rate during the nitrogen oxides performance testing. The operating 
limits for the selective noncatalytic reduction are calculated as the 
highest 1-hour average charge rate, lowest secondary chamber 
temperature, and lowest reagent flow rate measured during the most 
recent performance test demonstrating compliance with the nitrogen 
oxides emission limitations.
    (g) If you use a dry scrubber to comply with the emission 
limitations, you must measure the injection rate of each sorbent during 
the performance testing. The operating limit for the injection rate of 
each sorbent is calculated as the lowest 1-hour average injection rate 
of each sorbent measured during the most recent performance test 
demonstrating compliance with the hydrogen chloride emission 
limitations. For energy recovery units, when your unit operates at 
lower loads, multiply your sorbent injection rate by the load fraction, 
as defined in this subpart, to determine the required injection rate 
(e.g., for 50 percent load, multiply the injection rate operating limit 
by 0.5).
    (h) If you do not use a wet scrubber, electrostatic precipitator, 
or fabric filter to comply with the emission limitations, and if you do 
not determine compliance with your particulate matter emission 
limitation with either a particulate matter CEMS or a particulate 
matter CPMS, you must maintain opacity to less than or equal to ten 
percent opacity (1-hour block average).
    (i) If you use a PM CPMS to demonstrate compliance, you must 
establish your PM CPMS operating limit and determine compliance with it 
according to paragraphs (i)(1) through (5) of this section:
    (1) During the initial performance test or any such subsequent 
performance test that demonstrates compliance with the PM limit, record 
all hourly average output values (milliamps, or the digital signal 
equivalent) from the PM CPMS for the periods corresponding to the test 
runs (e.g., three 1-hour average PM CPMS output values for three 1-hour 
test runs):

[[Page 15891]]

    (i) Your PM CPMS must provide a 4-20 milliamp output, or the 
digital signal equivalent, and the establishment of its relationship to 
manual reference method measurements must be determined in units of 
milliamps or digital bits;
    (ii) Your PM CPMS operating range must be capable of reading PM 
concentrations from zero to a level equivalent to at least two times 
your allowable emission limit. If your PM CPMS is an auto-ranging 
instrument capable of multiple scales, the primary range of the 
instrument must be capable of reading PM concentration from zero to a 
level equivalent to two times your allowable emission limit; and
    (iii) During the initial performance test or any such subsequent 
performance test that demonstrates compliance with the PM limit, record 
and average all milliamp output values, or their digital equivalent, 
from the PM CPMS for the periods corresponding to the compliance test 
runs (e.g., average all your PM CPMS output values for three 
corresponding 2-hour Method 5I test runs).
    (2) If the average of your three PM performance test runs are below 
75 percent of your PM emission limit, you must calculate an operating 
limit by establishing a relationship of PM CPMS signal to PM 
concentration using the PM CPMS instrument zero, the average PM CPMS 
output values corresponding to the three compliance test runs, and the 
average PM concentration from the Method 5 or performance test with the 
procedures in (i)(1)through (5) of this section:
    (i) Determine your instrument zero output with one of the following 
procedures:
    (A) Zero point data for in-situ instruments should be obtained by 
removing the instrument from the stack and monitoring ambient air on a 
test bench;
    (B) Zero point data for extractive instruments should be obtained 
by removing the extractive probe from the stack and drawing in clean 
ambient air;
    (C) The zero point can also can be established obtained by 
performing manual reference method measurements when the flue gas is 
free of PM emissions or contains very low PM concentrations (e.g., when 
your process is not operating, but the fans are operating or your 
source is combusting only natural gas) and plotting these with the 
compliance data to find the zero intercept; and
    (D) If none of the steps in paragraphs (i)(2)(i)(A) through (C) of 
this section are possible, you must use a zero output value provided by 
the manufacturer.
    (ii) Determine your PM CPMS instrument average in milliamps, or the 
digital equivalent, and the average of your corresponding three PM 
compliance test runs, using equation 1:
[GRAPHIC] [TIFF OMITTED] TR16AP19.013

Where:

X1 = the PM CPMS output data points for the three runs 
constituting the performance test,
Y1 = the PM concentration value for the three runs 
constituting the performance test, and
n = the number of data points.

    (iii) With your instrument zero expressed in milliamps, or the 
digital equivalent, your three run average PM CPMS milliamp value, or 
its digital equivalent, and your three run average PM concentration 
from your three compliance tests, determine a relationship of mg/dscm 
per milliamp or digital signal equivalent, with equation 2:
[GRAPHIC] [TIFF OMITTED] TR16AP19.014

Where:

R = the relative mg/dscm per milliamp, or the digital equivalent, 
for your PM CPMS,
Y1 = the three run average mg/dscm PM concentration,
X1 = the three run average milliamp output, or the 
digital equivalent, from you PM CPMS, and
z = the milliamp or digital signal equivalent of your instrument 
zero determined from paragraph (i)(2)(i) of this section.

    (iv) Determine your source specific 30-day rolling average 
operating limit using the mg/dscm per milliamp value, or per digital 
signal equivalent, from equation 2 in equation 3, below. This sets your 
operating limit at the PM CPMS output value corresponding to 75 percent 
of your emission limit:
[GRAPHIC] [TIFF OMITTED] TR16AP19.015

Where:

Ol = the operating limit for your PM CPMS on a 30-day 
rolling average, in milliamps or their digital signal equivalent,
L = your source emission limit expressed in mg/dscm,

[[Page 15892]]

z = your instrument zero in milliamps or digital equivalent, 
determined from paragraph (i)(2)(i) of this section, and
R = the relative mg/dscm per milliamp, or per digital signal output 
equivalent, for your PM CPMS, from equation 2.
    (3) If the average of your three PM compliance test runs is at or 
above 75 percent of your PM emission limit you must determine your 
operating limit by averaging the PM CPMS milliamp or digital signal 
output corresponding to your three PM performance test runs that 
demonstrate compliance with the emission limit using equation 4 and you 
must submit all compliance test and PM CPMS data according to the 
reporting requirements in paragraph (i)(5) of this section:
[GRAPHIC] [TIFF OMITTED] TR16AP19.016

Where:

X1 = the PM CPMS data points for all runs i,
n = the number of data points, and
Oh = your site specific operating limit, in milliamps or 
digital signal equivalent.

    (4) To determine continuous compliance, you must record the PM CPMS 
output data for all periods when the process is operating and the PM 
CPMS is not out-of-control. You must demonstrate continuous compliance 
by using all quality-assured hourly average data collected by the PM 
CPMS for all operating hours to calculate the arithmetic average 
operating parameter in units of the operating limit (e.g., milliamps or 
digital signal bits, PM concentration, raw data signal) on a 30-day 
rolling average basis.
    (5) For PM performance test reports used to set a PM CPMS operating 
limit, the electronic submission of the test report must also include 
the make and model of the PM CPMS instrument, serial number of the 
instrument, analytical principle of the instrument (e.g., beta 
attenuation), span of the instruments primary analytical range, 
milliamp or digital signal value equivalent to the instrument zero 
output, technique by which this zero value was determined, and the 
average milliamp or digital signals corresponding to each PM compliance 
test run.


Sec.  60.2680  What if I do not use a wet scrubber, fabric filter, 
activated carbon injection, selective noncatalytic reduction, an 
electrostatic precipitator, or a dry scrubber to comply with the 
emission limitations?

    (a) If you use an air pollution control device other than a wet 
scrubber, activated carbon injection, selective noncatalytic reduction, 
fabric filter, an electrostatic precipitator, or a dry scrubber or 
limit emissions in some other manner, including mass balances, to 
comply with the emission limitations under Sec.  60.2670, you must 
petition the EPA Administrator for specific operating limits to be 
established during the initial performance test and continuously 
monitored thereafter. You must submit the petition at least sixty days 
before the performance test is scheduled to begin. Your petition must 
include the five items listed in paragraphs (a)(1) through (5) of this 
section:
    (1) Identification of the specific parameters you propose to use as 
additional operating limits;
    (2) A discussion of the relationship between these parameters and 
emissions of regulated pollutants, identifying how emissions of 
regulated pollutants change with changes in these parameters and how 
limits on these parameters will serve to limit emissions of regulated 
pollutants;
    (3) A discussion of how you will establish the upper and/or lower 
values for these parameters which will establish the operating limits 
on these parameters;
    (4) A discussion identifying the methods you will use to measure 
and the instruments you will use to monitor these parameters, as well 
as the relative accuracy and precision of these methods and 
instruments; and
    (5) A discussion identifying the frequency and methods for 
recalibrating the instruments you will use for monitoring these 
parameters.
    (b) [Reserved]

Model Rule--Performance Testing


Sec.  60.2690  How do I conduct the initial and annual performance 
test?

    (a) All performance tests must consist of a minimum of three test 
runs conducted under conditions representative of normal operations.
    (b) You must document that the waste burned during the performance 
test is representative of the waste burned under normal operating 
conditions by maintaining a log of the quantity of waste burned (as 
required in Sec.  60.2740(b)(1)) and the types of waste burned during 
the performance test.
    (c) All performance tests must be conducted using the minimum run 
duration specified in tables 2 and 6 through 9 of this subpart.
    (d) Method 1 of appendix A of this part must be used to select the 
sampling location and number of traverse points.
    (e) Method 3A or 3B of appendix A of this part must be used for gas 
composition analysis, including measurement of oxygen concentration. 
Method 3A or 3B of appendix A of this part must be used simultaneously 
with each method (except when using Method 9 and Method 22).
    (f) All pollutant concentrations, except for opacity, must be 
adjusted to 7 percent oxygen using equation 5 of this section:
[GRAPHIC] [TIFF OMITTED] TR16AP19.017

Where:

Cadj = pollutant concentration adjusted to 7 percent 
oxygen;
Cmeas = pollutant concentration measured on a dry basis;
(20.9-7) = 20.9 percent oxygen-7 percent oxygen (defined oxygen 
correction basis);

[[Page 15893]]

20.9 = oxygen concentration in air, percent; and
%O2 = oxygen concentration measured on a dry basis, 
percent.

    (g) You must determine dioxins/furans toxic equivalency by 
following the procedures in paragraphs (g)(1) through (4) of this 
section:
    (1) Measure the concentration of each dioxin/furan tetra- through 
octa-isomer emitted using EPA Method 23 at 40 CFR part 60, appendix A;
    (2) Quantify isomers meeting identification criteria 2, 3, 4, and 5 
in Section 5.3.2.5 of Method 23, regardless of whether the isomers meet 
identification criteria 1 and 7. You must quantify the isomers per 
Section 9.0 of Method 23. [Note: You may reanalyze the sample aliquot 
or split to reduce the number of isomers not meeting identification 
criteria 1 or 7 of Section 5.3.2.5.];
    (3) For each dioxin/furan (tetra- through octa-chlorinated) isomer 
measured in accordance with paragraph (g)(1) and (2) of this section, 
multiply the isomer concentration by its corresponding toxic 
equivalency factor specified in table 4 of this subpart; and
    (4) Sum the products calculated in accordance with paragraph (g)(3) 
of this section to obtain the total concentration of dioxins/furans 
emitted in terms of toxic equivalency.
    (h) Method 22 at 40 CFR part 60, appendix A-7 must be used to 
determine compliance with the fugitive ash emission limit in table 2 of 
this subpart or tables 6 through 9 of this subpart.
    (i) If you have an applicable opacity operating limit, you must 
determine compliance with the opacity limit using Method 9 at 40 CFR 
part 60, appendix A-4, based on three 1-hour blocks consisting of ten 
6-minute average opacity values, unless you are required to install a 
continuous opacity monitoring system, consistent with Sec.  60.2710 and 
Sec.  60.2730.
    (j) You must determine dioxins/furans total mass basis by following 
the procedures in paragraphs (j)(1) through (3) of this section:
    (1) Measure the concentration of each dioxin/furan tetra- through 
octa-chlorinated isomer emitted using EPA Method 23 at 40 CFR part 60, 
appendix A-7;
    (2) Quantify isomers meeting identification criteria 2, 3, 4, and 5 
in Section 5.3.2.5 of Method 23, regardless of whether the isomers meet 
identification criteria 1 and 7. You must quantify the isomers per 
Section 9.0 of Method 23. (Note: You may reanalyze the sample aliquot 
or split to reduce the number of isomers not meeting identification 
criteria 1 or 7 of Section 5.3.2.5.); and
    (3) Sum the quantities measured in accordance with paragraphs 
(j)(1) and (2) of this section to obtain the total concentration of 
dioxins/furans emitted in terms of total mass basis.


Sec.  60.2695  How are the performance test data used?

    You use results of performance tests to demonstrate compliance with 
the emission limitations in table 2 of this subpart or tables 6 through 
9 of this subpart.

Model Rule--Initial Compliance Requirements


Sec.  60.2700   How do I demonstrate initial compliance with the 
amended emission limitations and establish the operating limits?

    (a) You must conduct a performance test, as required under 
Sec. Sec.  60.2670 and 60.2690, to determine compliance with the 
emission limitations in table 2 of this subpart and tables 6 through 9 
of this subpart, to establish compliance with any opacity operating 
limits in Sec.  60.2675, to establish the kiln-specific emission limit 
in Sec.  60.2710(y), as applicable, and to establish operating limits 
using the procedures in Sec.  60.2675 or Sec.  60.2680. The performance 
test must be conducted using the test methods listed in table 2 of this 
subpart and tables 6 through 9 of this subpart and the procedures in 
Sec.  60.2690. The use of the bypass stack during a performance test 
shall invalidate the performance test.
    (b) As an alternative to conducting a performance test, as required 
under Sec. Sec.  60.2690 and 60.2670, you may use a 30-day rolling 
average of the 1-hour arithmetic average CEMS data, including CEMS data 
during startup and shutdown as defined in this subpart, to determine 
compliance with the emission limitations in Table 1 of this subpart or 
Tables 5 through 8 of this subpart. You must conduct a performance 
evaluation of each continuous monitoring system within 180 days of 
installation of the monitoring system. The initial performance 
evaluation must be conducted prior to collecting CEMS data that will be 
used for the initial compliance demonstration.


Sec.  60.2705   By what date must I conduct the initial performance 
test?

    (a) The initial performance test must be conducted no later than 
180 days after your final compliance date. Your final compliance date 
is specified in table 1 of this subpart.
    (b) If you commence or recommence combusting a solid waste at an 
existing combustion unit at any commercial or industrial facility and 
you conducted a test consistent with the provisions of this subpart 
while combusting the given solid waste within the 6 months preceding 
the reintroduction of that solid waste in the combustion chamber, you 
do not need to retest until 6 months from the date you reintroduce that 
solid waste.
    (c) If you commence or recommence combusting a solid waste at an 
existing combustion unit at any commercial or industrial facility and 
you have not conducted a performance test consistent with the 
provisions of this subpart while combusting the given solid waste 
within the 6 months preceding the reintroduction of that solid waste in 
the combustion chamber, you must conduct a performance test within 60 
days from the date you reintroduce solid waste.


Sec.  60.2706   By what date must I conduct the initial air pollution 
control device inspection?

    (a) The initial air pollution control device inspection must be 
conducted within 60 days after installation of the control device and 
the associated CISWI reaches the charge rate at which it will operate, 
but no later than 180 days after the final compliance date for meeting 
the amended emission limitations.
    (b) Within 10 operating days following an air pollution control 
device inspection, all necessary repairs must be completed unless the 
owner or operator obtains written approval from the state agency 
establishing a date whereby all necessary repairs of the designated 
facility must be completed.

Model Rule--Continuous Compliance Requirements


Sec.  60.2710   How do I demonstrate continuous compliance with the 
amended emission limitations and the operating limits?

    (a) General compliance with standards, considering some units may 
be able to switch between solid waste and non-waste fuel combustion, is 
specified in paragraph (a)(1) through (6) of this section.
    (1) The emission standards and operating requirements set forth in 
this subpart apply at all times.
    (2) If you cease combusting solid waste you may opt to remain 
subject to the provisions of this subpart. Consistent with the 
definition of CISWI, you are subject to the requirements of this 
subpart at least 6 months following the last date of solid waste 
combustion. Solid waste combustion is ceased when solid waste is not in 
the combustion

[[Page 15894]]

chamber (i.e., the solid waste feed to the combustor has been cut off 
for a period of time not less than the solid waste residence time).
    (3) If you cease combusting solid waste you must be in compliance 
with any newly applicable standards on the effective date of the waste-
to-fuel switch. The effective date of the waste-to-fuel switch is a 
date selected by you, that must be at least 6 months from the date that 
you ceased combusting solid waste, consistent with Sec.  60.2710(a)(2). 
Your source must remain in compliance with this subpart until the 
effective date of the waste-to-fuel switch.
    (4) If you own or operate an existing commercial or industrial 
combustion unit that combusted a fuel or non-waste material, and you 
commence or recommence combustion of solid waste, you are subject to 
the provisions of this subpart as of the first day you introduce or 
reintroduce solid waste to the combustion chamber, and this date 
constitutes the effective date of the fuel-to-waste switch. You must 
complete all initial compliance demonstrations for any Section 112 
standards that are applicable to your facility before you commence or 
recommence combustion of solid waste. You must provide 30 days prior 
notice of the effective date of the waste-to-fuel switch. The 
notification must identify:
    (i) The name of the owner or operator of the CISWI, the location of 
the source, the emissions unit(s) that will cease burning solid waste, 
and the date of the notice;
    (ii) The currently applicable subcategory under this subpart, and 
any 40 CFR part 63 subpart and subcategory that will be applicable 
after you cease combusting solid waste;
    (iii) The fuel(s), non-waste material(s) and solid waste(s) the 
CISWI is currently combusting and has combusted over the past 6 months, 
and the fuel(s) or non-waste materials the unit will commence 
combusting;
    (iv) The date on which you became subject to the currently 
applicable emission limits;
    (v) The date upon which you will cease combusting solid waste, and 
the date (if different) that you intend for any new requirements to 
become applicable (i.e., the effective date of the waste-to-fuel 
switch), consistent with paragraphs (a)(2) and (3) of this section.
    (5) All air pollution control equipment necessary for compliance 
with any newly applicable emissions limits which apply as a result of 
the cessation or commencement or recommencement of combusting solid 
waste must be installed and operational as of the effective date of the 
waste-to-fuel, or fuel-to-waste switch.
    (6) All monitoring systems necessary for compliance with any newly 
applicable monitoring requirements which apply as a result of the 
cessation or commencement or recommencement of combusting solid waste 
must be installed and operational as of the effective date of the 
waste-to-fuel, or fuel-to-waste switch. All calibration and drift 
checks must be performed as of the effective date of the waste-to-fuel, 
or fuel-to-waste switch. Relative accuracy tests must be performed as 
of the performance test deadline for PM CEMS (if PM CEMS are elected to 
demonstrate continuous compliance with the particulate matter emission 
limits). Relative accuracy testing for other CEMS need not be repeated 
if that testing was previously performed consistent with section 112 
monitoring requirements or monitoring requirements under this subpart.
    (b) You must conduct an annual performance test for the pollutants 
listed in table 2 of this subpart or tables 6 through 9 of this subpart 
and opacity for each CISWI as required under Sec.  60.2690. The annual 
performance test must be conducted using the test methods listed in 
table 2 of this subpart or tables 6 through 9 of this subpart and the 
procedures in Sec.  60.2690. Opacity must be measured using EPA 
Reference Method 9 at 40 CFR part 60. Annual performance tests are not 
required if you use CEMS or continuous opacity monitoring systems to 
determine compliance.
    (c) You must continuously monitor the operating parameters 
specified in Sec.  60.2675 or established under Sec.  60.2680 and as 
specified in Sec.  60.2735. Operation above the established maximum or 
below the established minimum operating limits constitutes a deviation 
from the established operating limits. Three-hour block average values 
are used to determine compliance (except for baghouse leak detection 
system alarms) unless a different averaging period is established under 
Sec.  60.2680 or, for energy recovery units, where the averaging time 
for each operating parameter is a 30-day rolling, calculated each hour 
as the average of the previous 720 operating hours. Operation above the 
established maximum, below the established minimum, or outside the 
allowable range of the operating limits specified in paragraph (a) of 
this section constitutes a deviation from your operating limits 
established under this subpart, except during performance tests 
conducted to determine compliance with the emission and operating 
limits or to establish new operating limits. Operating limits are 
confirmed or reestablished during performance tests.
    (d) You must burn only the same types of waste and fuels used to 
establish subcategory applicability (for ERUs) and operating limits 
during the performance test.
    (e) For energy recovery units, incinerators, and small remote 
units, you must perform annual visual emissions test for ash handling.
    (f) For energy recovery units, you must conduct an annual 
performance test for opacity using EPA Reference Method 9 at 40 CFR 
part 60 (except where particulate matter continuous monitoring system 
or CPMS are used) and the pollutants listed in table 7 of this subpart.
    (g) For facilities using a CEMS to demonstrate compliance with the 
carbon monoxide emission limit, compliance with the carbon monoxide 
emission limit may be demonstrated by using the CEMS, as described in 
Sec.  60.2730(o).
    (h) Coal and liquid/gas energy recovery units with annual average 
heat input rates greater than 250 MMBtu/hr may elect to demonstrate 
continuous compliance with the particulate matter emissions limit using 
a particulate matter CEMS according to the procedures in Sec.  
60.2730(n) instead of the CPMS specified in Sec.  60.2710(i). Coal and 
liquid/gas energy recovery units with annual average heat input rates 
less than 250 MMBtu/hr, incinerators, and small remote incinerators may 
also elect to demonstrate compliance using a particulate matter CEMS 
according to the procedures in Sec.  60.2730(n) instead of particulate 
matter testing with EPA Method 5 at 40 CFR part 60, appendix A-3 and, 
if applicable, the continuous opacity monitoring requirements in 
paragraph (i) of this section.
    (i) For energy recovery units with annual average heat input rates 
greater than or equal to 10 MMBtu/hr but less than 250 MMBtu/hr that do 
not use a wet scrubber, fabric filter with bag leak detection system, 
an electrostatic precipitator, particulate matter CEMS, or particulate 
matter CPMS, you must install, operate, certify and maintain a 
continuous opacity monitoring system (COMS) according to the procedures 
in Sec.  60.2730(m).
    (j) For waste-burning kilns, you must conduct an annual performance 
test for the pollutants (except mercury and particulate matter, and 
hydrogen chloride if no acid gas wet scrubber or dry scrubber is used) 
listed in table 8 of this subpart, unless you choose to demonstrate 
initial and continuous compliance using CEMS, as allowed in

[[Page 15895]]

paragraph (u) of this section. If you do not use an acid gas wet 
scrubber or dry scrubber, you must determine compliance with the 
hydrogen chloride emissions limit using a HCl CEMS according to the 
requirements in paragraph (j)(1) of this section. You must determine 
compliance with the mercury emissions limit using a mercury CEMS or an 
integrated sorbent trap monitoring system according to paragraph (j)(2) 
of this section. You must determine compliance with particulate matter 
using CPMS.
    (1) If you monitor compliance with the HCl emissions limit by 
operating an HCl CEMS, you must do so in accordance with Performance 
Specification 15 (PS 15) of appendix B to 40 CFR part 60, or, PS 18 of 
appendix B to 40 CFR part 60. You must operate, maintain, and quality 
assure a HCl CEMS installed and certified under PS 15 according to the 
quality assurance requirements in Procedure 1 of appendix F to 40 CFR 
part 60 except that the Relative Accuracy Test Audit requirements of 
Procedure 1 must be replaced with the validation requirements and 
criteria of sections 11.1.1 and 12.0 of PS 15. You must operate, 
maintain and quality assure a HCl CEMS installed and certified under PS 
18 according to the quality assurance requirements in Procedure 6 of 
appendix F to 40 CFR part 60. For any performance specification that 
you use, you must use Method 321 of appendix A to 40 CFR part 63 as the 
reference test method for conducting relative accuracy testing. The 
span value and calibration requirements in paragraphs (j)(1)(i) and 
(ii) of this section apply to all HCl CEMS used under this subpart:
    (i) You must use a measurement span value for any HCl CEMS of 0-10 
ppmvw unless the monitor is installed on a kiln without an inline raw 
mill. Kilns without an inline raw mill may use a higher span value 
sufficient to quantify all expected emissions concentrations. The HCl 
CEMS data recorder output range must include the full range of expected 
HCl concentration values which would include those expected during 
``mill off'' conditions. The corresponding data recorder range shall be 
documented in the site-specific monitoring plan and associated records; 
and
    (ii) In order to quality assure data measured above the span value, 
you must use one of the three options in paragraphs (j)(1)(ii)(A) 
through (C) of this section:
    (A) Include a second span that encompasses the HCl emission 
concentrations expected to be encountered during ``mill off'' 
conditions. This second span may be rounded to a multiple of 5 ppm of 
total HCl. The requirements of the appropriate HCl monitor performance 
specification shall be followed for this second span with the exception 
that a RATA with the mill off is not required;
    (B) Quality assure any data above the span value by proving 
instrument linearity beyond the span value established in paragraph 
(j)(1)(i) of this section using the following procedure. Conduct a 
weekly ``above span linearity'' calibration challenge of the monitoring 
system using a reference gas with a certified value greater than your 
highest expected hourly concentration or greater than 75% of the 
highest measured hourly concentration. The ``above span'' reference gas 
must meet the requirements of the applicable performance specification 
and must be introduced to the measurement system at the probe. Record 
and report the results of this procedure as you would for a daily 
calibration. The ``above span linearity'' challenge is successful if 
the value measured by the HCl CEMS falls within 10 percent of the 
certified value of the reference gas. If the value measured by the HCl 
CEMS during the above span linearity challenge exceeds 10 percent of 
the certified value of the reference gas, the monitoring system must be 
evaluated and repaired and a new ``above span linearity'' challenge met 
before returning the HCl CEMS to service, or data above span from the 
HCl CEMS must be subject to the quality assurance procedures 
established in (j)(1)(ii)(D) of this section. In this manner values 
measured by the HCl CEMS during the above span linearity challenge 
exceeding +/-20 percent of the certified value of the reference gas 
must be normalized using equation 6;
    (C) Quality assure any data above the span value established in 
paragraph (j)(1)(i) of this section using the following procedure. Any 
time two consecutive one-hour average measured concentration of HCl 
exceeds the span value you must, within 24 hours before or after, 
introduce a higher, ``above span'' HCl reference gas standard to the 
HCl CEMS. The ``above span'' reference gas must meet the requirements 
of the applicable performance specification and target a concentration 
level between 50 and 150 percent of the highest expected hourly 
concentration measured during the period of measurements above span, 
and must be introduced at the probe. While this target represents a 
desired concentration range that is not always achievable in practice, 
it is expected that the intent to meet this range is demonstrated by 
the value of the reference gas. Expected values may include above span 
calibrations done before or after the above-span measurement period. 
Record and report the results of this procedure as you would for a 
daily calibration. The ``above span'' calibration is successful if the 
value measured by the HCl CEMS is within 20 percent of the certified 
value of the reference gas. If the value measured by the HCl CEMS is 
not within 20 percent of the certified value of the reference gas, then 
you must normalize the stack gas values measured above span as 
described in paragraph (j)(1)(ii)(D) of this section. If the ``above 
span'' calibration is conducted during the period when measured 
emissions are above span and there is a failure to collect the one data 
point in an hour due to the calibration duration, then you must 
determine the emissions average for that missed hour as the average of 
hourly averages for the hour preceding the missed hour and the hour 
following the missed hour. In an hour where an ``above span'' 
calibration is being conducted and one or more data points are 
collected, the emissions average is represented by the average of all 
valid data points collected in that hour; and
    (D) In the event that the ``above span'' calibration is not 
successful (i.e., the HCl CEMS measured value is not within 20 percent 
of the certified value of the reference gas), then you must normalize 
the one-hour average stack gas values measured above the span during 
the 24-hour period preceding or following the ``above span'' 
calibration for reporting based on the HCl CEMS response to the 
reference gas as shown in equation 6:
[GRAPHIC] [TIFF OMITTED] TR16AP19.018

    Only one ``above span'' calibration is needed per 24-hour period.
    (2) Compliance with the mercury emissions limit must be determined 
using a mercury CEMS or integrated sorbent trap monitoring system 
according to the following requirements:

[[Page 15896]]

    (i) You must operate a mercury CEMS in accordance with performance 
specification 12A at 40 CFR part 60, appendix B or an integrated 
sorbent trap monitoring system in accordance with performance 
specification 12B at 40 CFR part 60, appendix B; these monitoring 
systems must be quality assured according to procedure 5 of 40 CFR 60, 
appendix F. For the purposes of emissions calculations when using an 
integrated sorbent trap monitoring system, the mercury concentration 
determined for each sampling period must be assigned to each hour 
during the sampling period. If you choose to comply with the 
production-rate based mercury limit for your waste-burning kiln, you 
must also monitor hourly clinker production and determine the hourly 
mercury emissions rate in pounds per million ton of clinker produced. 
You must demonstrate compliance with the mercury emissions limit using 
a 30-day rolling average of these 1-hour mercury concentrations or mass 
emissions rates, including CEMS data during startup and shutdown as 
defined in this subpart, calculated using equation 19-19 in section 
12.4.1 of EPA Reference Method 19 at 40 CFR part 60, appendix A-7 of 
this part. CEMS data during startup and shutdown, as defined in this 
subpart, are not corrected to 7 percent oxygen, and are measured at 
stack oxygen content;
    (ii) Owners or operators using a mercury CEMS or integrated sorbent 
trap monitoring system to determine mass emission rate must install, 
operate, calibrate and maintain an instrument for continuously 
measuring and recording the mercury mass emissions rate to the 
atmosphere according to the requirements of performance specification 6 
at 40 CFR part 60, appendix B and conducting an annual relative 
accuracy test of the continuous emission rate monitoring system 
according to section 8.2 of performance specification 6; and
    (iii) The owner or operator of a waste-burning kiln must 
demonstrate initial compliance by operating a mercury CEMS or 
integrated sorbent trap monitoring system while the raw mill of the in-
line kiln/raw mill is operating under normal conditions and including 
at least one period when the raw mill is off.
    (k) If you use an air pollution control device to meet the emission 
limitations in this subpart, you must conduct an initial and annual 
inspection of the air pollution control device. The inspection must 
include, at a minimum, the following:
    (1) Inspect air pollution control device(s) for proper operation; 
and
    (2) Develop a site-specific monitoring plan according to the 
requirements in paragraph (l) of this section. This requirement also 
applies to you if you petition the EPA Administrator for alternative 
monitoring parameters under Sec.  60.13(i).
    (l) For each CMS required in this section, you must develop and 
submit to the EPA Administrator for approval a site-specific monitoring 
plan according to the requirements of this paragraph (l) that addresses 
paragraphs (l)(1)(i) through (vi) of this section:
    (1) You must submit this site-specific monitoring plan at least 60 
days before your initial performance evaluation of your continuous 
monitoring system:
    (i) Installation of the continuous monitoring system sampling probe 
or other interface at a measurement location relative to each affected 
process unit such that the measurement is representative of control of 
the exhaust emissions (e.g., on or downstream of the last control 
device);
    (ii) Performance and equipment specifications for the sample 
interface, the pollutant concentration or parametric signal analyzer 
and the data collection and reduction systems;
    (iii) Performance evaluation procedures and acceptance criteria 
(e.g., calibrations);
    (iv) Ongoing operation and maintenance procedures in accordance 
with the general requirements of Sec.  60.11(d);
    (v) Ongoing data quality assurance procedures in accordance with 
the general requirements of Sec.  60.13; and
    (vi) Ongoing recordkeeping and reporting procedures in accordance 
with the general requirements of Sec.  60.7(b), (c) introductory text, 
(c)(1) and (4), and (d) through (g).
    (2) You must conduct a performance evaluation of each continuous 
monitoring system in accordance with your site-specific monitoring 
plan.
    (3) You must operate and maintain the continuous monitoring system 
in continuous operation according to the site-specific monitoring plan.
    (m) If you have an operating limit that requires the use of a flow 
monitoring system, you must meet the requirements in paragraphs (l) and 
(m)(1) through (4) of this section:
    (1) Install the flow sensor and other necessary equipment in a 
position that provides a representative flow;
    (2) Use a flow sensor with a measurement sensitivity at full scale 
of no greater than 2 percent;
    (3) Minimize the effects of swirling flow or abnormal velocity 
distributions due to upstream and downstream disturbances; and
    (4) Conduct a flow monitoring system performance evaluation in 
accordance with your monitoring plan at the time of each performance 
test but no less frequently than annually.
    (n) If you have an operating limit that requires the use of a 
pressure monitoring system, you must meet the requirements in 
paragraphs (l) and (n)(1) through (6) of this section:
    (1) Install the pressure sensor(s) in a position that provides a 
representative measurement of the pressure (e.g., PM scrubber pressure 
drop);
    (2) Minimize or eliminate pulsating pressure, vibration, and 
internal and external corrosion;
    (3) Use a pressure sensor with a minimum tolerance of 1.27 
centimeters of water or a minimum tolerance of 1 percent of the 
pressure monitoring system operating range, whichever is less;
    (4) Perform checks at the frequency outlined in your site-specific 
monitoring plan to ensure pressure measurements are not obstructed 
(e.g., check for pressure tap plugging daily);
    (5) Conduct a performance evaluation of the pressure monitoring 
system in accordance with your monitoring plan at the time of each 
performance test but no less frequently than annually; and
    (6) If at any time the measured pressure exceeds the manufacturer's 
specified maximum operating pressure range, conduct a performance 
evaluation of the pressure monitoring system in accordance with your 
monitoring plan and confirm that the pressure monitoring system 
continues to meet the performance requirements in your monitoring plan. 
Alternatively, install and verify the operation of a new pressure 
sensor.
    (o) If you have an operating limit that requires a pH monitoring 
system, you must meet the requirements in paragraphs (l) and (o)(1) 
through (4) of this section:
    (1) Install the pH sensor in a position that provides a 
representative measurement of scrubber effluent pH;
    (2) Ensure the sample is properly mixed and representative of the 
fluid to be measured;
    (3) Conduct a performance evaluation of the pH monitoring system in 
accordance with your monitoring plan at least once each process 
operating day; and
    (4) Conduct a performance evaluation (including a two-point 
calibration with one of the two buffer solutions having a pH within 1 
of the pH of the operating limit) of the pH monitoring system in 
accordance with your monitoring plan at the time of each performance 
test but no less frequently than quarterly.

[[Page 15897]]

    (p) If you have an operating limit that requires a secondary 
electric power monitoring system for an electrostatic precipitator, you 
must meet the requirements in paragraphs (l) and (p)(1) and (2) of this 
section:
    (1) Install sensors to measure (secondary) voltage and current to 
the precipitator collection plates; and
    (2) Conduct a performance evaluation of the electric power 
monitoring system in accordance with your monitoring plan at the time 
of each performance test but no less frequently than annually.
    (q) If you have an operating limit that requires the use of a 
monitoring system to measure sorbent injection rate (e.g., weigh belt, 
weigh hopper, or hopper flow measurement device), you must meet the 
requirements in paragraphs (l) and (q)(1) and (2) of this section:
    (1) Install the system in a position(s) that provides a 
representative measurement of the total sorbent injection rate; and
    (2) Conduct a performance evaluation of the sorbent injection rate 
monitoring system in accordance with your monitoring plan at the time 
of each performance test but no less frequently than annually.
    (r) If you elect to use a fabric filter bag leak detection system 
to comply with the requirements of this subpart, you must install, 
calibrate, maintain, and continuously operate a bag leak detection 
system as specified in paragraphs (l) and (r)(1) through (5) of this 
section:
    (1) Install a bag leak detection sensor(s) in a position(s) that 
will be representative of the relative or absolute particulate matter 
loadings for each exhaust stack, roof vent, or compartment (e.g., for a 
positive pressure fabric filter) of the fabric filter;
    (2) Use a bag leak detection system certified by the manufacturer 
to be capable of detecting particulate matter emissions at 
concentrations of 10 milligrams per actual cubic meter or less;
    (3) Conduct a performance evaluation of the bag leak detection 
system in accordance with your monitoring plan and consistent with the 
guidance provided in EPA-454/R-98-015 (incorporated by reference, see 
Sec.  60.17);
    (4) Use a bag leak detection system equipped with a device to 
continuously record the output signal from the sensor; and
    (5) Use a bag leak detection system equipped with a system that 
will sound an alarm when an increase in relative particulate matter 
emissions over a preset level is detected. The alarm must be located 
where it is observed readily by plant operating personnel.
    (s) For facilities using a CEMS to demonstrate initial and 
continuous compliance with the sulfur dioxide emission limit, 
compliance with the sulfur dioxide emission limit may be demonstrated 
by using the CEMS specified in Sec.  60.2730(l) to measure sulfur 
dioxide. The sulfur dioxide CEMS must follow the procedures and methods 
specified in paragraph (s) of this section. For sources that have 
actual inlet emissions less than 100 parts per million dry volume, the 
relative accuracy criterion for inlet sulfur dioxide CEMS should be no 
greater than 20 percent of the mean value of the reference method test 
data in terms of the units of the emission standard, or 5 parts per 
million dry volume absolute value of the mean difference between the 
reference method and the CEMS, whichever is greater:
    (1) During each relative accuracy test run of the CEMS required by 
performance specification 2 in appendix B of this part, collect sulfur 
dioxide and oxygen (or carbon dioxide) data concurrently (or within a 
30- to 60-minute period) with both the CEMS and the test methods 
specified in paragraphs (s)(1)(i) and (ii) of this section:
    (i) For sulfur dioxide, EPA Reference Method 6 or 6C, or as an 
alternative ANSI/ASME PTC 19.10-1981 (incorporated by reference, see 
Sec.  60.17) must be used; and
    (ii) For oxygen (or carbon dioxide), EPA Reference Method 3A or 3B, 
or as an alternative ANSI/ASME PTC 19.10-1981 (incorporated by 
reference, see Sec.  60.17), as applicable, must be used.
    (2) The span value of the CEMS at the inlet to the sulfur dioxide 
control device must be 125 percent of the maximum estimated hourly 
potential sulfur dioxide emissions of the unit subject to this subpart. 
The span value of the CEMS at the outlet of the sulfur dioxide control 
device must be 50 percent of the maximum estimated hourly potential 
sulfur dioxide emissions of the unit subject to this subpart.
    (3) Conduct accuracy determinations quarterly and calibration drift 
tests daily in accordance with procedure 1 in appendix F of this part.
    (t) For facilities using a CEMS to demonstrate initial and 
continuous compliance with the nitrogen oxides emission limit, 
compliance with the nitrogen oxides emission limit may be demonstrated 
by using the CEMS specified in Sec.  60.2730 to measure nitrogen 
oxides. The nitrogen oxides CEMS must follow the procedures and methods 
specified in paragraphs (t)(1) through (4) of this section:
    (1) During each relative accuracy test run of the CEMS required by 
performance specification 2 of appendix B of this part, collect 
nitrogen oxides and oxygen (or carbon dioxide) data concurrently (or 
within a 30- to 60-minute period) with both the CEMS and the test 
methods specified in paragraphs (t)(1)(i) and (ii) of this section:
    (i) For nitrogen oxides, EPA Reference Method 7 or 7E at 40 CFR 
part 60, appendix A-4 must be used; and
    (ii) For oxygen (or carbon dioxide), EPA Reference Method 3A or 3B, 
or as an alternative ANSI/ASME PTC 19.10-1981 (incorporated by 
reference, see Sec.  60.17), as applicable, must be used.
    (2) The span value of the CEMS must be 125 percent of the maximum 
estimated hourly potential nitrogen oxide emissions of unit.
    (3) Conduct accuracy determinations quarterly and calibration drift 
tests daily in accordance with procedure 1 in appendix F of this part.
    (4) The owner or operator of an affected facility may request that 
compliance with the nitrogen oxides emission limit be determined using 
carbon dioxide measurements corrected to an equivalent of 7 percent 
oxygen. If carbon dioxide is selected for use in diluent corrections, 
the relationship between oxygen and carbon dioxide levels must be 
established during the initial performance test according to the 
procedures and methods specified in paragraphs (t)(4)(i) through (iv) 
of this section. This relationship may be reestablished during 
performance compliance tests:
    (i) The fuel factor equation in Method 3B must be used to determine 
the relationship between oxygen and carbon dioxide at a sampling 
location. Method 3A, 3B, or as an alternative ANSI/ASME PTC 19.10-1981 
(incorporated by reference, see Sec.  60.17), as applicable, must be 
used to determine the oxygen concentration at the same location as the 
carbon dioxide monitor;
    (ii) Samples must be taken for at least 30 minutes in each hour;
    (iii) Each sample must represent a 1-hour average; and
    (iv) A minimum of 3 runs must be performed.
    (u) For facilities using a CEMS or an integrated sorbent trap 
monitoring system for mercury to demonstrate initial and continuous 
compliance with any of the emission limits of this subpart, you must 
complete the following:
    (1) Demonstrate compliance with the appropriate emission limit(s) 
using a 30-day rolling average of 1-hour arithmetic average emission 
concentrations, including CEMS or an integrated

[[Page 15898]]

sorbent trap monitoring system data during startup and shutdown, as 
defined in this subpart, calculated using equation 19-19 in section 
12.4.1 of EPA Reference Method 19 at appendix A-7 of this part. The 1-
hour arithmetic averages for CEMS must be calculated using the data 
points required under Sec.  60.13(e)(2). Except for CEMS or an 
integrated sorbent trap monitoring system data during startup and 
shutdown, the 1-hour arithmetic averages used to calculate the 30-day 
rolling average emission concentrations must be corrected to 7 percent 
oxygen (dry basis). Integrated sorbent trap monitoring system or CEMS 
data during startup and shutdown, as defined in this subpart, are not 
corrected to 7 percent oxygen, and are measured at stack oxygen 
content; and
    (2) Operate all CEMS and integrated sorbent trap monitoring systems 
in accordance with the applicable procedures under appendices B and F 
of this part.
    (v) Use of the bypass stack at any time is an emissions standards 
deviation for PM, HCl, lead, cadmium, mercury, nitrogen oxides, sulfur 
dioxide, and dioxin/furans.
    (w) For energy recovery units with a design heat input capacity of 
100 MMBtu/hr or greater that do not use a carbon monoxide CEMS, you 
must install, operate, and maintain an oxygen analyzer system as 
defined in Sec.  60.2875 according to the procedures in paragraphs 
(w)(1) through (4) of this section:
    (1) The oxygen analyzer system must be installed by the initial 
performance test date specified in Sec.  60.2675;
    (2) You must operate the oxygen trim system within compliance with 
paragraph (w)(3) of this section at all times;
    (3) You must maintain the oxygen level such that the 30-day rolling 
average that is established as the operating limit for oxygen is not 
below the lowest hourly average oxygen concentration measured during 
the most recent CO performance test; and
    (4) You must calculate and record a 30-day rolling average oxygen 
concentration using equation 19-19 in section 12.4.1 of EPA Reference 
Method 19 of Appendix A-7 of this part.
    (x) For energy recovery units with annual average heat input rates 
greater than or equal to 250 MMBtu/hr and waste-burning kilns, you must 
install, calibrate, maintain, and operate a PM CPMS and record the 
output of the system as specified in paragraphs (x)(1) through (8) of 
this section. For other energy recovery units, you may elect to use PM 
CPMS operated in accordance with this section. PM CPMS are suitable in 
lieu of using other CMS for monitoring PM compliance (e.g., bag leak 
detectors, ESP secondary power, PM scrubber pressure):
    (1) Install, calibrate, operate, and maintain your PM CPMS 
according to the procedures in your approved site-specific monitoring 
plan developed in accordance with paragraphs (l) and (x)(1)(i) through 
(iii) of this section:
    (i) The operating principle of the PM CPMS must be based on in-
stack or extractive light scatter, light scintillation, beta 
attenuation, or mass accumulation of the exhaust gas or representative 
sample. The reportable measurement output from the PM CPMS must be 
expressed as milliamps or the digital signal equivalent;
    (ii) The PM CPMS must have a cycle time (i.e., period required to 
complete sampling, measurement, and reporting for each measurement) no 
longer than 60 minutes; and
    (iii) The PM CPMS must be capable of detecting and responding to 
particulate matter concentrations increments no greater than 0.5 mg/
actual cubic meter.
    (2) During the initial performance test or any such subsequent 
performance test that demonstrates compliance with the PM limit, you 
must adjust the site-specific operating limit in accordance with the 
results of the performance test according to the procedures specified 
in Sec.  60.2675.
    (3) Collect PM CPMS hourly average output data for all energy 
recovery unit or waste-burning kiln operating hours. Express the PM 
CPMS output as milliamps or the digital signal equivalent.
    (4) Calculate the arithmetic 30-day rolling average of all of the 
hourly average PM CPMS output collected during all energy recovery unit 
or waste-burning kiln operating hours data (milliamps or their digital 
equivalent).
    (5) You must collect data using the PM CPMS at all times the energy 
recovery unit or waste-burning kiln is operating and at the intervals 
specified in paragraph (x)(1)(ii) of this section, except for periods 
of monitoring system malfunctions, repairs associated with monitoring 
system malfunctions, required monitoring system quality assurance or 
quality control activities (including, as applicable, calibration 
checks and required zero and span adjustments), and any scheduled 
maintenance as defined in your site-specific monitoring plan.
    (6) You must use all the data collected during all energy recovery 
unit or waste-burning kiln operating hours in assessing the compliance 
with your operating limit except:
    (i) Any data collected during monitoring system malfunctions, 
repairs associated with monitoring system malfunctions, or required 
monitoring system quality assurance or quality control activities 
conducted during monitoring system malfunctions are not used in 
calculations (report any such periods in your annual deviation report);
    (ii) Any data collected during periods when the monitoring system 
is out of control as specified in your site-specific monitoring plan, 
repairs associated with periods when the monitoring system is out of 
control, or required monitoring system quality assurance or quality 
control activities conducted during out-of-control periods are not used 
in calculations (report emissions or operating levels and report any 
such periods in your annual deviation report);
    (iii) Any PM CPMS data recorded during periods of CEMS data during 
startup and shutdown, as defined in this subpart.
    (7) You must record and make available upon request results of PM 
CPMS system performance audits, as well as the dates and duration of 
periods from when the PM CPMS is out of control until completion of the 
corrective actions necessary to return the PM CPMS to operation 
consistent with your site-specific monitoring plan.
    (8) For any deviation of the 30-day rolling average PM CPMS average 
value from the established operating parameter limit, you must:
    (i) Within 48 hours of the deviation, visually inspect the air 
pollution control device;
    (ii) If inspection of the air pollution control device identifies 
the cause of the deviation, take corrective action as soon as possible 
and return the PM CPMS measurement to within the established value;
    (iii) Within 30 days of the deviation or at the time of the annual 
compliance test, whichever comes first, conduct a PM emissions 
compliance test to determine compliance with the PM emissions limit. 
Within 45 days of the deviation, you must re-establish the CPMS 
operating limit. You are not required to conduct additional testing for 
any deviations that occur between the time of the original deviation 
and the PM emissions compliance test required under paragraph (x) of 
this section; and
    (iv) PM CPMS deviations leading to more than four required 
performance tests in a 12-month process operating period (rolling 
monthly) constitute a violation of this subpart.

[[Page 15899]]

    (y) When there is an alkali bypass and/or an in-line coal mill that 
exhaust emissions through a separate stack(s), the combined emissions 
are subject to the emission limits applicable to waste-burning kilns. 
To determine the kiln-specific emission limit for demonstrating 
compliance, you must:
    (1) Calculate a kiln-specific emission limit using equation 7:
    [GRAPHIC] [TIFF OMITTED] TR16AP19.019
    

Where:

Cks = Kiln stack concentration (ppmvd, mg/dscm, ng/dscm, 
depending on pollutant. Each corrected to 7% O2.)
Qab = Alkali bypass flow rate (volume/hr)
Cab = Alkali bypass concentration (ppmvd, mg/dscm, ng/
dscm, depending on pollutant. Each corrected to 7% O2.)
Qcm = In-line coal mill flow rate (volume/hr)
Ccm = In-line coal mill concentration (ppmvd, mg/dscm, 
ng/dscm, depending on pollutant. Each corrected to 7% 
O2.)
Qks = Kiln stack flow rate (volume/hr)

    (2) Particulate matter concentration must be measured downstream of 
the in-line coal mill. All other pollutant concentrations must be 
measured either upstream or downstream of the in-line coal mill.
    (3) For purposes of determining the combined emissions from kilns 
equipped with an alkali bypass or that exhaust kiln gases to a coal 
mill that exhausts through a separate stack, instead of installing a 
CEMS or PM CPMS on the alkali bypass stack or in-line coal mill stack, 
the results of the initial and subsequent performance test can be used 
to demonstrate compliance with the relevant emissions limit. A 
performance test must be conducted on an annual basis (between 11 and 
13 calendar months following the previous performance test).


Sec.  60.2715   By what date must I conduct the annual performance 
test?

    You must conduct annual performance tests between 11 and 13 
calendar months of the previous performance test.


Sec.  60.2716   By what date must I conduct the annual air pollution 
control device inspection?

    On an annual basis (no more than 12 months following the previous 
annual air pollution control device inspection), you must complete the 
air pollution control device inspection as described in Sec.  60.2706.


Sec.  60.2720   May I conduct performance testing less often?

    (a) You must conduct annual performance tests according to the 
schedule specified in Sec.  60.2715, with the following exceptions:
    (1) You may conduct a repeat performance test at any time to 
establish new values for the operating limits, as specified in Sec.  
60.2725. New operating limits become effective on the date that the 
performance test report is submitted to the EPA's Central Data Exchange 
or postmarked, per the requirements of Sec.  60.2795(b). The 
Administrator may request a repeat performance test at any time;
    (2) You must repeat the performance test within 60 days of a 
process change, as defined in Sec.  60.2875; and
    (3) You can conduct performance tests less often if you meet the 
following conditions: Your performance tests for the pollutant for at 
least 2 consecutive performance tests demonstrates that the emission 
level for the pollutant is no greater than the emission level specified 
in paragraph (a)(3)(i) or (ii) of this section, as applicable; there 
are no changes in the operation of the affected source or air pollution 
control equipment that could increase emissions; and you are not 
required to conduct a performance test for the pollutant in response to 
a request by the Administrator in paragraph (a)(1) of this section or a 
process change in paragraph (a)(2) of this section. In this case, you 
do not have to conduct a performance test for that pollutant for the 
next 2 years. You must conduct a performance test for the pollutant no 
more than 37 months following the previous performance test for the 
pollutant. If the emission level for your CISWI continues to meet the 
emission level specified in paragraph (a)(3)(i) or (ii) of this 
section, as applicable, you may choose to conduct performance tests for 
the pollutant every third year, as long as there are no changes in the 
operation of the affected source or air pollution control equipment 
that could increase emissions. Each such performance test must be 
conducted no more than 37 months after the previous performance test.
    (i) For particulate matter, hydrogen chloride, mercury, carbon 
monoxide, nitrogen oxides, sulfur dioxide, cadmium, lead, and dioxins/
furans, the emission level equal to 75 percent of the applicable 
emission limit in table 2 or tables 6 through 9 of this subpart, as 
applicable; and
    (ii) For fugitive emissions, visible emissions (of combustion ash 
from the ash conveying system) for 2 percent of the time during each of 
the three 1-hour observation periods.
    (4) If you are conducting less frequent testing for a pollutant as 
provided in paragraph (a)(3) of this section and a subsequent 
performance test for the pollutant indicates that your CISWI does not 
meet the emission level specified in paragraph (a)(3)(i) or (a)(3)(ii) 
of this section, as applicable, you must conduct annual performance 
tests for the pollutant according to the schedule specified in 
paragraph (a) of this section until you qualify for less frequent 
testing for the pollutant as specified in paragraph (a)(3) of this 
section.
    (b) [Reserved]


Sec.  60.2725   May I conduct a repeat performance test to establish 
new operating limits?

    (a) Yes. You may conduct a repeat performance test at any time to 
establish new values for the operating limits. The Administrator may 
request a repeat performance test at any time.
    (b) You must repeat the performance test if your feed stream is 
different than the feed streams used during any performance test used 
to demonstrate compliance.

Model Rule--Monitoring


Sec.  60.2730   What monitoring equipment must I install and what 
parameters must I monitor?

    (a) If you are using a wet scrubber to comply with the emission 
limitation under Sec.  60.2670, you must install, calibrate (to 
manufacturers' specifications), maintain, and operate devices (or 
establish methods) for monitoring the value of the operating parameters 
used to determine compliance with the operating limits listed in table 
3 of this subpart. These devices (or methods) must measure and record 
the values for these operating parameters at the frequencies indicated 
in table 3 of this subpart at all times except as specified in Sec.  
60.2735(a).
    (b) If you use a fabric filter to comply with the requirements of 
this subpart and you do not use a PM CPMS or PM CEMS for monitoring PM 
compliance,

[[Page 15900]]

you must install, calibrate, maintain, and continuously operate a bag 
leak detection system as specified in paragraphs (b)(1) through (8) of 
this section:
    (1) You must install and operate a bag leak detection system for 
each exhaust stack of the fabric filter;
    (2) Each bag leak detection system must be installed, operated, 
calibrated, and maintained in a manner consistent with the 
manufacturer's written specifications and recommendations;
    (3) The bag leak detection system must be certified by the 
manufacturer to be capable of detecting particulate matter emissions at 
concentrations of 10 milligrams per actual cubic meter or less;
    (4) The bag leak detection system sensor must provide output of 
relative or absolute particulate matter loadings;
    (5) The bag leak detection system must be equipped with a device to 
continuously record the output signal from the sensor;
    (6) The bag leak detection system must be equipped with an alarm 
system that will alert automatically an operator when an increase in 
relative particulate matter emission over a preset level is detected. 
The alarm must be located where it is observed easily by plant 
operating personnel;
    (7) For positive pressure fabric filter systems, a bag leak 
detection system must be installed in each baghouse compartment or 
cell. For negative pressure or induced air fabric filters, the bag leak 
detector must be installed downstream of the fabric filter; and
    (8) Where multiple detectors are required, the system's 
instrumentation and alarm may be shared among detectors.
    (c) If you are using something other than a wet scrubber, activated 
carbon, selective non-catalytic reduction, an electrostatic 
precipitator, or a dry scrubber to comply with the emission limitations 
under Sec.  60.2670, you must install, calibrate (to the manufacturers' 
specifications), maintain, and operate the equipment necessary to 
monitor compliance with the site-specific operating limits established 
using the procedures in Sec.  60.2680.
    (d) If you use activated carbon injection to comply with the 
emission limitations in this subpart, you must measure the minimum 
sorbent flow rate once per hour.
    (e) If you use selective noncatalytic reduction to comply with the 
emission limitations, you must complete the following:
    (1) Following the date on which the initial performance test is 
completed or is required to be completed under Sec.  60.2690, whichever 
date comes first, ensure that the affected facility does not operate 
above the maximum charge rate, or below the minimum secondary chamber 
temperature (if applicable to your CISWI) or the minimum reagent flow 
rate measured as 3-hour block averages at all times; and
    (2) Operation of the affected facility above the maximum charge 
rate, below the minimum secondary chamber temperature and below the 
minimum reagent flow rate simultaneously constitute a violation of the 
nitrogen oxides emissions limit.
    (f) If you use an electrostatic precipitator to comply with the 
emission limits of this subpart and you do not use a PM CPMS for 
monitoring PM compliance, you must monitor the secondary power to the 
electrostatic precipitator collection plates and maintain the 3-hour 
block averages at or above the operating limits established during the 
mercury or particulate matter performance test.
    (g) For waste-burning kilns not equipped with a wet scrubber or dry 
scrubber, you must install, calibrate, maintain, and operate a CEMS for 
monitoring hydrogen chloride emissions discharged to the atmosphere, as 
specified in Sec.  60.2710(j), and record the output of the system. You 
may substitute use of a HCl CEMS for conducting the HCl initial and 
annual testing with EPA Method 321 at 40 CFR part 63, appendix A. For 
units other than waste-burning kilns not equipped with a wet scrubber 
or dry scrubber, a facility may substitute use of a hydrogen chloride 
CEMS for conducting the hydrogen chloride initial and annual 
performance test. For units equipped with a hydrogen chloride CEMS, you 
are not required to monitor the minimum hydrogen chloride sorbent flow 
rate, monitoring the minimum scrubber liquor pH, and monitoring minimum 
injection rate.
    (h) To demonstrate continuous compliance with the particulate 
matter emissions limit, a facility may substitute use of either a 
particulate matter CEMS or a particulate matter CPMS for conducting the 
particulate matter annual performance test. For units equipped with a 
particulate matter CEMS, you are not required to use other CMS 
monitoring for PM compliance (e.g., bag leak detectors, ESP secondary 
power, PM scrubber pressure). A facility may also substitute use of a 
particulate matter CEMS for conducting the PM initial performance test.
    (i) To demonstrate initial and continuous compliance with the 
dioxin/furan emissions limit, a facility may substitute use of a 
continuous automated sampling system for the dioxin/furan initial and 
annual performance test. You must record the output of the system and 
analyze the sample according to EPA Method 23 at 40 CFR part 60, 
appendix A-7. This option to use a continuous automated sampling system 
takes effect on the date a final performance specification applicable 
to dioxin/furan from continuous monitors is published in the Federal 
Register. The owner or operator who elects to continuously sample 
dioxin/furan emissions instead of sampling and testing using EPA Method 
23 at 40 CFR part 60, appendix A-7 must install, calibrate, maintain 
and operate a continuous automated sampling system and must comply with 
the requirements specified in Sec.  60.58b(p) and (q). A facility may 
substitute continuous dioxin/furan monitoring for the minimum sorbent 
flow rate, if activated carbon sorbent injection is used solely for 
compliance with the dioxin/furan emission limit.
    (j) To demonstrate initial and continuous compliance with the 
mercury emissions limit, a facility may substitute use of a mercury 
CEMS or and integrated sorbent trap monitoring system for the mercury 
initial and annual performance test. The owner or operator who elects 
to continuously measure mercury emissions instead of sampling and 
testing using EPA Method 29 or 30B at 40 CFR part 60, appendix A-8, 
ASTM D6784-02 (Reapproved 2008) (incorporated by reference, see Sec.  
60.17), or an approved alternative method for measuring mercury 
emissions, must install, calibrate, maintain and operate the mercury 
CEMS or integrated sorbent trap monitoringsystem and must comply with 
performance specification 12A or performance specification 12B, 
respectively, and quality assurance procedure 5. For the purposes of 
emissions calculations when using an integrated sorbent trap monitoring 
system, the mercury concentration determined for each sampling period 
must be assigned to each hour during the sampling period. For units 
equipped with a mercury CEMS or an integrated sorbent trap monitoring 
system, you are not required to monitor the minimum sorbent flow rate, 
if activated carbon sorbent injection is used solely for compliance 
with the mercury emission limit. Waste-burning kilns must install, 
calibrate, maintain, and operate a mercury CEMS or an integrated 
sorbent trap monitoring system as specified in Sec.  60.2710(j).
    (k) To demonstrate initial and continuous compliance with the 
nitrogen oxides emissions limit, a

[[Page 15901]]

facility may substitute use of a CEMS for the nitrogen oxides initial 
and annual performance test to demonstrate compliance with the nitrogen 
oxides emissions limits. For units equipped with a nitrogen xides CEMS, 
you are not required to monitor the charge rate, secondary chamber 
temperature and reagent flow for selective noncatalytic reduction, if 
applicable:
    (1) Install, calibrate, maintain and operate a CEMS for measuring 
nitrogen oxides emissions discharged to the atmosphere and record the 
output of the system. The requirements under performance specification 
2 of appendix B of this part, the quality assurance procedure 1 of 
appendix F of this part and the procedures under Sec.  60.13 must be 
followed for installation, evaluation and operation of the CEMS; and
    (2) Compliance with the emission limit for nitrogen oxides must be 
determined based on the 30-day rolling average of the hourly emission 
concentrations using CEMS outlet data, as outlined in Sec.  60.2710(u).
    (l) To demonstrate initial and continuous compliance with the 
sulfur dioxide emissions limit, a facility may substitute use of a CEMS 
for the sulfur dioxide initial and annual performance test to 
demonstrate compliance with the sulfur dioxide emissions limits:
    (1) Install, calibrate, maintain and operate a CEMS for measuring 
sulfur dioxide emissions discharged to the atmosphere and record the 
output of the system. The requirements under performance specification 
2 of appendix B of this part, the quality assurance requirements of 
procedure 1 of appendix F of this part and the procedures under Sec.  
60.13 must be followed for installation, evaluation and operation of 
the CEMS; and
    (2) Compliance with the sulfur dioxide emission limit shall be 
determined based on the 30-day rolling average of the hourly arithmetic 
average emission concentrations using CEMS outlet data, as outlined in 
Sec.  60.2710(u).
    (m) For energy recovery units over 10 MMBtu/hr but less than 250 
MMBtu/hr annual average heat input rates that do not use a wet 
scrubber, fabric filter with bag leak detection system, an 
electrostatic precipitator, particulate matter CEMS, or particulate 
matter CPMS, you must install, operate, certify and maintain a 
continuous opacity monitoring system according to the procedures in 
paragraphs (m)(1) through (5) of this section by the compliance date 
specified in Sec.  60.2670. Energy recovery units that use a 
particulate matter CEMS to demonstrate initial and continuing 
compliance according to the procedures in Sec.  60.2730(n) are not 
required to install a continuous opacity monitoring system and must 
perform the annual performance tests for opacity consistent with Sec.  
60.2710(f):
    (1) Install, operate and maintain each continuous opacity 
monitoring system according to performance specification 1 at 40 CFR 
part 60, appendix B;
    (2) Conduct a performance evaluation of each continuous opacity 
monitoring system according to the requirements in Sec.  60.13 and 
according to performance specification 1 at 40 CFR part 60, appendix B;
    (3) As specified in Sec.  60.13(e)(1), each continuous opacity 
monitoring system must complete a minimum of one cycle of sampling and 
analyzing for each successive 10-second period and one cycle of data 
recording for each successive 6-minute period;
    (4) Reduce the continuous opacity monitoring system data as 
specified in Sec.  60.13(h)(1); and
    (5) Determine and record all the 6-minute averages (and 1-hour 
block averages as applicable) collected.
    (n) For coal and liquid/gas energy recovery units, incinerators, 
and small remote incinerators, an owner or operator may elect to 
install, calibrate, maintain and operate a CEMS for monitoring 
particulate matter emissions discharged to the atmosphere and record 
the output of the system. The owner or operator of an affected facility 
who continuously monitors particulate matter emissions instead of 
conducting performance testing using EPA Method 5 at 40 CFR part 60, 
appendix A-3 or monitoring with a particulate matter CPMS according to 
paragraph (r) of this section, must install, calibrate, maintain and 
operate a PM CEMS and must comply with the requirements specified in 
paragraphs (n)(1) through (10) of this section:
    (1) The PM CEMS must be installed, evaluated and operated in 
accordance with the requirements of performance specification 11 of 
appendix B of this part and quality assurance requirements of procedure 
2 of appendix F of this part and Sec.  60.13;
    (2) The initial performance evaluation must be completed no later 
than 180 days after the final compliance date for meeting the amended 
emission limitations, as specified under Sec.  60.2690 or within 180 
days of notification to the Administrator of use of the continuous 
monitoring system if the owner or operator was previously determining 
compliance by Method 5 at 40 CFR part 60, appendix A-3 performance 
tests, whichever is later;
    (3) The owner or operator of an affected facility may request that 
compliance with the particulate matter emission limit be determined 
using carbon dioxide measurements corrected to an equivalent of 7 
percent oxygen. The relationship between oxygen and carbon dioxide 
levels for the affected facility must be established according to the 
procedures and methods specified in Sec.  60.2710(t)(4)(i) through 
(iv);
    (4) The owner or operator of an affected facility must conduct an 
initial performance test for particulate matter emissions. If PM CEMS 
are elected for demonstrating compliance, and the initial performance 
test has not yet been conducted, then initial compliance must be 
determined by using the CEMS specified in paragraph (n) of this section 
to measure particulate matter. You must calculate a 30-day rolling 
average of 1-hour arithmetic average emission concentrations, including 
CEMS data during startup and shutdown, as defined in this subpart, 
using equation 19-19 in section 12.4.1 of EPA Reference Method 19 at 40 
CFR part 60, appendix A-7 of this part;
    (5) Continuous compliance with the particulate matter emission 
limit must be determined based on the 30-day rolling average calculated 
using equation 19-19 in section 12.4.1 of EPA Reference Method 19 at 40 
CFR part 60, Appendix A-7 of the part from the 1-hour arithmetic 
average of the CEMS outlet data.
    (6) At a minimum, valid continuous monitoring system hourly 
averages must be obtained as specified Sec.  60.2735;
    (7) The 1-hour arithmetic averages required under paragraph (n)(5) 
of this section must be expressed in milligrams per dry standard cubic 
meter corrected to 7 percent oxygen (or carbon dioxide)(dry basis) and 
must be used to calculate the 30-day rolling average emission 
concentrations. CEMS data during startup and shutdown, as defined in 
this subpart, are not corrected to 7 percent oxygen, and are measured 
at stack oxygen content. The 1-hour arithmetic averages must be 
calculated using the data points required under Sec.  60.13(e)(2);
    (8) All valid CEMS data must be used in calculating average 
emission concentrations even if the minimum CEMS data requirements of 
paragraph (n)(6) of this section are not met;
    (9) The CEMS must be operated according to performance 
specification 11 in appendix B of this part; and,
    (10) Quarterly and yearly accuracy audits and daily drift, system 
optics, and sample volume checks must be performed in accordance with 
procedure 2 in appendix F of this part.
    (o) To demonstrate initial and continuous compliance with the 
carbon monoxide emissions limit, a facility

[[Page 15902]]

may substitute use of a CEMS for the carbon monoxide initial and annual 
performance test to demonstrate compliance with the carbon monoxide 
emissions limits:
    (1) Install, calibrate, maintain, and operate a CEMS for measuring 
carbon monoxide emissions discharged to the atmosphere and record the 
output of the system. The requirements under performance specification 
4A or 4B of appendix B of this part, the quality assurance procedure 1 
of appendix F of this part and the procedures under Sec.  60.13 must be 
followed for installation, evaluation, and operation of the CEMS; and
    (2) Compliance with the carbon monoxide emission limit shall be 
determined based on the 30-day rolling average of the hourly arithmetic 
average emission concentrations, including CEMS data during startup and 
shutdown as defined in this subpart, using CEMS outlet data, as 
outlined in Sec.  60.2710(u).
    (p) The owner/operator of an affected source with a bypass stack 
shall install, calibrate (to manufacturers' specifications), maintain 
and operate a device or method for measuring the use of the bypass 
stack including date, time and duration.
    (q) For energy recovery units with a heat input capacity of 100 
MMBtu/hr or greater that do not use a carbon monoxide CEMS, you must 
install, operate and maintain the continuous oxygen monitoring system 
as defined in Sec.  60.2875 according to the procedures in paragraphs 
(q)(1) through (4) of this section:
    (1) The oxygen analyzer system must be installed by the initial 
performance test date specified in Sec.  60.2675;
    (2) You must operate the oxygen trim system within compliance with 
paragraph (q)(3) of this section at all times;
    (3) You must maintain the oxygen level such that the 30-day rolling 
average that is established as the operating limit for oxygen according 
to paragraph (q)(4) of this section is not below the lowest hourly 
average oxygen concentration measured during the most recent CO 
performance test; and
    (4) You must calculate and record a 30-day rolling average oxygen 
concentration using equation 19-19 in section 12.4.1 of EPA Reference 
Method 19 of Appendix A-7 of this part.
    (r) For energy recovery units with annual average heat input rates 
greater than or equal to 250 MMBtu/hr and waste-burning kilns, you must 
install, calibrate, maintain, and operate a PM CPMS and record the 
output of the system as specified in paragraphs (r)(1) through (8) of 
this section. For other energy recovery units, you may elect to use PM 
CPMS operated in accordance with this section. PM CPMS are suitable in 
lieu of using other CMS for monitoring PM compliance (e.g., bag leak 
detectors, ESP secondary power, PM scrubber pressure):
    (1) Install, calibrate, operate, and maintain your PM CPMS 
according to the procedures in your approved site-specific monitoring 
plan developed in accordance with Sec.  60.2710(l) and (r)(1)(i) 
through (iii) of this section:
    (i) The operating principle of the PM CPMS must be based on in-
stack or extractive light scatter, light scintillation, beta 
attenuation, or mass accumulation of the exhaust gas or representative 
sample. The reportable measurement output from the PM CPMS must be 
expressed as milliamps or the digital signal equivalent;
    (ii) The PM CPMS must have a cycle time (i.e., period required to 
complete sampling, measurement, and reporting for each measurement) no 
longer than 60 minutes; and
    (iii) The PM CPMS must be capable of detecting and responding to 
particulate matter concentrations increments no greater than 0.5 mg/
actual cubic meter.
    (2) During the initial performance test or any such subsequent 
performance test that demonstrates compliance with the PM limit, you 
must adjust the site-specific operating limit in accordance with the 
results of the performance test according to the procedures specified 
in Sec.  60.2675.
    (3) Collect PM CPMS hourly average output data for all energy 
recovery unit or waste-burning kiln operating hours. Express the PM 
CPMS output as milliamps or the digital signal equivalent.
    (4) Calculate the arithmetic 30-day rolling average of all of the 
hourly average PM CPMS output collected during all energy recovery unit 
or waste-burning kiln operating hours data (milliamps or digital bits).
    (5) You must collect data using the PM CPMS at all times the energy 
recovery unit or waste-burning kiln is operating and at the intervals 
specified in paragraph (r)(1)(ii) of this section, except for periods 
of monitoring system malfunctions, repairs associated with monitoring 
system malfunctions, required monitoring system quality assurance or 
quality control activities (including, as applicable, calibration 
checks and required zero and span adjustments), and any scheduled 
maintenance as defined in your site-specific monitoring plan.
    (6) You must use all the data collected during all energy recovery 
unit or waste-burning kiln operating hours in assessing the compliance 
with your operating limit except:
    (i) Any data collected during monitoring system malfunctions, 
repairs associated with monitoring system malfunctions, or required 
monitoring system quality assurance or quality control activities 
conducted during monitoring system malfunctions are not used in 
calculations (report any such periods in your annual deviation report);
    (ii) Any data collected during periods when the monitoring system 
is out of control as specified in your site-specific monitoring plan, 
repairs associated with periods when the monitoring system is out of 
control, or required monitoring system quality assurance or quality 
control activities conducted during out-of-control periods are not used 
in calculations (report emissions or operating levels and report any 
such periods in your annual deviation report); and
    (iii) Any PM CPMS data recorded during periods of CEMS data during 
startup and shutdown, as defined in this subpart.
    (7) You must record and make available upon request results of PM 
CPMS system performance audits, as well as the dates and duration of 
periods from when the PM CPMS is out of control until completion of the 
corrective actions necessary to return the PM CPMS to operation 
consistent with your site-specific monitoring plan.
    (8) For any deviation of the 30-day rolling average PM CPMS average 
value from the established operating parameter limit, you must:
    (i) Within 48 hours of the deviation, visually inspect the air 
pollution control device;
    (ii) If inspection of the air pollution control device identifies 
the cause of the deviation, take corrective action as soon as possible 
and return the PM CPMS measurement to within the established value;
    (iii) Within 30 days of the deviation or at the time of the annual 
compliance test, whichever comes first, conduct a PM emissions 
compliance test to determine compliance with the PM emissions limit and 
to verify the operation of the emissions control device(s). Within 45 
days of the deviation, you must re-establish the CPMS operating limit. 
You are not required to conduct additional testing for any deviations 
that occur between the time of the original deviation and the PM 
emissions compliance test required under this paragraph; and
    (iv) PM CPMS deviations leading to more than four required 
performance

[[Page 15903]]

tests in a 12-month process operating period (rolling monthly) 
constitute a violation of this subpart.
    (s) If you use a dry scrubber to comply with the emission limits of 
this subpart, you must monitor the injection rate of each sorbent and 
maintain the 3-hour block averages at or above the operating limits 
established during the hydrogen chloride performance test.
    (t) If you are required to monitor clinker production because you 
comply with the production-rate based mercury limit for your waste-
burning kiln, you must:
    (1) Determine hourly clinker production by one of two methods:
    (i) Install, calibrate, maintain, and operate a permanent weigh 
scale system to measure and record weight rates in tons-mass per hour 
of the amount of clinker produced. The system of measuring hourly 
clinker production must be maintained within 5 percent 
accuracy, or
    (ii) Install, calibrate, maintain, and operate a permanent weigh 
scale system to measure and record weight rates in tons-mass per hour 
of the amount of feed to the kiln. The system of measuring feed must be 
maintained within 5 percent accuracy. Calculate your hourly 
clinker production rate using a kiln-specific feed to clinker ratio 
based on reconciled clinker production determined for accounting 
purposes and recorded feed rates. Update this ratio monthly. Note that 
if this ratio changes at clinker reconciliation, you must use the new 
ratio going forward, but you do not have to retroactively change 
clinker production rates previously estimated.
    (2) Determine the accuracy of the system of measuring hourly 
clinker production (or feed mass flow if applicable) before the final 
compliance date of this rule and during each quarter of source 
operation.
    (3) Conduct accuracy checks in accordance with the procedures 
outlined in your site-specific monitoring plan under Sec.  60.2710(l).


Sec.  60.2735   Is there a minimum amount of monitoring data I must 
obtain?

    For each continuous monitoring system required or optionally 
allowed under Sec.  60.2730, you must monitor and collect data 
according to this section:
    (a) You must operate the monitoring system and collect data at all 
required intervals at all times compliance is required except for 
periods of monitoring system malfunctions or out-of-control periods, 
repairs associated with monitoring system malfunctions or out-of-
control periods (as specified in Sec.  60.2770(o)), and required 
monitoring system quality assurance or quality control activities 
including, as applicable, calibration checks and required zero and span 
adjustments. A monitoring system malfunction is any sudden, infrequent, 
not reasonably preventable failure of the monitoring system to provide 
valid data. Monitoring system failures that are caused in part by poor 
maintenance or careless operation are not malfunctions. You are 
required to effect monitoring system repairs in response to monitoring 
system malfunctions or out-of-control periods and to return the 
monitoring system to operation as expeditiously as practicable.
    (b) You may not use data recorded during the monitoring system 
malfunctions, repairs associated with monitoring system malfunctions or 
out-of control periods, or required monitoring system quality assurance 
or control activities in calculations used to report emissions or 
operating levels. You must use all the data collected during all other 
periods, including data normalized for above scale readings, in 
assessing the operation of the control device and associated control 
system.
    (c) Except for periods of monitoring system malfunctions or out-of-
control periods, repairs associated with monitoring system malfunctions 
or out-of-control periods, and required monitoring system quality 
assurance or quality control activities including, as applicable, 
calibration checks and required zero and span adjustments, failure to 
collect required data is a deviation of the monitoring requirements.

Model Rule--Recordkeeping and Reporting


Sec.  60.2740   What records must I keep?

    You must maintain the items (as applicable) as specified in 
paragraphs (a), (b), and (e) through (w) of this section for a period 
of at least 5 years:
    (a) Calendar date of each record;
    (b) Records of the data described in paragraphs (b)(1) through (7) 
of this section:
    (1) The CISWI charge dates, times, weights, and hourly charge 
rates;
    (2) Liquor flow rate to the wet scrubber inlet every 15 minutes of 
operation, as applicable;
    (3) Pressure drop across the wet scrubber system every 15 minutes 
of operation or amperage to the wet scrubber every 15 minutes of 
operation, as applicable;
    (4) Liquor pH as introduced to the wet scrubber every 15 minutes of 
operation, as applicable;
    (5) For affected CISWIs that establish operating limits for 
controls other than wet scrubbers under Sec.  60.2675(d) through (g) or 
Sec.  60.2680, you must maintain data collected for all operating 
parameters used to determine compliance with the operating limits. For 
energy recovery units using activated carbon injection or a dry 
scrubber, you must also maintain records of the load fraction and 
corresponding sorbent injection rate records; and
    (6) If a fabric filter is used to comply with the emission 
limitations, you must record the date, time, and duration of each alarm 
and the time corrective action was initiated and completed, and a brief 
description of the cause of the alarm and the corrective action taken. 
You must also record the percent of operating time during each 6-month 
period that the alarm sounds, calculated as specified in Sec.  
60.2675(c).
    (7) If you monitor clinker production in accordance with Sec.  
60.2730(t):
    (i) Hourly clinker rate produced if clinker production is measured 
directly;
    (ii) Hourly measured kiln feed rates and calculated clinker 
production rates if clinker production is not measured directly;
    (iii) 30-day rolling averages for mercury in pounds per million 
tons of clinker produced;
    (iv) The initial and quarterly accuracy of the system of measruing 
hourly clinker production (or feed mass flow).
    (c)-(d) [Reserved]
    (e) Identification of calendar dates and times for which data show 
a deviation from the operating limits in table 3 of this subpart or a 
deviation from other operating limits established under Sec.  
60.2675(d) through (g) or Sec.  60.2680 with a description of the 
deviations, reasons for such deviations, and a description of 
corrective actions taken.
    (f) The results of the initial, annual, and any subsequent 
performance tests conducted to determine compliance with the emission 
limits and/or to establish operating limits, as applicable. Retain a 
copy of the complete test report including calculations.
    (g) Records showing the names of CISWI operators who have completed 
review of the information in Sec.  60.2660(a) as required by Sec.  
60.2660(b), including the date of the initial review and all subsequent 
annual reviews.
    (h) Records showing the names of the CISWI operators who have 
completed the operator training requirements under Sec.  60.2635, met 
the criteria for qualification under Sec.  60.2645, and maintained or 
renewed their qualification under Sec.  60.2650 or Sec.  60.2655. 
Records must include documentation of training, the dates of

[[Page 15904]]

the initial and refresher training, and the dates of their 
qualification and all subsequent renewals of such qualifications.
    (i) For each qualified operator, the phone and/or pager number at 
which they can be reached during operating hours.
    (j) Records of calibration of any monitoring devices as required 
under Sec.  60.2730.
    (k) Equipment vendor specifications and related operation and 
maintenance requirements for the incinerator, emission controls, and 
monitoring equipment.
    (l) The information listed in Sec.  60.2660(a).
    (m) On a daily basis, keep a log of the quantity of waste burned 
and the types of waste burned (always required).
    (n) Maintain records of the annual air pollution control device 
inspections that are required for each CISWI subject to the emissions 
limits in table 2 of this subpart or tables 6 through 9 of this 
subpart, any required maintenance and any repairs not completed within 
10 days of an inspection or the timeframe established by the state 
regulatory agency.
    (o) For continuously monitored pollutants or parameters, you must 
document and keep a record of the following parameters measured using 
continuous monitoring systems. If you monitor emissions with a CEMS, 
you must indicate which data are CEMS data during startup and shutdown:
    (1) All 6-minute average levels of opacity;
    (2) All 1-hour average concentrations of sulfur dioxide emissions;
    (3) All 1-hour average concentrations of nitrogen oxides emissions;
    (4) All 1-hour average concentrations of carbon monoxide emissions;
    (5) All 1-hour average concentrations of particulate matter 
emissions;
    (6) All 1-hour average concentrations of mercury emissions;
    (7) All 1-hour average concentrations of HCl CEMS outputs;
    (8) All 1-hour average percent oxygen concentrations; and
    (9) All 1-hour average PM CPMS readings or particulate matter CEMS 
outputs.
    (p) Records indicating use of the bypass stack, including dates, 
times and durations.
    (q) If you choose to stack test less frequently than annually, 
consistent with Sec.  60.2720(a) through (c), you must keep annual 
records that document that your emissions in the previous stack test(s) 
were less than 75 percent of the applicable emission limit and document 
that there was no change in source operations including fuel 
composition and operation of air pollution control equipment that would 
cause emissions of the relevant pollutant to increase within the past 
year.
    (r) Records of the occurrence and duration of each malfunction of 
operation (i.e., process equipment) or the air pollution control and 
monitoring equipment.
    (s) Records of all required maintenance performed on the air 
pollution control and monitoring equipment.
    (t) Records of actions taken during periods of malfunction to 
minimize emissions in accordance with Sec.  60.11(d), including 
corrective actions to restore malfunctioning process and air pollution 
control and monitoring equipment to its normal or usual manner of 
operation.
    (u) For operating units that combust non-hazardous secondary 
materials that have been determined not to be solid waste pursuant to 
Sec.  241.3(b)(1) of this chapter, you must keep a record which 
documents how the secondary material meets each of the legitimacy 
criteria under Sec.  241.3(d)(1). If you combust a fuel that has been 
processed from a discarded non-hazardous secondary material pursuant to 
Sec.  241.3(b)(4), you must keep records as to how the operations that 
produced the fuel satisfies the definition of processing in Sec.  241.2 
and each of the legitimacy criteria in Sec.  241.3(d)(1) of this 
chapter. If the fuel received a non-waste determination pursuant to the 
petition process submitted under Sec.  241.3(c), you must keep a record 
that documents how the fuel satisfies the requirements of the petition 
process. For operating units that combust non-hazardous secondary 
materials as fuel per Sec.  241.4, you must keep records documenting 
that the material is a listed non-waste under Sec.  241.4(a).
    (v) Records of the criteria used to establish that the unit 
qualifies as a small power production facility under section 3(17)(C) 
of the Federal Power Act (16 U.S.C. 796(17)(C)) and that the waste 
material the unit is proposed to burn is homogeneous.
    (w) Records of the criteria used to establish that the unit 
qualifies as a cogeneration facility under section 3(18)(B) of the 
Federal Power Act (16 U.S.C. 796(18)(B)) and that the waste material 
the unit is proposed to burn is homogeneous.


Sec.  60.2745   Where and in what format must I keep my records?

    All records must be available onsite in either paper copy or 
computer-readable format that can be printed upon request, unless an 
alternative format is approved by the Administrator.


Sec.  60.2750   What reports must I submit?

    See table 5 of this subpart for a summary of the reporting 
requirements.


Sec.  60.2755   When must I submit my waste management plan?

    You must submit the waste management plan no later than the date 
specified in table 1 of this subpart for submittal of the final control 
plan.


Sec.  60.2760   What information must I submit following my initial 
performance test?

    You must submit the information specified in paragraphs (a) through 
(c) of this section no later than 60 days following the initial 
performance test. All reports must be signed by the facilities manager:
    (a) The complete test report for the initial performance test 
results obtained under Sec.  60.2700, as applicable;
    (b) The values for the site-specific operating limits established 
in Sec.  60.2675 or Sec.  60.2680; and
    (c) If you are using a fabric filter to comply with the emission 
limitations, documentation that a bag leak detection system has been 
installed and is being operated, calibrated, and maintained as required 
by Sec.  60.2730(b).


Sec.  60.2765   When must I submit my annual report?

    You must submit an annual report no later than 12 months following 
the submission of the information in Sec.  60.2760. You must submit 
subsequent reports no more than 12 months following the previous 
report. (If the unit is subject to permitting requirements under title 
V of the Clean Air Act, you may be required by the permit to submit 
these reports more frequently.)


Sec.  60.2770   What information must I include in my annual report?

    The annual report required under Sec.  60.2765 must include the 
items listed in paragraphs (a) through (p) of this section. If you have 
a deviation from the operating limits or the emission limitations, you 
must also submit deviation reports as specified in Sec. Sec.  60.2775, 
60.2780, and 60.2785:
    (a) Company name and address;
    (b) Statement by a responsible official, with that official's name, 
title, and signature, certifying the accuracy of the content of the 
report;
    (c) Date of report and beginning and ending dates of the reporting 
period;
    (d) The values for the operating limits established pursuant to 
Sec.  60.2675 or Sec.  60.2680;
    (e) If no deviation from any emission limitation or operating limit 
that applies

[[Page 15905]]

to you has been reported, a statement that there was no deviation from 
the emission limitations or operating limits during the reporting 
period;
    (f) The highest recorded 3-hour average and the lowest recorded 3-
hour average (30-day average for energy recovery units), as applicable, 
for each operating parameter recorded for the calendar year being 
reported;
    (g) Information recorded under Sec.  60.2740(b)(6) and (c) through 
(e) for the calendar year being reported;
    (h) For each performance test conducted during the reporting 
period, if any performance test is conducted, the process unit(s) 
tested, the pollutant(s) tested and the date that such performance test 
was conducted. Submit, following the procedure specified in Sec.  
60.2795(b)(1), the performance test report no later than the date that 
you submit the annual report;
    (i) If you met the requirements of Sec.  60.2720(a) or (b), and did 
not conduct a performance test during the reporting period, you must 
state that you met the requirements of Sec.  60.2720(a) or (b), and, 
therefore, you were not required to conduct a performance test during 
the reporting period;
    (j) Documentation of periods when all qualified CISWI operators 
were unavailable for more than 8 hours, but less than 2 weeks;
    (k) If you had a malfunction during the reporting period, the 
compliance report must include the number, duration, and a brief 
description for each type of malfunction that occurred during the 
reporting period and that caused or may have caused any applicable 
emission limitation to be exceeded. The report must also include a 
description of actions taken by an owner or operator during a 
malfunction of an affected source to minimize emissions in accordance 
with Sec.  60.11(d), including actions taken to correct a malfunction;
    (l) For each deviation from an emission or operating limitation 
that occurs for a CISWI for which you are not using a CMS to comply 
with the emission or operating limitations in this subpart, the annual 
report must contain the following information:
    (1) The total operating time of the CISWI at which the deviation 
occurred during the reporting period; and
    (2) Information on the number, duration, and cause of deviations 
(including unknown cause, if applicable), as applicable, and the 
corrective action taken.
    (m) If there were periods during which the continuous monitoring 
system, including the CEMS, was out of control as specified in 
paragraph (o) of this section, the annual report must contain the 
following information for each deviation from an emission or operating 
limitation occurring for a CISWI for which you are using a continuous 
monitoring system to comply with the emission and operating limitations 
in this subpart:
    (1) The date and time that each malfunction started and stopped;
    (2) The date, time, and duration that each CMS was inoperative, 
except for zero (low-level) and high-level checks;
    (3) The date, time, and duration that each continuous monitoring 
system was out-of-control, including start and end dates and hours and 
descriptions of corrective actions taken;
    (4) The date and time that each deviation started and stopped, and 
whether each deviation occurred during a period of malfunction or 
during another period;
    (5) A summary of the total duration of the deviation during the 
reporting period, and the total duration as a percent of the total 
source operating time during that reporting period;
    (6) A breakdown of the total duration of the deviations during the 
reporting period into those that are due to control equipment problems, 
process problems, other known causes, and other unknown causes;
    (7) A summary of the total duration of continuous monitoring system 
downtime during the reporting period, and the total duration of 
continuous monitoring system downtime as a percent of the total 
operating time of the CISWI at which the continuous monitoring system 
downtime occurred during that reporting period;
    (8) An identification of each parameter and pollutant that was 
monitored at the CISWI;
    (9) A brief description of the CISWI;
    (10) A brief description of the continuous monitoring system;
    (11) The date of the latest continuous monitoring system 
certification or audit; and
    (12) A description of any changes in continuous monitoring system, 
processes, or controls since the last reporting period.
    (n) If there were periods during which the continuous monitoring 
system, including the CEMS, was not out of control as specified in 
paragraph (o) of this section, a statement that there were not periods 
during which the continuous monitoring system was out of control during 
the reporting period.
    (o) A continuous monitoring system is out of control if any of the 
following occur:
    (1) The zero (low-level), mid-level (if applicable), or high-level 
calibration drift exceeds two times the applicable calibration drift 
specification in the applicable performance specification or in the 
relevant standard;
    (2) The continuous monitoring system fails a performance test audit 
(e.g., cylinder gas audit), relative accuracy audit, relative accuracy 
test audit, or linearity test audit; and
    (3) The continuous opacity monitoring system calibration drift 
exceeds two times the limit in the applicable performance specification 
in the relevant standard.
    (p) For energy recovery units, include the annual heat input and 
average annual heat input rate of all fuels being burned in the unit to 
verify which subcategory of energy recovery unit applies.


Sec.  60.2775   What else must I report if I have a deviation from the 
operating limits or the emission limitations?

    (a) You must submit a deviation report if any recorded 3-hour 
average (30-day average for energy recovery units or for PM CPMS) 
parameter level is above the maximum operating limit or below the 
minimum operating limit established under this subpart, if the bag leak 
detection system alarm sounds for more than 5 percent of the operating 
time for the 6-month reporting period, if a performance test was 
conducted that deviated from any emission limitation, if a 30-day 
average measured using a CEMS deviated from any emission limitation.
    (b) The deviation report must be submitted by August 1 of that year 
for data collected during the first half of the calendar year (January 
1 to June 30), and by February 1 of the following year for data you 
collected during the second half of the calendar year (July 1 to 
December 31).


Sec.  60.2780   What must I include in the deviation report?

    In each report required under Sec.  60.2775, for any pollutant or 
parameter that deviated from the emission limitations or operating 
limits specified in this subpart, include the four items described in 
paragraphs (a) through (d) of this section:
    (a) The calendar dates and times your unit deviated from the 
emission limitations or operating limit requirements;
    (b) The averaged and recorded data for those dates;
    (c) Durations and causes of the following:
    (1) Each deviation from emission limitations or operating limits 
and your corrective actions; and
    (2) Bypass events and your corrective actions.

[[Page 15906]]

    (d) A copy of the operating limit monitoring data during each 
deviation and for any test report that documents the emission levels 
the process unit(s) tested, the pollutant(s) tested and the date that 
the performance test was conducted. Submit, following the procedure 
specified in Sec.  60.2795(b)(1), the performance test report no later 
than the date that you submit the deviation report.


Sec.  60.2785   What else must I report if I have a deviation from the 
requirement to have a qualified operator accessible?

    (a) If all qualified operators are not accessible for 2 weeks or 
more, you must take the two actions in paragraphs (a)(1) and (2) of 
this section:
    (1) Submit a notification of the deviation within 10 days that 
includes the three items in paragraphs (a)(1)(i) through (iii) of this 
section:
    (i) A statement of what caused the deviation;
    (ii) A description of what you are doing to ensure that a qualified 
operator is accessible; and
    (iii) The date when you anticipate that a qualified operator will 
be available.
    (2) Submit a status report to the Administrator every 4 weeks that 
includes the three items in paragraphs (a)(2)(i) through (iii) of this 
section:
    (i) A description of what you are doing to ensure that a qualified 
operator is accessible;
    (ii) The date when you anticipate that a qualified operator will be 
accessible; and
    (iii) Request approval from the Administrator to continue operation 
of the CISWI.
    (b) If your unit was shut down by the Administrator, under the 
provisions of Sec.  60.2665(b)(2), due to a failure to provide an 
accessible qualified operator, you must notify the Administrator that 
you are resuming operation once a qualified operator is accessible.


Sec.  60.2790   Are there any other notifications or reports that I 
must submit?

    (a) Yes. You must submit notifications as provided by Sec.  60.7.
    (b) If you cease combusting solid waste but continue to operate, 
you must provide 30 days prior notice of the effective date of the 
waste-to-fuel switch, consistent with Sec.  60.2710(a). The 
notification must identify:
    (1) The name of the owner or operator of the CISWI, the location of 
the source, the emissions unit(s) that will cease burning solid waste, 
and the date of the notice;
    (2) The currently applicable subcategory under this subpart, and 
any 40 CFR part 63 subpart and subcategory that will be applicable 
after you cease combusting solid waste;
    (3) The fuel(s), non-waste material(s) and solid waste(s) the CISWI 
is currently combusting and has combusted over the past 6 months, and 
the fuel(s) or non-waste materials the unit will commence combusting;
    (4) The date on which you became subject to the currently 
applicable emission limits; and
    (5) The date upon which you will cease combusting solid waste, and 
the date (if different) that you intend for any new requirements to 
become applicable (i.e., the effective date of the waste-to-fuel 
switch), consistent with paragraphs (b)(2) and (3) of this section.


Sec.  60.2795   In what form can I submit my reports?

    (a) Submit initial, annual and deviation reports electronically or 
in paper format, postmarked on or before the submittal due dates. 
Beginning on April 16, 2021 or once the reporting form has been 
available in CEDRI for 1 year, whichever is later, you must submit 
subsequent reports on or before the submittal dates to the EPA via the 
Compliance and Emissions Data Reporting Interface (CEDRI), which CEDRI 
can be accessed through the EPA's Central Data Exchange (CDX) (https://cdx.epa.gov/). Use the appropriate electronic report in CEDRI for this 
subpart or an alternate electronic file format consistent with the 
extensible markup language (XML) schema listed on the CEDRI website 
(https://www3.epa.gov/ttn/chief/cedri/). When the date forms 
become available in CEDRI will be listed on the CEDRI website. The 
reports must be submitted by the deadlines specified in this subpart, 
regardless of the method in which the report is submitted.
    (b) Submit results of each performance test and CEMS performance 
evaluation required by this subpart as follows:
    (1) Within 60 days after the date of completing each performance 
test (see Sec.  60.8) required by this subpart, you must submit the 
results of the performance test following the procedure specified in 
either paragraph (b)(1)(i) or (b)(1)(ii) of this section:
    (i) For data collected using test methods supported by the EPA's 
Electronic Reporting Tool (ERT) as listed on the EPA's ERT website 
(https://www3.epa.gov/ttn/chief/ert/ert_info.html) at the time of the 
test, you must submit the results of the performance test to the EPA 
via the CEDRI. (CEDRI can be accessed through the EPA's CDX (https://cdx.epa.gov/).) Performance test data must be submitted in a file 
format generated through the use of the EPA's ERT or an alternate 
electronic file format consistent with the XML schema listed on the 
EPA's ERT website. If you claim that some of the performance test 
information being submitted is confidential business information (CBI), 
you must submit a complete file generated through the use of the EPA's 
ERT or an alternate electronic file consistent with the XML schema 
listed on the EPA's ERT website, including information claimed to be 
CBI, on a compact disc, flash drive, or other commonly used electronic 
storage media to the EPA. The electronic media must be clearly marked 
as CBI and mailed to U.S. EPA/OAQPS/CORE CBI Office, Attention: Group 
Leader, Measurement Policy Group, MD C404-02, 4930 Old Page Rd., 
Durham, NC 27703. The same ERT or alternate file with the CBI omitted 
must be submitted to the EPA via the EPA's CDX as described earlier in 
this paragraph; and
    (ii) For data collected using test methods that are not supported 
by the EPA's ERT as listed on the EPA's ERT website at the time of the 
test, you must submit the results of the performance test to the 
Administrator at the appropriate address listed in Sec.  60.4.
    (2) Within 60 days after the date of completing each continuous 
emissions monitoring system performance evaluation you must submit the 
results of the performance evaluation following the procedure specified 
in either paragraph (b)(1) or (2) of this section:
    (i) For performance evaluations of continuous monitoring systems 
measuring relative accuracy test audit (RATA) pollutants that are 
supported by the EPA's ERT as listed on the EPA's ERT website at the 
time of the evaluation, you must submit the results of the performance 
evaluation to the EPA via the CEDRI. CEDRI can be accessed through the 
EPA's CDX. Performance evaluation data must be submitted in a file 
format generated through the use of the EPA's ERT or an alternate file 
format consistent with the XML schema listed on the EPA's ERT website. 
If you claim that some of the performance evaluation information being 
submitted is CBI, you must submit a complete file generated through the 
use of the EPA's ERT or an alternate electronic file consistent with 
the XML schema listed on the EPA's ERT website, including information 
claimed to be CBI, on a compact disc, flash drive, or other commonly 
used electronic storage media to the EPA. The electronic storage media 
must be clearly marked as CBI and mailed to U.S. EPA/OAQPS/CORE CBI 
Office, Attention:

[[Page 15907]]

Group Leader, Measurement Policy Group, MD C404-02, 4930 Old Page Rd., 
Durham, NC 27703. The same ERT or alternate file with the CBI omitted 
must be submitted to the EPA via the EPA's CDX as described earlier in 
this paragraph; and
    (ii) For any performance evaluations of continuous monitoring 
systems measuring RATA pollutants that are not supported by the EPA's 
ERT as listed on the EPA's ERT website at the time of the evaluation, 
you must submit the results of the performance evaluation to the 
Administrator at the appropriate address listed in Sec.  60.4.
    (c) If you are required to electronically submit a report through 
the Compliance and Emissions Data Reporting Interface (CEDRI) in the 
EPA's Central Data Exchange (CDX), and due to a planned or actual 
outage of either the EPA's CEDRI or CDX systems within the period of 
time beginning 5 business days prior to the date that the submission is 
due, you will be or are precluded from accessing CEDRI or CDX and 
submitting a required report within the time prescribed, you may assert 
a claim of EPA system outage for failure to timely comply with the 
reporting requirement. You must submit notification to the 
Administrator in writing as soon as possible following the date you 
first knew, or through due diligence should have known, that the event 
may cause or caused a delay in reporting. You must provide to the 
Administrator a written description identifying the date, time and 
length of the outage; a rationale for attributing the delay in 
reporting beyond the regulatory deadline to the EPA system outage; 
describe the measures taken or to be taken to minimize the delay in 
reporting; and identify a date by which you propose to report, or if 
you have already met the reporting requirement at the time of the 
notification, the date you reported. In any circumstance, the report 
must be submitted electronically as soon as possible after the outage 
is resolved. The decision to accept the claim of EPA system outage and 
allow an extension to the reporting deadline is solely within the 
discretion of the Administrator.
    (d) If you are required to electronically submit a report through 
CEDRI in the EPA's CDX and a force majeure event is about to occur, 
occurs, or has occurred or there are lingering effects from such an 
event within the period of time beginning 5 business days prior to the 
date the submission is due, the owner or operator may assert a claim of 
force majeure for failure to timely comply with the reporting 
requirement. For the purposes of this section, a force majeure event is 
defined as an event that will be or has been caused by circumstances 
beyond the control of the affected facility, its contractors, or any 
entity controlled by the affected facility that prevents you from 
complying with the requirement to submit a report electronically within 
the time period prescribed. Examples of such events are acts of nature 
(e.g., hurricanes, earthquakes, or floods), acts of war or terrorism, 
or equipment failure or safety hazard beyond the control of the 
affected facility (e.g., large scale power outage). If you intend to 
assert a claim of force majeure, you must submit notification to the 
Administrator in writing as soon as possible following the date you 
first knew, or through due diligence should have known, that the event 
may cause or caused a delay in reporting. You must provide to the 
Administrator a written description of the force majeure event and a 
rationale for attributing the delay in reporting beyond the regulatory 
deadline to the force majeure event; describe the measures taken or to 
be taken to minimize the delay in reporting; and identify a date by 
which you propose to report, or if you have already met the reporting 
requirement at the time of the notification, the date you reported. In 
any circumstance, the reporting must occur as soon as possible after 
the force majeure event occurs. The decision to accept the claim of 
force majeure and allow an extension to the reporting deadline is 
solely within the discretion of the Administrator.


Sec.  60.2800   Can reporting dates be changed?

    If the Administrator agrees, you may change the semiannual or 
annual reporting dates. See Sec.  60.19(c) for procedures to seek 
approval to change your reporting date.

Model Rule--Title V Operating Permits


Sec.  60.2805   Am I required to apply for and obtain a Title V 
operating permit for my unit?

    Yes. Each CISWI and ACI subject to standards under this subpart 
must operate pursuant to a permit issued under Clean Air Act sections 
129(e) and Title V.

Model Rule--Air Curtain Incinerators (ACIs)


Sec.  60.2810   What is an air curtain incinerator?

    (a) An ACI operates by forcefully projecting a curtain of air 
across an open chamber or open pit in which combustion occurs. 
Incinerators of this type can be constructed above or below ground and 
with or without refractory walls and floor. Air curtain incinerators 
are not to be confused with conventional combustion devices with 
enclosed fireboxes and controlled air technology such as mass burn, 
modular, and fluidized bed combustors.
    (b) Air curtain incinerators that burn only the materials listed in 
paragraphs (b)(1) through (3) of this section are only required to meet 
the requirements under Sec.  60.2805 and under ``Air Curtain 
Incinerators'' (Sec. Sec.  60.2810 through 60.2870):
    (1) 100 percent wood waste;
    (2) 100 percent clean lumber; and
    (3) 100 percent mixture of only wood waste, clean lumber, and/or 
yard waste.


Sec.  60.2815   What are my requirements for meeting increments of 
progress and achieving final compliance?

    If you plan to achieve compliance more than 1 year following the 
effective date of state plan approval, you must meet the two increments 
of progress specified in paragraphs (a) and (b) of this section:
    (a) Submit a final control plan; and
    (b) Achieve final compliance.


Sec.  60.2820   When must I complete each increment of progress?

    Table 1 of this subpart specifies compliance dates for each of the 
increments of progress.


Sec.  60.2825   What must I include in the notifications of achievement 
of increments of progress?

    Your notification of achievement of increments of progress must 
include the three items described in paragraphs (a) through (c) of this 
section:
    (a) Notification that the increment of progress has been achieved;
    (b) Any items required to be submitted with each increment of 
progress (see Sec.  60.2840); and
    (c) Signature of the owner or operator of the incinerator.


Sec.  60.2830   When must I submit the notifications of achievement of 
increments of progress?

    Notifications for achieving increments of progress must be 
postmarked no later than 10 business days after the compliance date for 
the increment.


Sec.  60.2835   What if I do not meet an increment of progress?

    If you fail to meet an increment of progress, you must submit a 
notification to the Administrator postmarked within 10 business days 
after the date for that increment of progress in table 1 of this 
subpart. You must inform the Administrator that you did not meet the 
increment, and you must continue to submit reports each subsequent

[[Page 15908]]

calendar month until the increment of progress is met.


Sec.  60.2840   How do I comply with the increment of progress for 
submittal of a control plan?

    For your control plan increment of progress, you must satisfy the 
two requirements specified in paragraphs (a) and (b) of this section:
    (a) Submit the final control plan, including a description of any 
devices for air pollution control and any process changes that you will 
use to comply with the emission limitations and other requirements of 
this subpart; and
    (b) Maintain an onsite copy of the final control plan.


Sec.  60.2845   How do I comply with the increment of progress for 
achieving final compliance?

    For the final compliance increment of progress, you must complete 
all process changes and retrofit construction of control devices, as 
specified in the final control plan, so that, if the affected 
incinerator is brought online, all necessary process changes and air 
pollution control devices would operate as designed.


Sec.  60.2850   What must I do if I close my air curtain incinerator 
and then restart it?

    (a) If you close your incinerator but will reopen it prior to the 
final compliance date in your state plan, you must meet the increments 
of progress specified in Sec.  60.2815.
    (b) If you close your incinerator but will restart it after your 
final compliance date, you must complete emission control retrofits and 
meet the emission limitations on the date your incinerator restarts 
operation.


Sec.  60.2855   What must I do if I plan to permanently close my air 
curtain incinerator and not restart it?

    If you plan to close your incinerator rather than comply with the 
state plan, submit a closure notification, including the date of 
closure, to the Administrator by the date your final control plan is 
due.


Sec.  60.2860   What are the emission limitations for air curtain 
incinerators?

    After the date the initial stack test is required or completed 
(whichever is earlier), you must meet the limitations in paragraphs (a) 
and (b) of this section:
    (a) Maintain opacity to less than or equal to 10 percent opacity 
(as determined by the average of three 1-hour blocks consisting of ten 
6-minute average opacity values), except as described in paragraph (b) 
of this section; and
    (b) Maintain opacity to less than or equal to 35 percent opacity 
(as determined by the average of three 1-hour blocks consisting of ten 
6-minute average opacity values) during the startup period that is 
within the first 30 minutes of operation.


Sec.  60.2865   How must I monitor opacity for air curtain 
incinerators?

    (a) Use Method 9 of appendix A of this part to determine compliance 
with the opacity limitation.
    (b) Conduct an initial test for opacity as specified in Sec.  60.8 
no later than 180 days after your final compliance date.
    (c) After the initial test for opacity, conduct annual tests no 
more than 12 calendar months following the date of your previous test.


Sec.  60.2870   What are the recordkeeping and reporting requirements 
for air curtain incinerators?

    (a) Keep records of results of all initial and annual opacity tests 
onsite in either paper copy or electronic format, unless the 
Administrator approves another format, for at least 5 years.
    (b) Make all records available for submittal to the Administrator 
or for an inspector's onsite review.
    (c) Submit an initial report no later than 60 days following the 
initial opacity test that includes the information specified in 
paragraphs (c)(1) and (2) of this section:
    (1) The types of materials you plan to combust in your ACI; and
    (2) The results (as determined by the average of three 1-hour 
blocks consisting of ten 6-minute average opacity values) of the 
initial opacity tests.
    (d) Submit annual opacity test results within 12 months following 
the previous report.
    (e) Submit initial and annual opacity test reports as electronic or 
paper copy on or before the applicable submittal date and keep a copy 
onsite for a period of 5 years.

Model Rule--Definitions


Sec.  60.2875  What definitions must I know?

    Terms used but not defined in this subpart are defined in the Clean 
Air Act and subparts A and B of this part.
    30-day rolling average means the arithmetic mean of the previous 
720 hours of valid operating data. Valid data excludes periods when 
this unit is not operating. The 720 hours should be consecutive, but 
not necessarily continuous if operations are intermittent.
    Administrator means the Administrator of the U.S. Environmental 
Protection Agency or his/her authorized representative or Administrator 
of a State Air Pollution Control Agency.
    Agricultural waste means vegetative agricultural materials such as 
nut and grain hulls and chaff (e.g., almond, walnut, peanut, rice, and 
wheat), bagasse, orchard prunings, corn stalks, coffee bean hulls and 
grounds, and other vegetative waste materials generated as a result of 
agricultural operations.
    Air curtain incinerator (ACI) means an incinerator that operates by 
forcefully projecting a curtain of air across an open chamber or pit in 
which combustion occurs. Incinerators of this type can be constructed 
above or below ground and with or without refractory walls and floor. 
Air curtain incinerators are not to be confused with conventional 
combustion devices with enclosed fireboxes and controlled air 
technology such as mass burn, modular, and fluidized bed combustors.
    Annual heat input means the heat input for the 12 months preceding 
the compliance demonstration.
    Auxiliary fuel means natural gas, liquified petroleum gas, fuel 
oil, or diesel fuel.
    Average annual heat input rate means annual heat input divided by 
the hours of operation for the 12 months preceding the compliance 
demonstration.
    Bag leak detection system means an instrument that is capable of 
monitoring particulate matter loadings in the exhaust of a fabric 
filter (i.e., baghouse) in order to detect bag failures. A bag leak 
detection system includes, but is not limited to, an instrument that 
operates on triboelectric, light scattering, light transmittance, or 
other principle to monitor relative particulate matter loadings.
    Burn-off oven means any rack reclamation unit, part reclamation 
unit, or drum reclamation unit. A burn-off oven is not an incinerator, 
waste-burning kiln, an energy recovery unit or a small, remote 
incinerator under this subpart.
    Bypass stack means a device used for discharging combustion gases 
to avoid severe damage to the air pollution control device or other 
equipment.
    Calendar quarter means three consecutive months (nonoverlapping) 
beginning on: January 1, April 1, July 1, or October 1.
    Calendar year means 365 consecutive days starting on January 1 and 
ending on December 31.
    CEMS data during startup and shutdown means the following:
    (1) For incinerators and small remote incinerators: CEMS data 
collected during the first hours of operation of a CISWI startup from a 
cold start until waste is fed into the unit and the hours

[[Page 15909]]

of operation following the cessation of waste material being fed to the 
CISWI during a unit shutdown. For each startup event, the length of 
time that CEMS data may be claimed as being CEMS data during startup 
must be 48 operating hours or less. For each shutdown event, the length 
of time that CEMS data may be claimed as being CEMS data during 
shutdown must be 24 operating hours or less;
    (2) For energy recovery units: CEMS data collected during the 
startup or shutdown periods of operation. Startup begins with either 
the first-ever firing of fuel in a boiler or process heater for the 
purpose of supplying useful thermal energy (such as steam or heat) for 
heating, cooling or process purposes, or producing electricity, or the 
firing of fuel in a boiler or process heater for any purpose after a 
shutdown event. Startup ends four hours after when the boiler or 
process heater makes useful thermal energy (such as heat or steam) for 
heating, cooling, or process purposes, or generates electricity, 
whichever is earlier. Shutdown begins when the boiler or process heater 
no longer makes useful thermal energy (such as heat or steam) for 
heating, cooling, or process purposes and/or generates electricity or 
when no fuel is being fed to the boiler or process heater, whichever is 
earlier. Shutdown ends when the boiler or process heater no longer 
makes useful thermal energy (such as steam or heat) for heating, 
cooling, or process purposes and/or generates electricity, and no fuel 
is being combusted in the boiler or process heater; and
    (3) For waste-burning kilns: CEMS data collected during the periods 
of kiln operation that do not include normal operations. Startup means 
the time from when a shutdown kiln first begins firing fuel until it 
begins producing clinker. Startup begins when a shutdown kiln turns on 
the induced draft fan and begins firing fuel in the main burner. 
Startup ends when feed is being continuously introduced into the kiln 
for at least 120 minutes or when the feed rate exceeds 60 percent of 
the kiln design limitation rate, whichever occurs first. Shutdown means 
the cessation of kiln operation. Shutdown begins when feed to the kiln 
is halted and ends when continuous kiln rotation ceases.
    Chemical recovery unit means combustion units burning materials to 
recover chemical constituents or to produce chemical compounds where 
there is an existing commercial market for such recovered chemical 
constituents or compounds. A chemical recovery unit is not an 
incinerator, a waste-burning kiln, an energy recovery unit or a small, 
remote incinerator under this subpart. The following seven types of 
units are considered chemical recovery units:
    (1) Units burning only pulping liquors (i.e., black liquor) that 
are reclaimed in a pulping liquor recovery process and reused in the 
pulping process;
    (2) Units burning only spent sulfuric acid used to produce virgin 
sulfuric acid;
    (3) Units burning only wood or coal feedstock for the production of 
charcoal;
    (4) Units burning only manufacturing byproduct streams/residue 
containing catalyst metals that are reclaimed and reused as catalysts 
or used to produce commercial grade catalysts;
    (5) Units burning only coke to produce purified carbon monoxide 
that is used as an intermediate in the production of other chemical 
compounds;
    (6) Units burning only hydrocarbon liquids or solids to produce 
hydrogen, carbon monoxide, synthesis gas, or other gases for use in 
other manufacturing processes; and
    (7) Units burning only photographic film to recover silver.
    Chemotherapeutic waste means waste material resulting from the 
production or use of antineoplastic agents used for the purpose of 
stopping or reversing the growth of malignant cells.
    Clean lumber means wood or wood products that have been cut or 
shaped and include wet, air-dried, and kiln-dried wood products. Clean 
lumber does not include wood products that have been painted, pigment-
stained, or pressure-treated by compounds such as chromate copper 
arsenate, pentachlorophenol, and creosote.
    Commercial and industrial solid waste incineration unit (CISWI) 
means any distinct operating unit of any commercial or industrial 
facility that combusts, or has combusted in the preceding 6 months, any 
solid waste as that term is defined in 40 CFR part 241. If the 
operating unit burns materials other than traditional fuels as defined 
in Sec.  241.2 that have been discarded, and you do not keep and 
produce records as required by Sec.  60.2740(u), the operating unit is 
a CISWI. While not all CISWIs will include all of the following 
components, a CISWI includes, but is not limited to, the solid waste 
feed system, grate system, flue gas system, waste heat recovery 
equipment, if any, and bottom ash system. The CISWI does not include 
air pollution control equipment or the stack. The CISWI boundary starts 
at the solid waste hopper (if applicable) and extends through two 
areas: The combustion unit flue gas system, which ends immediately 
after the last combustion chamber or after the waste heat recovery 
equipment, if any; and the combustion unit bottom ash system, which 
ends at the truck loading station or similar equipment that transfers 
the ash to final disposal. The CISWI includes all ash handling systems 
connected to the bottom ash handling system.
    Contained gaseous material means gases that are in a container when 
that container is combusted.
    Continuous emission monitoring system (CEMS) means the total 
equipment that may be required to meet the data acquisition and 
availability requirements of this subpart, used to sample, condition 
(if applicable), analyze, and provide a record of emissions.
    Continuous monitoring system (CMS) means the total equipment, 
required under the emission monitoring sections in applicable subparts, 
used to sample and condition (if applicable), to analyze, and to 
provide a permanent record of emissions or process parameters. A 
particulate matter continuous parameter monitoring system (PM CPMS) is 
a type of CMS.
    Cyclonic burn barrel means a combustion device for waste materials 
that is attached to a 55 gallon, open-head drum. The device consists of 
a lid, which fits onto and encloses the drum, and a blower that forces 
combustion air into the drum in a cyclonic manner to enhance the mixing 
of waste material and air. A cyclonic burn barrel is not an 
incinerator, a waste-burning kiln, an energy recovery unit or a small, 
remote incinerator under this subpart.
    Deviation means any instance in which an affected source subject to 
this subpart, or an owner or operator of such a source:
    (1) Fails to meet any requirement or obligation established by this 
subpart, including but not limited to any emission limitation, 
operating limit, or operator qualification and accessibility 
requirements; and
    (2) Fails to meet any term or condition that is adopted to 
implement an applicable requirement in this subpart and that is 
included in the operating permit for any affected source required to 
obtain such a permit.
    Dioxins/furans means tetra-through octachlorinated dibenzo-p-
dioxins and dibenzofurans.
    Discard means, for purposes of this subpart and 40 CFR part 60, 
subpart DDDD, only, burned in an incineration unit without energy 
recovery.
    Drum reclamation unit means a unit that burns residues out of drums 
(e.g., 55 gallon drums) so that the drums can be reused.

[[Page 15910]]

    Dry scrubber means an add-on air pollution control system that 
injects dry alkaline sorbent (dry injection) or sprays an alkaline 
sorbent (spray dryer) to react with and neutralize acid gas in the 
exhaust stream forming a dry powder material. Sorbent injection systems 
in fluidized bed boilers and process heaters are included in this 
definition. A dry scrubber is a dry control system.
    Energy recovery means the process of recovering thermal energy from 
combustion for useful purposes such as steam generation or process 
heating.
    Energy recovery unit means a combustion unit combusting solid waste 
(as that term is defined by the Administrator in 40 CFR part 241) for 
energy recovery. Energy recovery units include units that would be 
considered boilers and process heaters if they did not combust solid 
waste.
    Energy recovery unit designed to burn biomass (Biomass) means an 
energy recovery unit that burns solid waste, biomass, and non-coal 
solid materials but less than 10 percent coal, on a heat input basis on 
an annual average, either alone or in combination with liquid waste, 
liquid fuel or gaseous fuels.
    Energy recovery unit designed to burn coal (Coal) means an energy 
recovery unit that burns solid waste and at least 10 percent coal on a 
heat input basis on an annual average, either alone or in combination 
with liquid waste, liquid fuel or gaseous fuels.
    Energy recovery unit designed to burn liquid waste materials and 
gas (Liquid/gas) means an energy recovery unit that burns a liquid 
waste with liquid or gaseous fuels not combined with any solid fuel or 
waste materials.
    Energy recovery unit designed to burn solid materials (Solids) 
includes energy recovery units designed to burn coal and energy 
recovery units designed to burn biomass.
    Fabric filter means an add-on air pollution control device used to 
capture particulate matter by filtering gas streams through filter 
media, also known as a baghouse.
    Foundry sand thermal reclamation unit means a type of part 
reclamation unit that removes coatings that are on foundry sand. A 
foundry sand thermal reclamation unit is not an incinerator, a waste-
burning kiln, an energy recovery unit or a small, remote incinerator 
under this subpart.
    Incinerator means any furnace used in the process of combusting 
solid waste (as that term is defined by the Administrator in 40 CFR 
part 241) for the purpose of reducing the volume of the waste by 
removing combustible matter. Incinerator designs include single chamber 
and two-chamber.
    In-line coal mill means those coal mills using kiln exhaust gases 
in their process. Coal mills with a heat source other than the kiln or 
coal mills using exhaust gases from the clinker cooler alone are not an 
in-line coal mill.
    In-line kiln/raw mill means a system in a Portland Cement 
production process where a dry kiln system is integrated with the raw 
mill so that all or a portion of the kiln exhaust gases are used to 
perform the drying operation of the raw mill, with no auxiliary heat 
source used. In this system the kiln is capable of operating without 
the raw mill operating, but the raw mill cannot operate without the 
kiln gases, and consequently, the raw mill does not generate a separate 
exhaust gas stream.
    Kiln means an oven or furnace, including any associated preheater 
or precalciner devices, in-line raw mills, in-line coal mills or alkali 
bypasses used for processing a substance by burning, firing or drying. 
Kilns include cement kilns that produce clinker by heating limestone 
and other materials for subsequent production of Portland Cement. 
Because the alkali bypass, in-line raw mill and in-line coal mill are 
considered an integral part of the kiln, the kiln emissions limits also 
apply to the exhaust of the alkali bypass, in-line raw mill and in-line 
coal mill.
    Laboratory analysis unit means units that burn samples of materials 
for the purpose of chemical or physical analysis. A laboratory analysis 
unit is not an incinerator, waste-burning kiln, an energy recovery unit 
or a small, remote incinerator under this subpart.
    Load fraction means the actual heat input of an energy recovery 
unit divided by heat input during the performance test that established 
the minimum sorbent injection rate or minimum activated carbon 
injection rate, expressed as a fraction (e.g., for 50 percent load the 
load fraction is 0.5).
    Low-level radioactive waste means waste material which contains 
radioactive nuclides emitting primarily beta or gamma radiation, or 
both, in concentrations or quantities that exceed applicable federal or 
state standards for unrestricted release. Low-level radioactive waste 
is not high-level radioactive waste, spent nuclear fuel, or by-product 
material as defined by the Atomic Energy Act of 1954 (42 U.S.C. 
2014(e)(2)).
    Malfunction means any sudden, infrequent, and not reasonably 
preventable failure of air pollution control equipment, process 
equipment, or a process to operate in a normal or usual manner. 
Failures that are caused, in part, by poor maintenance or careless 
operation are not malfunctions.
    Minimum voltage or amperage means 90 percent of the lowest test-run 
average voltage or amperage to the electrostatic precipitator measured 
during the most recent particulate matter or mercury performance test 
demonstrating compliance with the applicable emission limits.
    Modification or modified CISWI means a CISWI that has been changed 
later than August 7, 2013, and that meets one of two criteria:
    (1) The cumulative cost of the changes over the life of the unit 
exceeds 50 percent of the original cost of building and installing the 
CISWI (not including the cost of land) updated to current costs 
(current dollars). To determine what systems are within the boundary of 
the CISWI used to calculate these costs, see the definition of CISWI; 
and
    (2) Any physical change in the CISWI or change in the method of 
operating it that increases the amount of any air pollutant emitted for 
which section 129 or section 111 of the Clean Air Act has established 
standards.
    Municipal solid waste or municipal-type solid waste means 
household, commercial/retail, or institutional waste. Household waste 
includes material discarded by residential dwellings, hotels, motels, 
and other similar permanent or temporary housing. Commercial/retail 
waste includes material discarded by stores, offices, restaurants, 
warehouses, nonmanufacturing activities at industrial facilities, and 
other similar establishments or facilities. Institutional waste 
includes materials discarded by schools, by hospitals (nonmedical), by 
nonmanufacturing activities at prisons and government facilities, and 
other similar establishments or facilities. Household, commercial/
retail, and institutional waste does include yard waste and refuse-
derived fuel. Household, commercial/retail, and institutional waste 
does not include used oil; sewage sludge; wood pallets; construction, 
renovation, and demolition wastes (which include railroad ties and 
telephone poles); clean wood; industrial process or manufacturing 
wastes; medical waste; or motor vehicles (including motor vehicle parts 
or vehicle fluff).
    Opacity means the degree to which emissions reduce the transmission 
of light and obscure the view of an object in the background.
    Operating day means a 24-hour period between 12:00 midnight and the 
following midnight during which any amount of solid waste is combusted 
at any time in the CISWI.
    Oxygen analyzer system means all equipment required to determine 
the

[[Page 15911]]

oxygen content of a gas stream and used to monitor oxygen in the boiler 
or process heater flue gas, boiler/process heater, firebox, or other 
appropriate location. This definition includes oxygen trim systems and 
certified oxygen CEMS. The source owner or operator is responsible to 
install, calibrate, maintain, and operate the oxygen analyzer system in 
accordance with the manufacturer's recommendations.
    Oxygen trim system means a system of monitors that is used to 
maintain excess air at the desired level in a combustion device over 
its operating range. A typical system consists of a flue gas oxygen 
and/or carbon monoxide monitor that automatically provides a feedback 
signal to the combustion air controller or draft controller.
    Part reclamation unit means a unit that burns coatings off parts 
(e.g., tools, equipment) so that the parts can be reconditioned and 
reused.
    Particulate matter means total particulate matter emitted from 
CISWIs as measured by Method 5 or Method 29 of appendix A of this part.
    Pathological waste means waste material consisting of only human or 
animal remains, anatomical parts, and/or tissue, the bags/containers 
used to collect and transport the waste material, and animal bedding 
(if applicable).
    Performance evaluation means the conduct of relative accuracy 
testing, calibration error testing, and other measurements used in 
validating the continuous monitoring system data.
    Performance test means the collection of data resulting from the 
execution of a test method (usually three emission test runs) used to 
demonstrate compliance with a relevant emission standard as specified 
in the performance test section of the relevant standard.
    Process change means any of the following physical or operational 
changes:
    (1) A physical change (maintenance activities excluded) to the 
CISWI which may increase the emission rate of any air pollutant to 
which a standard applies;
    (2) An operational change to the CISWI where a new type of non-
hazardous secondary material is being combusted;
    (3) A physical change (maintenance activities excluded) to the air 
pollution control devices used to comply with the emission limits for 
the CISWI (e.g., replacing an electrostatic precipitator with a fabric 
filter); and
    (4) An operational change to the air pollution control devices used 
to comply with the emission limits for the affected CISWI (e.g., change 
in the sorbent injection rate used for activated carbon injection).
    Rack reclamation unit means a unit that burns the coatings off 
racks used to hold small items for application of a coating. The unit 
burns the coating overspray off the rack so the rack can be reused.
    Raw mill means a ball or tube mill, vertical roller mill or other 
size reduction equipment, that is not part of an in-line kiln/raw mill, 
used to grind feed to the appropriate size. Moisture may be added or 
removed from the feed during the grinding operation. If the raw mill is 
used to remove moisture from feed materials, it is also, by definition, 
a raw material dryer. The raw mill also includes the air separator 
associated with the raw mill.
    Reconstruction means rebuilding a CISWI and meeting two criteria:
    (1) The reconstruction begins on or after August 7, 2013; and
    (2) The cumulative cost of the construction over the life of the 
incineration unit exceeds 50 percent of the original cost of building 
and installing the CISWI (not including land) updated to current costs 
(current dollars). To determine what systems are within the boundary of 
the CISWI used to calculate these costs, see the definition of CISWI.
    Refuse-derived fuel means a type of municipal solid waste produced 
by processing municipal solid waste through shredding and size 
classification. This includes all classes of refuse-derived fuel 
including two fuels:
    (1) Low-density fluff refuse-derived fuel through densified refuse-
derived fuel; and
    (2) Pelletized refuse-derived fuel.
    Responsible official means one of the following:
    (1) For a corporation: A president, secretary, treasurer, or vice-
president of the corporation in charge of a principal business 
function, or any other person who performs similar policy or decision-
making functions for the corporation, or a duly authorized 
representative of such person if the representative is responsible for 
the overall operation of one or more manufacturing, production, or 
operating facilities applying for or subject to a permit and either:
    (i) The facilities employ more than 250 persons or have gross 
annual sales or expenditures exceeding $25 million (in second quarter 
1980 dollars); or
    (ii) The delegation of authority to such representatives is 
approved in advance by the permitting authority;
    (2) For a partnership or sole proprietorship: a general partner or 
the proprietor, respectively;
    (3) For a municipality, state, federal, or other public agency: 
Either a principal executive officer or ranking elected official. For 
the purposes of this part, a principal executive officer of a Federal 
agency includes the chief executive officer having responsibility for 
the overall operations of a principal geographic unit of the agency 
(e.g., a Regional Administrator of EPA); or
    (4) For affected facilities:
    (i) The designated representative in so far as actions, standards, 
requirements, or prohibitions under Title IV of the Clean Air Act or 
the regulations promulgated thereunder are concerned; or
    (ii) The designated representative for any other purposes under 
part 60.
    Shutdown means, for incinerators and small, remote incinerators, 
the period of time after all waste has been combusted in the primary 
chamber.
    Small, remote incinerator means an incinerator that combusts solid 
waste (as that term is defined by the Administrator in 40 CFR part 241) 
and combusts 3 tons per day or less solid waste and is more than 25 
miles driving distance to the nearest municipal solid waste landfill.
    Soil treatment unit means a unit that thermally treats petroleum-
contaminated soils for the sole purpose of site remediation. A soil 
treatment unit may be direct-fired or indirect fired. A soil treatment 
unit is not an incinerator, a waste-burning kiln, an energy recovery 
unit or a small, remote incinerator under this subpart.
    Solid waste means the term solid waste as defined in 40 CFR 241.2.
    Solid waste incineration unit means a distinct operating unit of 
any facility which combusts any solid waste (as that term is defined by 
the Administrator in 40 CFR part 241) material from commercial or 
industrial establishments or the general public (including single and 
multiple residences, hotels and motels). Such term does not include 
incinerators or other units required to have a permit under section 
3005 of the Solid Waste Disposal Act. The term ``solid waste 
incineration unit'' does not include:
    (1) Materials recovery facilities (including primary or secondary 
smelters) which combust waste for the primary purpose of recovering 
metals;
    (2) Qualifying small power production facilities, as defined in 
section 3(17)(C) of the Federal Power Act (16 U.S.C. 769(17)(C)), or 
qualifying cogeneration facilities, as defined in section 3(18)(B) of 
the Federal Power

[[Page 15912]]

Act (16 U.S.C. 796(18)(B)), which burn homogeneous waste (such as units 
which burn tires or used oil, but not including refuse-derived fuel) 
for the production of electric energy or in the case of qualifying 
cogeneration facilities which burn homogeneous waste for the production 
of electric energy and steam or forms of useful energy (such as heat) 
which are used for industrial, commercial, heating or cooling purposes; 
or
    (3) Air curtain incinerators provided that such incinerators only 
burn wood wastes, yard wastes and clean lumber and that such air 
curtain incinerators comply with opacity limitations to be established 
by the Administrator by rule.
    Space heater means a unit that meets the requirements of 40 CFR 
279.23. A space heater is not an incinerator, a waste-burning kiln, an 
energy recovery unit or a small, remote incinerator under this subpart.
    Standard conditions, when referring to units of measure, means a 
temperature of 68 [deg]F (20 [deg]C) and a pressure of 1 atmosphere 
(101.3 kilopascals).
    Startup period means, for incinerators and small, remote 
incinerators, the period of time between the activation of the system 
and the first charge to the unit.
    Useful thermal energy means energy (i.e., steam, hot water, or 
process heat) that meets the minimum operating temperature and/or 
pressure required by any energy use system that uses energy provided by 
the affected energy recovery unit.
    Waste-burning kiln means a kiln that is heated, in whole or in 
part, by combusting solid waste (as the term is defined by the 
Administrator in 40 CFR part 241). Secondary materials used in Portland 
cement kilns shall not be deemed to be combusted unless they are 
introduced into the flame zone in the hot end of the kiln or mixed with 
the precalciner fuel.
    Wet scrubber means an add-on air pollution control device that uses 
an aqueous or alkaline scrubbing liquor to collect particulate matter 
(including nonvaporous metals and condensed organics) and/or to absorb 
and neutralize acid gases.
    Wood waste means untreated wood and untreated wood products, 
including tree stumps (whole or chipped), trees, tree limbs (whole or 
chipped), bark, sawdust, chips, scraps, slabs, millings, and shavings. 
Wood waste does not include:
    (1) Grass, grass clippings, bushes, shrubs, and clippings from 
bushes and shrubs from residential, commercial/retail, institutional, 
or industrial sources as part of maintaining yards or other private or 
public lands;
    (2) Construction, renovation, or demolition wastes; or
    (3) Clean lumber.

 Table 1 to Subpart DDDD of Part 60--Model Rule--Increments of Progress
                        and Compliance Schedules
------------------------------------------------------------------------
    Comply with these increments of
                progress                        By these dates \1\
------------------------------------------------------------------------
Increment 1-Submit final control plan..  (Dates to be specified in state
                                          plan).
Increment 2-Final compliance...........  (Dates to be specified in state
                                          plan).\2\
------------------------------------------------------------------------
\1\ Site-specific schedules can be used at the discretion of the state.
\2\ The date can be no later than 3 years after the effective date of
  state plan approval or December 1, 2005 for CISWIs that commenced
  construction on or before November 30, 1999. The date can be no later
  than 3 years after the effective date of approval of a revised state
  plan or February 7, 2018, for CISWIs that commenced construction on or
  before June 4, 2010.


 Table 2 to Subpart DDDD of Part 60--Model Rule--Emission Limitations That Apply to Incinerators Before [Date To
                                         Be Specified in State Plan] \1\
----------------------------------------------------------------------------------------------------------------
                                                                                             And determining
        For the air pollutant             You must meet this      Using this averaging    compliance using this
                                       emission limitation \2\          time \3\                method \3\
----------------------------------------------------------------------------------------------------------------
Cadmium..............................  0.004 milligrams per     3-run average (1 hour    Performance test
                                        dry standard cubic       minimum sample time      (Method 29 of appendix
                                        meter.                   per run).                A of this part).
Carbon monoxide......................  157 parts per million    3-run average (1 hour    Performance test
                                        by dry volume.           minimum sample time      (Method 10, 10A, or
                                                                 per run).                10B, of appendix A of
                                                                                          this part).
Dioxins/furans (toxic equivalency      0.41 nanograms per dry   3-run average (1 hour    Performance test
 basis).                                standard cubic meter.    minimum sample time      (Method 23 of appendix
                                                                 per run).                A of this part).
Hydrogen chloride....................  62 parts per million by  3-run average (For       Performance test
                                        dry volume.              Method 26, collect a     (Method 26 or 26A at
                                                                 minimum volume of 120    40 CFR part 60,
                                                                 liters per run. For      appendix A-8).
                                                                 Method 26A, collect a
                                                                 minimum volume of 1
                                                                 dry standard cubic
                                                                 meter per run).
Lead.................................  0.04 milligrams per dry  3-run average (1 hour    Performance test
                                        standard cubic meter.    minimum sample time      (Method 29 of appendix
                                                                 per run).                A of this part).
Mercury..............................  0.47 milligrams per dry  3-run average (1 hour    Performance test
                                        standard cubic meter.    minimum sample time      (Method 29 or 30B at
                                                                 per run).                40 CFR part 60,
                                                                                          appendix A-8) or ASTM
                                                                                          D6784-02 (Reapproved
                                                                                          2008).\4\
Opacity..............................  10 percent.............  Three 1-hour blocks      Performance test
                                                                 consisting of ten 6-     (Method 9 at 40 CFR
                                                                 minute average opacity   part 60, appendix A-
                                                                 values.                  4).
Nitrogen oxides......................  388 parts per million    3-run average (1 hour    Performance test
                                        by dry volume.           minimum sample time      (Methods 7 or 7E at 40
                                                                 per run).                CFR part 60, appendix
                                                                                          A-4).
Particulate matter...................  70 milligrams per dry    3-run average (1 hour    Performance test
                                        standard cubic meter.    minimum sample time      (Method 5 or 29 of
                                                                 per run).                appendix A of this
                                                                                          part).

[[Page 15913]]

 
Sulfur dioxide.......................  20 parts per million by  3-run average (1 hour    Performance test
                                        dry volume.              minimum sample time      (Method 6 or 6c of
                                                                 per run).                appendix A of this
                                                                                          part).
----------------------------------------------------------------------------------------------------------------
\1\ Applies only to incinerators subject to the CISWI standards through a state plan or the Federal plan prior
  to June 4, 2010. The date specified in the state plan can be no later than 3 years after the effective date of
  approval of a revised state plan or February 7, 2018.
\2\ All emission limitations (except for opacity) are measured at 7 percent oxygen, dry basis at standard
  conditions.
\3\ In lieu of performance testing, you may use a CEMS or, for mercury, an integrated sorbent trap monitoring
  system, to demonstrate initial and continuing compliance with an emissions limit, as long as you comply with
  the CEMS or integrated sorbent trap monitoring system requirements applicable to the specific pollutant in
  Sec.  Sec.   60.2710 and 60.2730. As prescribed in Sec.   60.2710(u), if you use a CEMS or integrated sorbent
  trap monitoring system to demonstrate compliance with an emissions limit, your averaging time is a 30-day
  rolling average of 1-hour arithmetic average emission concentrations.
\4\ Incorporated by reference, see Sec.   60.17.


               Table 3 to Subpart DDDD of Part 60--Model Rule--Operating Limits for Wet Scrubbers
----------------------------------------------------------------------------------------------------------------
                                  You must establish          And monitor using these minimum frequencies
 For these operating parameters     these operating  -----------------------------------------------------------
                                        limits         Data measurement     Data recording      Averaging time
----------------------------------------------------------------------------------------------------------------
Charge rate.....................  Maximum charge      Continuous........  Every hour........  Daily (batch
                                   rate.                                                       units). 3-hour
                                                                                               rolling
                                                                                               (continuous and
                                                                                               intermittent
                                                                                               units).\1\
Pressure drop across the wet      Minimum pressure    Continuous........  Every 15 minutes..  3-hour rolling.\1\
 scrubber or amperage to wet       drop or amperage.
 scrubber.
Scrubber liquor flow rate.......  Minimum flow rate.  Continuous........  Every 15 minutes..  3-hour rolling.\1\
Scrubber liquor pH..............  Minimum pH........  Continuous........  Every 15 minutes..  3-hour rolling.\1\
----------------------------------------------------------------------------------------------------------------
\1\ Calculated each hour as the average of the previous 3 operating hours.


    Table 4 to Subpart DDDD of Part 60--Model Rule--Toxic Equivalency
                                 Factors
------------------------------------------------------------------------
                                                       Toxic equivalency
                 Dioxin/furan isomer                        factor
------------------------------------------------------------------------
2,3,7,8-tetrachlorinated dibenzo-p-dioxin...........                   1
1,2,3,7,8-pentachlorinated dibenzo-p-dioxin.........                 0.5
1,2,3,4,7,8-hexachlorinated dibenzo-p-dioxin........                 0.1
1,2,3,7,8,9-hexachlorinated dibenzo-p-dioxin........                 0.1
1,2,3,6,7,8-hexachlorinated dibenzo-p-dioxin........                 0.1
1,2,3,4,6,7,8-heptachlorinated dibenzo-p-dioxin.....                0.01
octachlorinated dibenzo-p-dioxin....................               0.001
2,3,7,8-tetrachlorinated dibenzofuran...............                 0.1
2,3,4,7,8-pentachlorinated dibenzofuran.............                 0.5
1,2,3,7,8-pentachlorinated dibenzofuran.............                0.05
1,2,3,4,7,8-hexachlorinated dibenzofuran............                 0.1
1,2,3,6,7,8-hexachlorinated dibenzofuran............                 0.1
1,2,3,7,8,9-hexachlorinated dibenzofuran............                 0.1
2,3,4,6,7,8-hexachlorinated dibenzofuran............                 0.1
1,2,3,4,6,7,8-heptachlorinated dibenzofuran.........                0.01
1,2,3,4,7,8,9-heptachlorinated dibenzofuran.........                0.01
octachlorinated dibenzofuran........................               0.001
------------------------------------------------------------------------


              Table 5 to Subpart DDDD of Part 60--Model Rule--Summary of Reporting Requirements \1\
----------------------------------------------------------------------------------------------------------------
               Report                       Due date                   Contents                  Reference
----------------------------------------------------------------------------------------------------------------
Waste Management Plan..............  No later than the date   Waste management    Sec.   60.2755.
                                      specified in table 1    plan.
                                      for submittal of the
                                      final control plan.
Initial Test Report................  No later than 60 days    Complete test       Sec.   60.2760.
                                      following the initial   report for the initial
                                      performance test.       performance test.
                                                              The values for the
                                                              site-specific operating
                                                              limits.
                                                              Installation of
                                                              bag leak detection systems
                                                              for fabric filters.

[[Page 15914]]

 
Annual report......................  No later than 12         Name and address..  Sec.  Sec.   60.2765
                                      months following the    Statement and        and 60.2770.
                                      submission of the       signature by responsible
                                      initial test report.    official.
                                      Subsequent reports      Date of report....
                                      are to be submitted     Values for the
                                      no more than 12         operating limits.
                                      months following the    Highest recorded 3-
                                      previous report.        hour average and the
                                                              lowest 3-hour average, as
                                                              applicable, (or 30-day
                                                              average, if applicable)
                                                              for each operating
                                                              parameter recorded for the
                                                              calendar year being
                                                              reported.
                                                              If a performance
                                                              test was conducted during
                                                              the reporting period, the
                                                              results of the test.
                                                              If a performance
                                                              test was not conducted
                                                              during the reporting
                                                              period, a statement that
                                                              the requirements of Sec.
                                                              60.2720(a) were met.
                                                              Documentation of
                                                              periods when all qualified
                                                              CISWI operators were
                                                              unavailable for more than
                                                              8 hours but less than 2
                                                              weeks.
                                                              If you are
                                                              conducting performance
                                                              tests once every 3 years
                                                              consistent with Sec.
                                                              60.2720(a), the date of
                                                              the last 2 performance
                                                              tests, a comparison of the
                                                              emission level you
                                                              achieved in the last 2
                                                              performance tests to the
                                                              75 percent emission limit
                                                              threshold required in Sec.
                                                                60.2720(a) and a
                                                              statement as to whether
                                                              there have been any
                                                              operational changes since
                                                              the last performance test
                                                              that could increase
                                                              emissions.
                                                              Any malfunction,
                                                              deviation, or continuous
                                                              monitoring system out of
                                                              control periods
                                                              information as specified
                                                              in Sec.   60.2770(k)
                                                              through (o).
                                                              Fuel input
                                                              information for energy
                                                              recovery unit subcategory
                                                              verification as specified
                                                              in Sec.   60.2770(p).
Emission limitation or operating     By August 1 of that      Dates and times of  Sec.   60.2775 and
 limit deviation report.              year for data           deviation.                   60.2780.
                                      collected during the    Averaged and
                                      first half of the       recorded data for those
                                      calendar year. By       dates.
                                      February 1 of the       Duration and
                                      following year for      causes of each deviation
                                      data collected during   and the corrective actions
                                      the second half of      taken.
                                      the calendar year.      Copy of operating
                                                              limit monitoring data and
                                                              any test reports.
                                                              Dates, times and
                                                              causes for monitor
                                                              downtime incidents.
Qualified Operator Deviation         Within 10 days of        Statement of cause  Sec.   60.2785(a)(1).
 Notification.                        deviation.              of deviation.
                                                              Description of
                                                              efforts to have an
                                                              accessible qualified
                                                              operator.
                                                              The date a
                                                              qualified operator will be
                                                              accessible.
Qualified Operator Deviation Status  Every 4 weeks            Description of      Sec.   60.2785(a)(2).
 Report.                              following deviation.    efforts to have an
                                                              accessible qualified
                                                              operator.
                                                              The date a
                                                              qualified operator will be
                                                              accessible.
                                                              Request for
                                                              approval to continue
                                                              operation.
Qualified Operator Deviation         Prior to resuming        Notification that   Sec.   60.2785(b).
 Notification of Resumed Operation.   operation.              you are resuming operation.
----------------------------------------------------------------------------------------------------------------
\1\ This table is only a summary, see the referenced sections of the rule for the complete requirements.


  Table 6 to Subpart DDDD of Part 60--Model Rule--Emission Limitations That Apply to Incinerators on and After
                                    [Date To Be Specified in State Plan] \1\
----------------------------------------------------------------------------------------------------------------
                                                                                             And determining
        For the air pollutant             You must meet this      Using this averaging    compliance using this
                                       emission limitation \2\          time \3\                method \3\
----------------------------------------------------------------------------------------------------------------
Cadmium..............................  0.0026 milligrams per    3-run average (collect   Performance test
                                        dry standard cubic       a minimum volume of 2    (Method 29 at 40 CFR
                                        meter.                   dry standard cubic       part 60, appendix A-
                                                                 meters).                 8). Use ICPMS for the
                                                                                          analytical finish.
Carbon monoxide......................  17 parts per million     3-run average (1 hour    Performance test
                                        dry volume.              minimum sample time      (Method 10 at 40 CFR
                                                                 per run).                part 60, appendix A-
                                                                                          4).
Dioxins/furans (total mass basis)....  4.6 nanograms per dry    3-run average (collect   Performance test
                                        standard cubic meter.    a minimum volume of 2    (Method 23 at 40 CFR
                                                                 dry standard cubic       part 60, appendix A-
                                                                 meters).                 7).
Dioxins/furans (toxic equivalency      0.13 nanograms per dry   3-run average (collect   Performance test
 basis).                                standard cubic meter.    a minimum volume of 2    (Method 23 at 40 CFR
                                                                 dry standard cubic       part 60, appendix A-
                                                                 meters).                 7).

[[Page 15915]]

 
Hydrogen chloride....................  29 parts per million     3-run average (For       Performance test
                                        dry volume.              Method 26, collect a     (Method 26 or 26A at
                                                                 minimum volume of 60     40 CFR part 60,
                                                                 liters per run. For      appendix A-8).
                                                                 Method 26A, collect a
                                                                 minimum volume of 1
                                                                 dry standard cubic
                                                                 meter per run).
Lead.................................  0.015 milligrams per     3-run average (collect   Performance test
                                        dry standard cubic       a minimum volume of 2    (Method 29 at 40 CFR
                                        meter.                   dry standard cubic       part 60, appendix A-
                                                                 meters).                 8). Use ICPMS for the
                                                                                          analytical finish.
Mercury..............................  0.0048 milligrams per    3-run average (For       Performance test
                                        dry standard cubic       Method 29 an ASTM        (Method 29 or 30B at
                                        meter.                   D6784-02 (Reapproved     40 CFR part 60,
                                                                 2008),\4\ collect a      appendix A-8) or ASTM
                                                                 minimum volume of 2      D6784-02 (Reapproved
                                                                 dry standard cubic       2008).\4\
                                                                 meters per run. For
                                                                 Method 30B, collect a
                                                                 minimum sample as
                                                                 specified in Method
                                                                 30B at 40 CFR part 60,
                                                                 appendix A).
Nitrogen oxides......................  53 parts per million     3-run average (for       Performance test
                                        dry volume.              Method 7E, 1 hour        (Method 7 or 7E at 40
                                                                 minimum sample time      CFR part 60, appendix
                                                                 per run).                A-4).
Particulate matter filterable........  34 milligrams per dry    3-run average (collect   Performance test
                                        standard cubic meter.    a minimum volume of 1    (Method 5 or 29 at 40
                                                                 dry standard cubic       CFR part 60, appendix
                                                                 meter).                  A-3 or appendix A-8).
Sulfur dioxide.......................  11 parts per million     3-run average (1 hour    Performance test
                                        dry volume.              minimum sample time      (Method 6 or 6c at 40
                                                                 per run).                CFR part 60, appendix
                                                                                          A-4).
Fugitive ash.........................  Visible emissions for    Three 1-hour             Visible emission test
                                        no more than 5% of the   observation periods.     (Method 22 at 40 CFR
                                        hourly observation                                part 60, appendix A-
                                        period.                                           7).
----------------------------------------------------------------------------------------------------------------
\1\ The date specified in the state plan can be no later than 3 years after the effective date of approval of a
  revised state plan or February 7, 2018.
\2\ All emission limitations are measured at 7 percent oxygen, dry basis at standard conditions. For dioxins/
  furans, you must meet either the total mass basis limit or the toxic equivalency basis limit.
\3\ In lieu of performance testing, you may use a CEMS or, for mercury, an integrated sorbent trap monitoring
  system, to demonstrate initial and continuing compliance with an emissions limit, as long as you comply with
  the CEMS or integrated sorbent trap monitoring system requirements applicable to the specific pollutant in
  Sec.  Sec.   60.2710 and 60.2730. As prescribed in Sec.   60.2710(u), if you use a CEMS or integrated sorbent
  trap monitoring system to demonstrate compliance with an emissions limit, your averaging time is a 30-day
  rolling average of 1-hour arithmetic average emission concentrations.
\4\ Incorporated by reference, see Sec.   60.17.


 Table 7 to Subpart DDDD of Part 60--Model Rule--Emission Limitations That Apply to Energy Recovery Units After
                              May 20, 2011 [Date To Be Specified in State Plan] \1\
----------------------------------------------------------------------------------------------------------------
                                  You must meet this emission limitation
                                                    \2\                       Using this        And determining
      For the air pollutant      ---------------------------------------- averaging time \3\   compliance using
                                      Liquid/gas            Solids                              this method \3\
----------------------------------------------------------------------------------------------------------------
Cadmium.........................  0.023 milligrams    Biomass-0.0014      3-run average       Performance test
                                   per dry standard    milligrams per      (collect a          (Method 29 at 40
                                   cubic meter.        dry standard        minimum volume of   CFR part 60,
                                                       cubic meter.        2 dry standard      appendix A-8).
                                                      Coal-0.0017          cubic meters).      Use ICPMS for the
                                                       milligrams per                          analytical
                                                       dry standard                            finish.
                                                       cubic meter.
Carbon monoxide.................  35 parts per        Biomass-260 parts   3-run average (1    Performance test
                                   million dry         per million dry     hour minimum        (Method 10 at 40
                                   volume.             volume.             sample time per     CFR part 60,
                                                      Coal-95 parts per    run).               appendix A-4).
                                                       million dry
                                                       volume.
Dioxins/furans (total mass        2.9 nanograms per   Biomass-0.52        3-run average       Performance test
 basis).                           dry standard        nanograms per dry   (collect a          (Method 23 at 40
                                   cubic meter.        standard cubic      minimum volume of   CFR part 60,
                                                       meter.              4 dry standard      appendix A-7).
                                                      Coal-5.1 nanograms   cubic meter).
                                                       per dry standard
                                                       cubic meter.
Dioxins/furans (toxic             0.32 nanograms per  Biomass-0.12        3-run average       Performance test
 equivalency basis).               dry standard        nanograms per dry   (collect a          (Method 23 at 40
                                   cubic meter.        standard cubic      minimum volume of   CFR part 60,
                                                       meter.              4 dry standard      appendix A-7).
                                                      Coal-0.075           cubic meters).
                                                       nanograms per dry
                                                       standard cubic
                                                       meter.

[[Page 15916]]

 
Hydrogen chloride...............  14 parts per        Biomass-0.20 parts  3-run average (for  Performance test
                                   million dry         per million dry     Method 26,          (Method 26 or 26A
                                   volume.             volume.             collect a minimum   at 40 CFR part
                                                      Coal-58 parts per    of 120 liters;      60, appendix A-
                                                       million dry         for Method 26A,     8).
                                                       volume.             collect a minimum
                                                                           volume of 1 dry
                                                                           standard cubic
                                                                           meter).
Lead............................  0.096 milligrams    Biomass-0.014       3-run average       Performance test
                                   per dry standard    milligrams per      (collect a          (Method 29 at 40
                                   cubic meter.        dry standard        minimum volume of   CFR part 60,
                                                       cubic meter.        2 dry standard      appendix A-8).
                                                      Coal-0.057           cubic meters).      Use ICPMS for the
                                                       milligrams per                          analytical
                                                       dry standard                            finish.
                                                       cubic meter.
Mercury.........................  0.0024 milligrams   Biomass-0.0022      3-run average (For  Performance test
                                   per dry standard    milligrams per      Method 29 and       (Method 29 or 30B
                                   cubic meter.        dry standard        ASTM D6784-02       at 40 CFR part
                                                       cubic meter.        (Reapproved         60, appendix A-8)
                                                      Coal-0.013           2008),\4\ collect   or ASTM D6784-02
                                                       milligrams per      a minimum volume    (Reapproved
                                                       dry standard        of 2 dry standard   2008).\4\
                                                       cubic meter.        cubic meters per
                                                                           run. For Method
                                                                           30B, collect a
                                                                           minimum sample as
                                                                           specified in
                                                                           Method 30B at 40
                                                                           CFR part 60,
                                                                           appendix A).
Nitrogen oxides.................  76 parts per        Biomass-290 parts   3-run average (for  Performance test
                                   million dry         per million dry     Method 7E, 1 hour   (Method 7 or 7E
                                   volume.             volume.             minimum sample      at 40 CFR part
                                                      Coal-460 parts per   time per run).      60, appendix A-
                                                       million dry                             4).
                                                       volume.
Particulate matter filterable...  110 milligrams per  Biomass-11          3-run average       Performance test
                                   dry standard        milligrams per      (collect a          (Method 5 or 29
                                   cubic meter.        dry standard        minimum volume of   at 40 CFR part
                                                       cubic meter.        1 dry standard      60, appendix A-3
                                                      Coal-130             cubic meter).       or appendix A-8)
                                                       milligrams per                          if the unit has
                                                       dry standard                            an annual average
                                                       cubic meter.                            heat input rate
                                                                                               less than or
                                                                                               equal to 250
                                                                                               MMBtu/hr; or PM
                                                                                               CPMS (as
                                                                                               specified in Sec.
                                                                                                 60.2710(x)) if
                                                                                               the unit has an
                                                                                               annual average
                                                                                               heat input rate
                                                                                               greater than 250
                                                                                               MMBtu/hr.
Sulfur dioxide..................  720 parts per       Biomass-7.3 parts   3-run average (1    Performance test
                                   million dry         per million dry     hour minimum        (Method 6 or 6c
                                   volume.             volume.             sample time per     at 40 CFR part
                                                      Coal-850 parts per   run).               60, appendix A-
                                                       million dry                             4).
                                                       volume.
Fugitive ash....................  Visible emissions   Visible emissions   Three 1-hour        Visible emission
                                   for no more than    for no more than    observation         test (Method 22
                                   5 percent of the    5 percent of the    periods.            at 40 CFR part
                                   hourly              hourly                                  60, appendix A-
                                   observation         observation                             7).
                                   period.             period.
----------------------------------------------------------------------------------------------------------------
\1\ The date specified in the state plan can be no later than 3 years after the effective date of approval of a
  revised state plan or February 7, 2018.
\2\ All emission limitations (except for opacity) are measured at 7 percent oxygen, dry basis at standard
  conditions. For dioxins/furans, you must meet either the total mass basis limit or the toxic equivalency basis
  limit.
\3\ In lieu of performance testing, you may use a CEMS or, for mercury, an integrated sorbent trap monitoring
  system, to demonstrate initial and continuing compliance with an emissions limit, as long as you comply with
  the CEMS or integrated sorbent trap monitoring system requirements applicable to the specific pollutant in
  Sec.  Sec.   60.2710 and 60.2730. As prescribed in Sec.   60.2710(u), if you use a CEMS or integrated sorbent
  trap monitoring system to demonstrate compliance with an emissions limit, your averaging time is a 30-day
  rolling average of 1-hour arithmetic average emission concentrations.
\4\ Incorporated by reference, see Sec.   60.17.


Table 8 to Subpart DDDD of Part 60--Model Rule--Emission Limitations That Apply to Waste-Burning Kilns After May
                                20, 2011 [Date To Be Specified in State Plan] \1\
----------------------------------------------------------------------------------------------------------------
                                                                                             And determining
        For the air pollutant             You must meet this      Using this averaging    compliance using this
                                       emission limitation \2\          time \3\              method \3\ \4\
----------------------------------------------------------------------------------------------------------------
Cadmium..............................  0.0014 milligrams per    3-run average (collect   Performance test
                                        dry standard cubic       a minimum volume of 2    (Method 29 at 40 CFR
                                        meter.                   dry standard cubic       part 60, appendix A-
                                                                 meters).                 8).

[[Page 15917]]

 
Carbon monoxide......................  110 (long kilns)/790     3-run average (1 hour    Performance test
                                        (preheater/              minimum sample time      (Method 10 at 40 CFR
                                        precalciner) parts per   per run).                part 60, appendix A-
                                        million dry volume.                               4).
Dioxins/furans (total mass basis)....  1.3 nanograms per dry    3-run average (collect   Performance test
                                        standard cubic meter.    a minimum volume of 4    (Method 23 at 40 CFR
                                                                 dry standard cubic       part 60, appendix A-
                                                                 meters).                 7).
Dioxins/furans (toxic equivalency      0.075 nanograms per dry  3-run average (collect   Performance test
 basis).                                standard cubic meter.    a minimum volume of 4    (Method 23 at 40 CFR
                                                                 dry standard cubic       part 60, appendix A-
                                                                 meters).                 7).
Hydrogen chloride....................  3.0 parts per million    3-run average (collect   If a wet scrubber or
                                        dry volume.              a minimum volume of 1    dry scrubber is used,
                                                                 dry standard cubic       performance test
                                                                 meter), or 30-day        (Method 321 at 40 CFR
                                                                 rolling average if HCl   part 63, appendix A of
                                                                 CEMS is being used.      this part). If a wet
                                                                                          scrubber or dry
                                                                                          scrubber is not used,
                                                                                          HCl CEMS as specified
                                                                                          in Sec.   60.2710(j).
Lead.................................  0.014 milligrams per     3-run average (collect   Performance test
                                        dry standard cubic       a minimum volume of 2    (Method 29 at 40 CFR
                                        meter.                   dry standard cubic       part 60, appendix A-
                                                                 meters).                 8).
Mercury..............................  0.011 milligrams per     30-day rolling average.  Mercury CEMS or
                                        dry standard cubic                                integrated sorbent
                                        meter.                                            trap monitoring system
                                       Or.....................                            (performance
                                       58 pounds/million tons                             specification 12A or
                                        of clinker.                                       12B, respectively, of
                                                                                          appendix B and
                                                                                          procedure 5 of
                                                                                          appendix F of this
                                                                                          part), as specified in
                                                                                          Sec.   60.2710(j).
Nitrogen oxides......................  630 parts per million    3-run average (for       Performance test
                                        dry volume.              Method 7E, 1 hour        (Method 7 or 7E at 40
                                                                 minimum sample time      CFR part 60, appendix
                                                                 per run).                A-4).
Particulate matter filterable........  13.5 milligrams per dry  30-day rolling average.  PM CPMS (as specified
                                        standard cubic meter.                             in Sec.   60.2710(x)).
Sulfur dioxide.......................  600 parts per million    3-run average (for       Performance test
                                        dry volume.              Method 6, collect a      (Method 6 or 6c at 40
                                                                 minimum of 20 liters;    CFR part 60, appendix
                                                                 for Method 6C, 1 hour    A-4).
                                                                 minimum sample time
                                                                 per run).
----------------------------------------------------------------------------------------------------------------
\1\ The date specified in the state plan can be no later than 3 years after the effective date of approval of a
  revised state plan or February 7, 2018.
\2\ All emission limitations are measured at 7 percent oxygen (except for CEMS and integrated sorbent trap
  monitoring system data during startup and shutdown), dry basis at standard conditions. For dioxins/furans, you
  must meet either the total mass basis limit or the toxic equivalency basis limit.
\3\ In lieu of performance testing, you may use a CEMS or, for mercury, an integrated sorbent trap monitoring
  system, to demonstrate initial and continuing compliance with an emissions limit, as long as you comply with
  the CEMS or integrated sorbent trap monitoring system requirements applicable to the specific pollutant in
  Sec.  Sec.   60.2710 and 60.2730. As prescribed in Sec.   60.2710(u), if you use a CEMS or integrated sorbent
  trap monitoring system to demonstrate compliance with an emissions limit, your averaging time is a 30-day
  rolling average of 1-hour arithmetic average emission concentrations.
\4\ Alkali bypass and in-line coal mill stacks are subject to performance testing only, as specified in
  60.2710(y)(3). They are not subject to the CEMS, integrated sorbent trap monitoring system, or CPMS
  requirements that otherwise may apply to the main kiln exhaust.


  Table 9 to Subpart DDDD of Part 60--Model Rule--Emission Limitations That Apply to Small, Remote Incinerators
                           After May 20, 2011 [Date To Be Specified in State Plan] \1\
----------------------------------------------------------------------------------------------------------------
                                                                                             And determining
        For the air pollutant             You must meet this      Using this averaging    compliance using this
                                       emission limitation \2\          time \3\                method \3\
----------------------------------------------------------------------------------------------------------------
Cadmium..............................  0.95 milligrams per dry  3-run average (collect   Performance test
                                        standard cubic meter.    a minimum volume of 1    (Method 29 at 40 CFR
                                                                 dry standard cubic       part 60, appendix A-
                                                                 meters per run).         8).
Carbon monoxide......................  64 parts per million     3-run average (1 hour    Performance test
                                        dry volume.              minimum sample time      (Method 10 at 40 CFR
                                                                 per run).                part 60, appendix A-
                                                                                          4).
Dioxins/furans (total mass basis)....  4,400 nanograms per dry  3-run average (collect   Performance test
                                        standard cubic meter.    a minimum volume of 1    (Method 23 at 40 CFR
                                                                 dry standard cubic       part 60, appendix A-
                                                                 meters per run).         7).
Dioxins/furans (toxic equivalency      180 nanograms per dry    3-run average (collect   Performance test
 basis).                                standard cubic meter.    a minimum volume of 1    (Method 23 at 40 CFR
                                                                 dry standard cubic       part 60, appendix A-
                                                                 meters).                 7).
Fugitive ash.........................  Visible emissions for    Three 1-hour             Visible emissions test
                                        no more than 5 percent   observation periods.     (Method 22 at 40 CFR
                                        of the hourly                                     part 60, appendix A-
                                        observation period.                               7).

[[Page 15918]]

 
Hydrogen chloride....................  300 parts per million    3-run average (For       Performance test
                                        dry volume.              Method 26, collect a     (Method 26 or 26A at
                                                                 minimum volume of 120    40 CFR part 60,
                                                                 liters per run. For      appendix A-8).
                                                                 Method 26A, collect a
                                                                 minimum volume of 1
                                                                 dry standard cubic
                                                                 meter per run).
Lead.................................  2.1 milligrams per dry   3-run average (collect   Performance test
                                        standard cubic meter.    a minimum volume of 1    (Method 29 at 40 CFR
                                                                 dry standard cubic       part 60, appendix A-
                                                                 meters).                 8). Use ICPMS for the
                                                                                          analytical finish.
Mercury..............................  0.0053 milligrams per    3-run average (For       Performance test
                                        dry standard cubic       Method 29 and ASTM       (Method 29 or 30B at
                                        meter.                   D6784-02 (Reapproved     40 CFR part 60,
                                                                 2008),\3\ collect a      appendix A-8) or ASTM
                                                                 minimum volume of 2      D6784-02 (Reapproved
                                                                 dry standard cubic       2008).\4\
                                                                 meters per run. For
                                                                 Method 30B, collect a
                                                                 minimum sample as
                                                                 specified in Method
                                                                 30B at 40 CFR part 60,
                                                                 appendix A).
Nitrogen oxides......................  190 parts per million    3-run average (for       Performance test
                                        dry volume.              Method 7E, 1 hour        (Method 7 or 7E at 40
                                                                 minimum sample time      CFR part 60, appendix
                                                                 per run).                A-4).
Particulate matter (filterable)......  270 milligrams per dry   3-run average (collect   Performance test
                                        standard cubic meter.    a minimum volume of 1    (Method 5 or 29 at 40
                                                                 dry standard cubic       CFR part 60, appendix
                                                                 meters).                 A-3 or appendix A-8).
Sulfur dioxide.......................  150 parts per million    3-run average (for       Performance test
                                        dry volume.              Method 6, collect a      (Method 6 or 6c at 40
                                                                 minimum of 20 liters     CFR part 60, appendix
                                                                 per run; for Method      A-4).
                                                                 6C, 1 hour minimum
                                                                 sample time per run).
----------------------------------------------------------------------------------------------------------------
\1\ The date specified in the state plan can be no later than 3 years after the effective date of approval of a
  revised state plan or February 7, 2018.
\2\ All emission limitations (except for opacity) are measured at 7 percent oxygen, dry basis at standard
  conditions. For dioxins/furans, you must meet either the total mass basis limit or the toxic equivalency basis
  limit.
\3\ In lieu of performance testing, you may use a CEMS or, for mercury, an integrated sorbent trap monitoring
  system, to demonstrate initial and continuing compliance with an emissions limit, as long as you comply with
  the CEMS or integrated sorbent trap monitoring system requirements applicable to the specific pollutant in
  Sec.  Sec.   60.2710 and 60.2730. As prescribed in Sec.   60.2710(u), if you use a CEMS or integrated sorbent
  trap monitoring system to demonstrate compliance with an emissions limit, your averaging time is a 30-day
  rolling average of 1-hour arithmetic average emission concentrations.
\4\ Incorporated by reference, see Sec.   60.17.

[FR Doc. 2019-05529 Filed 4-15-19; 8:45 am]
 BILLING CODE 6560-50-P

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