Revisions to Reporting and Recordkeeping Requirements, and Confidentiality Determinations Under the Greenhouse Gas Reporting Program; Final Rule, 63749-63799 [2014-23780]
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Part III
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40 CFR Part 98
Revisions to Reporting and Recordkeeping Requirements, and
Confidentiality Determinations Under the Greenhouse Gas Reporting
Program; Final Rule
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Federal Register / Vol. 79, No. 206 / Friday, October 24, 2014 / Rules and Regulations
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 98
[EPA–HQ–OAR–2010–0929; FRL–9916–76–
OAR]
RIN 2060–AQ81
Revisions to Reporting and
Recordkeeping Requirements, and
Confidentiality Determinations Under
the Greenhouse Gas Reporting
Program; Final Rule
Environmental Protection
Agency.
ACTION: Final rule.
AGENCY:
The Environmental Protection
Agency (EPA) is amending the reporting
and recordkeeping requirements of the
Greenhouse Gas Reporting Program.
These amendments include an
alternative verification approach in lieu
of collecting certain data elements for
which the EPA has identified disclosure
concerns and for which the reporting
deadline was deferred until March 31,
2015. The alternative verification
approach includes the addition of new
verification, recordkeeping, and
reporting requirements while
maintaining the EPA’s ability to verify
emissions and ensure compliance with
the Greenhouse Gas Reporting Program.
In conjunction with the amendments,
the EPA is establishing final
SUMMARY:
confidentiality determinations for the
new data elements added in this action.
DATES: This final rule is effective on
November 24, 2014.
ADDRESSES: All documents in the docket
are listed in the https://
www.regulations.gov index. Although
listed in the index, some information is
not publicly available, e.g., confidential
business information (CBI) or other
information whose disclosure is
restricted by statute. Certain other
material, such as copyrighted material,
will be publicly available only in hard
copy. Publicly available docket
materials are available either
electronically in https://
www.regulations.gov or in hard copy at
the Air Docket, EPA/DC, William
Jefferson Clinton Building West, Room
B102, 1301 Constitution Ave. NW.,
Washington, DC. This Docket Facility is
open from 8:30 a.m. to 4:30 p.m.,
Monday through Friday, excluding legal
holidays. The telephone number for the
Public Reading Room is (202) 566–1744,
and the telephone number for the Air
Docket is (202) 566–1742.
FOR FURTHER GENERAL INFORMATION
CONTACT: Carole Cook, Climate Change
Division, Office of Atmospheric
Programs (MC–6207J), Environmental
Protection Agency, 1200 Pennsylvania
Ave. NW., Washington, DC 20460;
telephone number: (202) 343–9263; fax
number: (202) 343–2342; email address:
GHGreporting@epa.gov. For technical
information, contact the Greenhouse
Gas Reporting Rule Helpline at: https://
www.epa.gov/climatechange/emissions/
ghgrule_contactus.htm. Alternatively,
contact Carole Cook at 202–343–9263.
Worldwide Web (WWW). In addition
to being available in the docket, an
electronic copy of this final rule,
memoranda to the docket, and all other
related information will also be
available through the WWW on the
EPA’s greenhouse gas reporting rule
Web site at https://www.epa.gov/
climatechange/emissions/
ghgrulemaking.html.
SUPPLEMENTARY INFORMATION:
Regulated Entities. This final rule
revision on reporting and recordkeeping
requirements and verification
procedures affects entities that must
submit annual greenhouse gas (GHG)
reports under the Greenhouse Gas
Reporting Program (GHGRP) (40 CFR
part 98). The Administrator has
determined that 40 CFR part 98 is
subject to the provisions of Clean Air
Act (CAA) section 307(d). See CAA
section 307(d)(1)(V) (the provisions of
CAA section 307(d) apply to ‘‘such
other actions as the Administrator may
determine’’). Entities affected by this
final rule are owners and operators of
facilities that are direct emitters of
GHGs, which include those listed in
Table 1 of this preamble:
TABLE 1—EXAMPLES OF AFFECTED ENTITIES BY CATEGORY
Category
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General Stationary
Sources.
Fuel
NAICS
Combustion
Adipic Acid Production .............................
Aluminum Production ...............................
Ammonia Manufacturing ...........................
Cement Production ...................................
Ferroalloy Production ...............................
Glass Production ......................................
HCFC–22 Production and HFC–23 Destruction.
Hydrogen Production ................................
Iron and Steel Production .........................
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Examples of affected facilities
...........................
Facilities operating boilers, process heaters, incinerators, turbines, and internal
combustion engines.
Manufacturers of lumber and wood products.
Pulp and paper mills.
Chemical manufacturers.
Petroleum refineries and manufacturers of coal products.
Manufacturers of rubber and miscellaneous plastic products.
Steel works, blast furnaces.
Electroplating, plating, polishing, anodizing, and coloring.
Manufacturers of motor vehicle parts and accessories.
Electric, gas, and sanitary services.
Health services.
Educational services.
Ethyl alcohol manufacturing facilities.
Meat processing facilities.
Frozen fruit, juice, and vegetable manufacturing facilities.
Fruit and vegetable canning facilities.
Adipic acid manufacturing facilities.
Primary aluminum production facilities.
Anhydrous and aqueous ammonia production facilities.
Portland cement manufacturing plants.
Ferroalloys manufacturing facilities.
Flat glass manufacturing facilities.
Glass container manufacturing facilities.
Other pressed and blown glass and glassware manufacturing facilities.
Chlorodifluoromethane manufacturing facilities.
321 ...................
322 ...................
325 ...................
324 ...................
316, 326, 339 ...
331 ...................
332 ...................
336 ...................
221 ...................
622 ...................
611 ...................
325193 .............
311611 .............
311411 .............
311421 .............
325199 .............
331312 .............
325311 .............
327310 .............
331112 .............
327211 .............
327213 .............
327212 .............
325120 .............
325120 .............
331111 .............
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Hydrogen production facilities.
Integrated iron and steel mills, steel companies, sinter plants, blast furnaces,
basic oxygen process furnace shops.
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TABLE 1—EXAMPLES OF AFFECTED ENTITIES BY CATEGORY—Continued
Category
NAICS
Examples of affected facilities
Lead Production .......................................
331419 .............
331492 .............
327410 .............
325311 .............
32511 ...............
325199 .............
325110 .............
325182 .............
486210 .............
221210 .............
211 ...................
211112 .............
324110 .............
325312 .............
322110 .............
322121 .............
322130 .............
327910 .............
325181 .............
212391 .............
325188 .............
331419 .............
331492 .............
Primary lead smelting and refining facilities.
Secondary lead smelting and refining facilities.
Calcium oxide, calcium hydroxide, dolomitic hydrates manufacturing facilities.
Nitric acid production facilities.
Ethylene dichloride production facilities.
Acrylonitrile, ethylene oxide, methanol production facilities.
Ethylene production facilities.
Carbon black production facilities.
Pipeline transportation of natural gas.
Natural gas distribution facilities.
Extractors of crude petroleum and natural gas.
Natural gas liquid extraction facilities.
Petroleum refineries.
Phosphoric acid manufacturing facilities.
Pulp mills.
Paper mills.
Paperboard mills.
Silicon carbide abrasives manufacturing facilities.
Alkalies and chlorine manufacturing facilities.
Soda ash, natural, mining and/or beneficiation.
Titanium dioxide manufacturing facilities.
Primary zinc refining facilities.
Zinc dust reclaiming facilities, recovering from scrap and/or alloying purchased
metals.
Frozen fruit, juice and vegetable manufacturing facilities.
Fruit and vegetable canning facilities.
Pulp mills.
Paper mills.
Newsprint mills.
Paperboard mills.
Meat processing facilities.
Frozen fruit, juice and vegetable manufacturing facilities.
Fruit and vegetable canning facilities.
Ethanol manufacturing facilities.
Lime Production ........................................
Nitric Acid Production ...............................
Petrochemical Production .........................
Petroleum and Natural Gas Systems .......
Petroleum Refineries ................................
Phosphoric Acid Production .....................
Pulp and Paper Manufacturing .................
Silicon Carbide Production .......................
Soda Ash Manufacturing ..........................
Titanium Dioxide Production ....................
Zinc Production .........................................
Wastewater Treatment a ...........................
311411
311421
322110
322121
322122
322130
311611
311411
311421
325193
.............
.............
.............
.............
.............
.............
.............
.............
.............
.............
a The inputs to emission equations (for which reporting was deferred to 2015) in these categories were evaluated following the four-step process set forth in the memorandum entitled ‘‘Process for Evaluating and Potentially Amending Part 98 Inputs to Emission Equations’’ (Docket ID
No. EPA–HQ–OAR–2010–0929). Refer to Section 1.B of the proposal preamble (78 FR 55994, September 11, 2013) for further information regarding this evaluation. No amendment to the subpart affecting this industry category was proposed as a result of the evaluation. Accordingly,
this final action does not include any amendment to this subpart. Refer to Section II.B of this preamble for further discussion of the EPA’s
decision.
Table 1 of this preamble is not
intended to be exhaustive, but rather
provides a guide for readers regarding
facilities and suppliers likely to be
affected by this action. Types of
facilities other than those listed in this
table might also be affected by this
action. To determine whether you are
affected by this action, you should
carefully examine the applicability
criteria found in 40 CFR part 98, subpart
A or the relevant criteria in the subparts.
If you have questions regarding the
applicability of this action to a
particular facility or supplier, consult
the person listed in the preceding FOR
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FURTHER GENERAL INFORMATION CONTACT
section.
Many facilities that are affected by 40
CFR part 98 have GHG emissions from
multiple source categories listed in
Table 1 of this preamble.
Judicial Review. Under CAA section
307(b)(1), judicial review of this final
rule is available only by filing a petition
for review in the U.S. Court of Appeals
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for the District of Columbia Circuit (the
Court) by December 23, 2014. 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.
Section 307(d)(7)(B) of the CAA also
provides a mechanism for the EPA to
convene a proceeding for
reconsideration, ‘‘[i]f the person raising
an objection can demonstrate to EPA
that it was impracticable to raise such
objection within [the period for public
comment] or if the grounds for such
objection arose after the period for
public comment (but within the time
specified for judicial review) and if such
objection is of central relevance to the
outcome of the rule.’’ Any person
seeking to make such a demonstration to
us should submit a Petition for
Reconsideration to the Office of the
Administrator, Environmental
Protection Agency, Room 3000, William
Jefferson Clinton Building, 1200
PO 00000
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Pennsylvania Ave. NW., Washington,
DC 20460, with a copy to the person
listed in the preceding FOR FURTHER
GENERAL 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 20004. Note that 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.
Acronyms and Abbreviations. The
following acronyms and abbreviations
are used in this document.
CAA Clean Air Act
CaO Calcium oxide
CAR Climate Action Reserve
CBI Confidential business information
CEMS continuous emissions monitoring
system
CFR Code of Federal Regulations
CKD Cement kiln dust
CO2 Carbon dioxide
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e-GGRT Electronic Greenhouse Gas
Reporting Tool
EPA U.S. Environmental Protection Agency
FISMA Federal Information Security
Management Act of 2002
FR Federal Register
FTC Federal Trade Commission
GHG Greenhouse gas
GHGRP Greenhouse Gas Reporting Program
HCFC–22 Chlorodifluoromethane
HFC Hydrofluorocarbons
HTML Hypertext markup language
ICR Information Collection Request
IVT Inputs Verification Tool
KA Ketone-alcohol oil (or cyclohexanol)
lb Pound
MMBtu Million British thermal units
N2O Nitrous oxide
NAICS North American Industry
Classification System
NIST National Institute of Standards and
Technology
NTTAA National Technology Transfer and
Advancement Act
OMB Office of Management & Budget
PUC Public utility commission
RFA Regulatory Flexibility Act
SSM Startup, shutdown, and malfunction
TLS Transport Layer Security
TRI Toxics Release Inventory
UMRA Unfunded Mandates Reform Act
U.S. United States
WWW Worldwide Web
XML Extensible markup language
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Organization of This Document. The
following outline is provided to aid in
locating information in this preamble.
I. Executive Summary, Background, and
Overview
A. How is this preamble organized?
B. Executive Summary
C. Background on the Action
D. Subparts Covered in the Final Rule
E. Legal Authority
II. Summary of Final Amendments to Part 98
A. Addition of a Requirement for Certain
Reporters To Use an Inputs Verification
Tool (IVT) to Enter Certain Data
Elements
B. Removal of the Requirement To Report
Certain Data Elements
C. Revision of Recordkeeping
Requirements for Facilities Required To
Use IVT
D. Addition of Reporting Requirements for
Certain Facilities Required To Use IVT
III. Summary of Final Confidentiality
Determinations for New Data Elements
A. Summary of Final CBI Determinations
B. Response to Public Comments
IV. Impacts of the Final Rule
A. How were the costs of this final rule
estimated?
B. Do the final confidentiality
determinations change the impacts of the
final amendments?
V. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory
Planning and Review and Executive
Order 13563: Improving Regulation and
Regulatory Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act (RFA)
D. Unfunded Mandates Reform Act
(UMRA)
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E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
G. Executive Order 13045: Protection of
Children From Environmental Health
Risks and Safety Risks
H. Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution, or Use
I. National Technology Transfer and
Advancement Act
J. Executive Order 12898: Federal Actions
To Address Environmental Justice in
Minority Populations and Low-Income
Populations
K. Congressional Review Act
I. Executive Summary, Background,
and Overview
A. How is this preamble organized?
Section I of this preamble provides
background information regarding the
origin of the final amendments. Section
I also discusses the EPA’s legal
authority under the CAA to promulgate
and amend the Greenhouse Gas
Reporting Rule (40 CFR part 98,
hereinafter referred to as ‘‘Part 98’’) and
the EPA’s legal authority to make
confidentiality determinations for new
data elements required by this
amendment. Section II of this preamble
describes the final amendments to Part
98, which includes the EPA’s proposed
alternative verification approach.
Section II of this preamble also
describes the major changes made since
proposal to the alternative verification
approach and provides brief summaries
of significant public comments and the
EPA’s responses thereto. Section III of
this preamble finalizes the
confidentiality determinations for the
new data reporting elements being
added to Part 98 in this action. Section
IV of this preamble discusses the
impacts of the final amendments.
Section V of this preamble describes the
statutory and executive order
requirements applicable to this action.
identified must be entered into IVT.1
IVT will perform electronic verification
on the entered inputs to emission
equations and use the entered inputs to
calculate the emission equation results.
IVT will not retain the entered inputs
(i.e., the inputs are not reporting
requirements under Part 98); instead,
IVT will conduct certain checks (e.g.,
accuracy of the inputs and the
calculated emissions values) at the time
of data entry and generate a verification
summary. The EPA will not have access
to the entered inputs either during the
time of entry or any time thereafter.
However, the verification summary,
which will be accessible to the EPA
once the reporter has completed using
IVT and the annual report is submitted,
will provide the EPA with information
to conduct further verification if
necessary.
• For 23 subparts, removing the
requirement to report 378 inputs to
emission equations for which reporting
was deferred to 2015 and for which
disclosure concerns have been
identified.2
• For reporters required to use IVT,
specifying the format for maintaining
records of data entered into IVT so that
all such records are maintained in a
consistent format; and for each facility
subject to the IVT requirement,
lengthening the record retention period
from 3 to 5 years for all data entered
into IVT and for other records
maintained by the reporting facility
under Part 98 (including subparts not
required to use IVT).
• For certain reporters required to use
IVT, adding new data elements to be
reported.
The EPA is not amending the
reporting requirements for 151 inputs to
emission equations for which reporting
was deferred, but for which disclosure
concerns were not identified and the
data remain useful. For these inputs to
emission equations, the deferral will
B. Executive Summary
The EPA is finalizing the proposed
alternative verification approach for the
GHGRP, with some changes made in
response to public comments. The
alternative verification approach
includes amendments to reporting and
recordkeeping requirements of Part 98,
as follows:
• Adding a requirement for certain
reporters under 23 subparts to use an
EPA-provided inputs verification tool
(IVT). For these subparts, 324 inputs to
emission equations for which reporting
was deferred to 2015 and for which
disclosure concerns have been
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1 Under this final action, IVT would not be
required to be used by reporters for any reported
GHG for which the reporter uses a continuous
emissions monitoring system (CEMS) or an EPAapproved alternative method—as allowed under 40
CFR 98.33(a)(5), 98.53(a)(2), and 98.223(a)(2) to
calculate the reported GHG value, rather than using
inputs to emission equations (for which reporting
was deferred to 2015) and the associated EPAprovided calculation methodologies to calculate the
reported GHG value.
2 As mentioned above, there are 378 equation
inputs for which reporting was deferred to 2015 and
for which the EPA determined there are disclosure
concerns, and 324 of these equation inputs must be
entered into IVT. Fifty-four of the 378 equation
inputs do not need to be entered into IVT because
these equation inputs are redundant to other
equations inputs being entered into IVT or are
otherwise not needed for verification.
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expire on March 31, 2015, by which
date these inputs must be reported.3
This alternative verification approach
builds on the EPA’s experience and
success with electronic reporting and
verification during the first 4 years of
the GHGRP. This alternative verification
approach, which includes additional
verification checks that IVT will
conduct on data entered into IVT
(during the data entry process), provides
the EPA with information necessary to
identify facilities with potential
reporting errors and conduct further
verification following the submission of
annual reports. This alternative
verification approach, including its
associated revisions to recordkeeping
and reporting requirements, provides an
alternative to collecting certain data
elements for which disclosure concerns
have been identified, while maintaining
the EPA’s ability to verify data and
ensure compliance with the GHGRP.
Also, in conjunction with the
amendments, the EPA is establishing
confidentiality determinations for the
new data elements finalized in this
action.
C. Background on the Action
On October 30, 2009, the EPA
published the Greenhouse Gas
Reporting Rule, 40 CFR part 98,
requiring annual reporting of GHG data
from a broad range of industry sectors
(74 FR 56260). Under Part 98, the EPA
requires annual reporting of data from
certain facilities and suppliers above
specified emission or quantity-supplied
thresholds. On July 7, 2010 (75 FR
39094) and subsequent proposals (77 FR
1434, January 10, 2012; 77 FR 10434,
February 22, 2012), we proposed
confidentiality determinations for the
data elements required to be reported.
The confidentiality of each reported
data element was determined using a
two-step approach: (1) Grouping data
elements into 22 data categories (e.g.,
inputs to emission equations, emissions,
and unit/process operating
characteristics that are not inputs to
emission equations for direct emitter
source categories) and (2) making
confidentiality determinations either
categorically or on the basis of
individual data elements. Refer to both
the July 7, 2010 proposal (75 FR 39097)
and the May 26, 2011 final rule (76 FR
30785–30786) for more detailed
descriptions of this process. Refer to the
May 26, 2011 final rule also for a
discussion of individual data element
3 In this action, the EPA is providing an option
for Subpart W reporters to delay reporting of six
inputs to emission equations for two reporting years
in specific situations. Refer to section III.A.3 of this
preamble for further discussion on this topic.
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confidentiality determinations. The EPA
has established final confidentiality
determinations for part 98 data elements
except those in the ‘‘inputs to emission
equations’’ category (May 26, 2011, 76
FR 30782; August 13, 2012, 77 FR
48072; and August 24, 2012, 77 FR
51477).4 We proposed that ‘‘inputs to
emission equations’’ meet the definition
of ‘‘emission data’’ under 40 CFR
2.301(a)(2)(i). Because, under section
114(c) of the CAA, emission data are not
entitled to confidential treatment, we
did not evaluate whether such data
elements would qualify as CBI,
including whether disclosure would
likely cause substantial competitive
harm to the reporting facilities (75 FR
39105 and 39108, July 7, 2010).
Following our proposal, we received
numerous industry comments
expressing concerns regarding potential
disclosure of many of these data
elements. In light of the comments, the
EPA expressed that ‘‘these concerns
warranted an in-depth evaluation of the
potential impact from the release of
inputs to emission equations’’ and that
the EPA would ‘‘complete this
evaluation and take appropriate final
actions regarding inputs to equations
before these data elements are reported
to EPA and potentially be subject to
release.’’ (76 FR 53060, August 25,
2011). In a document published on
December 27, 2010, we issued a call for
information (75 FR 81366) requesting
additional information to assist us in
conducting our evaluation. To allow
sufficient time to complete this
evaluation through notice and comment,
we deferred the reporting deadline for
data elements assigned to the ‘‘inputs to
emission equation’’ category. Reporting
of certain of these data elements was
deferred to March 31, 2013, as specified
in Table A–6 to subpart A; and reporting
of the remainder of these data elements
was deferred to March 31, 2015, as
specified in Table A–7 to subpart A (see
the August 25, 2011 final rule, 76 FR
53057).
Our process for the abovementioned
evaluation was documented in the final
deferral document (76 FR 53057, August
25, 2011) and the accompanying
memorandum entitled ‘‘Process for
Evaluating and Potentially Amending
Part 98 Inputs to Emission Equations’’
4 There are a small number of data elements
(besides data elements categorized as ‘‘inputs to
emission equations’’) for which we have not made
final confidentiality determinations because we
concluded that a determination of confidentiality
for the data element should be made on a case-bycase facility basis. For example, annual ferroalloy
product production capacity in subpart K
(ferroalloy production), was not assigned a
confidentiality determination; see 76 FR 30782,
May 26, 2011.
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63753
(Docket ID No. EPA–HQ–OAR–2010–
0929). As discussed in the final deferral
document and memorandum, our
evaluation involved a four-step process,
as follows:
• Step 1: Determine whether each data
element assigned to the ‘‘inputs to emission
equations’’ category is already publicly
available.
• Step 2: For data elements assigned to the
‘‘inputs to emission equations’’ category that
are not publicly available, evaluate whether
disclosure of the information is likely to
result in substantial competitive harm.
• Step 3: For data elements assigned to the
‘‘inputs to emission equations’’ category that
are likely to cause substantial competitive
harm if disclosed, evaluate potential
alternative calculation methods.
• Step 4: For data elements assigned to the
‘‘inputs to emission equations’’ category that
are likely to cause substantial competitive
harm if disclosed, evaluate potential
alternative verification methods.
Using each step of the four-step
evaluation process, the EPA evaluated
data elements for which reporting was
deferred to March 31, 2015.5 The results
of the evaluation were documented in
the four following memoranda available
in the EPA’s Docket ID No. EPA–HQ–
OAR–2010–0929:
• ‘‘Evaluation of Public Availability of
Inputs to Emission Equations for which
Reporting was Deferred to March 31, 2015,’’
August 2013.
• ‘‘Evaluation of Competitive Harm from
Disclosure of ‘Inputs to Equations’ Data
Elements Deferred to March 31, 2015,’’
August 2013.
• ‘‘Evaluation of Alternative Calculation
Methods,’’ August 2013.
• ‘‘Evaluation of Alternative Verification
Approaches For Greenhouse Gas Reporting
Rule Subparts for which Reporting of Inputs
to Emission Equations was Deferred to March
31, 2015,’’ August 2013.
Based on the results of this
evaluation, the EPA proposed on
September 11, 2013 (78 FR 55994)
amendments to the recordkeeping and
reporting provisions for 24 subparts of
Part 98, including an alternative
5 Based on the same four-step process, we also
evaluated all data elements for which reporting was
deferred to March 31, 2013 (Table A–6 to Part 98),
which did not result in amendments to Part 98.
Accordingly, affected facilities were required to
report by April 1, 2013 these data elements for
reporting years 2010 through 2012 and must
include them in annual reports for subsequent
reporting years, as required by Part 98. For a
discussion of this evaluation, refer to the EPA’s
memorandum ‘‘Summary of Evaluation of
Greenhouse Gas Reporting Program (GHGRP) Part
98 ‘‘Inputs to Emission Equations’’ Data Elements
Deferred Until 2013’’ (December 17, 2012), available
at https://www.epa.gov/ghgreporting/documents/
pdf/2012/documents/2013-inputs-memo.pdf. In
addition, the reporting of the inputs to emission
equations in subpart I was addressed by
amendments published on November 13, 2013 (77
FR 68162).
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verification approach, to address the
inputs to emission equations for which
disclosure concerns were identified in
these subparts. The public comment
period for the proposed rule
amendments was initially scheduled to
end on November 12, 2013. The EPA
received requests to extend the public
comment period, and the EPA
published a document in the Federal
Register on November 6, 2013 (78 FR
66674) extending the public comment
period to November 26, 2013.
In this action, the EPA is finalizing
the proposed alternative verification
approach for 23 subparts of the GHGRP
with some changes from the proposed
rule. The EPA had proposed
amendments but is not taking final
action on subpart L inputs to emission
equations. Final action on subpart L
inputs to emission equations will be
addressed in a separate rulemaking.6
Responses to comments submitted on
the proposed amendments can be found
in both Section II of this preamble and
the document ‘‘Greenhouse Gas
Reporting Rule—Revisions to Reporting
and Recordkeeping Requirements, and
Proposed Confidentiality
Determinations Under the Greenhouse
Gas Reporting Program: EPA’s
Responses to Public Comments’’ (see
Docket ID No. EPA–HQ–OAR–2010–
0929).
D. Subparts Covered in the Final Rule
The final amendments remove certain
reporting requirements and add certain
verification requirements for all
subparts listed in Table 2 of this
preamble. Table 2 of this preamble
includes most of the subparts of Part 98
with inputs to emission equations for
which the reporting deadline was
deferred until 2015. Subpart I is not
included in Table 2 of this preamble
because reporting of the inputs to
emission equations for subpart I was
addressed by amendments published on
November 13, 2013 (77 FR 68162). As
mentioned above, subpart L is not
included in Table 2 of this preamble
because the EPA’s final decision on
reporting of the inputs to emission
equations for subpart L will be
addressed in a separate rulemaking.
Subpart II is not listed in Table 2 of this
preamble because no subpart II inputs to
emission equations were determined to
have disclosure concerns, so no subpart
II inputs are removed from reporting
under this amendment. Subpart W is
excluded from Table 2 of this preamble
as well, because no inputs to emission
equations in subpart W are being
removed from reporting. Refer to the
memorandum ‘‘Final Evaluation of
Competitive Harm from Disclosure of
‘Inputs to Equations’ Data Elements
Deferred to March 31, 2015,’’ September
2014 (refer to Docket ID No. EPA–HQ–
OAR–2010–0929) for discussions about
the EPA’s harm analysis results for
subparts W and II. Refer to Section II.B
of this preamble for a discussion of
amendments to subpart W.
Additionally, parts of these final rule
amendments affect subparts not listed in
Table 2 of this preamble. Specifically,
for owners or operators of facilities
subject to both a subpart listed in Table
2 of this preamble and a subpart of Part
98 not listed in Table 2 of this preamble,
the amended recordkeeping duration
applies to the facility’s records required
for all Part 98 subparts (to which the
reporter is subject). Refer to Sections
II.C and III.B of the proposal preamble
for further discussion of this
recordkeeping amendment (78 FR
55994, September 11, 2013).
Additionally, owners or operators of
facilities reporting under subparts E, H,
O, Q, W, Y, AA, CC, and II, as well as
certain owners and operators reporting
under subpart C, must report inputs to
emission equations for which reporting
was deferred to 2015 and disclosure
concerns were not identified for
reporting years 2010 through 2013 in
the reporting year 2014 annual report.7
Refer to Section III.A.3 of the proposal
preamble for further discussion of this
reporting amendment (78 FR 55994,
September 11, 2013).
TABLE 2—SUBPARTS AFFECTED BY THE FINAL AMENDMENTS REMOVING CERTAIN REPORTING AND ADDING CERTAIN
VERIFICATION REQUIREMENTS a
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Subpart
C—General Stationary Fuel Combustion—Stationary fuel combustion sources (e.g., individual units, aggregations of units, common pipes, or
common stacks) excluding those that contain at least one combustion unit connected to a fuel-fired electric generator owned or operated by
an entity that is subject to regulation of customer billing rates by the public utility commission (PUC) (excluding generators connected to combustion units subject to 40 CFR part 98, subpart D) and that are located at a facility for which the sum of the nameplate capacities for all
such electric generators is greater than or equal to 1 megawatt electric output.b c
E—Adipic Acid Production.
F—Aluminum Production.
G—Ammonia Manufacturing.
H—Cement Production.
K—Ferroalloy Production.
N—Glass Production.
O—HCFC–22 Production and HFC–23 Destruction.
P—Hydrogen Production.
Q—Iron and Steel Production.
R—Lead Production.
S—Lime Manufacturing.
U—Miscellaneous Uses of Carbonate.
V—Nitric Acid Production.
X—Petrochemical Production.
Y—Petroleum Refineries.
Z—Phosphoric Acid Production.
AA—Pulp and Paper Manufacturing.
BB—Silicon Carbide Production.
CC—Soda Ash Manufacturing.
EE—Titanium Dioxide Production.
6 Accordingly, comments received covering solely
topics related to subpart L will be addressed in a
separate rulemaking.
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7 For six data elements in subpart W, reporting of
the data for reporting year 2013 may be delayed
until reporting year 2015 in specific cases. Refer to
section II.B.2 of this preamble for further discussion
of this optional reporting delay. Further, final
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action on the inputs to emission equations whose
reporting deadline was deferred until 2015 in
Subpart L will be addressed in a separate
rulemaking.
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63755
TABLE 2—SUBPARTS AFFECTED BY THE FINAL AMENDMENTS REMOVING CERTAIN REPORTING AND ADDING CERTAIN
VERIFICATION REQUIREMENTS a—Continued
Subpart
GG—Zinc Production.
TT—Industrial Waste Landfills.
a This final action does not remove reporting requirements or require use of IVT for any reported GHG value for which the reporter uses a continuous emissions monitoring system (CEMS) or an EPA-approved alternative method—as allowed under 40 CFR 98.33(a)(5), 98.53(a)(2), and
98.223(a)(2)—to calculate the reported GHG value, rather than using inputs to emission equations for which reporting was deferred to March 31,
2015, and the associated EPA-provided calculation methodologies to calculate the reported GHG value.
b Includes one deferred input to an emission equations, 40 CFR 98.3(d)(3)(v), which is specified in subpart A of Part 98 and applies to only
certain reporters under subpart C.
c These subpart C sources may elect to report inputs to emission equations rather than use IVT.
E. Legal Authority
The EPA is amending Part 98 under
its existing CAA authority provided in
CAA section 114. As stated in the
preamble to the 2009 final GHG
reporting rule (74 FR 56260, October 30,
2009), CAA section 114(a)(1) provides
the EPA broad authority to require the
information to be reported by this rule
because such data would inform and are
relevant to the EPA’s carrying out a
wide variety of CAA provisions. See the
preambles to the proposed (74 FR
16448, April 10, 2009) and final Part 98
(74 FR 56260, October 30, 2009) for
further information.
In addition, pursuant to sections 114,
301, and 307 of the CAA, the EPA has
established final confidentiality
determinations for the new data
elements required by this amendment.
Section 114(c) of the CAA requires that
the EPA make publicly available
information obtained under CAA
section 114, except for information
(excluding emission data) that qualifies
for confidential treatment. The
Administrator has determined that this
action (Part 98 amendment and
confidentiality determinations) is
subject to the provisions of CAA section
307(d).
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II. Summary of Final Amendments to
Part 98
The EPA is finalizing the proposed
alternative verification approach for the
GHGRP, with some changes made in
response to public comments. A
detailed description of the alternative
verification approach is available in the
preamble to the proposed rule (78 FR
55994, September 11, 2013).
Additionally, the EPA is finalizing its
CBI determinations for the new
reporting elements added to Part 98 in
this action, with changes made in
response to public comments.
This section of the preamble describes
the final amendments to Part 98,
organized according to the following
four general areas:
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• Addition of a requirement for facilities
subject to the subparts listed in Table 2 of
this preamble to use IVT to enter 324 inputs
to emission equations into IVT for which
reporting was deferred to 2015 and for which
disclosure concerns were identified.
• Removal of the requirement to report 378
inputs to emission equations for which
reporting was deferred to 2015 and for which
disclosure concerns were identified.8
• Revision of recordkeeping requirements
for facilities required to use IVT.
• Addition of new reporting elements for
certain facilities required to use IVT.
These four areas of final amendments
are described in more detail in Sections
II.A through II.D of this preamble.
Specifically, each of these sections
includes a summary of final
amendments, a summary of major
changes since proposal, and a summary
of the major comments and the EPA’s
responses thereto. The comment
response document (Docket ID. No.
EPA–HQ–OAR–2010–0929) includes a
complete listing of all comments
received on the proposed rule (78 FR
55994, September 11, 2013) and the
EPA’s responses.
Additional rationale for these
amendments is available in the
preamble to the proposed rule (78 FR
55994, September 11, 2013).
The final amendments also include
minor changes from the proposed rule
that harmonize regulatory text to be
consistent with other provisions in 40
CFR part 98, clarify regulatory text, and
correct minor errors in the proposal.
These changes are described in the
memorandum ‘‘Summary and
Explanation of Minor Changes Since the
Proposed Rule’’ (Docket ID No. EPA–
HQ–OAR–2010–0929).
8 As mentioned above, there are 378 equation
inputs for which reporting was deferred to 2015 and
for which the EPA determined there are disclosure
concerns, and 324 of these equation inputs must be
entered into IVT. Fifty-four of the 378 equation
inputs do not need to be entered into IVT because
these equation inputs are redundant to other
equations inputs being entered into IVT or are
otherwise not needed for verification.
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A. Addition of a Requirement for
Certain Reporters To Use an Inputs
Verification Tool (IVT) To Enter Certain
Data Elements
1. Summary of Final Amendments to
Part 98
The EPA is finalizing the proposed
requirement that IVT be used by
facilities subject to the subparts listed in
Table 2 of this preamble, with some
exceptions for certain subpart C sources,
as further discussed in Section II.A.2 of
this preamble. Most commenters
generally supported use of IVT as an
effective method for verifying
emissions. Using entered inputs to
emission equations, IVT calculates the
equation results, conducts electronic
verification checks on the inputs, and
generates a verification summary, as
follows. IVT will be deployed within
the Electronic Greenhouse Gas
Reporting Tool (e-GGRT) and will be
integrated without interrupting the
current electronic reporting process.
Reporters will enter data into e-GGRT
that are required to be reported in the
annual report, and will also enter into
e-GGRT (via IVT) the inputs to emission
equations for which reporting is no
longer required under the amendments.
IVT will use these entered data to
calculate the equation results, conduct
electronic verification checks on the
entered inputs to emission equations,
and generate a verification summary
that informs the EPA about the
verification results without specifying
the entered inputs to emission
equations. IVT will not retain the
entered inputs to emission equations,
which will not be electronically
accessible to the EPA during their entry
or anytime thereafter. Instead, the EPA
will rely on the verification summary,
which will become accessible to the
EPA after annual report submittal, and
other follow-up verification procedures
described in the proposed rule for
conducting verification. Sources subject
to multiple subparts under Part 98 are
required to use IVT for only those
subparts listed in Table 2 of this
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preamble. Reporters must use IVT
starting with reporting year 2014. A
detailed description of IVT and these
requirements is provided in the
proposal preamble (78 FR 55994,
September 11, 2013), the memorandum
‘‘Technical Approach and Design for
Inputs Verification Tool,’’ August 2013
(refer to Docket ID No. EPA–HQ–OAR–
2010–0929), and Section II.A.3 of this
preamble.
The inputs to emission equations
required to be entered into IVT are
specified in the ‘‘verification software
records’’ provisions in the
recordkeeping section of each subpart
specified in Table 2 of this preamble.
Subpart C sources (e.g., individual
units, aggregations of units, common
pipes, or common stacks) that do not
meet the following criteria have the
option to use IVT or to report these
deferred inputs to emission equations
for which reporting was deferred to
2015: Contain at least one combustion
unit connected to a fuel-fired electric
generator owned or operated by an
entity that is subject to regulation of
customer billing rates by the public
utility commission (PUC) (excluding
generators connected to combustion
units subject to 40 CFR part 98, subpart
D) and are located at a facility for which
the sum of the nameplate capacities for
all such electric generators is greater
than or equal to 1 megawatt electric
output. For those sources who choose to
report their inputs to emission
equations, e-GGRT will require the
reporters to waive the right to make
confidentiality claims before they can be
reported via e-GGRT.
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2. Summary of Changes Since Proposal
This section provides a brief summary
of changes to the requirement to use IVT
since proposal. The EPA’s rationale for
these changes is provided in Section
II.A.3 of this preamble as part of the
EPA’s response to the related
comment(s).
The changes to the proposed
requirement to use IVT are as follows:
• The EPA has revised one of the criteria
in 40 CFR 98.36(f) that specifies which
stationary fuel combustion sources (e.g.,
individual units, aggregations of units,
common pipes, or common stacks) subject to
subpart C of part 98 are required to report
inputs to emission equations for which
reporting was deferred to 2015. At proposal,
40 CFR 98.36(f)(1) stated that the stationary
combustion source contains at least one
combustion unit connected to a fuel-fired
electric generator granted access by the
Public Utilities Commission to deliver power
to the local or regional power grid (excluding
generators that are connected to combustion
units that are subject to subpart D of the
part). In the final rule, this criterion is
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revised to state that the stationary fuel
combustion source contains at least one
combustion unit connected to a fuel-fired
electric generator that is owned or operated
by an entity that is subject to regulation of
customer billing rates by the public utility
commission (excluding generators that are
connected to combustion units that are
subject to subpart D of the part).
• For sources that do not meet the criteria
specified in 40 CFR 98.36(f), the EPA has
added an option in 40 CFR 98.3(d)(3)(v) and
40 CFR 98.36(a) to either elect to use IVT or,
if potential disclosure is not a concern to the
reporters, to report these inputs to emission
equations. For reporting year 2014, if a
subpart C source elects not to use IVT, the
source is required to report their subpart C
inputs to emission equations for which
reporting was deferred to 2015 for reporting
years 2010 through 2014 in the reporting year
2014 annual report. If this source is not
required to use IVT for other subparts listed
in Table 2 of this preamble, the source would
not be subject to the extended recordkeeping
requirements of 5 years.9
• The EPA has revised the proposed
amendments to 40 CFR 98.5(b) to add an
option for reporters subject to using IVT to
enter an explanation into IVT in cases where
IVT has produced a warning message for an
entered data value (e.g., the value is outside
the EPA’s expected range), but the reporter
believes that the data value is accurate as
entered.
• The EPA has revised its method for
specifying which inputs to emission
equations must be entered into IVT. At
proposal, 40 CFR 98.5(b) indicated which
inputs to emission equations must be entered
into IVT by referring to equations specified
in proposed Table A–8 of Part 98. In the final
rule, the EPA identifies the inputs to
emission equations that must be entered into
IVT in a ‘‘verification software records’’
provision in the recordkeeping section of
each affected subpart. Therefore, proposed
Table A–8 is not included in the final rule.
Refer to Section II.C of this preamble for
further discussion of these ‘‘verification
software records’’ provisions.
Additionally, in response to public
comments, the EPA is making changes
related to implementation of the
alternative verification approach. These
changes do not involve regulatory
amendments to Part 98, but do improve
the design and use of the IVT and
address questions and concerns raised
by commenters. A summary of these
changes follows.
IVT Testing. The EPA will provide an
opportunity well in advance of the
March 2015 reporting deadline for
stakeholders to test and provide
feedback to the EPA on IVT for the 23
subparts addressed in this final action
via a compliance assistance open testing
period, or ‘‘sandbox.’’ Refer to Section
9 If the source is required to use IVT for other
subparts, the source must retain records for all
subparts (including subpart C) for a period of 5
years.
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II.A.3 of this preamble for a description
of ‘‘sandbox’’ testing and further
discussion of this opportunity. The EPA
encourages all stakeholders to
participate in the sandbox testing
because this testing will provide a
valuable opportunity for reporters to
preview and familiarize themselves
with the new application for all
applicable subparts before the open
reporting period begins, typically in
mid-February. The EPA intends to offer
sandbox testing from October through
December 2014, providing testing by
subpart on a rolling basis. Participants
who identify an error in IVT will have
the opportunity to provide feedback to
the EPA regarding their IVT testing
experience. Such feedback will ensure a
higher quality IVT for reporting in early
2015 and subsequent years. For details
on the sandbox testing, including a
schedule of when testing will occur for
each of the 23 subparts, please see
https://www.epa.gov/ghgreporting/
reporters/training/inputs-verifier.html.
IVT Design. In response to commenter
input, the EPA has revised the IVT
design to improve the ease of use and
the efficiency of the data entry process,
instructions, help screens, warnings,
and error messages. Refer to Section
II.A.3 of this preamble for further
discussion of these revisions. See the
EPA’s comment response document in
Docket ID No. EPA–HQ–OAR–2010–
0929 for a list of all public comments
regarding additional improvements to
IVT and the EPA’s responses, including
revisions to address errors identified by
commenters.
3. Summary of Comments and
Responses
This section provides a brief summary
of the significant comments received in
response to the proposed requirement to
use IVT, and the EPA’s responses. The
EPA’s comment response document in
Docket ID No. EPA–HQ–OAR–2010–
0929 provides a complete listing of all
related comments and the EPA’s
responses.
Comment: One commenter asserted
that the verification approach that the
EPA has used during the deferral period
has been successful, is efficient, and
should be adopted as EPA’s permanent
approach for verification, rather than
requiring facilities to use IVT. The
commenter asserted that, during this
deferral period, verification checks have
been conducted through e-GGRT on
data that have been reported to the EPA.
The commenter believes that while the
EPA has identified reporting errors
during these years, such concerns will
become increasingly rare as reporters
become more familiar with and are able
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to streamline the reporting process. The
commenter asserted that in situations
where the EPA is not able to verify the
data, the EPA can continue to follow-up
with facilities. The commenter also
asserted that the interim verification
approach used by the EPA has strong
parallels to other ‘‘certification’’
requirements that the EPA has long
deemed sufficient to ensure compliance
in similar circumstances. Finally, the
commenter asserted that because the
interim verification approach has been
successful, the risk of entering CBI into
an unproven system that has the
potential to be insecure is not justified.
Response: As the commenter notes,
the EPA has been conducting
verification checks using data other than
inputs to emission equations. Although
the checks to date gave us some
confidence in the submitted data, the
verification approach being finalized in
this action allows for more precise
checks to be conducted and therefore a
more robust verification approach.
Specifically, requiring that the inputs to
emission equations (for which
disclosure concerns were identified) be
entered into IVT allows the tool to
verify reported emissions by calculating
the emission equation results as well as
conducting verification checks on the
entered inputs to emission equations.
These checks are designed to ensure
that calculations are performed correctly
by the reporter and that appropriate data
were used to calculate emissions. While
the EPA agrees that over time,
commenters will become more familiar
with e-GGRT and IVT and the increased
familiarity may help to reduce reporting
errors, it is important that the Agency’s
verification process is as robust as it can
be to ensure the accuracy of the
submitted data. The verification
approach finalized in this action will
accomplish that goal while at the same
time addressing the concerns regarding
potential disclosure of sensitive
information.
Regarding the comment that the
verification approach used during the
deferral period is similar to ‘‘other
certification requirements that the EPA
has long deemed sufficient to ensure
compliance in similar circumstances,’’ it
is not clear which programs to which
the commenter is referring. As the EPA
stated in the memorandum ‘‘Evaluation
of Alternative Verification Approaches
For Greenhouse Gas Reporting Rule
Subparts for which Reporting of Inputs
to Emission Equations was Deferred to
March 31, 2015’’ (EPA–HQ–OAR–2010–
0929–0048), the EPA considered the
verification approach used by the EPA’s
Toxics Release Inventory (TRI) program,
which requires self-certification that the
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information reported is accurate, and
includes electronic data checks and
follow-up conducted by the EPA.
However, the TRI is a different type of
program than the GHGRP in that it does
not require specific monitoring and
calculation approaches, but rather
requires that estimates be based on the
best available information. In contrast,
the GHGRP prescribes a set of specific
calculation methods, or equations, for
individual source categories, processes,
and emission units, so that data
collected from multiple facilities are
consistent and comparable. Given the
additional specification required by the
GHGRP, the EPA concluded that the
more precise checks that will be
conducted by IVT are warranted.
The EPA addresses the comment
about IVT’s security and the assertion
that the system is unproven later in this
section of the preamble.
Comment: One commenter expressed
concern regarding the language used in
40 CFR 98.36(f)(1), indicating that the
language is vague and confusing. The
commenter stated that the phrase
‘‘granted access by the Public Utilities
Commission (PUC) to deliver power to
the local or regional electric power grid’’
could result in confusion or overlybroad reporting of CBI. The commenter
explained that some jurisdictions
impose only registration and other
ministerial requirements on units
granted access; whereas some
jurisdictions ‘‘engage in direct price and
other regulation of vertically integrated
and other utility operations that grant or
restrict franchise rights.’’ The
commenter cautioned that it is not clear
what level of regulation constitutes a
‘‘grant of access’’ under the rule,
explaining that all units, regardless of
type or regulatory regime, require
‘‘access’’ to a local or regional grid in
some form to make off-site sales of
power.
The commenter recommended that
the EPA avoid misinterpretation of 40
CFR 98.36(f) by clarifying in the final
rule that only units subject to regulation
as ‘‘public utilities under the laws and
regulations of a given state’’ (as opposed
to those under other Federal regulations
or not otherwise subject to State utility
commission oversight of operations and
rates as ‘‘public utilities’’) should be
considered as having been ‘‘granted
access by the Public Utilities
Commission to deliver power to the
local or regional electric power grid.’’
The commenter also stated that it is
incorrect to assume that information
provided to PUCs or similar institutions
is also disclosed publicly, and that the
EPA should clarify how it will address
such information if the PUC treats that
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63757
information as CBI or it is otherwise not
available to the public.
Response: For the reasons stated
below, the EPA agrees that the proposed
40 CFR 98.36(f)(1) does not clearly
define the combustion units that must
report subpart C inputs to emission
equations for which reporting was
deferred to 2015. Proposed 40 CFR
98.36(f) specified that: (1) The stationary
combustion source contains at least one
combustion unit connected to a fuelfired electric generator that has been
granted access by the Public Utilities
Commission to deliver power to the
local or regional electric power grid
(excluding generators that are connected
to combustion units that are subject to
subpart D of the part); and (2) The
stationary fuel combustion source is
located at a facility for which the sum
of the nameplate capacities for all
electric generators specified in
paragraph (f)(1) of the section is greater
than or equal to 1 megawatt electric
output.10 As indicated in the
memorandum, ‘‘Evaluation of
Competitive Harm from Disclosure of
‘Inputs to Equations’ Data Elements
Deferred to March 31, 2015,’’ August
2013 (refer to Docket ID No. EPA–HQ–
OAR–2010–0929), the EPA had found
no disclosure concerns for any
combustion source meeting the
proposed criteria in 40 CFR 98.36(f)(1),
including combustion sources owned or
operated both by power producers
whose primary purpose is selling
electricity and by power producers
whose primary purpose is not selling
electricity. It was the EPA’s
understanding at the time that both
types of power producers are granted
access to the grid by the PUC, that such
grant requires that the associated
consumer billing rates be regulated by
PUCs and that, therefore, the power
producers experience a high level of
transparency due to the practice of the
owner or operator disclosing fuel costs
to the PUC through ratemaking
procedures. Based on the above
understanding, the EPA had concluded
that releasing these data would not
reveal any proprietary information
about facility or process performance,
design, and operation; cost to do
business; raw material usage; or
production.
In light of the comment above, the
EPA further investigated the reporting
obligations of the owner or operators of
power producers to PUCs. Based on
these investigations, the EPA
established that the PUC does not
10 We received no comment on the proposed
criterion (2), and we are therefore finalizing that
criterion as proposed.
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typically grant access to the grid, but
sometimes requires utilities to grant
other power producers access to the
grid. The EPA recognized that not all
power producers that are granted access
to the grid are subject to regulation of
rates by PUCs, and therefore some of
these power producers do not
experience the high level of
transparency that would be associated
with the disclosure of fuel costs to the
PUC through ratemaking procedures. As
a result, the EPA cannot conclude that
there would be no disclosure concerns
associated with the release of these data
for power producers based on their
connectivity to the grid, given that some
power producers connected to the grid
are not subject to regulation of rates by
the PUC. The new understanding and
resulting harm analysis described above
are also reflected in the memorandum
‘‘Final Evaluation of Competitive Harm
from Disclosure of ‘Inputs to Equations’
Data Elements Deferred to March 31,
2015,’’ September 2014 (refer to Docket
ID No. EPA–HQ–OAR–2010–0929).
Given that the EPA found no disclosure
concerns with respect to those power
producers subject to regulatory
oversight of consumer billing rates by a
PUC, the EPA has changed proposed 40
CFR 98.36(f)(1) in the final rule to more
clearly and accurately describe the
combustion units that must report as
those units owned or operated by an
entity that is subject to regulation of
customer billing rates by the public
utility commission. Power producers
subject to regulatory oversight of
consumer billing rates by a PUC include
investor-owned utilities (IOUs) (i.e., the
most common type of utility regulated
by PUCs), non-utility generators, and
consumer-owned utilities (COUs) that
are subject to regulation of customer
billing rates by a PUC. Because
industrial plants that generate electricity
are not subject to regulation of customer
billing rates by a PUC, power producers
owned or operated by industrial plants
would not meet this revised reporting
criterion in 40 CFR 98.36(f)(1).
The commenter recommended
replacing the proposed language
‘‘granted access by the PUC to deliver
power to the grid’’ with ‘‘subject to
regulation as a public utility under the
laws and regulations of a given state.’’
The terminology ‘‘public utility’’ could
be interpreted to refer only to COUs,
which are sometimes called ‘‘public
power,’’ but excluding IOUs, which
would not be appropriate because IOUs
are subject to regulatory oversight of
consumer billing rates by a PUC and
therefore experience a high level of
transparency. Also, the commenter’s
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suggested phrase ‘‘under the laws and
regulations of a given state’’ could be
interpreted as meaning any state law or
regulation, regardless of whether they
are associated with PUCs. Given that
virtually all facilities generating
electricity are governed to some degree
by other state laws and regulations, and
those regulated by the PUC might not be
regulated for ratemaking purposes, this
suggested text would expand the
reporting requirement beyond those
facilities subject to regulation of rates by
the PUC, which is the basis for our
finding of transparency. Accordingly,
the EPA has determined that the rule
text suggested by the commenter was
overly broad. The EPA has determined
that the text ‘‘owned by an entity subject
to regulation of customer billing rates by
a public utility commission’’ more
accurately describes the power
producers for which we found no
disclosure concerns and therefore must
report the subpart C inputs to emission
equations for which reporting was
deferred until 2015.
The EPA agrees with the comment
that not all information that is provided
to PUCs may necessarily be made
available to the public; however, the
EPA believes that power producers
subject to regulation of rates by PUCs
generally experience a high level of
transparency. The EPA has received no
comment refuting the high level of
transparency or stating that there are
disclosure concerns associated with
these subpart C inputs to emission
equations. The final criterion (‘‘subject
to regulation of customer billing rates by
PUCs’’) was formulated to capture
power producers that are utilities in
states with so-called ‘‘regulated’’
electricity markets. In these states,
power producers are generally owned
by vertically integrated utilities, which
operate as monopolies and sell power to
customers at rates that are established
through PUC proceedings. Given this
monopolistic market for power
producers subject to regulation of rates
by PUCs, the EPA does not identify any
disclosure concerns with reporting the
inputs to emission equations in subpart
C for reporters that meet the final
criterion. In contrast, in ‘‘deregulated’’
or ‘‘restructured’’ states that have
unbundled generation and delivery,
independent power producers may
compete to sell electricity, which is then
delivered through a regulated
distribution utility. These independent
producers are not subject to PUC
ratemaking procedures, and they will
therefore not be required to report
subpart C inputs to emission equation
data for their combustion units. For the
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reasons stated above, the EPA concludes
that clarifying the scope of the criteria
to be those power producers that are
subject to regulation of customer billing
rates by PUCs accurately specifies
facilities identified as having no
disclosure concerns with the release of
these data.
Specifically, the final 40 CFR 98.36(f)
provides the following criteria to
indicate which stationary fuel
combustion sources (e.g., individual
unit, aggregation of units, common pipe,
or common stack) must report their
inputs to emission equations for which
reporting was deferred to 2015: (1) The
stationary fuel combustion source
contains at least one combustion unit
connected to a fuel-fired electric
generator owned or operated by an
entity that is subject to regulation of
customer billing rates by the public
utility commission (excluding
generators that are connected to
combustion units that are subject to
subpart D of the part); and (2) The
stationary fuel combustion source is
located at a facility for which the sum
of the nameplate capacities for all
electric generators specified in
paragraph (f)(1) of the section is greater
than or equal to 1 megawatt electric
output. For any stationary fuel
combustion source subject to subpart C
that does not meet these criteria, the
final rule provides an option for the
source either to use IVT starting in
reporting year 2014 or to report these
data to the EPA, including reporting the
data specified in revised Table A–7 for
reporting years 2010 through 2013.11
Refer to the comment summary and the
EPA’s response immediately following
this response for further discussion
about this new option.
Comment: Three commenters asserted
that the EPA not require them to use
IVT. They asserted that reporters under
subpart HH (municipal solid waste
landfills) have not expressed disclosure
concerns regarding inputs to equations
during comment periods for previous
rulemakings, and that the proposal did
not take this into consideration as it did
not include an option to allow reporters
to submit data to the EPA rather than
use IVT. They further asserted that
under the proposal, they would be
required to use IVT for only a single
equation input (quantity of fuel
combusted under subpart C, Tier 1), and
that the burden to their industry
associated with use of IVT is not
warranted, given that the single
11 As discussed above, the e-GGRT will require
that such reporter waive any confidentiality claim
for its facility’s inputs to emission equations before
such data can be entered into e-GGRT.
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equation input is associated with less
than 1 percent of reported GHG
emissions from the industry. The
commenters expressed concern that
imposing the proposed requirements
associated with IVT on landfills would
be burdensome, and indicated that they
would be willing to report the single
data element to the EPA. They
recommended that the EPA exclude Tier
1 reporters from being required to use
IVT.
Response: The IVT requirements in
the final amendments for subpart C,
which covers a wide range of industries,
address disclosure concerns identified
for certain ‘‘inputs to emission
equations’’ data elements. However,
these commenters expressed that they
do not have disclosure concerns with
their fuel use data, the single input
required for Tier 1 reporting under
subpart C. For these commenters who
are not concerned with reporting their
fuel use quantity under subpart C, the
EPA sees no reason to insist that they
use IVT instead of reporting such data.
In addition, the fact that these
commenters have not identified
disclosure concerns with any inputs to
equations suggests that it is likely that
landfills using other subpart C
calculation methods besides Tier 1 may
similarly prefer to report inputs to
emission equations data elements under
subpart C instead of using the IVT.
Further, given the wide range of
industries reporting under subpart C, it
is possible that there are other
industries that do not have disclosure
concerns with fuel quantity and other
equation inputs for subpart C
calculation methods. For any such
subpart C reporter, the EPA similarly
sees no reason to insist that it use IVT
instead of reporting such data.
Accordingly, the EPA is revising 40 CFR
98.36 to make it optional for subpart C
sources that do not meet the criteria for
electric generators in 40 CFR 98.36(f) 12
to use IVT. As such, under the final
rule, a subpart C reporter, except for
those meeting the criteria of 40 CFR
98.36(f), who does not have disclosure
concerns for the subpart C inputs to
emission equation data elements may
waive confidentiality claims and report
such data instead of using IVT. Before
e-GGRT will accept entry of these inputs
to emission equations data, it will
require that the reporter waive
confidentiality claims of such data.
If a subpart C source elects to report
these data for reporting year 2014, the
12 Sources meeting the criteria in 40 CFR 98.36(f)
must report their subpart C inputs to emission
equations that were deferred from reporting until
2015.
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source is required to report these data
for reporting years 2010 through 2013 as
part of the reporting year 2014 annual
report. If a source elects to use IVT in
reporting year 2014, and then the source
elects in a future year to report these
data, the reporter will not be obligated
to report these data for any prior year.
Comment: Six commenters
recommended that the EPA allow
reporters time to test IVT prior to the
start of reporting for reporting year
2014, using a fully functional
‘‘sandbox’’ testing environment similar
to that used previously for e-GGRT
testing. These commenters urged the
EPA to allow sandbox testing for each
affected subpart, arguing that the
subpart X prototype developed for
commenter review at proposal allowed
them to review only the design and
functionality of the prototype for
subpart X. They stressed that additional
testing is necessary to ensure IVT works
for all affected subparts. Two
commenters noted that sandbox testing
would allow errors in the software to be
found and corrected prior to
implementation. Commenters also noted
that sandbox testing of each subpart
would enable them to determine
whether IVT calculates emission
equation results correctly and stated
that sandbox testing would provide an
opportunity for reporters to compare
results of the calculations in IVT against
the values calculated using the optional
calculation spreadsheets. Other
commenters requested sandbox testing
because it would allow them to review
and comment on the verification ranges
incorporated in IVT. One commenter
stated that testing could provide
important information that may result in
improvements to IVT that obviate the
need for reporters to over-ride error
messages. Other commenters expressed
concern about protection of CBI and
concluded that rigorous testing of each
affected subpart is critical to ensuring
confidential data are protected.
Four commenters recommended that
the EPA allow sandbox testing of the
XML version of IVT. These commenters
noted that the pilot IVT provided very
limited testing for reporters using the
XML option. They noted that the testing
was limited to only one subpart, that
only one sample XML file was provided
for testing, and that the EPA did not
provide the XML schema. Two
commenters requested that the EPA
provide additional time for reporters to
review and test the XML IVT for each
subpart. The complexity of the XML
option, they argue, makes thorough
testing of any XML schema essential.
Eight commenters asserted that the
pilot tool available during the comment
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63759
period for the subpart X mass balance
methodology was too limited, and as a
result provided limited value in
assessing the burden of the tool for the
other methodologies and subparts that
would be required to use the tool. Two
of these commenters noted that because
subpart X has different inputs to
equation data elements and equations
than other subparts, they were unable to
provide adequate feedback on the tool
during the comment period. Two of
these commenters suggested that the
EPA develop a pilot reporting tool for
their subpart of interest, and re-propose
the verification tool for that subpart to
provide ample opportunity to provide
public comment on the burden
associated with the use of the tool.
Three of these commenters asserted that
because the pilot testing for subpart X
was limited to the mass balance
methodology, it provided limited value
to assess the ease of use and burden of
the tool for the other methodologies
within subpart X.
Two commenters indicated that
reporters need more time in 2015 to
complete their annual reports than in
previous years. One commenter stated
that in the past, the EPA has provided
industry just a handful of weeks before
the reporting deadline to update all of
its data systems, input all of its data into
e-GGRT, correct any errors, complete
internal reviews of the reports, and to
submit the reports. The commenter
noted that the short timeframe was
extremely challenging in past years.
Both commenters indicated that it
would be unacceptable for the EPA to
provide another short timeframe in
2015, considering the new requirements
to back-report 2010 through 2013 data
and use the new IVT. One commenter
requested that the inputs verification
tool be fully functional by January 1,
2015 to allow reporters to undergo the
required software development so that
their systems accurately ‘‘sync’’ with the
new version of e-GGRT. The commenter
suggested that the EPA include language
in Subpart A to indicate that for each
day past January 1, 2015 that the
upgraded e-GGRT is not available, the
reporting deadline will be extended by
one day.
Response: During the public comment
period, the EPA provided a subpart X
prototype for testing and comment. This
prototype allowed reporters to review
the overall design, structure, and
functionality of IVT, which applies to
all subparts that are to use the tool. It
was not necessary to have a prototype
for every subpart during the open
comment period because the overall
design of IVT is the same irrespective of
the specific methodologies, or
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equations, in each subpart. Specifically,
the tool demonstrated the following
functions that apply to all subparts that
are to use the tool: How IVT functions
within e-GGRT, how to navigate from eGGRT to IVT and vice versa, how inputs
are entered into IVT, how IVT calculates
equation results based on the inputs to
emission equations entered, how an
emission equation result calculated in
IVT is transferred to the annual
reporting form in e-GGRT, how the
reporter may override an emission value
calculated by IVT, how the results of the
verification checks conducted in IVT
appear in the verification summary,
how a reporter may enter inputs to
emission equations into IVT over
multiple e-GGRT sessions without
having to start over each time the
reporter logs out of e-GGRT (by saving
them on their local computer), and how
to use the XML bulk upload feature
rather than using webforms. Reporters
were also able to generate the list of
inputs entered into IVT that must be
kept as a record, view the format of the
records file created, and test the
downloading of the records file for
recordkeeping purposes. These features
that were available for testing represent
all of the key functions of IVT.
Comments on any of the above features
received during the public comment
period would apply to all subparts that
are required to use IVT and not just the
subpart X prototype. The feedback
assisted the EPA in determining
improvements to the design and
functionality of IVT for all subparts with
the IVT requirement.
Although providing IVT for all
subparts during the comment period
was not necessary, the EPA agrees with
the commenters that both the EPA and
reporters would benefit from the
opportunity to test IVT for all applicable
subparts prior to the beginning of
reporting for reporting year 2014.
Accordingly, the EPA will offer
reporters an opportunity prior to the
beginning of the reporting year 2014
open reporting period (which is
typically in mid-February) to view and
provide feedback on the IVT modules
for all 23 subparts listed in Table 2 of
this preamble. The EPA will use a
sandbox testing environment similar to
that used previously for e-GGRT testing.
The EPA intends to offer sandbox
testing from October through December
2014, providing testing by subpart on a
rolling basis. For details on the sandbox
testing, including a schedule of when
testing will occur for each of the 23
subparts, please see https://
www.epa.gov/ghgreporting/reporters/
training/inputs-verifier.html. We are
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17:25 Oct 23, 2014
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confident that this sandbox testing
period will provide reporters the time
needed to sync their systems with IVT
prior to the open reporting period for
reporting year 2014, and submit their
reports by March 31, 2015.
As previously provided for in the
2010 sandbox for testing of e-GGRT, the
sandbox environment for IVT will
provide participants an opportunity to
try IVT functions for all 23 subparts,
including navigating between IVT
screens, entering data, testing the XML
uploading option (saving XML files to
local drives, and uploading XML files to
IVT), checking the built-in calculation
algorithms, and accessing Help content.
Participants will be assigned a test
facility for which they will be able to
enter mock data for any IVT subpart
module they wish to test.
Sandbox participants may notify the
EPA should they identify an error, bug,
or technical glitch in IVT. The EPA
plans to conduct extensive testing to
ensure that IVT calculates the emissions
correctly for all subparts; however,
should any calculation or other subpartspecific errors remain, these can be
detected during the sandbox period and
addressed prior to the open reporting
period. Because extensive internal
testing will have been conducted prior
to the compliance assistance ‘‘sandbox’’
being made available, the EPA does not
anticipate major issues during the
sandbox period that cannot be
addressed prior to the open reporting
period.
Regarding the comment that
additional time is needed due to the
back-reporting of a significant amount of
information, the EPA notes that, with
the exception of subpart W, only a
handful of inputs to equations in each
subpart must be back-reported for years
2010 through 2013 (i.e., reporters
typically will have no more than 10
inputs to equations in each of these
subparts to report for these years.)
Further, as discussed above, because the
system will have gone through extensive
testing followed by an IVT sandbox
period for reporters to sync their
systems with IVT before it is opened for
reporting, we are confident that the
reporters will have sufficient time to
submit their reports, including back
reporting a small number of inputs for
reporting years 2010 through 2013. For
subpart W, which has a substantial
number of inputs to be back-reported to
the EPA for these years, the EPA plans
to use a spreadsheet to collect this data,
and anticipates publishing the
spreadsheet in October 2014. This will
allow facilities to begin data entry into
the spreadsheet prior to the open
reporting period. The spreadsheet can
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then be uploaded to e-GGRT during the
open reporting season. Refer to Section
II.B.1 of this preamble for a discussion
of the timing of entering inputs to
emission equations for reporting years
2011 through 2013 for subpart W. In
light of the extensive testing and the
sandbox period, which will allow
reporters to sync their systems with IVT
prior to the open reporting period, and
the EPA’s plans to make the subpart W
spreadsheet for 2010 through 2013
available in October, we have
determined that the typical reporting
period of approximately six weeks is
sufficient.
As requested by commenters, sandbox
participants may provide input on the
ranges that the EPA has identified for
the reasonable range verification checks
on the inputs entered into IVT. As is the
case for all expected range checks used
as part of the electronic verification
process, the EPA will set initial ranges
and will continually refine ranges as
additional information is obtained.
Should the EPA receive feedback on
expected range checks during the
sandbox period, the EPA will review the
feedback and adjust the ranges prior to
the open reporting period as
appropriate. Also, as is the case for all
expected range checks conducted in eGGRT, the reporter may enter any value
into IVT regardless of the reasonable
range. The expected ranges are not used
by the EPA as a final determination
regarding data quality or compliance;
rather, they are used as a first step of the
verification process and are further
investigated. Finally, as is discussed in
more detail later in this section of this
preamble, during the reporting process,
the reporter will have the opportunity to
add a comment to the EPA associated
with individual verification warnings in
IVT. As a result, if reporters feel that an
explanation is needed as to why a
particular range was exceeded or that
the range within IVT needs to be
adjusted, they may do so as part of the
annual reporting process.
Regarding the comments on the XML
upload reporting option, the EPA notes
that during the public comment period,
we published an XML schema for the
IVT prototype, as well as two sample
files to be used with the prototype, an
XML Inputs Verifier file and an XML
Annual Report File. The sandbox that
will be available for IVT will also
include this XML upload reporting
option. For subparts with XML
reporters, the EPA will provide the XML
schema for the inputs to equations data
entered into IVT and example XML files
to use for testing the XML upload
approach. The EPA agrees that changes
to the XML schema need to be
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thoroughly tested, and the EPA plans to
do so prior to releasing the XML schema
for e-GGRT and IVT.
The EPA disagrees with the comments
that the pilot verification tool provided
at proposal for the mass balance
methodology in subpart X was of
limited value for assessing the burden of
use for other methodologies and
subparts required to use IVT. As
discussed in detail above, the overall
design of the IVT is the same
irrespective of the differences in
methodologies and subparts.
Accordingly, the subpart X prototype
allowed reporters to review the overall
design, structure, and functionality of
IVT for all subparts that are to use the
tool. Based on their experience with the
subpart X prototype, reporters may
assess the burden associated with other
subparts by comparing the number and
complexity of equations in other
subparts to the equations in subpart X.
Further, in the proposed Impacts
Analysis, ‘‘Assessment of Cost Impacts
of 2015 Inputs Proposal—Revisions to
Reporting, Recordkeeping, and
Verification Requirements Under the
Greenhouse Gas Reporting Program,’’
August 2013 (available in the EPA’s
Docket ID No. EPA–HQ–OAR–2010–
0929), the EPA stated that the burden
for entering inputs to equations into IVT
is no different than it would be to enter
them into e-GGRT for reporting to the
EPA. The EPA did not receive
comments on the proposed Impacts
analysis. For the reasons stated above,
we do not believe that it is necessary to
re-propose the tool with all subparts to
provide an opportunity to comment on
the burden of using the tool for all
subparts, as suggested by several
commenters. Refer to the next comment
and response for additional detail on the
specific comments provided to the EPA
on IVT design and functionality and
how the EPA is addressing those
comments.
Regarding the comment that rigorous
testing of each affected subpart is
critical to ensuring that data are
adequately protected, refer to comments
and responses later in this section on
how the EPA is ensuring that inputs
entered into IVT are not retained by the
EPA.
Comment: Many commenters
provided useful suggestions for
improvements to IVT. For example,
some commenters recommended IVT
include functions that allow reporters to
automatically populate web form fields
in situations where the data are reported
on a recurring basis (e.g., weekly,
monthly, etc.) and are likely to remain
constant over time. Other commenters
recommended IVT allow data to be
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copied from external spreadsheets or
other data files instead of being entered
individually into IVT. These
commenters noted that this approach
would save time and avoid unnecessary
transcription errors. Three commenters
recommended that IVT flag any data
entry errors related to the data being
outside an acceptable range directly
following data entry, rather than on a
separate screen. One of these
commenters requested that IVT should
provide more information regarding the
error triggered (e.g., whether the entered
data are above or below the expected
range). These commenters stressed that
alerting reporters to errors at the
moment of data entry would help
reporters identify errors more quickly.
Three commenters recommended an
additional comment field be added to
IVT that allows reporters to respond to
IVT error messages. They maintained
that this approach would streamline the
verification process and save time for
both the EPA and reporters by
potentially avoiding follow-up after the
report has been submitted to the EPA.
Response: The EPA has reviewed the
commenters’ suggested improvements to
IVT and, with the exception of one
suggestion described below, has
incorporated these improvements in
IVT. The EPA agrees with the suggestion
that reporters should have the ability to
automatically populate web form fields
in situations where the data required to
be entered were collected on a recurring
basis (e.g., weekly, monthly, etc.). For
example, in subpart X, for the gas
stream entry fields, reporters will be
able to automatically populate the
monthly carbon content and molecular
weight of the feedstock with the first
month’s values since those values may
remain constant in many cases. The
EPA anticipates that this change in IVT
will improve the efficiency of the data
entry process and reduce chances for
errors associated with manual entry.
Regarding the recommendation to allow
data to be copied from external
spreadsheets or other data files instead
of being entered individually into IVT,
the EPA agrees with commenters that
this capability would reduce burden
and errors associated with manual data
entry. For each data element for which
the reporter is required to enter values
collected at a frequency greater than
monthly, the EPA is providing an offline tool to convert spreadsheets to the
XML input format, for use with IVT.
The EPA has evaluated commenters’
concerns regarding the flagging of data
errors when they are entered into IVT.
As discussed in the proposed rule, IVT
provides ‘‘real-time’’ checks as data are
entered into IVT, similar to checks in e-
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63761
GGRT. The results of these checks,
called validation messages in IVT, will
be easily accessible within e-GGRT at
the time of entry. Although such
warnings will be on a separate screen,
there are direct links to such screens to
ensure that it is easy to navigate to IVT
to revise data as needed. This is the
same for all validation checks that are
currently conducted and displayed
within e-GGRT for all reporters.
Although we recognize the potential
usefulness of this suggestion, this type
of design change would require a
significant amount of resources, and
cannot be done prior to the reporting
period for reporting year 2014. The EPA
is always open to making changes to eGGRT and IVT over time, and may
consider whether it is feasible to show
validation messages on the same screen
on which the data are being entered
and, if so, whether to make such
adjustment in IVT.
The EPA agrees with commenters that
IVT should provide more information
regarding the error triggered (e.g.,
whether entered data are above or below
the expected range). Accordingly, in
response to these comments, IVT will
include an ‘‘out of range’’ message in
the verification summary that indicates
the range being used for each data
element entered as well as whether the
value entered was above or below the
range. We anticipate that this additional
information will make the verification
process more efficient by reducing the
amount of follow-up required for
verification.
Finally, the EPA has considered
commenter recommendations for
addition of a comment field allowing
reporters to respond to IVT error
messages, explaining why a potential
error may not be an error, such as when
an entered equation input is found to be
out of range or has otherwise triggered
a message on the verification summary.
The EPA recognizes that, in some cases,
reporters may have inputs to emission
equations that are legitimately outside
of identified ranges due to unique
circumstances. In cases such as these,
we agree with commenters that this
option will reduce the amount of
follow-up required of the EPA and
reporters. As such, we have
implemented this change in IVT.
Comment: Eight commenters raised
security concerns regarding data entered
into IVT. These commenters wanted
additional information on how IVT
would protect sensitive data and
assurances that the data would not be
inadvertently disclosed. One commenter
stated that the security of IVT was
particularly important to facilities that
are required to comply with certain U.S.
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export control requirements. Four
commenters were concerned about
security during the period of transient
storage while the user is logged into IVT
of data. Some commenters asked for
clarification on where the data will
reside during this period, while other
commenters wanted the EPA to
demonstrate that data would only be
stored temporarily and that no data
would be retained during a system
crash. Some commenters wanted
additional information about who
would have access to the data during
this transient storage of the data. One
commenter wanted the EPA to confirm
that data with disclosure concerns
entered into IVT would not be
accessible to EPA personnel. Two
commenters were concerned that
outside vendors would have access to
data in the transient storage area. Three
commenters were concerned about the
security of data transmitted over the
Internet. Two commenters were
concerned that data could be
intercepted during transmission by
proxy servers and that data may still be
stored in these proxy servers after the
session ends. One commenter expressed
concern that use of XML files to input
data into IVT raises security concerns
because the format is easily readable,
containing the definitions needed to
decipher the data values. This
commenter was also concerned that
malicious or inadvertent HTML codes
can be inserted into XML files thereby
causing other security vulnerabilities.
Other commenters wanted the EPA to
confirm that IVT will not submit
confidential information over the
Internet.
Response: IVT is designed to operate
securely within e-GGRT, as a transient
process, such that data entered into IVT
would be temporarily housed in the IVT
system while the reporter is actively
using IVT. The IVT system is designed
so that entered inputs data are placed
only in session (server memory). The
entered inputs will not be saved to the
underlying EPA database, nor will they
be saved to the server’s file system. The
EPA has taken the following steps to
ensure that inputs data are not
mistakenly appended to data that are
saved (e.g., when saving validation and
verification summary records to the
database) and to ensure that information
saved to the server logs does not contain
user-entered inputs data. IVT has not
been configured to use the server’s file
system to temporarily save files. Instead,
IVT is configured only to use memory
for transient housing of inputs data
while the reporter is actively using IVT.
This configuration applies to inputs
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data entered into IVT webforms or data
uploaded from a local ‘inputs’ file
through the IVT webforms, as well as
inputs data uploaded through the XML
upload process. As with data entered
through the webform, IVT will not save
uploaded XML files to the underlying
EPA database or to the server’s file
system, but will only retain the data in
server memory for the duration of the
session. Uploaded XML files will be
validated against a published schema
definition (i.e., published document
prescribing the required format of the
file), so in many cases XML files
containing ‘‘malicious or inadvertent
HTML codes’’ would be rejected by the
system as not being well-formed. If
‘‘malicious or inadvertent HTML codes’’
were inserted into an XML in a manner
that did not render it invalid, the file
would be rejected by a process that
inspects uploaded files for script tags.
Therefore, the system is not vulnerable
to any potential HTML code appended
to these files. The entered inputs to
emission equations are then erased
when the user’s session with e-GGRT
ends.
Regarding the comments that
unauthorized persons may be able to
access data that are temporarily in
session while the reporter is actively
using IVT and the concerns with
transmission of data over the Internet
and potential data interception, the EPA
complies with the strict security
procedures and guidance governing
access to federal data servers established
by the National Institutes of Standards
and Technology (NIST) and in
accordance with the Federal
Information Security Management Act
of 2002 (FISMA). All EPA information
systems must meet the security
requirements defined in the NIST
Special Publication 800–53.13
Adherence to the NIST Federal
Information Systems requirements are
intended to protect EPA information
systems, including e-GGRT, from a
diverse set of threats including hostile
cyber-attacks, natural disasters,
structural failures, and human errors. As
such, the program keeps a security plan
up to date and conducts annual reviews
of the security controls. Furthermore, in
order to address the security concerns
noted by the commenter regarding
unauthorized access to data while it is
in session on the server, the EPA has
identified an additional security layer
beyond the NIST requirements to
encrypt the transient session data used
by the server while the reporter is
actively using IVT. The session data will
be encrypted with a key unique to that
13 https://csrc.nist.gov/publications/PubsSPs.html.
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user’s session. As a result, the EPA has
concluded that this suite of protections
is sufficient to address concerns raised
regarding the possibility of
unauthorized persons accessing data in
the transient housing area while the
reporter is actively using IVT.
Regarding the comments expressing
concern over transmission of data over
the Internet and potential data
interception, the inputs data entered by
a reporter in the web form are encrypted
via Transport Layer Security (TLS)
security protocol. TLS is a standard
security protocol providing an
encrypted link between the client (the
user’s browser) and the EPA’s servers.
TLS encryption ensures that entered
data are secure from the browser to the
EPA server. Normal Internet HTTP
communication sends data between the
client and the server in plain text.
Application of the TLS protocol to
HTTP communication (HTTPS) will
ensure that the inputs data are
encrypted rather than in plain text
while in transit. TLS encryption ensures
that data are completely secure from the
user’s browser to the e-GGRT servers.
Although data are transferred over the
Internet through proxy servers, due to
TLS encryption, the inputs data would
never be in plain text and could not be
deciphered by intermediate or proxy
servers. TLS is the standard security
protocol used to protect the transfer of
many types of sensitive data, including
credit card numbers, banking data, and
similar information requiring maximum
protection. The EPA does not use proxy
servers for its e-GGRT database, but
relies completely on dedicated server
space at the National Computer Center.
Therefore, TLS termination takes place
only on secured e-GGRT servers. The
EPA will always use these secure
servers (identified with the ‘‘https’’
prefix), which identify that the TLS
security protocol is applied, and IVT
will not incorporate inputs to emission
equations data into URLs. This also
applies to data transferred through XML
upload. XML data uploaded by a user
will also be encrypted via TLS security
protocol and will not be in plain text
while in transit. If intercepted while in
transit, the XML data would be
encrypted and therefore indecipherable.
These encrytion procedures will protect
data as they are transferred between the
client’s browser and the EPA’s servers.
IVT is also designed to protect data in
the instance of a system malfunction. In
the event of a system crash, all session
data are lost, including the session key
that would be capable of decrypting that
data. There are no processes in place to
save any information during a system
crash. Therefore, if a reporter enters data
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into IVT and the IVT system
malfunctions, the reporter’s data are not
stored in any way and cannot be
recovered.
Regarding an earlier comment that
IVT is an unproven system, the EPA
disagrees with this comment. The EPA
designed a prototype to demonstrate the
functionality of the tool. As stated
earlier in this preamble, this prototype
allowed reporters to review the overall
design, structure, and functionality of
IVT, which applies to all subparts
required to use the tool. For additional
information on this topic, please see the
discussion earlier in this preamble on
the prototype and ‘‘sandbox’’ testing.
In summary, the EPA has taken
several steps to add safeguards and to
build multiple security ‘‘layers’’ into the
system to prevent release of the data as
they are transmitted to the EPA’s servers
and temporarily housed while the user
is actively using IVT, but are not
retained in the server memory after the
user’s e-GGRT session ends. The EPA is
confident that the described security
procedures will adequately protect the
data entered into IVT.
Comment: Six commenters stated that
they consider equation input data
required to be entered into IVT to be CBI
and expressed concern that the EPA has
not gone far enough to legally protect
these data from public disclosure. Four
commenters described how these data
meet the five-part criteria specified in
40 CFR 2.208 for confidential treatment.
The commenters asserted that the EPA
recognized in its proposed rule that
these data are entitled to protection
from public disclosure. The commenters
questioned why, given this recognition,
the EPA has not afforded these data CBI
protection under the CAA. Two
commenters questioned why the EPA
was silent in its proposal as to whether
these data are to be afforded CBI
protection, instead focusing on revising
reporting and recordkeeping
requirements for these data.
Five of the commenters referred to a
continued risk associated with the
proposed verification approach that
equation inputs entered into IVT will be
available to the public or subject to
disclosure under the CAA. Four
commenters noted that section 114(c)
requires that the EPA must provide
‘‘emission data’’ to the public, if
requested. One of these commenters
described the continued risk as related
to the EPA’s inspection of facility
records, indicating that the EPA did not
include provisions in the proposal
explaining whether or how records of
equation input data entered into IVT are
to be afforded CBI protection or
otherwise protected from public
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disclosure as a result of Agency review
of records. The commenter further
stated that the proposed rule does not
set forth a requirement that the EPA can
access these data only through an
official enforcement-related action that
might afford the information privileged
status and provide some security from
public release, nor, according to the
commenter, are there provisions to
ensure that non-enforcement staff or
EPA contractors cannot access the data
and inadvertently release these data or
otherwise render the information
unprotected.
Three commenters further expressed
concern that by retaining any residual
risk of disclosure of equation input data
entered into IVT, 40 CFR part 98 could
potentially subject reporters to antitrust
liability. The commenters explained
that equation input data required to be
entered into IVT include cost- and
output-related information that is a
significant determinant of prices,
including information regarding fuel
production and distribution, which
provides details about plant operations
and inputs, nature, and location of
sources.
The six commenters contended that
the EPA must take further steps to
address the remaining ‘‘residual risk’’ of
disclosure under the CAA of equation
input data required to be entered into
IVT. Five of the commenters urged the
EPA to provide CBI protection to
equation inputs entered into IVT. Four
of the commenters urged the EPA to
address their concerns about disclosure
by explicitly stating in the final rule that
data entered into IVT qualify for
confidential treatment under the EPA’s
regulations and should not be deemed
‘‘emission data.’’ One commenter
requested that the EPA address their
concerns about disclosure by including
in the final rule language expressly
recognizing the CBI status of these data.
One commenter urged the EPA to
further address concerns about the
residual risk of disclosure by clarifying,
in the preamble to the final rule, that
equation input data entered into IVT
remain at all times in the possession of
the company entering the data and thus
are not subject to disclosure under any
other Federal law as a result of entry
into IVT.
Response: As explained below, the
EPA has not determined either in this
rulemaking or any other final action that
the equation input data entered into IVT
are entitled to CBI protection. The EPA
previously amended Part 98 to defer the
reporting of inputs to emission
equations data elements to allow the
Agency time to evaluate concerns raised
by some reporters regarding potential
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public disclosure of some of these data
elements and to take appropriate action
(76 FR 53057, August 25, 2011). The
four-step evaluation, which was
designed to inform the Agency whether
and what further action may be
appropriate, includes discussions of
potential disclosure scenarios as well as
consideration of alternative emission
calculation and verification methods.14
The evaluation does not include
establishing confidentiality status for
any data that the EPA assigns to the
inputs to emission equations category.
Any such determination must be made
in accordance with the CAA and the
EPA’s implementing regulations under
40 CFR part 2, subpart B. Based on the
evaluation,15 we had proposed, and are
now taking final action, to replace the
requirement to report certain inputs to
emission equations by 2015 with a
requirement to enter these data into IVT.
Although the final rule addresses
potential disclosure concerns with
respect to certain inputs by providing an
alternative verification tool (i.e., IVT)
instead of requiring reporting of these
inputs, it does not include final
confidentiality determinations for any
equation input data required to be
entered into IVT, nor has the EPA stated
anywhere in the rulemaking record that
such data are entitled to CBI protection.
The EPA therefore has not concluded
that any such data (inputs to emission
equations) are entitled to CBI protection.
Regarding the comments that
expressed concern about the EPA’s
ability to protect equation input data
entered into IVT, the concern may have
stemmed from a mistaken belief that the
EPA will have possession of such data.
That is not the case as explained in
detail here, as well as in the response to
comment immediately above, Section
II.A of the preamble to the proposed
rule (78 FR 55994, September 11, 2013),
and the memorandum ‘‘Technical
Approach and Design for Inputs
Verification Tool,’’ August 2013 (refer to
Docket ID No. EPA–HQ–OAR–2010–
14 For a description of the evaluation process,
please see the memorandum titled ‘‘Process for
Evaluating and Potentially Amending Part 98 Inputs
to Emission Equations’’ (Docket ID No. EPA–HQ–
OAR–2010–0929).
15 The results of the evaluation were documented
in the four following memoranda available in the
EPA’s Docket ID No. EPA–HQ–OAR–2010–0929:
‘‘Evaluation of Public Availability of Inputs to
Emission Equations for which Reporting was
Deferred to March 31, 2015,’’ August 2013;
‘‘Evaluation of Competitive Harm from Disclosure
of ‘Inputs to Equations’ Data Elements Deferred to
March 31, 2015,’’ August 2013; ‘‘Evaluation of
Alternative Calculation Methods,’’ August 2013;
‘‘Evaluation of Alternative Verification Approaches
For Greenhouse Gas Reporting Rule Subparts for
which Reporting of Inputs to Emission Equations
was Deferred to March 31, 2015,’’ August 2013.
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0929). During the time period that a
reporter is entering data (i.e., inputs to
emissions equations) into IVT, the EPA
will have no access to the data being
entered. Further, when a reporter logs
out of IVT, none of the data entered into
IVT are retained in the EPA’s electronic
systems. To address concerns about
potential release of these data via the
Internet, the EPA provides further
clarifications regarding the security of
IVT elsewhere in this section of the
preamble. Given that the EPA will have
no access to, nor possession of, data
entered into IVT, such data will not be
considered to be agency records as
defined by the Freedom of Information
Act or the Federal Records Act, and the
EPA cannot conceive, and the
commenters did not explain, which
federal law would require the EPA to
release information that it does not
have. For the same reason, the EPA also
rejects any suggestion that the Agency is
legally required to protect or make
confidentiality determinations for
equation input data entered into IVT.
The commenters have not identified any
law or regulation that requires the EPA
to protect data not in the EPA’s
possession, nor do we believe that any
such duty exists. For the reasons stated
above, we disagree with the comments
that the EPA must provide CBI
protection to equation input data
entered into IVT.
With respect to the commenter’s
inquiry on how records of equation
input data entered into IVT, which are
required to be kept on-site, are protected
from public disclosure as a result of
Agency review of records, we describe
below the verification process,
including follow-up on-site visits. As
described below, we do not envision
that an onsite review of records for
purposes of verifying emissions
reported using inputs that are entered
into IVT would necessitate or typically
involve collection of those records.
Rather, visual inspections would likely
suffice to determine whether or not a
facility is in compliance.
As described below, the EPA has
developed a robust electronic
verification and communication system
in order to ensure high quality data are
reported under the GHGRP, and the
verification summaries from IVT will be
integrated into that process. This
electronic verification approach helps to
minimize the need for on-site review
which helps to reduce the burden and
costs to the EPA and reporters. Likely
scenarios under which a GHGRP
inspection could occur due to
information received from the IVT
verification summaries are described
below. As described below, none of
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these activities typically involve the
EPA’s collection of the inputs entered
into the IVT.
As explained in the proposed rule, the
first step of the verification process will
include review of the verification
summary generated by the IVT in
conjunction with the results of the
verification checks that are currently
used on the annual report data. In the
event that the EPA’s review results in
remaining questions regarding data
quality, the EPA plans to follow-up with
the facility initially via email or phone
to determine whether a reporting error
has occurred. For example, if the EPA
learns from the facility that the facility’s
production doubled in a given year due
to unusually high demand, the EPA may
then understand the increase in
emissions, certain out of range
warnings, and determine that there is
not a data quality issue. If the EPA is
unable to resolve the issue via phone
and email, an on-site visit may be
needed. The EPA anticipates that these
visits would likely include a review of
the records required to be kept which,
as mentioned above, include the record
of the inputs to emission equations that
were entered into IVT as well as an
examination of the monitoring
equipment. Depending on the results of
the verification summary for a particular
facility, the EPA envisions two general
scenarios for these on-site visits. One
scenario would be that the verification
summary produced by IVT for a
particular facility indicates that the
reported emissions values matched the
values calculated by IVT but other
verification checks show that certain
inputs are outside the EPA’s expected
range(s). In that scenario, the EPA
anticipates that if a site visit is needed,
the site visit would focus on the
accuracy of the inputs entered into IVT.
To verify the accuracy of the inputs
entered into IVT, the EPA would likely
check whether data entered into IVT are
consistent with other records required
to be kept by the facility. For example,
if an input to an equation is a monthly
average of a value that is measured daily
by a particular on-site monitor and the
daily measured values are also required
records, the EPA may confirm that the
input entered into IVT is in fact the
average of the daily values. In addition,
the EPA may confirm that the on-site
monitor meets the specifications
prescribed in Part 98, such as
calibration and accuracy specifications.
If calibration and accuracy
specifications do not comply with Part
98 requirements, then a substantive
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error 16 would likely be identified, and
the facility would need to resubmit their
report. If the inputs at issue comport
with the on-site records, then there
would be no further action necessary by
either the EPA or the reporter. As
described above, because we envision
that verification would be completed
while on-site, we do not expect that
there would be a need to collect inputs
records.
In the second scenario, an on-site visit
that is conducted in a situation when
the verification summary produced by
IVT indicates a discrepancy between the
reported emissions and the emission
equation results calculated by IVT, the
EPA anticipates that the visit would
focus on determining the root cause of
the discrepancy. The EPA would ask the
facility to demonstrate how their
emissions calculations yielded a result
different from the one calculated
through the use of IVT. The EPA expects
that such discrepancy is likely a result
of mathematical error(s), which would
likely constitute a substantive error, and
the facility would need to resubmit their
report.
In both of these scenarios, the EPA
envisions that the discrepancies would
be resolved on-site and that collecting
the on-site records of inputs would not
be necessary. Despite the above, we do
not rule out the possibility that
collection of certain records could be
necessary under unique circumstances
not contemplated above. However, the
EPA does not know at this point what
records would be removed, the specific
circumstances under which they would
be collected and the reasons for such
collection, and therefore we cannot
address at this time how such records
would be treated. Should that occur, the
EPA will treat the collected information
according to applicable laws and
regulations.
Regarding the comments asserting
that 40 CFR part 98 could potentially
subject reporters to antitrust liability,
the EPA reiterates that information
entered into IVT is not reported to or
collected by the EPA. As a result, it does
not become an agency record and,
therefore, it is not subject to Freedom of
16 40 CFR 98.3(h)(3) defines substantive error as
an error that impacts the quantity of GHG emissions
reported or otherwise prevents the reported data
from being validated or verified. 40 CFR 98.3(h)
states that once a substantive error is identified, an
owner or operator shall, within 45 days of receipt
of the notification, either resubmit the report that,
for each identified substantive error, corrects the
identified substantive error (in accordance with the
applicable requirements of this part) or provide
information demonstrating that the previously
submitted report does not contain the identified
substantive error or that the identified error is not
a substantive error.
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Information Act or other required
disclosures related to agency records.
B. Removal of the Requirement To
Report Certain Data Elements
1. Summary of Final Amendments to
Part 98
The EPA is removing the requirement
to report 396 data elements in the 23
subparts listed in Table 2 of this
preamble. Of these 396 data elements
removed from reporting, 378 data
elements are removed due to disclosure
concerns and 18 data elements are
removed because these data elements
are redundant to other inputs being
reported or are no longer useful to be
reported to the EPA in the absence of
other inputs to emission equations that
will no longer be reported (refer to the
discussion below for further
explanation). Of the 378 data elements
removed from reporting due to
disclosure concerns, 324 data elements
will be entered into IVT.17 We are
finalizing the proposed amendments to
remove reporting requirements and
63765
require entry of these data elements into
IVT, with changes specified in Section
II.B.2 of this preamble.
Table 3 of this preamble provides a
summary of the number of data
elements removed from reporting for
each subpart. Refer to Table 1 in the
memorandum ‘‘Data Elements Deferred
to March 31, 2015: Final List of ‘Inputs
to Equations’ Data Elements Not To Be
Reported,’’ September 2014, (refer to
Docket ID No. EPA–HQ–OAR–2010–
0929) for a list of these 396 data
elements removed from reporting.
TABLE 3—SUBPARTS FOR WHICH REPORTING REQUIREMENTS ARE REMOVED
Number of inputs
to emission
equations for
which
reporting was
deferred to 2015
(‘‘deferred inputs’’)
Subpart
Number of
deferred inputs for
which reporting is
removed
b 26
b 26
21
29
8
16
13
3
15
7
86
10
9
6
21
c 19
75
4
31
3
10
2
8
4
11
29
8
14
13
3
12
7
85
10
9
6
21
c 19
70
4
28
3
4
2
8
4
C—General Stationary Fuel Combustion—Stationary fuel combustion sources excluding sources that
contain at least one combustion unit connected to a fuel-fired electric generator owned or operated
by an entity that is subject to regulation of customer billing rates by the public utility commission (excluding generators connected to combustion units subject to 40 CFR part 98, subpart D) and that
are located at a facility for which the sum of the nameplate capacities for all such electric generators
is greater than or equal to 1 megawatt electric output a .........................................................................
E—Adipic Acid Production ...........................................................................................................................
F—Aluminum Production .............................................................................................................................
G—Ammonia Manufacturing .......................................................................................................................
H—Cement Production ................................................................................................................................
K—Ferroalloy Production .............................................................................................................................
N—Glass Production ...................................................................................................................................
O—HCFC–22 Production and HFC–23 Destruction ...................................................................................
P—Hydrogen Production .............................................................................................................................
Q—Iron and Steel Production .....................................................................................................................
R—Lead Production ....................................................................................................................................
S—Lime Manufacturing ...............................................................................................................................
U—Miscellaneous Uses of Carbonate ........................................................................................................
V—Nitric Acid Production ............................................................................................................................
X—Petrochemical Production ......................................................................................................................
Y—Petroleum Refineries .............................................................................................................................
Z—Phosphoric Acid Production ...................................................................................................................
AA—Pulp and Paper Manufacturing ...........................................................................................................
BB—Silicon Carbide Production ..................................................................................................................
CC—Soda Ash Manufacturing ....................................................................................................................
EE—Titanium Dioxide Production ...............................................................................................................
GG—Zinc Production ...................................................................................................................................
TT—Industrial Waste Landfills .....................................................................................................................
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a These subpart C sources may elect to report inputs to emission equations rather than use IVT. Additionally, the reporting requirements are
not amended for stationary fuel combustion sources that contain at least one combustion unit connected to a fuel-fired electric generator owned
or operated by an entity that is subject to regulation of customer billing rates by the PUC (excluding generators connected to combustion units
subject to 40 CFR part 98, subpart D) and that are located at a facility for which the sum of the nameplate capacities for all such electric generators is greater than or equal to 1 megawatt electric output.
b Includes one deferred input to an emission equations, 40 CFR 98.3(d)(3)(v), which is specified in subpart A of part 98 and applies to only certain reporters under 40 CFR part 98, subpart C.
c There were 2 additional inputs to emission equations for which reporting was deferred to 2015; however, these two inputs are not reflected in
this table because the inputs were removed from Part 98 by a previous rulemaking (78 FR 71904, November 29, 2013).
The EPA is finalizing the proposed
amendments to exclude from reporting
18 deferred inputs to emission
equations for which no disclosure
concerns have been identified. As
explained in the preamble to the
proposed rule (78 FR 56005, September
11, 2013), while posing no disclosure
concerns, these data elements are
redundant to other inputs being
reported or are no longer useful to be
reported in the absence of other inputs
to emission equations that will no
longer be reported; they are not needed
to be reported to the EPA for data
verification and they are also not
helpful in informing future GHG policy
development. For further information
17 As mentioned above, there are 378 equation
inputs for which reporting was deferred to 2015 and
for which the EPA determined there are disclosure
concerns, and 324 of these equation inputs must be
entered into IVT. Fifty-four of the 378 equation
inputs do not need to be entered into IVT because
these equation inputs are redundant to other
equations inputs being entered into IVT or are
otherwise not needed for verification.
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on these 18 data elements, please see
the memorandum ‘‘Data Elements
Deferred to March 31, 2015: Final List
of Data Elements Not To Be Reported,’’
September 2014 (refer to Docket ID No.
EPA–HQ–OAR–2010–0929).
For the remaining inputs to emission
equations for which reporting was
deferred to 2015 for the 23 subparts
listed in Table 2 of this preamble, the
EPA is not amending the reporting
requirements because the EPA has not
identified disclosure concerns
associated with their public release, and
reporting of these data elements remains
useful to the EPA for data verification as
well as for informing future GHG policy
development. Deferral of reporting of
these inputs to emission equations
expires on March 31, 2015. As a result,
by March 31, 2015, 151 inputs to
emission equations must be reported for
reporting year 2014 and all prior
reporting years, except as described
below for six inputs to emission
equations in subpart W of part 98. These
151 data inputs must also be reported in
the annual report for all future reporting
years, except as specified below for the
six inputs to emission equations in
subpart W. Refer to Section III.A.3 of the
preamble to the proposed rule (78 FR
56005, September 11, 2013) for further
discussion about how 2010 through
2014 data will be included in the 2014
annual report. For a list of these 151
deferred inputs to emission equations
that will be reported, refer to Table 2 of
the memorandum cited above.
Additionally, to clarify which data
elements must be reported for previous
reporting years 2010 through 2013, the
EPA is finalizing its proposed revision
of Table A–7 of Part 98, ‘‘Data Elements
That Are Inputs To Emission Equations
And For Which The Reporting Deadline
Is March 31, 2015’’, which includes
these 151 inputs to emission equations
that must be reported.
For the purposes of reporting the
subpart W inputs for reporting years
2011 through 2014, the EPA plans to use
a spreadsheet format that will be
uploaded to e-GGRT. Recognizing the
substantial amount of information that
facilities will be entering into the
spreadsheet, the EPA anticipates
publishing the spreadsheet in October
2014. This will allow facilities to begin
data entry into the spreadsheet prior to
the open reporting period. The
spreadsheet can then be uploaded to eGGRT during the open reporting season.
For subpart W, the EPA is finalizing
the proposed decision to require subpart
W facilities to report all inputs to
emission equations for which reporting
was deferred to 2015; however, in the
final rule, in response to comment, the
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EPA is providing an option for reporters
to delay reporting of six of these inputs
to emission equations for two reporting
years for specific situations related to
two types of exploratory wells,
delineation and wildcat wells (as
defined in this final rule in 40 CFR
98.238), starting with reporting year
2013.
2. Summary of Changes Since Proposal
This section provides a brief summary
of changes since proposal to the
proposed requirement to use IVT. The
EPA’s rationale for these changes is
provided in Section II.A.3 as part of the
EPA’s response to the related
comment(s).
The changes to the list of data
elements removed from reporting and
required to be entered into IVT are as
follows:
• The proposed amendments, specifically
at 40 CFR 98.5(b), required that the inputs to
emission equations for the calculation
methods listed in the proposed Table A–8,
‘‘Calculation Methods For Which Inputs To
the Calculation Methods Must be Entered
Into Verification Software Specified By the
Administrator,’’ be entered into IVT. In the
final rule, the EPA removed the proposed
Table A–8 of part 98, replacing it with a new
‘‘verification software records’’ provision in
the recordkeeping section of each affected
subpart, which lists for each subpart each
equation input that must be entered into IVT.
• The proposed amendments required that
the data element in 40 CFR 98.196(b)(8) be
entered into IVT. After proposal, we
discovered that this data element is not an
input to an emission equation. Further, it is
no longer needed for verification because the
proposed new data element (40 CFR
98.196(b)(18)), which is being finalized in
this action, will be sufficient for verification
purposes. Therefore, in the final rule, we are
removing the reporting requirement for this
data element.
• The proposed amendments did not
require that the input to Equation F–4 be
entered into IVT, because this input is not
required to be reported under Part 98. Based
on a suggestion from a commenter, in the
final rule we are requiring that the input to
Equation F–4 be entered into IVT. Although
part 98 does not require reporting of this
input, the commenter stated that this input
should be entered into IVT, and we agree that
it is needed for calculating and verifying
emissions in subpart F.
• The EPA is replacing eight reporting
elements, which were incorrectly identified
in the final deferral rulemaking (76 FR 53057,
August 25, 2011) as inputs to Equations F–
2 and F–3 and were, therefore, incorrectly
proposed (78 FR 55994, September 11, 2013)
to be entered into IVT (instead of the correct
inputs to Equations F–2 and F–3). As a result
of a comment received, the EPA discovered
that it had previously misidentified eight
data elements as inputs to Equations F–2 and
F–3, mistakenly required and then deferred
their reporting under part 98, and recently
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mistakenly proposed their entry into IVT.
These misidentified data elements are annual
values; whereas the inputs to these two
equations are monthly values, which are not
required to be reported under Part 98. In light
of the error, the EPA is requiring in this final
rule that the correct inputs (monthly values)
for Equations F–2 and F–3 be entered into
IVT. Further, given that the EPA had
previously incorrectly required the reporting
of these eight annual values as inputs to
Equations F–2 and F–3, and given that the
actual inputs (i.e., the monthly values) for
Equations F–2 and F–3 will be entered into
IVT, the EPA does not need these eight
annual values for verification. The EPA is
therefore finalizing the removal of reporting
of these eight annual values for Equations F–
2 and F–3. Refer to the EPA’s comment
response document in Docket ID No. EPA–
HQ–OAR–2010–0929 for further discussion
of this comment supporting entry into IVT of
monthly input data for Equations F–2
through F–4 and the EPA’s response.
• For a given sub-basin, in the following
situations, the EPA is providing the option to
delay for two reporting years the reporting of
six data elements associated with delineation
or wildcat wells starting in reporting year
2013:
—For gas well completions or workovers
with hydraulic fracturing, where wildcat
wells and/or delineation wells are the only
wells in a sub-basin that can be used for
the measurement; and
—for onshore production storage tanks,
where wildcat wells and/or delineation
wells are the only wells in a sub-basin.
These six data elements are: (1) Measured
flow rate of backflow during well completion
(40 CFR 98.236(c)(6)(i)(B)); (2) measured flow
rate of backflow during well workover (40
CFR 98.236 (c)(6)(i)(D)); (3) total number of
days of backflow from all wells during
completions (40 CFR 98.236 (c)(6)(i)(E)); (4)
total number of days of backflow from all
wells during workovers (40 CFR 98.236
(c)(6)(i)(F)); (5) total volume of oil from all
wellhead separators sent to tank(s) in barrels
per year (40 CFR 98.236(c)(8)(i)(F)); and (6)
total volume of sales oil from all wells in
barrels per year (40 CFR 98.236(c)(8)(ii)(A)).
For reporting years 2011 and 2012, the two
year delay would still require reporting by
March 31, 2015. As a result, there is no need
to delay reporting for these two reporting
years. Refer to Section II.B.3 of this preamble
for the EPA’s rationale for this decision. If the
2-year delay in reporting is used, the reporter
must report the following information in the
current reporting year: indicate for each
delayed reporting element that one of the two
situations listed above is true (e.g., for gas
well completions or workovers with
hydraulic fracturing, wildcat wells and/or
delineation wells are the only wells in a subbasin that can be used for the measurement).
In addition, when reporters report the
delayed inputs to emission equations after
the 2 year delay, they must also report the
API well ID numbers for the applicable
wildcat and/or delineation wells in the subbasin for which the reporting element was
delayed.
• For purposes of part 98, the EPA has
added to 40 CFR 90.238 definitions of
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‘‘delineation well’’ and ‘‘wildcat well.’’
‘‘Delineation well’’ is defined as a well
drilled in order to determine the boundary of
a field or producing reservoir. ‘‘Wildcat well’’
is defined as a well outside known fields or
the first well drilled in an oil or gas field
where no other oil and gas production exists.
These definitions are consistent with the
definitions of ‘‘delineation well’’ and
‘‘wildcat well’’ in 40 CFR part 60, subpart
OOOO. Refer to Section II.B.2 of this
preamble for the EPA’s rationale for this
decision.
• The EPA has removed from reporting the
inputs to emission equations in 40 CFR
98.226(i), (j), (m)(4), (m)(5), and (p). These
data must be entered into IVT, except for 40
CFR 98.226(j). Refer to Section II.B.3 of this
preamble for the EPA’s rationale for this
decision.
3. Summary of Comments and
Responses
This section summarizes the
significant comments and responses
related to the proposed amendments to
remove reporting requirements and
require entry of data into IVT. The
EPA’s comment response document in
Docket ID No. EPA–HQ–OAR–2010–
0929 provides a complete listing of all
comments related to this topic and the
EPA’s responses.
Comment: One commenter asserted
that all 9 inputs to emission equations
reported under 40 CFR 98.226(i), (j),
(m)(4) and (5), and (p) would reveal
process design, process performance,
and operational efficiencies data
regarding a nitric acid train. The
commenter further noted that the EPA
indicated in section 2.2 of its
memorandum, ‘‘Evaluation of
Competitive Harm from Disclosure of
‘Inputs to Equations’ Data Elements
Deferred to March 31, 2015,’’ August
2013 (refer to Docket ID No. EPA–HQ–
OAR–2010–0929), that these types of
data could be used to determine facility
operational conditions and would,
therefore, have disclosure concerns.
Response: In the EPA’s proposed
harm analysis cited above in the
comment summary, the EPA stated that
the 9 inputs to emission equations
reported under 40 CFR 98.226(i), (j),
(m)(4) and (5), and (p) would not reveal
any proprietary information about cost
to do business, raw material usage,
production, or facility or process
performance, design, and operation, as
long as the emission factors required to
be reported in 40 CFR 98.226(m)(1) are
not reported. As a result of this
comment, the EPA further investigated
the operational conditions at current
nitric acid facilities, and considered the
specific case when there are nitric acid
facilities that have non-operational
nitric acid trains and others that are in
the process of installing or upgrading
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NOX control devices, some of which can
also serve as N2O abatement (i.e., nonselective catalytic reduction). In light of
this, the data reported under 40 CFR
98.226(i), (j), (m)(4), (m)(5), and (p), if
reported over a multiple-year period
where facilities are making changes to
the operational status of their trains
and/or abatement systems, could be
used to determine train-specific
conditions at the facility, such as
efficiency losses, equipment
degradation, changes in nitric acid
demand, and/or the installation of N2O
abatement technology. As a result, the
EPA agrees with the commenter that the
deferred inputs to emission equations
reported under 40 CFR 98.226(i), (j),
(m)(4), (m)(5), and (p) (destruction
efficiency and fraction control factor of
the abatement technology, abatement
utilization factor, and nitrous oxide
(N2O) concentration and volumetric
flow rate per test run during
performance test of each train) would
reveal information about process design,
process performance, and operational
efficiencies of a nitric acid train,
regardless of whether the emission
factors required to be reported in 40
CFR 98.226(m)(1) are not reported.
Therefore, the EPA has concluded that
these data have disclosure concerns,
and the EPA is removing these data
from the reporting requirements in the
final rule. Reporters will be required to
enter these data into IVT, except 40 CFR
98.226(j), which is not needed to be
entered into IVT for verification
purposes because IVT generates this
value using the inputs entered into
Equation V–2 and Equation V–2.
Comment: One commenter expressed
concern about reporting information on
exploratory wells in Subpart W,
especially when the wells are located in
step-out areas where no prior reporting
exists for a given sub-basin (including
vertical or horizontal wells). The
commenter explained that the problem
occurs when an exploratory well is the
sole well in a sub-basin (including
vertical or horizontal wells) and is not
reported in combination with other
wells, thereby shielding any individual
well’s contribution. The commenter
noted that its concerns are related to the
timing of releasing the information to
the public, as the commenter stated that
the information is most sensitive if it is
made available too early during the
exploration or initial development
stages. The commenter stated that the
success of a well in exploratory areas
could be inferred if detailed data are
provided to the public too soon during
the exploration and assessment period.
The commenter provided an example of
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63767
such an occurrence: An exploratory well
completed in December of the reporting
year, data reported to the EPA by end
of March of the following year and then
released by the EPA to the public within
a few months during the same year. The
commenter stated that early release of
data regarding operating characteristics
of such wells, including postflowback
flaring/venting volumes, could cause
competitive harm if made publicly
available too early.
The commenter noted that Federal
law and State codes allow companies to
designate as confidential the data
obtained from exploratory wells,
especially in new discovery areas or
areas that are being explored for
development. The commenter further
noted that the original intent of State oil
and gas commissions to allow
withholding of select drilling and
production information from early
release to the public was to allow
competitive exploration by searching for
new pockets of oil or gas and
experimenting with new tools and
techniques. The commenter stated that
releasing data on such wells through the
GHGRP—despite the fact that they are
held confidential by other regulatory
bodies—could cause substantial
competitive harm and lead to a loss of
investment value. The commenter
explained that competitive harm could
occur if the public could obtain detailed
high-resolution operational information
on a well-by-well basis and on a daily
or weekly basis.
The commenter requested that the
EPA categorically determine that all
information associated with exploratory
wells, with the exception of well ID and
location, be classified as CBI for a
period of at least 24 months from the
start of exploration. The commenter
recommended either of two suggested
approaches under the GHGRP: (1)
Companies would report all data to the
EPA as mandated by subpart W, but the
EPA would hold the reported data as
CBI and not include it in its public data
release for at least 24 months (this could
be accomplished by a flagging system
(or a ‘‘radio button’’) in e-GGRT that
could also allow for a short informative
text on why that particular well
information is to be maintained
confidential); or (2) the EPA could set
up a deferral system where initial data
on exploratory wells will be well ID and
location information and the remaining
data would be backfilled by companies
after a period of 24 months. The
commenter added that neither option
would require case-by-case review of
companies’ information, and both are
consistent with the approach taken by
state oil and gas commissions and are
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protective of companies’ commercial
investment interests.
Response: The EPA reviewed the
types of data identified by the
commenter as having disclosure
concerns for exploratory wells: ‘‘data
regarding operating characteristics . . .
including post-flowback flaring/venting
volumes.’’ In our proposed
memorandum ‘‘Evaluation of
Competitive Harm from Disclosure of
‘Inputs to Equations’ Data Elements
Deferred to March 31, 2015,’’ August
2013 (refer to Docket ID No. EPA–HQ–
OAR–2010–0929), the EPA stated
regarding exploratory wells, that
because onshore production data are
reported under the GHGRP at a subbasin level, as defined by county
boundaries, the data are aggregated to a
large enough scale that disclosure of the
data collected under subpart W would
not reveal any proprietary information
about the facility or cost to do business.
After further investigation in response
to the comment received, and review of
the state laws protecting these types of
data, the EPA has determined that, in
the following situations which were not
specifically considered in the proposed
rule, early public disclosure of certain
deferred inputs to emission equations
associated with wildcat wells and/or
delineation wells could reveal the well
productivity, thereby resulting in the
loss of investment value:
• For gas well completions or workovers
with hydraulic fracturing, where wildcat
wells and/or delineation wells are the only
wells in a sub-basin that can be used for the
measurement; and
• For onshore production storage tanks,
where wildcat wells and/or delineation wells
are the only wells in a sub-basin.
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The inputs to emission equations (for
which reporting was deferred to 2015)
that could reveal well productivity for
wildcat and/or delineation wells in the
applicable situations listed above are as
follows:
• For gas well completions or workovers
with hydraulic fracturing, the measured flow
rate of backflow during well completion (40
CFR 98.236(c)(6)(i)(B));
• For gas well completions or workovers
with hydraulic fracturing, the measured flow
rate of backflow during well workover (40
CFR 98.236(c)(6)(i)(D));
• For gas well completions or workovers
with hydraulic fracturing, the total number of
days of backflow from all wells during
completions (40 CFR 98.236(c)(6)(i)(E));
• For gas well completions or workovers
with hydraulic fracturing, the total number of
days of backflow from all wells during
workovers (40 CFR 98.236(c)(6)(i)(F));
• For onshore production storage tanks,
the total volume of oil from all wellhead
separators with wellhead gas-liquid separator
oil throughput greater than or equal to 10
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barrels per day sent to tank(s) in barrels per
year (40 CFR 98.236(c)(8)(i)(F)); and
• For onshore production storage tanks,
the total volume of sales oil from all wells
with oil production greater than or equal to
10 barrels/day in barrels per year (40 CFR
98.236(c)(8)(ii)(A)).
These six inputs to emission
equations data elements are themselves
a small subset of the inputs to emission
equations data elements (for which
reporting was deferred to 2015)
collected in subpart W, as there are 90
such inputs to emission equations in
subpart W. Further, wildcat and
delineation wells represent a relatively
small percentage of the wells being
reported under the GHGRP for these
data elements. As such, in the interim
period before these data are reported to
the EPA, the EPA will be able to verify
the majority of the emissions using the
inputs to equations that will be reported
to the EPA. For the six inputs to
emission equations that may be delayed
for 2 years, the EPA will verify
emissions using other data reported to
the EPA, and will conclude verification
upon receipt of the data. The EPA agrees
with the commenter that a 2-year delay
of reporting is sufficient to prevent early
public disclosure of these data and will
provide sufficient time for the reporter
to thoroughly conduct an assessment of
the well. Given the results of this
evaluation, the EPA determined that, for
these six inputs to emission equations,
in those cases where a reporter has
wildcat wells or delineation wells in a
sub-basin and these wells meet one of
the two situations described above,
reporters should be provided an option
to delay reporting of the given input for
two reporting years starting in reporting
year 2013. There is no early public
disclosure concern for these inputs for
reporting years 2011 and 2012 because
2 years would already have passed
before they are to be reported in March
31, 2015. As a result, there is no need
to delay reporting for these two
reporting years. For reporting years 2013
and thereafter, this delay will prevent
early public disclosure of information
regarding well productivity. In such
cases, if the 2-year delay in reporting is
used, the reporter must report the
following information in the current
reporting year: indicate for each delayed
reporting element that one of the two
situations listed above is true (e.g., for
gas well completions or workovers with
hydraulic fracturing, wildcat wells and/
or delineation wells are the only wells
in a sub-basin that can be used for the
measurement). In addition, when
reporters report the delayed inputs to
emission equations after the 2 year
delay, they must also report the API
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well ID numbers for the applicable
wildcat and/or delineation wells in the
sub-basin for which the reporting
element was delayed.
The EPA also determined that
additional definitions are necessary in
order to clarify and specify the types of
exploratory wells (delineation and
wildcat wells) covered by the 2-year
delay of reporting option. The EPA is
adopting the terms and definitions used
to describe delineation wells and
wildcat wells in the new source
performance standards for the oil and
gas sector under 40 CFR part 60, subpart
OOOO, as reporters under 40 CFR part
98, subpart W are also complying with
40 CFR part 60, subpart OOOO
requirements. To minimize confusion
for reporters and be consistent with 40
CFR part 60, subpart OOOO, the final
rule includes the terms and definitions
of a ‘‘delineation well’’ and ‘‘wildcat
well,’’ as used in 40 CFR part 60,
subpart OOOO. ‘‘Delineation well’’ is
defined as a well drilled in order to
determine the boundary of a field or
producing reservoir. ‘‘Wildcat well’’ is
defined as a well outside known fields
or the first well drilled in an oil or gas
field where no other oil and gas
production exists.
C. Revision of Recordkeeping
Requirements for Facilities Required To
Use IVT
1. Summary of Final Amendments to
Part 98
The EPA is finalizing the proposed
revisions to recordkeeping requirements
for facilities required to use IVT. For
each facility required to use IVT, the
facility is required to retain all records
starting with records for reporting year
2010, including records for subparts not
subject to using IVT, for 5 years, rather
than the 3-year record retention period
required for non-IVT users. In other
words, if any facility subject to using
IVT is also subject to a subpart of Part
98 not listed in Table 2 of this preamble,
the facility is required to maintain the
records required for those other subparts
for 5 years. Facilities subject to IVT are
also required to maintain a record of all
inputs to emission equations entered
into IVT, in the format provided by IVT.
At the time the reporter completes entry
of data into IVT, the facility is required
to download from IVT a file that lists
the entered data and maintain a copy of
the file as a record of the entered inputs.
As specified in 40 CFR 98.3(g), subpart
A, this file may be maintained in
electronic or hard copy format. Refer to
Sections II.C and III.B of the proposal
preamble (78 FR 55994, September 11,
2013) for further discussion of these
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amendments to the Part 98
recordkeeping requirements being
finalized in this action.
The EPA has added a new
‘‘verification software records’’
provision to the recordkeeping section
of each subpart listed in Table 2 of this
preamble to list all inputs to emission
equations required to be entered into
IVT. As mentioned above, a list of the
entered inputs must be downloaded
from IVT and maintained as records.
We are also revising an error in 40
CFR 98.3(g), as proposed. As discussed
in Section III.B of the proposal preamble
(78 FR 55994, September 11, 2013), in
a previous action amending this
paragraph (76 FR 73866, November 29,
2011), our intention was to amend the
second sentence of the paragraph
regarding record retention duration;
however, the third sentence regarding
record format was inadvertently
amended. As a result, as proposed, we
are removing the second sentence of 40
CFR 98.3(g) and reinstating the previous
third sentence of 40 CFR 98.3(g)
(regarding format of records). Refer to
Section II.B of this preamble for further
discussion of this new provision.
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2. Summary of Changes Since Proposal
The EPA is making no changes to the
proposed revisions to recordkeeping
requirements for IVT users. To clarify
which data are entered into IVT and
must be kept as records (i.e., the data
included in the file generated by IVT to
be maintained as a record), the EPA is
adding a ‘‘verification software records’’
provision to the recordkeeping section
of each subpart specified in Table 2 of
this preamble. Each ‘‘verification
software records’’ provision lists the
inputs to equations required to be
entered into IVT and required to be
maintained as a record.
3. Summary of Comments and
Responses
This section summarizes the
significant comments and responses
related to the proposed amendments to
the recordkeeping requirements for IVT
users. The EPA’s comment response
document in Docket ID No. EPA–HQ–
OAR–2010–0929 provides a complete
listing of all comments and responses
related to this topic.
Comment: Three commenters
supported the EPA’s extension of the
records retention period. Eight
commenters opposed the EPA’s
proposal to extend the record retention
time from 3 to 5 years. Five of the eight
commenters indicated that this
proposed requirement would add
significantly more burden to owners
with multiple reporting facilities, where
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some facilities would be subject to a 3year record retention schedule and some
of which would be subject to a 5-year
record retention period. Three of these
commenters presented this argument in
the context of landfills, where one
owner would have multiple landfills,
and only certain of the landfills would
be subject to using IVT due to being
subject to subpart C. One of the five
commenters explained that owners of
multiple facilities in remote locations
(e.g., offshore production platforms,
compressor stations, fuel supply
terminals) rely on data centers and
centralized archiving procedures to
maintain accurate records and back-up
documentation for demonstrating
compliance for some records. The
commenter provided one example of a
scenario where an owner of multiple
facilities subject to subparts C, W, and
NN would be subject to use of IVT due
to subpart C. The commenter indicated
that this requirement would create
confusion by requiring that data
maintained in the central data centers
be organized according to two different
record retention periods. Additionally,
the commenter asserted, for a given
reporter (e.g., gas processing plant
subject to subparts C and W), some
records are maintained on site and other
are maintained in a central data
exchange. The commenter added that
the requirement to keep records
according to two different retention
periods would substantially increase the
volume of records required. Another
commenter also pointed out the
increased confusion associated with
maintaining records for multiple record
duration periods.
Two commenters contended that this
revision conflicts with the justification
the EPA previously made for requiring
3 years in the 2009 promulgated GHGRP
rule, citing that the EPA determined it
was sufficient time to audit and review,
reduces recordkeeping burden, and is
consistent with recordkeeping
requirements in other Federal programs.
Two of the commenters stated that the
EPA did not provide sufficient
justification for extending the record
retention time. Two of the commenters
disagreed with the EPA’s rationale that
the extra time is needed for follow-up
with reporters because IVT would
generate an immediate flag on a realtime basis of any input errors and
follow-up could be immediate. One of
these commenters further disagreed
with the EPA’s rationale that the extra
time would allow the EPA inspectors
time for appropriate assessment of
compliance, because the EPA could
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63769
accomplish this with timely inspections
that do not need the extra time.
One commenter expressed concern
that the proposed extra retention time
would be an unfair burden because it
only applies to those sources using IVT
and not all sources. The commenter
added that sources using IVT would be
unfairly subjected to potential
additional fines and penalties for
noncompliance for an extra 2 years,
while other sources would not be
subject to this noncompliance issue.
The commenter concluded that
requiring the verification IVT users to
retain information longer would lead to
unjustified prejudices against these
source categories.
Six of the eight commenters that
opposed the EPA’s proposal to extend
the record retention time from 3 to 5
years also opposed the EPA’s proposal
that this 5-year record retention
requirement for IVT users be extended
to all subparts applicable to a reporter.
The six commenters opposed this
additional requirement for the same
reasons they opposed the 5-year
retention period.
Response: The EPA is finalizing in
this action this proposed amendment to
recordkeeping requirements for IVT
users as part of the alternative
verification approach included in these
amendments. As previously stated in
the proposal preamble (September 11,
2013, 78 FR 55994), the EPA considered
whether the current record retention
period and record format requirements
would be sufficient to allow the EPA to
perform data verification under this
alternative verification approach. We
considered:
• The time we would need to follow up
with reporters to further verify reported GHG
emissions.
• The desirability of retaining multiple
years of data records to allow for appropriate
assessment of compliance and for analyses of
trends for policy analysis purposes.
• The format of records, and whether the
current format would be adequate for our
verification process. For example, we
considered whether records of inputs to
emission equations (for which reporting was
deferred to 2015) contained in multiple
separate documents (as currently allowed
under Part 98) would allow an EPA inspector
to efficiently analyze the consistency of the
data elements and use the data elements to
perform calculations to confirm reported
GHG emissions.
This revision to the recordkeeping
timeframe is part of the new verification
approach using IVT that is being
finalized today. Given the large number
of reporters under the subparts
identified in Table 2 of this preamble
(over 2,000 facilities) and the likely
increase in follow-up activities under
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the new approach, it is important that
relevant records are available to the EPA
for follow-up activities with facilities,
including on-site audits if necessary,
regarding potential errors,
discrepancies, or questions. When an
EPA employee visits a facility, it is
important that the employee be able to
examine not only the current year’s
records but those from previous years as
well, because previous years’ data will
provide year-to-year comparisons,
which are useful for verifying the
current year’s data. A 5-year record
retention period ensures the availability
of relevant records for the follow-up
activities described above.
Regarding the general comment that
this proposed 5-year record retention
requirement would add significantly
more burden to owners with multiple
reporting facilities, the EPA disagrees
with this assertion. Given that reporters
are already required to maintain records
for 3 years, the reporter is not required
to do anything more than keep the
records for an additional 2 years. Only
one commenter provided a description
of the additional burden for these types
of owners. The commenter referred to a
scenario where one parent company has
multiple facilities subject to different
combinations of subparts NN, C, and W
(where some facilities are in remote
locations, such as offshore production
platforms, compressor stations, and fuel
supply terminals). As such, the parent
company is subject to both a 3-year
record duration for some facilities and
a 5-year record duration for other
facilities. The commenter described the
burden as being associated with the
need for their records that are
maintained in their central data centers
to be organized according to two
different record retention periods.
However, the commenter did not
provide any additional information or
data to support their claim that the
increased burden associated with this
scenario would be significant, and the
EPA does not understand how saving
data electronically for an additional 2
years would require significant
additional burden. The EPA received no
comments on its proposed impacts
analysis, which concluded that there is
no additional burden imposed on
keeping records for 2 additional years
(refer to Section V of the proposal
preamble, September 11, 2013, 78 FR
55994). Lastly, if a parent company does
not want to maintain some facilities’
records for 3 years and others for 5
years, there is nothing in this
rulemaking that prevents owners from
maintaining all records for a period of
5 years.
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Regarding the comment that this 5year record duration requirement
conflicts with the EPA’s justification in
the 2009 promulgated GHGRP rule that
the 3-year duration is adequate, the
EPA’s rationales for extending the
recordkeeping period under the new
verification approach using IVT do not
conflict with the previous justification
for the 3-year recordkeeping
requirement in the 2009 rulemaking
because the 2009 GHGRP rule (74 FR
56260) did not include the alternative
verification approach being finalized
today. Since the IVT approach was not
part of the 2009 rulemaking, the
previous consideration did not take into
account this new approach that is being
finalized today. Further, at the time the
previous justification was made, not
only was there no IVT approach, the
inputs to equations, which were
necessary for verifying emissions under
the 2009 rule, were required to be
reported timely with the annual reports.
In light of the subsequent changes to the
verification approach and input
reporting, it is unreasonable to suggest
that the previous justification for a 3year recordkeeping period still applies.
The commenter did not identify or
explain any deficiency in the EPA’s
rationales for extending the record
keeping period to accommodate the IVT
approach.
Regarding the comment that this 5year record duration requirement is
inconsistent with recordkeeping
requirements in other Federal programs,
the other Federal programs referred to
by the commenter (i.e., Department of
Energy (DOE) and Acid Rain Program
(ARP)) are not using the alternative
verification approach associated with
this action. As such, comparison to DOE
or ARP reporting programs is not
appropriate. The EPA also notes that the
EPA’s National Emission Standards for
Hazardous Air Pollutants require 5-year
record retention (see 40 CFR 63.10(b)).
Regarding the comment that the EPA
does not need extra time to allow for
follow-up with reporters because IVT
would generate an immediate flag on a
real-time basis of any input errors and
follow-up could be immediate, based on
its experience with data verification for
reporting years 2010 through 2012, the
EPA anticipates situations where the
verification summary will indicate
discrepancies between reported GHG
emissions and the GHG emission
equation results calculated by IVT as
well as other verification results that
will require further attention. In certain
situations, the EPA will need additional
time to follow up with these reporters
to resolve discrepancies, as further
described above.
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Regarding the comment that the EPA
does not need extra time because the
EPA could accomplish this alternative
verification approach with ‘‘timely
inspections,’’ as further described
above, the EPA anticipates more direct
follow-up activities under the
alternative verification approach
associated with this action. Given the
large number of sources reporting to the
GHGRP and limited resources, any
direct follow-up with facilities would be
more effective with the ability to access
5 years of data.
In response to the comment that the
proposed extra retention time would be
an unfair burden because certain
sources would be unfairly subjected to
potential additional fines and penalties
for noncompliance for an extra 2 years,
it is important to note that different
facilities within the Greenhouse Gas
Reporting Program are subject to
different verifications approaches
(reporting inputs to emissions equations
versus using IVT). Different verification
approaches necessitate different
reporting and record keeping
requirements to ensure the success of
the individual verification approach.
Further, we do not believe that the 5year record retention period is complex
or otherwise difficult or burdensome to
implement; if a facility uses IVT, it must
keep all of its record for 5 years. Given
that a reporter is already required to
maintain records for 3 years, this 5-year
recordkeeping requirement does not
require any action beyond keeping these
records for an additional 2 years. In any
event, the commenters did not provide
any information to support the claim
that 2 additional years of record
maintenance would somehow trigger
additional fines and penalties. Further,
the commenter provided no comment
on the EPA’s proposed impacts analysis,
which concluded that there is no
additional burden imposed on keeping
records for 2 additional years (refer to
Section V of the proposal preamble,
September 11, 2013, 78 FR 55994).
Regarding the comments opposing
extending the 5-year record retention
requirement to all subparts for IVT
users, the EPA proposed this provision
because during a site visit, if questions
arise regarding the accuracy of equation
inputs entered into IVT, it may be
necessary to examine other
recordkeeping information not entered
into IVT, such as a monitoring plan or
recordkeeping information in a different
subpart, in order to fully investigate the
accuracy of the data at issue. For
example, a lime production facility with
natural gas-fired kilns may report
combustion emissions under subpart C,
CO2 process emissions from lime kilns
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under subpart S, and CO2 supply under
subpart PP. As part of the site visit, the
EPA may check for inconsistencies in
the quantities of CO2 collected and
transferred off site (reported under
subpart PP) compared with the CO2
process emissions reported under
subpart S. Specifically, if a facility
reported collecting 32,000 metric tons
under subpart PP but reported
generating only 30,000 metric tons of
CO2 in their lime kilns, then the EPA
may need to check the records and
review the monitoring plan for both
subpart S and PP to determine why this
inconsistency occurred. If this facility
also elected to report the natural gas
combusted (i.e., the facility elects not to
use IVT for subpart C), then the EPA
would also use the fuel quantity data to
check for unexpected inconsistencies in
the subpart S data using parameters
such as the ratio of CO2 emissions to
fuel consumption and looking for
significant changes in such parameters
when compared to data from previous
years. As part of this process, the EPA
may examine the monitoring plan
associated with all of the subparts
reported by this facility to ensure that
the correct monitoring was conducted
by the facility. In this example, if
facilities were allowed to retain records
for only 3 years for subparts for which
IVT was not used, the EPA’s verification
and compliance activities would be
impacted by incomplete records for
subparts C and PP when compared with
subpart S. As the above example
illustrates, records necessary to verify
data submitted by a facility using IVT
may include that facility’s data from
subparts not subject to IVT. It is
therefore necessary to ensure that all
data necessary for verification are
available, and this 5-year record
retention period requirement will
provide assurance of on-site data
availability. The EPA received no
additional rationale opposing this
provision beyond the rationales
presented against the 5-year record
duration requirement. The EPA received
no details to contradict the EPA’s
proposed impacts analysis, which
concluded that this proposed
requirement would impose no
additional burden (refer to Section V of
the proposal preamble, September 11,
2013, 78 FR 55994). As such, the EPA
is finalizing the proposed requirement
for IVT users to maintain records for all
subparts for a period of 5 years.
Comment: One commenter suggested
that the recordkeeping section of each
subpart be modified to clearly specify
which records related to IVT must be
maintained. The commenter argued that
e-GGRT is a reporting tool, but not a
regulation, such that it would not be
appropriate for IVT to dictate which
records must be maintained.
63771
Response: The EPA had requested
comment on whether additional
specificity within the recordkeeping
requirements of each subpart would
improve the clarity of the specific
records that are required to be retained.
After considering the commenter’s
request, the EPA agrees with the
recommendation to specify each record
that reporters must maintain. In the
final rule, each subpart listed in Table
2 of this preamble includes, in the
recordkeeping section, a new
‘‘verification software records’’
provision that specifies each data
element in that subpart that must be
entered into IVT and maintained as a
record.
D. Addition of Reporting Requirements
for Certain Facilities Required To Use
IVT
1. Summary of Final Amendments to
Part 98
The EPA is finalizing the proposed
addition of new reporting requirements
for facilities required to use IVT for
subparts E, G, H, P, Q, S, V, X, and AA
of part 98, with changes to the proposed
amendments for subparts E, V, Y, and
AA, as discussed in Section II.D.2 of
this preamble. The final list of new data
elements being added in this action is
in Table 4 of this preamble.
TABLE 4—NEW DATA ELEMENTS BEING FINALIZED IN TODAY’S ACTION FOR SUBPARTS E, G, H, P, Q, S, V, X, AND AA
OF PART 98
Subpart name
New data element description
E ....................................
Adipic Acid Production .....................................
G ....................................
Ammonia Production ........................................
H ....................................
Cement Production ..........................................
P ....................................
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Subpart
Hydrogen Production .......................................
If only cyclohexane is oxidized to produce adipic acid: the annual
quantity of cyclohexane (tons) used to produce adipic acid. If materials other than cyclohexane are oxidized to produce adipic acid:
the annual quantity of cyclohexanone and cyclohexanol mixture
(metric tons) used to produce adipic acid.
Annual percent nitrous oxide (N2O) emission reduction for all production units combined.
Annual ammonia production (metric tons, sum of all process units reported within subpart G).
Annual methanol production (metric tons) for each process unit.
Annual clinker production (metric tons).
Annual average clinker carbon dioxide (CO2) emission factor for the
facility, averaged across all kilns (metric tons CO2/metric ton clinker produced).
Annual average cement kiln dust (CKD) CO2 emission factor for the
facility, averaged across all kilns (metric tons CO2/metric ton CKD
produced).
Name and annual quantity (metric tons) of each carbon-containing
fuel and feedstock.
Annual methanol production (metric tons) for each process unit.
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TABLE 4—NEW DATA ELEMENTS BEING FINALIZED IN TODAY’S ACTION FOR SUBPARTS E, G, H, P, Q, S, V, X, AND AA
OF PART 98—Continued
Subpart name
New data element description
Q ....................................
Iron and Steel Production ................................
S ....................................
V ....................................
Lime Manufacturing .........................................
Nitric Acid Production ......................................
X ....................................
Petrochemical Production ................................
AA ..................................
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Subpart
Pulp and Paper Manufacturing ........................
If you use the carbon mass balance method in 40 CFR 98.173(b)(1)
to determine CO2 emissions: The annual mass (metric tons) of all
gaseous, liquid, and solid fuels (combined) used in process units
specified in Equations Q–1 through Q–7 of subpart Q, calculated
as specified in Equation Q–9 of subpart Q being finalized in this
action. Do not include fuel used in a stationary combustion unit
where emissions are reported under subpart C.
If you use the carbon mass balance method in 40 CFR 98.173(b)(1)
to determine CO2 emissions: The annual mass (metric tons) of all
non-fuel material inputs (combined) specified in Equations Q–1
through Q–7 of subpart Q, calculated as specified in Equation Q–
10 of subpart Q being finalized in this action.
If you use the carbon mass balance method in 40 CFR 98.173(b)(1)
to determine CO2 emissions: The annual mass (metric tons) of all
solid and liquid products and byproducts (combined) specified in
Equations Q–1 through Q–7 of subpart Q, calculated as specified
in Equation Q–11 of subpart Q being finalized in this action.
If you use the carbon mass balance method in 40 CFR 98.173(b)(1)
to determine CO2 emissions: The weighted average carbon content of all gaseous, liquid, and solid fuels (combined) included in
Equation Q–9 of subpart Q being finalized in this action, calculated
as specified in Equation Q–12 of subpart Q being finalized in this
action.
If you use the carbon mass balance method in 40 CFR 98.173(b)(1)
to determine CO2 emissions: The weighted average carbon content of all non-fuel inputs to all furnaces (combined) included in
Equation Q–10 of subpart Q being finalized in this action, calculated as specified in Equation Q–13 of subpart Q being finalized
in this action.
If you use the carbon mass balance method in 40 CFR 98.173(b)(1)
to determine CO2 emissions: The weighted average carbon content of all solid and liquid products and byproducts from all furnaces (combined) included in Equation Q–11 of subpart Q being finalized in this action, calculated as specified in Equation Q–14 of
subpart Q being finalized in this action.
Annual quantity (tons) of lime product sold, by type.
Annual percent N2O emission reduction for all nitric acid trains combined.
If using the CEMS method to calculate GHG emissions: Name and
annual quantity (in metric tons) of each product. If using the mass
balance method to calculate GHG emissions: Name and annual
quantity (in metric tons) of each product used in Equations X–1,
X–2, and X–3 of subpart X.
If using the CEMS method to calculate GHG emissions: Name and
annual quantity (in metric tons) of each carbon-containing feedstock. If using the mass balance method to calculate GHG emissions: Name and annual quantity (in metric tons) of each carboncontaining feedstock used in Equations X–1, X–2, and X–3 of subpart X.
For each pulp mill lime kiln: Quantity of calcium oxide (CaO) produced (metric tons).
For each pulp mill lime kiln: Percentage of annual heat input, individually for each fossil fuel type.
The EPA is also adding six new
equations (Equations Q–9 through Q–14
of part 98) to subpart Q, as proposed, to
specify how to calculate and report each
of the six new data elements added to
subpart Q in this action. Final
confidentiality determinations for the
data elements specified in Table 4 are
presented in Section III of this
preamble.
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2. Summary of Changes Since Proposal
This section provides a brief summary
of changes since proposal. The EPA’s
rationale for these changes is provided
in Section II.D.3 of this preamble as part
of the EPA’s response to the related
comment(s). In cases where the EPA is
making a change that was not related to
a public comment, a summary of the
rationale is included in this section.
The changes to the proposed addition
of new reporting requirements for
facilities required to use IVT are as
follows:
• In the final rule, the new data element
for subpart E, 40 CFR 98.56(m), specifies that
if only cyclohexane is oxidized to produce
adipic acid, the reporter must report the
annual quantity of cyclohexane used to
produce adipic acid; otherwise, if materials
other than cyclohexane are oxidized to
produce adipic acid, the reporter must report
the annual quantity of cyclohexanone and
cyclohexanol mixture used to produce adipic
acid. Refer to Section II.D.3 of this preamble
for the rationale for this revision.
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• The EPA is not finalizing the proposed
addition of two new data elements to subpart
AA: The annual mass of steam generated
(proposed as 40 CFR 98.276(m)(1)) and the
ratio of the unit’s maximum rated heat input
capacity to its design rated steam output
capacity (proposed as 40 CFR 98.276(m)(2)).
Refer to Section II.D.3 of this preamble for
the rationale for this revision.
• The EPA is revising the new data
element added to subpart V (40 CFR
98.226(q)) to read ‘‘annual percent N2O
emission reduction for all nitric acid trains
combined.’’ The text ‘‘nitric acid trains’’
replaces proposed text ‘‘production units’’ to
be consistent with the terminology used
elsewhere in subpart V. This rationale is
documented in ‘‘Summary and Explanation
of Minor Changes Since the Proposed Rule’’
(Docket ID No. EPA–HQ–OAR–2010–0929).
• The EPA is not finalizing the proposed
addition of the following three new data
elements to subpart Y, which were proposed
to be required to be reported when Equation
Y–3 is used to calculate flare CO2 emissions:
Annual quantity of flare gas combusted,
annual average molecular weight of flare gas
combusted, and annual average carbon
content of flare gas combusted, all for normal
operations and startup, shutdown, and
malfunction (SSM) events combined. The
EPA included these new elements in the
proposal to supplement the IVT verification
approach by minimizing the need for
potential follow-up activities (e.g., phone
calls, emails, site visits, etc.) to verify
reported GHG emissions from flares using
Equation Y–3 to calculate emissions.
Specifically, such information would allow
the EPA to verify and reconcile potential
differences between reported emissions and
emissions equation results calculated by IVT,
and therefore minimize the need for followup via phone, email or site visits. At the time
of proposal, the EPA did not consider the
proposed new reporting elements in
conjunction with the monitoring
requirements associated with Equation Y–1a
and Y–1b. In the process of finalizing this
rulemaking, the EPA realized that, under the
current rule, if the flare gas composition
(which determines molecular weight and
carbon content) is measured weekly or more
frequently, reporters are required to use
either Equation Y–1a or Y–1b to calculate
flare CO2 emissions. Reporters that either do
not measure the composition of flare gas or
conduct such measurements but less
frequently than weekly may use Equation Y–
3, which does not require such values to
calculate routine flare gas emissions. As a
result, requiring reporters to report annual
averages of molecular weight and carbon
content when using Equation Y–3 would
undermine the purpose of Equation Y–3 by
requiring facilities that do not currently
measure these values to now have to
determine and report these values. These
facilities would now have to conduct such
measurements or provide the values through
other means. In the case where reporters do
not measure these values, they would likely
report the values determined for the subset
of flare emissions related to SSM events,
which would not be representative of the
annual average, and therefore would not be
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useful for verification. As a result, the EPA
is not finalizing the proposed reporting of the
annual average molecular weight of flare gas
combusted and annual average carbon
content of flare gas combusted, both for
normal operations and SSM events
combined. Further, given that the three
proposed data elements were to be used
together to provide an alternative method of
estimating emissions, requiring reporting of
the annual quantity of flare gas combusted
would not be useful in the absence of the
other two data elements. The EPA is
therefore not requiring the reporting of these
three data elements in the final rule and will
continue to rely on the general IVT
verification approach for verifying flare CO2
emissions using Equation Y–3.
3. Summary of Comments and
Responses
This section summarizes the
significant comments and responses
related to the proposed addition of new
reporting requirements for facilities
required to use IVT. See the EPA’s
comment response document in Docket
ID No. EPA–HQ–OAR–2010–0929 for a
complete listing of all comments and
responses related to this topic.
Comment: One commenter suggested
that the amount of cyclohexanone and
cyclohexanol combined (also called
ketone-alcohol oil or (KA) used to
manufacture adipic acid should be
substituted for cyclohexane for the
verification of N2O emissions from
adipic acid manufacturing. The
commenter indicated that they use an
EPA-approved alternate method, as
allowed under 40 CFR 98.53(a)(2) to
report N2O emissions, and the proposed
new data element would not fairly
represent emissions from their
manufacturing facility. The commenter
explained that the EPA is assuming that
adipic acid is manufactured wholly via
the oxidation of cyclohexane to KA,
which is then further oxidized with
nitric acid to adipic acid. The
commenter stated that this assumes that
all the KA used in the nitric acid
oxidation comes from cyclohexane
oxidation and all the KA produced is
used to produce adipic acid. However,
the commenter stated that, in reality,
KA can be purchased or sold
commercially as well as produced using
materials other than cyclohexane. The
commenter noted that they operate an
alternate process to produce KA in
addition to the cyclohexane-based KA
production.
Response: The EPA agrees with the
commenter that the proposed new data
element for subpart E (i.e., 40 CFR
98.56(m), the annual quantity of
cyclohexane fed to all production lines,
combined) will be useful to the EPA for
verification purposes for only those
reporters that are producing all adipic
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63773
acid from cyclohexane. At proposal, the
EPA had assumed that all KA used to
produce adipic acid was produced by
the reporting facility using cyclohexane.
Based on this commenter input and
further consideration, the EPA has
determined that there are cases where
either the KA used by the reporting
facility to create adipic acid is
purchased from another KA producer or
the reporting facility uses materials
other than cyclohexane to produce KA
(such as the facility represented by the
commenter). In a case where the KA
used by the reporting facility to create
adipic acid is purchased from another
KA producer, the reporting facility may
not know whether and how much
cyclohexane was used to produce the
KA. Likewise, in cases where the
reporting facility uses materials other
than cyclohexane to produce KA (which
may then be used to produce adipic
acid), the reported annual quantity of
cyclohexane used to produce adipic
acid would not be applicable and,
therefore, not useful to EPA for
verification of reported GHG emissions
(representing all adipic acid produced)
because this quantity of cyclohexane
would represent only part (or none, if
no cyclohexane is used) of the KA used
to produce adipic acid. In cases where
a reporter is producing KA using
materials other than cyclohexane, or
where a reporter is purchasing KA, the
EPA has changed the new data element
to be the quantity of KA fed to adipic
acid production lines. In the final rule,
the EPA has revised the new data
element to specify that if only
cyclohexane is oxidized to produce
adipic acid, the reporter must report the
annual quantity of cyclohexane used to
produce adipic acid; otherwise, the
reporter must report the annual quantity
of KA used to produce adipic acid.
Regarding the comment that some
adipic acid producers are selling some
of the KA produced, these adipic acid
producers will be required to report a
corrected quantity of cyclohexane or
KA, as applicable, used to produce
adipic acid to account for any KA sold.
Regarding the comment that some
adipic acid producers purchase KA to
produce adipic acid, these reporters will
be required to report the annual
quantity of KA used to produce adipic
acid under 40 CFR 98.56(m)(2).
Comment: One commenter supported
the reporting for two new data elements
proposed to be reported for subpart AA:
(1) Quantity of calcium oxide (CaO)
produced (metric tons), and (2) percent
of annual heat input, individually for
each fossil fuel type. The commenter
opposed the reporting of two other data
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elements proposed to be reported for
subpart AA for each chemical recovery
furnace and chemical recovery
combustion unit for which Equation C–
2c of subpart C is not used to calculate
CO2 emissions: (1) Annual mass of
steam generated (pound (lb) steam),
individually for each fossil fuel type
and for spent liquor solids, and (2) Ratio
of the unit’s maximum rated heat input
capacity to its design rated steam output
capacity (MMBtu/lb steam),
individually for each fossil fuel type
and for spent liquor solids. The
commenter contended that these
requirements are unclear and
unnecessary and should be removed
from the final rule. The commenter
asserted that these proposed reporting
requirements for pulp mills directly
contradict the requirement in 40 CFR
98.36(e)(2)(ii)(D) that requires stationary
fuel combustion units to report the
steam and heat/steam ratio only if
Equation C–2c is used. Regarding
recovery units not using Equation C–2c,
the commenter indicated that
determining these two data elements
would be overly burdensome because
determining steam generation by fuel
type would be very difficult. The
commenter explained that most
recovery furnaces only use spent
pulping liquor as their fuel and some
may use other fuels for either start-up or
for flame stabilization, but, generally,
the fuels are liquid; and, other than
using a percent of fuel to estimate the
amount of steam generation per fuel
type, the commenter did not know of
any other method to determine the
amount of steam generation per fuel
type. As such, the commenter requested
that these two proposed new data
elements (annual mass of steam
generated and ratio of the unit’s
maximum rated heat input capacity to
its design rated steam output capacity)
be eliminated in the final rule.
Response: The EPA thanks the
commenter for their support for
reporting the quantity of CaO produced,
and percent of annual heat input,
individually for each fossil fuel type.
These two data elements are added as
proposed. Regarding the other two data
elements (annual mass of steam
generated (lb steam), individually for
each fossil fuel type and for spent liquor
solids, and ratio of the unit’s maximum
rated heat input capacity to its design
rated steam output capacity (MMBtu/lb
steam), individually for each fossil fuel
type and for spent liquor solids), the
EPA included these new elements in the
proposal to supplement the IVT
verification approach because having
such information would allow the EPA
to verify and reconcile potential
differences between reported emissions
and emissions equation results
calculated by IVT and therefore
minimize the need for follow-up via
phone, email or on-site visit. However,
as the EPA stated in the proposal
preamble (September 11, 2013), the
proposal to collect these two data
elements was also based in part on the
EPA’s incorrect assumption that the
proposed new reporting elements would
be readily available for affected
facilities, or easily calculated using data
already required to be collected. In light
of the comment, and after further
investigation of the method available to
reporters to calculate steam generated
by fuel type, the EPA has learned that
generating these two new data reporting
elements would require a significant
investment in time. Upon further
consideration, the EPA concludes that
any potential time saved from the
reduced follow-up activities due to
collection of these two data elements is
outweighed by the significant resources
and time required for the facilities to
generate these data. The EPA is
therefore not requiring the reporting of
these two data elements in the final rule
and will continue to rely on the general
IVT verification approach for verifying
chemical recovery furnace and chemical
recovery combustion unit emissions.
For the reasons stated above, the EPA is
not finalizing these two new data
elements in this final action.
III. Summary of Final Confidentiality
Determinations for New Data Elements
A. Summary of Final CBI
Determinations
The EPA is finalizing the proposed
data category assignment and
confidentiality determination for each
new data element added in this final
rule 18 except 40 CFR 98.226(q). For 40
CFR 98.226(q), the EPA is finalizing the
proposed data category assignment, but
is not making any final confidentiality
determination. The EPA’s rationale for
this change is provided in Section III.B
of this preamble.
For the 16 new data elements listed in
Table 5 of this preamble, the EPA has
determined that they are entitled to
confidential treatment, as proposed.
Specifically, the EPA is finalizing the
proposed category assignments of these
data elements to the ‘‘Production/
Throughput Data that are Not Inputs to
Emission Equations’’ and ‘‘Raw
Materials Consumed that are Not Inputs
to Emission Equations’’ data categories
and the application of the categorical
confidentiality determinations made for
these categories in the 2011 final CBI
rule (76 FR 30782, May 26, 2011) to
these data elements.
TABLE 5—DATA ELEMENTS ASSIGNED TO THE ‘‘PRODUCTION/THROUGHPUT DATA THAT ARE NOT INPUTS TO EMISSION
EQUATIONS’’ AND ‘‘RAW MATERIALS CONSUMED THAT ARE NOT INPUTS TO EMISSION EQUATIONS’’ DATA CATEGORIES
Subpart
Final citation
Data element
‘‘Production/Throughput Data That Are Not Inputs to Emission Equations’’ Data Category
40 CFR 98.76(b)(14) .....................
H—Cement Kilns .............................
P—Hydrogen Production .................
S—Lime Manufacturing ...................
X—Petrochemical ............................
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G—Ammonia Production .................
40
40
40
40
40
CFR
CFR
CFR
CFR
CFR
18 EPA is not finalizing the addition of all the data
elements proposed to be added to the rule. Five
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98.76(b)(15) .....................
98.86(b)(16) .....................
98.166(e) .........................
98.196(b)(18) ...................
98.246(a)(13) and (b)(10)
Annual ammonia production (metric tons, sum of all process lines reported within subpart G).
Annual methanol production (metric tons) for each process unit.
Annual clinker production (metric tons).
Annual methanol production (metric tons) for each process unit.
Annual quantity (tons) of lime product sold, by type.
If using the CEMS method to calculate GHG emissions: Name and
annual quantity (in metric tons) of each product. If using the mass
balance method to calculate GHG emissions: Name and annual
quantity (in metric tons) of each product used in Equations X–1,
X–2, and X–3 of subpart X.
data elements are not being added to the rule. The
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EPA’s rationale for this change is provided in
Section III.B of this preamble.
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63775
TABLE 5—DATA ELEMENTS ASSIGNED TO THE ‘‘PRODUCTION/THROUGHPUT DATA THAT ARE NOT INPUTS TO EMISSION
EQUATIONS’’ AND ‘‘RAW MATERIALS CONSUMED THAT ARE NOT INPUTS TO EMISSION EQUATIONS’’ DATA CATEGORIES—Continued
Subpart
Final citation
Data element
AA—Pulp and Paper .......................
40 CFR 98.276(l)(1) ......................
For each pulp mill lime kiln: Quantity of calcium oxide (CaO) produced (metric tons).
‘‘Raw Materials Consumed That Are Not Inputs to Emission Equations’’ Data Category
E—Adipic Acid Production ...............
40 CFR 98.56(m) ..........................
P—Hydrogen Production .................
40 CFR 98.166(b)(7) .....................
Q—Iron and Steel ............................
40 CFR 98.176(e)(6)(i) ..................
40 CFR 98.176(e)(6)(ii) .................
40 CFR 98.176(e)(6)(iii) ................
40 CFR 98.176(e)(6)(iv) ................
40 CFR 98.176(e)(6)(v) .................
40 CFR 98.176(e)(6)(vi) ................
X—Petrochemical ............................
40 CFR 98.246(a)(12) and (b)(9) ..
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The five new data elements listed
below in Table 6 of this preamble were
proposed to be assigned to the ‘‘Unit
Process Operating Characteristics that
are Not Inputs to Emission Equations’’
category, for which EPA has not
established a categorical confidentiality
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If only cyclohexane is oxidized to produce adipic acid, report the annual quantity of cyclohexane (tons) used to produce adipic acid. If
materials other than cyclohexane are oxidized to produce adipic
acid, report the annual quantity of cyclohexanone and
cyclohexanol mixture (tons) used to produce adipic acid.
Name and annual quantity (metric tons) of each carbon-containing
fuel and feedstock.
If you use the carbon mass balance method in 40 CFR 98.173(b)(1)
to determine CO2 emissions: The annual mass (metric tons) of all
gaseous, liquid, and solid fuels (combined) used in process units
specified in Equations Q–1 through Q–7, calculated as specified in
a new Equation Q–9 of subpart Q in the final rule amendments.
Does not include fuel used in a stationary combustion unit where
emissions are reported under subpart C.
If you use the carbon mass balance method in 40 CFR 98.173(b)(1)
to determine CO2 emissions: The annual mass (metric tons) of all
non-fuel material inputs (combined) specified in Equations Q–1
through Q–7 of subpart Q, calculated as specified in a new Equation Q–10 of subpart Q in the final rule amendments.
If you use the carbon mass balance method in 40 CFR 98.173(b)(1)
to determine CO2 emissions: The annual mass (metric tons) of all
solid and liquid products and byproducts (combined) specified in
Equations Q–1 through Q–7, calculated as specified in a new
Equation Q–11 of subpart Q in the final rule amendments.
If you use the carbon mass balance method in 40 CFR 98.173(b)(1)
to determine CO2 emissions: The weighted average carbon content of all gaseous, liquid, and solid fuels (combined) included in
Equation Q–9 of subpart Q, calculated as specified in a new Equation Q–12 of subpart Q in the final rule amendments.
If you use the carbon mass balance method in 40 CFR 98.173(b)(1)
to determine CO2 emissions: The weighted average carbon content of all non-fuel inputs to all furnaces (combined) included in
Equation Q–10 of subpart Q, calculated as specified in a new
Equation Q–13 of subpart Q in the final rule amendments.
If you use the carbon mass balance method in 40 CFR 98.173(b)(1)
to determine CO2 emissions: The weighted average carbon content of all solid and liquid products and byproducts from all furnaces (combined) included in a new Equation Q–11 of subpart Q
in the final rule amendments, calculated as specified in new Equation Q–14 of subpart Q in the final rule amendments.
If using the CEMS method to calculate GHG emissions: Name and
annual quantity (in metric tons) of each carbon-containing feedstock. If using the mass balance method to calculate GHG emissions: Name and annual quantity (in metric tons) of each carboncontaining feedstock used in Equations X–1, X–2, and X–3 of subpart X.
determination. Individual
confidentiality determinations were
proposed for these data elements, which
are shown in Table 6 below. In this
action, the EPA is finalizing the
categorical assignments and
confidentiality determinations for four
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of the five new data elements listed in
Table 6, as proposed. The EPA revised
the confidentiality determination for the
new data element in subpart V, as
shown in Table 6.
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TABLE 6—FINAL CONFIDENTIALITY DETERMINATIONS FOR NEW DATA ELEMENTS ASSIGNED TO THE ‘‘UNIT/PROCESS
OPERATING CHARACTERISTICS THAT ARE NOT INPUTS TO EMISSION EQUATIONS’’
Subpart
Citation
Data element
Confidentiality
determination
Final rationale for confidentiality
determination
E—Adipic Acid Production.
40 CFR 98.56(n) ..
Annual percent N2O emission reduction for all production units combined.
Not CBI .................
H—Cement Kilns ...
40 CFR
98.86(b)(17).
Annual average clinker CO2 emission
factor for the facility, averaged
across all kilns (metric tons CO2/
metric ton clinker produced).
Annual average cement kiln dust
(CKD) CO2 emission factor for the
facility, averaged across all kilns
(metric tons CO2/metric ton CKD
produced).
Annual percent N2O emission reduction for all nitric acid trains combined.
For each pulp mill lime kiln: Percent of
annual heat input, individually for
each fossil fuel type.
CBI ........................
The annual facility percent N2O reduction could not be used to calculate
adipic acid production. The level of
N2O reductions varies by the type
of abatement technology, the environment in which the abatement
technology is operating, the age of
the abatement technology, the age
of the catalyst used, and the maintenance level of the abatement
technology.
This data element could be used to
back calculate a facility’s clinker
production data, which would result
in competitive disadvantage.
This data element could provide information about the efficiency of the
operation, which would result in
competitive disadvantage.
40 CFR
98.86(b)(18).
V—Nitric Acid Production.
40 CFR 98.226(q)
AA—Pulp and
Paper.
40 CFR
98.276(l)(2).
a ND
ND a ......................
Non-CBI ................
Refer to Section III.B of this preamble
for the rationale for this determination.
Release of this data would not result
in competitive harm because lime
kiln fossil fuel use as a fraction of
design heat input was reported to
the EPA as part of a 2011 ICR survey, and facilities reporting via the
survey made no CBI claims regarding fuel type and percent of design
heat input.
= No determination is being finalized.
B. Response to Public Comments
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CBI ........................
The EPA received several comments
related to the proposed confidentiality
determinations for new data elements.
Several commenters provided support
for the EPA’s proposed confidentiality
determinations for new data elements
proposed to be reported in subparts G,
H, S, P, Y, and AA. These comments
may be found in the EPA’s comment
response document in Docket ID No.
EPA–HQ–OAR–2010–0929. We received
several comments questioning the
proposed confidentiality determination
of several new data elements, including
requests that the data elements be
treated as confidential, or that the
confidentiality be determined on a caseby-case basis, and summaries of these
comments and EPA’s responses thereto
are provided below. Additional
comments and the EPA’s responses may
be found in the comment response
document noted above.
Comment: One commenter provided
comments on confidentiality
determinations for new data elements
proposed for subpart V (Nitric Acid
Production). The commenter expressed
support for the inclusion of the data
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element ‘‘annual percent nitrous oxide
emissions reduction for all production
units combined’’ (40 CFR 98.226(q)) in
the ‘‘Unit/Process ‘Operating’
Characteristics That Are Not Inputs to
Emission Equations’’ data category.
However, the commenter disagreed with
the EPA’s proposed determination that
the data element is considered not
confidential. The commenter disagreed
with the EPA’s assertion that the data
could not be used to calculate nitric
acid production for an individual train
because it is an aggregate number,
stating that for facility with only a single
nitric acid train with N2O abatement,
this would not hold true. The
commenter further asserted that the EPA
was incorrect to assume that the data are
publicly available through the voluntary
Climate Action Reserve (CAR). The
commenter stated that although some
industry members participate in the
CAR and release the information,
several do not. The commenter
contested that it is inappropriate for the
EPA to base part of its decision on the
voluntary reporting of some facilities.
As an alternative, the commenter
requested that the EPA not make a
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confidentiality determination for this
data element as it has done for other
data elements and, instead, allow
individual reporters to assert CBI claims
for the data element.
Response: The EPA agrees with the
commenter that the annual percent
nitrous oxide emissions reduction for all
production units combined is not
publicly available on an annual basis
through the CAR for all facilities
reporting under this subpart, and notes
that the EPA did not indicate such was
the case in the proposed rule. At
proposal, the EPA did not specifically
consider the situation where a facility
has only one nitric acid train. After
further investigation in response to the
comment received, the EPA agrees that,
in cases where a facility has only one
nitric acid train with N2O, the data
element ‘‘annual percent nitrous oxide
emissions reduction for all production
units combined’’ (40 CFR 98.226(q))
could be used to calculate nitric acid
production. For facilities with only one
nitric acid train with N2O abatement,
the reporting of annual percent N2O
emissions reductions, together with
annual N2O emissions from nitric acid
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production (as required to be reported
in 40 CFR 98.3(c)(4)), the destruction
efficiency (as required to be reported in
40 CFR 98.226(i)), and the abatement
utilization factor (as required to be
reported in 40 CFR 98.226(j)), could be
used to back-calculate the mass of nitric
acid produced. Further, the EPA cannot
conclude that in specific situations, if a
facility adds a nitric acid train from one
year to the next, and the EPA publishes
this data for the year that the facility has
two nitric acid trains, that data revealing
the annual percent nitrous oxide
emissions reductions for all production
units combined could not be backcalculated or estimated for the previous
year (when the facility had one nitric
acid train.)
However, if a facility reports this
information to the CAR and it is
publicly available, the EPA sees no
reason why the same data could not be
published through the Greenhouse Gas
Reporting Program, regardless of the
number of nitric acid trains at the
facility. In light of the above, the EPA
cannot make a confidentiality
determination that applies to all
facilities required to report this data
element. Therefore, the EPA is not
finalizing a confidentiality
determination for this data element. In
Table 6 of this preamble, the
determination for this data element is
designated as ‘‘ND,’’ which means that
no determination has been made. The
EPA will make a confidentiality
determination for this data element on
a case by case basis.
Comment: One commenter provided
support for the confidentiality
determinations for three new data
elements proposed in subpart Y: Annual
quantity of flare gas combusted (40 CFR
98.256(e)(11)(i)); annual average
molecular weight of flare gas combusted
(40 CFR 98.256(e)(11)(ii)); and annual
average carbon content of flare gas
combusted (40 CFR 98.256(e)(11)(iii)).
The three data elements, which are only
required when using Equation Y–3 of
subpart Y, were assigned to the ‘‘Unit/
Process ‘Operating’ Characteristics that
Are Not Inputs to Emission Equations’’
Data Category’’ and were not classified
as CBI in the proposal. Another
commenter disagreed with the EPA’s
determination that these data are not
confidential. The commenter explained
that the flared gases are process gases,
and would reveal characteristics of iron
and steel processes. The commenter
stated that the data elements may reveal
operating efficiency, provide
information that would allow
competitors to infer production costs
and process characteristics, and enable
them to gain a competitive advantage.
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The commenter asserted that the data
elements are CBI and must be
considered CBI in the final rule.
Response: The EPA proposed to
collect these three data elements to
assist the EPA in verifying reported
GHG emissions associated with flaring
gas when Equation Y–3 is used. The
EPA is not finalizing the reporting of
these data elements. Refer to Section
II.D.2 of this preamble for further
discussion of the EPA’s rationale for this
decision.
IV. Impacts of the Final Rule
The EPA has determined that the cost
associated with this final action will be
$438,000 in the first year of
implementation and $55,000 in each
subsequent year, as further summarized
below. A full discussion of the impacts
may be found in the memorandum,
‘‘Assessment of Cost Impacts of 2015
Inputs Proposal—Revisions to
Reporting, Recordkeeping, and
Verification Requirements Under the
Greenhouse Gas Reporting Program,’’
August 2013, available in the EPA’s
Docket ID No. EPA–HQ–OAR–2010–
0929.
A. How were the costs of this final rule
estimated?
1. Inputs Verification Tool
The data elements required to be used
for calculating the annual GHG
emissions values, and the cost
associated with collecting these data
elements, have not changed from the
estimate made during the original
rulemaking process. The time associated
with entry of these inputs to emission
equations into e-GGRT (including into
the new IVT) is expected to be
equivalent to the time originally
anticipated for data entry. Prior to using
IVT, as currently required, reporters
must use their own calculation tool
(e.g., calculator, calculation software) to
calculate the annual GHG emissions
values, using the same sets of equations
and entering the same data elements
that they would enter into the tool.
The EPA does recognize however that
there may be some time associated with
learning the new procedures for IVT and
we have estimated a cost of
approximately $67 per facility, or
$383,000 for the first year for all affected
facilities. During their first session using
IVT, reporters would need to spend
approximately one hour to become
familiar with how the tool operates
within e-GGRT. The requirement to use
IVT would not result in any change in
the respondent activity of entering these
data into e-GGRT. Once the reporter has
become familiar with the tool, the EPA
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63777
does not anticipate any additional
burden. The cost includes technical,
clerical, and managerial labor hours. For
further information about this cost
estimate, refer to the memorandum
‘‘Assessment of Cost Impacts of 2015
Inputs Final Rule—Revisions to
Reporting, Recordkeeping, and
Verification Requirements Under the
Greenhouse Gas Reporting Program’’
September 2014 and the supporting
statement for the information collection
request, ‘‘Supporting Statement,
Environmental Protection Agency:
Revisions to Reporting and
Recordkeeping Requirements, and Final
Confidentiality Determinations Under
the Greenhouse Gas Reporting Program,
Office of Management and Budget
(OMB) Control Number 2060–0629, ICR
Number 2300.12,’’ both available in
Docket ID No. EPA–HQ–OAR–2010–
0929.
2. New Data Elements
We are adding 21 new data elements
that were not previously required to be
reported under Part 98 (see Section II.D
of this preamble for further discussion).
These data elements must be reported
by facilities in certain subparts that are
required to use IVT. Of these 21 data
elements, seven data elements are
related to annual production or raw
material usage, which are collected by a
facility as a routine part of conducting
business. For these data elements, we
are not requiring that reporters comply
with specific data collection or
monitoring requirements beyond the
methods commonly used for accounting
purposes. The other 14 data elements to
be reported are calculated values using
data currently required to be collected
to perform emissions calculations. For
all of these additional data elements, the
EPA has estimated a nominal additional
cost to report the data element and
fulfill the recordkeeping requirements.
The total costs associated with reporting
and recordkeeping for the 21 data
elements in 9 subparts is $55,000. These
costs represent the cost for all affected
facilities in the first year.
B. Do the final confidentiality
determinations change the impacts of
the final amendments?
The final confidentiality
determinations for the new data
elements would not affect whether and
how data are reported and, therefore,
would not impose any additional
burden on sources. Whether a data
reporting element is determined to be
CBI, not CBI, or emission data, the
reporting element is reported to the EPA
through e-GGRT in the same manner.
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V. Statutory and Executive Order
Reviews
information collection requirements
contained in this final rule.
A. Executive Order 12866: Regulatory
Planning and Review and Executive
Order 13563: Improving Regulation and
Regulatory Review
C. Regulatory Flexibility Act (RFA)
The RFA generally requires an agency
to prepare a regulatory flexibility
analysis of any rule subject to notice
and comment rulemaking requirements
under the Administrative Procedure Act
or any other statute unless the agency
certifies that the rule will not have a
significant economic impact on a
substantial number of small entities.
Small entities include small businesses,
small organizations, and small
governmental jurisdictions.
For purposes of assessing the impacts
of these final rule amendments and
confidentiality determinations on small
entities, small entity is defined as: (1) A
small business as defined by the Small
Business Administration’s (SBA)
regulations at 13 CFR 121.201; (2) a
small governmental jurisdiction that is a
government of a city, county, town,
school district or special district with a
population of less than 50,000; or (3) a
small organization that is any not-forprofit enterprise which is independently
owned and operated and is not
dominant in its field. After considering
the economic impacts of these final
amendments on small entities, I certify
that this action will not have a
significant economic impact on a
substantial number of small entities.
The small entities directly regulated by
these final rule amendments include
small businesses across all sectors of the
economy encompassed by Part 98, small
governmental jurisdictions, and small
non-profits. We have determined that
these facilities will experience impacts
of roughly a first-year cost of $67 per
facility for learning new procedures for
the verification tool and an annual cost
of $93 per facility for the recordkeeping
and reporting of 21 new data elements.
Although these final rule amendments
will not have a significant economic
impact on a substantial number of small
entities, the EPA nonetheless has tried
to reduce the impact of this rule on
small entities. The EPA supports a
‘‘help desk’’ for the GHGRP, which will
be available to answer questions on the
provisions in this final rulemaking.
This action is not a ‘‘significant
regulatory action’’ under the terms of
Executive Order 12866 (58 FR 51735,
October 4, 1993) and is therefore not
subject to review under Executive
Orders 12866 and 13563 (76 FR 3821,
January 21, 2011).
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B. Paperwork Reduction Act
The information collection
requirements in this final rule have been
submitted for approval to the OMB
under the Paperwork Reduction Act, 44
U.S.C. 3501 et seq. The Information
Collection Request (ICR) document
prepared by the EPA has been assigned
EPA ICR number 2300.12. The
information collection requirements are
not enforceable until OMB approves
them.
This action finalizes amendments to
reporting and recordkeeping
requirements and verification
procedures for the GHGRP. In addition,
the EPA is publishing confidentiality
determinations for the new data
elements added in this action. The
amendments to the reporting
requirements in the source categoryspecific subparts are not anticipated to
result in significant burden for
reporters. The data elements required to
be reported are expected to be readily
available for affected facilities, or easily
calculated using data already required
to be collected (e.g., a monthly value
was previously reported and an annual
value is to be reported).
Impacts associated with the changes
to the reporting requirements in each
subpart are detailed in the
memorandum ‘‘Assessment of Cost
Impacts of 2015 Inputs Final Rule—
Revisions to Reporting, Recordkeeping,
and Verification Requirements under
the Greenhouse Gas Reporting
Program,’’ September 2014, (see Docket
ID No. EPA–HQ–OAR–2010–0929).
Burden is defined at 5 CFR 1320.3(b).
An agency may not conduct or
sponsor, and a person is not required to
respond to, a collection of information
unless it displays a currently valid OMB
control number. The OMB control
numbers for the EPA’s regulations in 40
CFR are listed in 40 CFR part 9. When
this ICR is approved by OMB, the
Agency will publish a technical
amendment to 40 CFR part 9 in the
Federal Register to display the OMB
control number for the approved
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D. Unfunded Mandates Reform Act
(UMRA)
The final amendments and
confidentiality determinations do not
contain a Federal mandate that may
result in expenditures of $100 million or
more for State, local, and tribal
governments, in the aggregate, or the
private sector in any one year. This
action finalizes the following
requirements: (1) Requirements for
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certain reporters under 23 subparts to
use an EPA-provided IVT instead of
reporting certain data elements for
which disclosure concerns have been
identified, (2) lengthening the record
retention time for reporters required to
use IVT, and (3) new data elements to
be reported for certain reporters using
IVT and confidentiality determinations
for these new data element. As
discussed in Section IV of this
preamble, for the first year, the total
collective impact on regulated entities is
(1) $383,000, or $67 per entity, for using
IVT; and (2) $55,000, or $93 per entity,
for the final new data elements to be
reported. Thus, the final amendments
and confidentiality determinations are
not subject to the requirements of
sections 202 or 205 of UMRA.
This final rule is also not subject to
the requirements of section 203 of
UMRA because it contains no regulatory
requirements that might significantly or
uniquely affect small governments. This
action amends reporting and
recordkeeping requirements and
verification procedures for certain
reporters in the GHGRP. In addition, the
EPA is finalizing confidentiality
determinations for the new data
elements added in this action. As
discussed in Section IV of this
preamble, the total collective impact on
regulated entities is $438,000 in the first
year, and $55,000 annually thereafter.
Because this impact on each individual
facility is estimated to be approximately
$67–$160 in the first year and $93
annually thereafter, the EPA has
determined that the provisions in this
action will not significantly impact
small governments. In addition, because
none of the provisions apply
specifically to small governments, the
EPA has determined that the provisions
in this action will not uniquely impact
small governments. Therefore, this
action is not subject to the requirements
of section 203 of the UMRA.
E. Executive Order 13132: Federalism
The final rule 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, as specified in
Executive Order 13132. The final
amendments and confidentiality
determinations apply to facilities that
directly emit greenhouses gases and fuel
and chemicals suppliers. These changes
do not apply to governmental entities
unless the government entity owns a
facility that directly emits GHGs above
threshold levels (such as a large
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stationary combustion device), so
relatively few government facilities will
be affected. Moreover, for government
facilities that are subject to the rule, the
final revisions will not have a
significant cost impact. This final rule
also does not limit the power of States
or localities to collect GHG data and/or
regulate GHG emissions. Thus,
Executive Order 13132 does not apply
to this rule.
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
This final rule does not have tribal
implications, as specified in Executive
Order 13175 (65 FR 67249, November 9,
2000). The final amendments and
confidentiality determinations apply
directly to facilities that directly emit
GHGs or that are suppliers of GHGs.
They will not have tribal implications
unless the tribal entity owns a facility
that directly emits GHGs above
threshold levels (such as a landfill or
large combustion device). Relatively few
tribal facilities would be affected. Thus,
Executive Order 13175 does not apply
to this action.
tkelley on DSK3SPTVN1PROD with RULES3
G. Executive Order 13045: Protection of
Children From Environmental Health
Risks and Safety Risks
The EPA interprets Executive Order
13045 (62 FR 19885, April 23, 1997) as
applying only to those regulatory
actions that concern health or safety
risks, such that the analysis required
under section 5–501 of the Executive
Order has the potential to influence the
regulation. This final rule is not subject
to Executive Order 13045 because it
does not establish an environmental
standard intended to mitigate health or
safety risks.
H. Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution, or Use
This final rule is not a ‘‘significant
energy action’’ as defined in Executive
Order 13211 (66 FR 28355, May 22,
2001), because it is not likely to have a
significant adverse effect on the supply,
distribution, or use of energy. Part 98
relates to monitoring, reporting, and
recordkeeping and does not impact
energy supply, distribution, or use. This
final rule amends reporting and
recordkeeping requirements and
verification procedures for the GHGRP.
In addition, the EPA is finalizing
confidentiality determinations for the
new data elements added in this
rulemaking. These final amendments
and confidentiality determinations do
not make any changes to the existing
monitoring, recordkeeping, or reporting
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requirements under Part 98 that affect
the supply, distribution, or use of
energy.
I. National Technology Transfer and
Advancement Act
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (NTTAA), Public Law No.
104–113, 12(d) (15 U.S.C. 272 note)
directs the EPA to use voluntary
consensus standards in its regulatory
activities unless to do so would be
inconsistent with applicable law or
otherwise impractical. Voluntary
consensus standards are technical
standards (e.g., materials specifications,
test methods, sampling procedures, and
business practices) that are developed or
adopted by voluntary consensus
standards bodies. NTTAA directs the
EPA to provide Congress, through the
OMB, explanations when the Agency
decides not to use available and
applicable voluntary consensus
standards.
This final rulemaking does not
involve any new technical standards.
Therefore, the EPA is not considering
the use of any voluntary consensus
standards.
J. Executive Order 12898: Federal
Actions To Address Environmental
Justice in Minority Populations and
Low-Income Populations
Executive Order 12898 (59 FR 7629,
February 16, 1994) establishes Federal
executive policy on environmental
justice. Its main provision directs
Federal agencies, to the greatest extent
practicable and permitted by law, to
make environmental justice part of their
mission by identifying and addressing,
as appropriate, disproportionately high
and adverse human health or
environmental effects of their programs,
policies, and activities on minority
populations and low-income
populations in the United States.
The EPA has determined that these
final rule amendments and
confidentiality determinations will not
have disproportionately high and
adverse human health or environmental
effects on minority or low-income
populations because the amendments
do not affect the level of protection
provided to human health or the
environment. This is because the final
amendments address information
collection and reporting and verification
procedures.
K. Congressional Review Act
The Congressional Review Act, 5
U.S.C. 801 et seq., as added by the Small
Business Regulatory Enforcement
Fairness Act of 1996, generally provides
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63779
that before a rule may take effect, the
agency promulgating the rule must
submit a rule report, which includes a
copy of the rule, to each House of the
Congress and to the Comptroller General
of the United States. The EPA will
submit a report containing this rule and
other required information to the U.S.
Senate, the U.S. House of
Representatives, and the Comptroller
General of the United States prior to
publication of the rule in the Federal
Register. A major rule cannot take effect
until 60 days after it is published in the
Federal Register. This action is not a
‘‘major rule’’ as defined by 5 U.S.C.
804(2). This rule will be effective on
November 24, 2014.
List of Subjects 40 CFR Part 98
Environmental protection,
Administrative practice and procedure,
Greenhouse gases, Reporting and
recordkeeping requirements.
Dated: September 26, 2014.
Gina McCarthy,
Administrator.
For the reasons stated in the
preamble, the Environmental Protection
Agency amends title 40, chapter I, of the
Code of Federal Regulations as follows:
PART 98—MANDATORY
GREENHOUSE GAS REPORTING
1. The authority citation for part 98
continues to read as follows:
■
Authority: 42 U.S.C. 7401, et seq.
Subpart A—General Provision
2. Section 98.3 is amended by revising
paragraphs (c)(4)(vii), (d)(3)(v), (g)
introductory text, and (g)(2)(i) to read as
follows:
■
§ 98.3 What are the general monitoring,
reporting, recordkeeping and verification
requirements of this part?
*
*
*
*
*
(c) * * *
(4) * * *
(vii) The owner or operator of a
facility is not required to report the data
elements specified in Table A–6 of this
subpart for calendar years 2010 through
2011 until March 31, 2013. The owner
or operator of a facility is not required
to report the data elements specified in
Table A–7 of this subpart for calendar
years 2010 through 2013 until March 31,
2015 (as part of the annual report for
reporting year 2014), except as
otherwise specified in Table A–7 of this
subpart.
*
*
*
*
*
(d) * * *
(3) * * *
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(v) For each stationary fuel
combustion source that meets the
criteria specified in § 98.36(f), report
any facility operating data or process
information used for the GHG emission
calculations. A stationary fuel
combustion source that does not meet
the criteria specified in § 98.36(f) must
either report the data specified in this
paragraph (d)(3)(v) in the annual report
or use verification software according to
§ 98.5(b) in lieu of reporting the data
specified in this paragraph.
*
*
*
*
*
(g) Recordkeeping. An owner or
operator that is required to report GHGs
under this part must keep records as
specified in this paragraph (g). Except as
otherwise provided in this paragraph,
retain all required records for at least 3
years from the date of submission of the
annual GHG report for the reporting
year in which the record was generated.
The records shall be kept in an
electronic or hard-copy format (as
appropriate) and recorded in a form that
is suitable for expeditious inspection
and review. If the owner or operator of
a facility is required under § 98.5(b) to
use verification software specified by
the Administrator, then all records
required for the facility under this part
must be retained for at least 5 years from
the date of submission of the annual
GHG report for the reporting year in
which the record was generated, starting
with records for reporting year 2010.
Upon request by the Administrator, the
records required under this section must
be made available to EPA. Records may
be retained off site if the records are
readily available for expeditious
inspection and review. For records that
are electronically generated or
maintained, the equipment or software
necessary to read the records shall be
made available, or, if requested by EPA,
electronic records shall be converted to
paper documents. You must retain the
following records, in addition to those
records prescribed in each applicable
subpart of this part:
*
*
*
*
*
(2) * * *
(i) The GHG emissions calculations
and methods used. For data required by
§ 98.5(b) to be entered into verification
software specified in § 98.5(b), maintain
the entered data in the format generated
by the verification software according to
§ 98.5(b).
*
*
*
*
*
■ 3. Section 98.5 is revised to read as
follows:
§ 98.5
How is the report submitted?
(a) Each GHG report and certificate of
representation for a facility or supplier
must be submitted electronically in
accordance with the requirements of
§ 98.4 and in a format specified by the
Administrator.
(b) For reporting year 2014 and
thereafter, you must enter into
verification software specified by the
Administrator the data specified in the
verification software records provision
in each applicable recordkeeping
section. For each data element entered
into the verification software, if the
software produces a warning message
for the data value and you elect not to
revise the data value, you may provide
an explanation in the verification
software of why the data value is not
being revised.
■ 4. Table A–7 to Subpart A of Part 98
is revised to read as follows:
TABLE A–7 TO SUBPART A OF PART 98—DATA ELEMENTS THAT ARE INPUTS TO EMISSION EQUATIONS AND FOR WHICH
THE REPORTING DEADLINE IS MARCH 31, 2015
Specific data elements for which reporting date is March 31,
2015 (‘‘All’’ means all data elements in the cited paragraph
are not required to be reported until March 31, 2015)
Rule citation (40 CFR part 98)
A ................................................
C ................................................
C ................................................
98.3(d)(3)(v) .....................................................
98.36(b)(9)(iii) ...................................................
98.36(c)(2)(ix) ...................................................
C ................................................
C ................................................
C ................................................
98.36(e)(2)(i) ....................................................
98.36(e)(2)(ii)(A) ...............................................
98.36(e)(2)(ii)(C) ...............................................
C
C
C
C
C
C
C
E
E
E
E
E
E
H
H
L
tkelley on DSK3SPTVN1PROD with RULES3
Subpart
................................................
................................................
................................................
................................................
................................................
................................................
................................................
................................................
................................................
................................................
................................................
................................................
................................................
................................................
................................................
................................................
98.36(e)(2)(ii)(D) ...............................................
98.36(e)(2)(iv)(A) ..............................................
98.36(e)(2)(iv)(C) ..............................................
98.36(e)(2)(iv)(F) ..............................................
98.36(e)(2)(ix)(D) ..............................................
98.36(e)(2)(ix)(E) ..............................................
98.36(e)(2)(ix)(F) ..............................................
98.56(g) ............................................................
98.56(h) ............................................................
98.56(j)(4) .........................................................
98.56(j)(5) .........................................................
98.56(j)(6) .........................................................
98.56(l) .............................................................
98.86(b)(11) ......................................................
98.86(b)(13) ......................................................
98.126(b)(1) ......................................................
L ................................................
L ................................................
98.126(b)(2) ......................................................
98.126(b)(6) ......................................................
L ................................................
98.126(b)(7) ......................................................
L ................................................
98.126(b)(8)(i) ..................................................
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All.a
Only estimate of the heat input.a
Only estimate of the heat input from each type of fuel listed in
Table C–2 of subpart C of this part.a
All.a
All.a
Only HHV value for each calendar month in which HHV determination is required.a
All.a
All.a
All.a
All.a
All.a
All.a
All.a
All.
All.
All.
All.
All.
All.
All.
Name of raw kiln feed or raw material.
Only data used in calculating the absolute errors and data
used in calculating the relative errors.
All.
Only mass of each fluorine-containing reactant fed into the
process.
Only mass of each fluorine-containing product produced by
the process.
Only mass of each fluorine-containing product that is removed from the process and fed into the destruction device.
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63781
TABLE A–7 TO SUBPART A OF PART 98—DATA ELEMENTS THAT ARE INPUTS TO EMISSION EQUATIONS AND FOR WHICH
THE REPORTING DEADLINE IS MARCH 31, 2015—Continued
Specific data elements for which reporting date is March 31,
2015 (‘‘All’’ means all data elements in the cited paragraph
are not required to be reported until March 31, 2015)
Rule citation (40 CFR part 98)
L ................................................
98.126(b)(8)(ii) ..................................................
L ................................................
98.126(b)(8)(iii) .................................................
L ................................................
98.126(b)(8)(iv) .................................................
L
L
L
L
L
L
L
L
tkelley on DSK3SPTVN1PROD with RULES3
Subpart
................................................
................................................
................................................
................................................
................................................
................................................
................................................
................................................
98.126(b)(8)(v) .................................................
98.126(b)(9)(i) ..................................................
98.126(b)(9)(ii) ..................................................
98.126(b)(9)(iii) .................................................
98.126(b)(10) ....................................................
98.126(b)(11) ....................................................
98.126(b)(12) ....................................................
98.126(c)(1) ......................................................
L ................................................
L ................................................
L ................................................
L ................................................
L ................................................
O ...............................................
O ...............................................
O ...............................................
Q ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
98.126(c)(2) ......................................................
98.126(d) ..........................................................
98.126(f)(1) .......................................................
98.126(g)(1) ......................................................
98.126(h)(2) ......................................................
98.156(d)(2) ......................................................
98.156(d)(3) ......................................................
98.156(d)(4) ......................................................
98.176(f)(1) .......................................................
98.236(c)(1)(i) ...................................................
98.236(c)(1)(ii) ..................................................
98.236(c)(1)(iii) .................................................
98.236(c)(2)(i) ...................................................
98.236(c)(3)(i) ...................................................
98.236(c)(3)(ii) ..................................................
98.236(c)(3)(iii) .................................................
98.236(c)(3)(iv) .................................................
98.236(c)(4)(i)(A) ..............................................
98.236(c)(4)(i)(B) ..............................................
98.236(c)(4)(i)(C) ..............................................
98.236(c)(4)(i)(D) ..............................................
98.236(c)(4)(i)(E) ..............................................
98.236(c)(4)(i)(F) ..............................................
98.236(c)(4)(i)(G) .............................................
98.236(c)(4)(i)(H) ..............................................
98.236(c)(4)(ii)(A) .............................................
98.236(c)(5)(i)(D) ..............................................
98.236(c)(5)(ii)(C) .............................................
98.236(c)(6)(i)(B) ..............................................
98.236(c)(6)(i)(D) ..............................................
98.236(c)(6)(i)(E) ..............................................
98.236(c)(6)(i)(F) ..............................................
98.236(c)(6)(i)(G) .............................................
98.236(c)(6)(i)(H) ..............................................
98.236(c)(6)(ii)(A) .............................................
98.236(c)(6)(ii)(B) .............................................
98.236(c)(7)(i)(A) ..............................................
98.236(c)(8)(i)(F) ..............................................
98.236(c)(8)(i)(K) ..............................................
98.236(c)(8)(ii)(A) .............................................
98.236(c)(8)(ii)(H) .............................................
98.236(c)(8)(iii)(A) ............................................
98.236(c)(8)(iii)(B) ............................................
98.236(c)(8)(iii)(G) ............................................
98.236(c)(12)(ii) ................................................
98.236(c)(12)(v) ................................................
98.236(c)(13)(i)(E) ............................................
98.236(c)(13)(i)(F) ............................................
98.236(c)(13)(ii)(A) ...........................................
98.236(c)(13)(ii)(B) ...........................................
98.236(c)(13)(iii)(A) ..........................................
98.236(c)(13)(iii)(B) ..........................................
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Only mass of each fluorine-containing by-product that is removed from the process and fed into the destruction device.
Only mass of each fluorine-containing reactant that is removed from the process and fed into the destruction device.
Only mass of each fluorine-containing by-product that is removed from the process and recaptured.
All.
All.
All.
All.
All.
All.
All.
Only quantity of the process activity used to estimate emissions.
All.
Only estimate of missing data.
All.
All.
All.
All.
All.
All.
All.
All.
All.
All.
All.
All.
Only Calculation Methodology 2 of § 98.233(d).
All.
All.
All.
All.
All.
All.
All.
All.
All.
All.
All.
All.
All.
All.b
All.b
All.b
All.b
Only the amount of natural gas required.
Only the amount of natural gas required.
All.
All.
Only for Equation W–14A of § 98.233.
All.b
All.
All.b
All.
All.
All.
All.
All.
All.
All.
All.
All.
All.
All.
All.
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Federal Register / Vol. 79, No. 206 / Friday, October 24, 2014 / Rules and Regulations
TABLE A–7 TO SUBPART A OF PART 98—DATA ELEMENTS THAT ARE INPUTS TO EMISSION EQUATIONS AND FOR WHICH
THE REPORTING DEADLINE IS MARCH 31, 2015—Continued
Specific data elements for which reporting date is March 31,
2015 (‘‘All’’ means all data elements in the cited paragraph
are not required to be reported until March 31, 2015)
Subpart
Rule citation (40 CFR part 98)
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
W ...............................................
Y ................................................
Y ................................................
Y ................................................
98.236(c)(13)(v)(A) ...........................................
98.236(c)(14)(i)(B) ............................................
98.236(c)(14)(ii)(A) ...........................................
98.236(c)(14)(ii)(B) ...........................................
98.236(c)(14)(iii)(A) ..........................................
98.236(c)(14)(iii)(B) ..........................................
98.236(c)(14)(v)(A) ...........................................
98.236(c)(15)(ii)(A) ...........................................
98.236(c)(15)(ii)(B) ...........................................
98.236(c)(16)(viii) .............................................
98.236(c)(16)(ix) ...............................................
98.236(c)(16)(x) ................................................
98.236(c)(16)(xi) ...............................................
98.236(c)(16)(xii) ..............................................
98.236(c)(16)(xiii) .............................................
98.236(c)(16)(xiv) .............................................
98.236(c)(16)(xv) ..............................................
98.236(c)(16)(xvi) .............................................
98.236(c)(17)(ii) ................................................
98.236(c)(17)(iii) ...............................................
98.236(c)(17)(iv) ...............................................
98.236(c)(18)(i) .................................................
98.236(c)(18)(ii) ................................................
98.236(c)(19)(iv) ...............................................
98.236(c)(19)(vii) ..............................................
98.256(h)(5)(i) ..................................................
98.256(k)(4) ......................................................
98.256(n)(3) ......................................................
Y ................................................
98.256(o)(4)(vi) .................................................
AA .............................................
CC .............................................
CC .............................................
CC .............................................
CC .............................................
CC .............................................
CC .............................................
II ................................................
II ................................................
II ................................................
98.276(e) ..........................................................
98.296(b)(10)(i) ................................................
98.296(b)(10)(ii) ................................................
98.296(b)(10)(iii) ...............................................
98.296(b)(10)(iv) ...............................................
98.296(b)(10)(v) ...............................................
98.296(b)(10)(vi) ...............................................
98.356(d)(2) ......................................................
98.356(d)(3) ......................................................
98.356(d)(4) ......................................................
II ................................................
98.356(d)(5) ......................................................
II ................................................
98.356(d)(6) ......................................................
All.
All.
All.
All.
All.
All.
All.
All.
All.
All.
All.
All.
All.
All.
All.
All.
All.
All.
All.
All.
All.
All.
All.
All.
All.
Only value of the correction.
Only mole fraction of methane in coking gas.
All (if used in Equation Y–21 of § 98.253 to calculate emissions from equipment leaks).
Only tank-specific methane composition data and gas generation rate data.
All.
All.
All.
All.
All.
All.
All.
All (if conducting weekly sampling).
All (if conducting weekly sampling).
Only weekly average temperature (if conducting weekly sampling).
Only weekly average moisture content (if conducting weekly
sampling).
Only weekly average pressure (if conducting weekly sampling).
a Required to be reported only by: (1) Stationary fuel combustion sources (e.g., individual units, aggregations of units, common pipes, or common stacks) subject to subpart C of this part that contain at least one combustion unit connected to a fuel-fired electric generator owned or operated by an entity that is subject to regulation of customer billing rates by the PUC (excluding generators connected to combustion units subject to
40 CFR part 98, subpart D) and that are located at a facility for which the sum of the nameplate capacities for all such electric generators is
greater than or equal to 1 megawatt electric output; and (2) stationary fuel combustion sources (e.g., individual units, aggregations of units, common pipes, or common stacks) subject to subpart C of this part that do not meet the criteria in (1) of this footnote that elect to report these data
elements, as provided in § 98.36(a), for reporting year 2014.
b This rule citation provides an option to delay reporting of this data element for certain wildcat wells and/or delineation wells.
The revisions and additions read as
follows:
tkelley on DSK3SPTVN1PROD with RULES3
Subpart C—General Stationary Fuel
Combustion Sources
■
5. Section 98.36 is amended by:
a. Revising paragraph (a);
b. Revising paragraph (b)(9)(iii) and
adding paragraph (b)(9)(iv);
■ c. Revising paragraphs (c)(2)(ix) and
(x);
■ d. Revising paragraph (e)(2)(ii)(C) and
adding paragraph (e)(2)(ii)(E); and
■ e. Adding paragraph (f).
§ 98.36
■
■
■
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Data reporting requirements.
(a) In addition to the facility-level
information required under § 98.3, the
annual GHG emissions report shall
contain the unit-level or process-level
data specified in paragraphs (b) through
(f) of this section, as applicable, for each
stationary fuel combustion source (e.g.,
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individual unit, aggregation of units,
common pipe, or common stack) except
as otherwise provided in this paragraph
(a). For the data specified in paragraphs
(b)(9)(iii), (c)(2)(ix), (e)(2)(i), (e)(2)(ii)(A),
(e)(2)(ii)(C), (e)(2)(ii)(D), (e)(2)(iv)(A),
(e)(2)(iv)(C), (e)(2)(iv)(F), and
(e)(2)(ix)(D) through (F) of this section,
the owner or operator of a stationary
fuel combustion source that does not
meet the criteria specified in paragraph
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Federal Register / Vol. 79, No. 206 / Friday, October 24, 2014 / Rules and Regulations
(f) of this section may elect either to
report the data specified in this sentence
in the annual report or to use
verification software according to
§ 98.5(b) in lieu of reporting these data.
If you elect to use this verification
software, you must use the verification
software according to § 98.5(b) for all of
these data that apply to the stationary
fuel combustion source.
(b) * * *
(9) * * *
(iii) An estimate of the heat input
from each type of fuel listed in Table C–
2 of this subpart that was combusted in
the unit during the report year.
(iv) The annual CH4 and N2O
emissions for each type of fuel listed in
Table C–2 of this subpart that was
combusted in the unit during the report
year, expressed in metric tons of each
gas and in metric tons of CO2e.
*
*
*
*
*
(c) * * *
(2) * * *
(ix) An estimate of the heat input from
each type of fuel listed in Table C–2 of
this subpart that was combusted in the
units sharing the common stack or duct
during the report year.
(x) For each type of fuel listed in
Table C–2 of this subpart that was
combusted during the report year in the
units sharing the common stack or duct
during the report year, the annual CH4
and N2O mass emissions from the units
sharing the common stack or duct,
expressed in metric tons of each gas and
in metric tons of CO2e.
*
*
*
*
*
(e) * * *
(2) * * *
(ii) * * *
(C) The high heat values used in the
CO2 emissions calculations for each
type of fuel combusted during the
reporting year, in mmBtu per short ton
for solid fuels, mmBtu per gallon for
liquid fuels, and mmBtu per scf for
gaseous fuels. Report a HHV value for
each calendar month in which HHV
determination is required. If multiple
values are obtained in a given month,
report the arithmetic average value for
the month.
*
*
*
*
*
(E) For each HHV used in the CO2
emissions calculations for each type of
fuel combusted during the reporting
year, indicate whether the HHV is a
measured value or a substitute data
value.
*
*
*
*
*
(f) Each stationary fuel combustion
source (e.g., individual unit, aggregation
of units, common pipe, or common
stack) subject to reporting under
paragraph (b) or (c) of this section must
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indicate if both of the following two
conditions are met:
(1) The stationary fuel combustion
source contains at least one combustion
unit connected to a fuel-fired electric
generator owned or operated by an
entity that is subject to regulation of
customer billing rates by the public
utility commission (excluding
generators that are connected to
combustion units that are subject to
subpart D of this part).
(2) The stationary fuel combustion
source is located at a facility for which
the sum of the nameplate capacities for
all electric generators specified in
paragraph (f)(1) of this section is greater
than or equal to 1 megawatt electric
output.
■ 6. Section 98.37 is revised to read as
follows:
§ 98.37
Records that must be retained.
In addition to the requirements of
§ 98.3(g), you must retain:
(a) The applicable records specified in
§§ 98.34(f) and (g), 98.35(b), and
98.36(e).
(b) Verification software records. For
each stationary fuel combustion source
that elects to use the verification
software specified in § 98.5(b) rather
than report data specified in paragraphs
(b)(9)(iii), (c)(2)(ix), (e)(2)(i), (e)(2)(ii)(A),
(e)(2)(ii)(C), (e)(2)(ii)(D), (e)(2)(iv)(A),
(e)(2)(iv)(C), (e)(2)(iv)(F), and
(e)(2)(ix)(D) through (F) of this section,
you must keep a record of the file
generated by the verification software
for the applicable data specified in
paragraphs (b)(1) through (36) of this
section. Retention of this file satisfies
the recordkeeping requirement for the
data in paragraphs (b)(1) through (36) of
this section.
(1) Mass of each solid fuel combusted
(tons/year) (Equation C–1 of § 98.33).
(2) Volume of each liquid fuel
combusted (gallons/year) (Equation C–
1).
(3) Volume of each gaseous fuel
combusted (scf/year) (Equation C–1).
(4) Annual natural gas usage (therms/
year) (Equation C–1a of § 98.33).
(5) Annual natural gas usage (mmBtu/
year) (Equation C–1b of § 98.33).
(6) Mass of each solid fuel combusted
(tons/year) (Equation C–2a of § 98.33).
(7) Volume of each liquid fuel
combusted (gallons/year) (Equation C–
2a).
(8) Volume of each gaseous fuel
combusted (scf/year) (Equation C–2a).
(9) Measured high heat value of each
solid fuel, for month (which may be the
arithmetic average of multiple
determinations), or, if applicable, an
appropriate substitute data value
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63783
(mmBtu per ton) (Equation C–2b of
§ 98.33).
(10) Measured high heat value of each
liquid fuel, for month (which may be
the arithmetic average of multiple
determinations), or, if applicable, an
appropriate substitute data value
(mmBtu per gallons) (Equation C–2b).
(11) Measured high heat value of each
gaseous fuel, for month (which may be
the arithmetic average of multiple
determinations), or, if applicable, an
appropriate substitute data value
(mmBtu per scf) (Equation C–2b).
(12) Mass of each solid fuel
combusted during month (tons)
(Equation C–2b).
(13) Volume of each liquid fuel
combusted during month (gallons)
(Equation C–2b).
(14) Volume of each gaseous fuel
combusted during month (scf) (Equation
C–2b).
(15) Total mass of steam generated by
municipal solid waste or each solid fuel
combustion during the reporting year
(pounds steam) (Equation C–2c of
§ 98.33).
(16) Ratio of the boiler’s maximum
rated heat input capacity to its design
rated steam output capacity (MMBtu/
pounds steam) (Equation C–2c).
(17) Annual mass of each solid fuel
combusted (short tons/year) (Equation
C–3 of § 98.33).
(18) Annual average carbon content of
each solid fuel (percent by weight,
expressed as a decimal fraction)
(Equation C–3).
(19) Annual volume of each liquid
fuel combusted (gallons/year) (Equation
C–4 of § 98.33).
(20) Annual average carbon content of
each liquid fuel (kg C per gallon of fuel)
(Equation C–4).
(21) Annual volume of each gaseous
fuel combusted (scf/year) (Equation C–
5 of § 98.33).
(22) Annual average carbon content of
each gaseous fuel (kg C per kg of fuel)
(Equation C–5).
(23) Annual average molecular weight
of each gaseous fuel (kg/kg-mole)
(Equation C–5).
(24) Molar volume conversion factor
at standard conditions, as defined in
§ 98.6 (scf per kg-mole) (Equation C–5).
(25) Identify for each fuel if you will
use the default high heat value from
Table C–1 of this subpart, or actual high
heat value data (Equation C–8 of
§ 98.33).
(26) High heat value of each solid fuel
(mmBtu/tons) (Equation C–8).
(27) High heat value of each liquid
fuel (mmBtu/gallon) (Equation C–8).
(28) High heat value of each gaseous
fuel (mmBtu/scf) (Equation C–8).
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(29) Cumulative annual heat input
from combustion of each fuel (mmBtu)
(Equation C–10 of § 98.33).
(30) Total quantity of each solid fossil
fuel combusted in the reporting year, as
defined in § 98.6 (pounds) (Equation C–
13 of § 98.33).
(31) Total quantity of each liquid
fossil fuel combusted in the reporting
year, as defined in § 98.6 (gallons)
(Equation C–13).
(32) Total quantity of each gaseous
fossil fuel combusted in the reporting
year, as defined in § 98.6 (scf) (Equation
C–13).
(33) High heat value of the each solid
fossil fuel (Btu/lb) (Equation C–13).
(34) High heat value of the each liquid
fossil fuel (Btu/gallons) (Equation C–13).
(35) High heat value of the each
gaseous fossil fuel (Btu/scf) (Equation
C–13).
(36) Fuel-specific carbon based Ffactor per fuel (scf CO2/mmBtu)
(Equation C–13).
Subpart E—Adipic Acid Production
7. Section 98.56 is amended by:
a. Revising the introductory text;
b. Removing and reserving paragraphs
(b), (c), and (j)(1) and (3); and
■ c. Adding paragraphs (m) and (n).
The revisions and additions read as
follows:
■
■
■
§ 98.56
Data reporting requirements.
tkelley on DSK3SPTVN1PROD with RULES3
Records that must be retained.
In addition to the information
required by § 98.3(g), you must retain
the records specified in paragraphs (a)
through (i) of this section at the facility
level:
*
*
*
*
*
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Subpart F—Aluminum Production
9. Section 98.66 is amended by:
a. Removing and reserving paragraphs
(a) and (c)(2);
■ b. Revising paragraphs (c)(3), (e)(1),
and (f)(1); and
■ c. Removing and reserving paragraph
(g).
The revisions read as follows:
■
■
§ 98.66
In addition to the information
required by § 98.3(c), each annual report
must contain the information specified
in paragraphs (a) through (n) of this
section at the facility level.
*
*
*
*
*
(m) If only cyclohexane is oxidized to
produce adipic acid and the quantity is
known, report the information specified
in paragraph (m)(1) of this section. If
materials other than cyclohexane are
oxidized to produce adipic acid, report
the information specified in paragraph
(m)(2) of this section.
(1) Annual quantity of cyclohexane
(tons) used to produce adipic acid.
(2) Annual quantity of cyclohexanone
and cyclohexanol mixture (tons) used to
produce adipic acid.
(n) Annual percent N2O emission
reduction for all production units
combined.
■ 8. Section 98.57 is amended by
revising the introductory text and
adding paragraph (i) to read as follows:
§ 98.57
(i) Verification software records. You
must keep a record of the file generated
by the verification software specified in
§ 98.5(b) for the applicable data
specified in paragraphs (i)(1) through (3)
of this section. Retention of this file
satisfies the recordkeeping requirement
for the data in paragraphs (i)(1) through
(3) of this section.
(1) Annual adipic acid production
from each adipic acid production unit
(tons) (Equations E–2, E–3a, E–3b, E–3c,
and E–3d of § 98.53).
(2) Production rate per test run during
the performance test for each
production unit test run (tons adipic
acid produced/hr) (Equation E–1 of
§ 98.53).
(3) Annual adipic acid production per
N2O abatement technology during
which N2O abatement technology was
used (tons adipic acid produced)
(Equation E–2).
Data reporting requirements.
*
*
*
*
*
(c) * * *
(3) The last date when the smelterspecific-slope coefficients (or
overvoltage emission factors) were
measured.
*
*
*
*
*
(e) * * *
(1) Annual anode consumption if
using the method in § 98.63(g).
*
*
*
*
*
(f) * * *
(1) Annual paste consumption if using
the method in § 98.63(g).
*
*
*
*
*
■ 10. Section 98.67 is amended by
adding paragraph (i) to read as follows:
§ 98.67
Records that must be retained.
*
*
*
*
*
(i) Verification software records. You
must keep a record of the file generated
by the verification software specified in
§ 98.5(b) for the applicable data
specified in paragraphs (i)(1) through
(30) of this section. Retention of this file
satisfies the recordkeeping requirement
for the data in paragraphs (i)(1) through
(30) of this section.
(1) Slope coefficient per potline per
month (kg CF4/metric ton Al)/(AE-Mins/
cell-day)) (Equation F–2 of § 98.63).
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(2) Anode effect minutes per cell-day
per potline per month (AE-Mins/cellday) (Equation F–2).
(3) Anode effect frequency per potline
per month (AE/cell-day) (Equation F–2).
(4) Anode effect duration per potline
per month (minutes) (Equation F–2).
(5) Metal production of aluminum per
potline per month (metric tons)
(Equation F–2).
(6) Overvoltage emission factor per
potline per month (kg CF4/metric ton
Al) (Equation F–3 of § 98.63).
(7) Metal production of aluminum per
potline per month (metric tons)
(Equation F–3).
(8) Weight fraction of C2F6/CF4 per
potline per month (kg C2F6/kg CF4)
(Equation F–4 of § 98.63).
(9) Net annual prebaked anode
consumption (metric tons C/metric tons
Al) (Equation F–5 of § 98.63).
(10) Annual metal production of
aluminum (metric tons) (Equation F–5).
(11) Sulfur content in baked anode
(weight percent) (Equation F–5).
(12) Ash content in baked anode
(weight percent) (Equation F–5).
(13) Annual paste consumption
(metric ton/metric ton Al) (Equation F–
6 of § 98.63).
(14) Annual metal production of
aluminum (metric tons) (Equation F–6).
(15) Annual emissions of cyclohexane
soluble matter (kg/metric ton Al)
(Equation F–6).
(16) Binder content of paste (weight
percent) (Equation F–6).
(17) Sulfur content of pitch (weight
percent) (Equation F–6).
(18) Ash content of pitch (weight
percent) (Equation F–6).
(19) Hydrogen content of pitch
(weight percent) (Equation F–6).
(20) Sulfur content in calcined coke
(weight percent) (Equation F–6).
(21) Ash content in calcined coke
(weight percent) (Equation F–6).
(22) Carbon in skimmed dust from
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17:25 Oct 23, 2014
Jkt 235001
§ 98.86
Data reporting requirements.
*
*
*
*
*
(b) * * *
(13) Name of raw kiln feed or raw
material.
*
*
*
*
*
(15) Method used to determine the
monthly clinker production from each
kiln.
(16) Annual clinker production
(metric tons).
(17) Annual average clinker CO2
emission factor for the facility, averaged
across all kilns (metric tons CO2/metric
ton clinker produced).
(18) Annual average CKD CO2
emission factor for the facility, averaged
across all kilns (metric tons CO2/metric
ton CKD produced).
■ 14. Section 98.87 is amended by
adding paragraph (c) to read as follows:
§ 98.87
Records that must be retained.
*
*
*
*
*
(c) Verification software records. You
must keep a record of the file generated
by the verification software specified in
§ 98.5(b) for the applicable data
specified in paragraphs (c)(1) through
(17) of this section. Retention of this file
satisfies the recordkeeping requirement
for the data in paragraphs (c)(1) through
(17) of this section.
(1) Identify per kiln per month if
clinker is measured directly, or is
calculated from raw feed (Equation H–
2 of § 98.83 and the method in
§ 98.84(d)).
(2) Quantity of raw kiln feed in month
from kiln (tons) (Equation H–2 and the
method in § 98.84(d)).
(3) Kiln-specific factor per kiln per
month (ton clinker per ton raw feed)
(Equation H–2 and the method in
§ 98.84(d)).
(4) Quantity of clinker produced in
month from kiln (tons) (Equation H–2
and the method in § 98.84(d)).
(5) Cement kiln dust (CKD) not
recycled to the kiln in quarter from kiln
(tons) (Equation H–2 and the method in
§ 98.84(d)).
(6) Monthly total CaO content of
clinker per kiln (weight fraction)
(Equation H–3 of § 98.83).
(7) Monthly non-calcined CaO content
of clinker per kiln (weight fraction)
(Equation H–3).
(8) Monthly total MgO content of
clinker per kiln (weight fraction)
(Equation H–3).
(9) Monthly non-calcined MgO
content of clinker per kiln (weight
fraction) (Equation H–3).
(10) Quarterly total CaO content of
cement kiln dust not recycled to each
kiln (weight fraction) (Equation H–4 of
§ 98.83).
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63785
(11) Quarterly non-calcined CaO
content of cement kiln dust not recycled
to each kiln (weight fraction) (Equation
H–4).
(12) Quarterly total MgO content of
cement kiln dust not recycled to each
kiln (weight fraction) (Equation H–4).
(13) Quarterly non-calcined MgO
content of cement kiln dust not recycled
to each kiln (weight fraction) (Equation
H–4).
(14) The amount of each raw material
consumed annually per kiln (tons/yr
(dry basis)) (Equation H–5 of § 98.83).
(15) The amount of each raw kiln feed
consumed annually per kiln (tons/yr
(dry basis)) (Equation H–5).
(16) Organic carbon content of each
raw material per kiln, as determined in
§ 98.84(c). Default value is 0.002 weight
fraction (Equation H–5).
(17) Organic carbon content of
combined raw kiln feed per kiln, as
determined in § 98.84(c). Default value
is 0.002 weight fraction (Equation H–5).
Subpart K—Ferroalloy Production
15. Section 98.116 is amended by:
a. Revising paragraph (b).
b. Removing and reserving paragraphs
(e)(4) and (5); and
■ c. Revising paragraph (e)(6).
The revisions read as follows:
■
■
■
§ 98.116
Data reporting requirements.
*
*
*
*
*
(b) If a CEMS is used to measure CO2
emissions, report the annual production
for each ferroalloy product identified in
§ 98.110, from each EAF (tons).
*
*
*
*
*
(e) * * *
(6) List the method used for the
determination of carbon content for
each material included for the
calculation of annual process CO2
emissions for each EAF (e.g., supplier
provided information, analyses of
representative samples you collected).
*
*
*
*
*
■ 16. Section 98.117 is amended by
revising the introductory text and
adding paragraph (e) to read as follows:
§ 98.117
Records that must be retained.
In addition to the records required by
§ 98.3(g), you must retain the records
specified in paragraphs (a) through (e) of
this section for each EAF, as applicable.
*
*
*
*
*
(e) Verification software records. You
must keep a record of the file generated
by the verification software specified in
§ 98.5(b) for the applicable data
specified in paragraphs (e)(1) through
(13) of this section. Retention of this file
satisfies the recordkeeping requirement
for the data in paragraphs (e)(1) through
(13) of this section.
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(1) Carbon content in reducing agent
(percent by weight, expressed as a
decimal fraction) (Equation K–1 of
§ 98.113).
(2) Annual mass of reducing agent
fed, charged, or otherwise introduced
into the EAF (tons) (Equation K–1).
(3) Carbon content of carbon electrode
(percent by weight, expressed as a
decimal fraction) (Equation K–1).
(4) Annual mass of carbon electrode
consumed in the EAF (tons) (Equation
K–1).
(5) Carbon content in ore (percent by
weight, expressed as a decimal fraction)
(Equation K–1).
(6) Annual mass of ore charged to the
EAF (tons) (Equation K–1).
(7) Carbon content in flux material
(percent by weight, expressed as a
decimal fraction) (Equation K–1).
(8) Annual mass of flux material fed,
charged, or otherwise introduced into
the EAF to facilitate slag formation
(tons) (Equation K–1).
(9) Carbon content in alloy product
(percent by weight, expressed as a
decimal fraction) (Equation K–1).
(10) Annual mass of alloy product
produced/tapped in the EAF (tons)
(Equation K–1).
(11) Carbon content in non-product
outgoing material (percent by weight,
expressed as a decimal fraction)
(Equation K–1).
(12) Annual mass of non-product
outgoing material removed from EAF
(tons) (Equation K–1).
(13) CH4 emission factor selected from
Table K–1 of this subpart for each
product (kg of CH4 emissions/metric ton
of alloy product) (Equation K–3 of
§ 98.113).
Subpart N—Glass Production
17. Section 98.146 is amended by
revising paragraph (b)(2) and removing
and reserving paragraphs (b)(4) and (6)
to read as follows:
■
§ 98.146
Data reporting requirements.
*
*
*
*
*
(b) * * *
(2) Annual quantity of each carbonatebased raw material charged (tons) to all
furnaces combined.
*
*
*
*
*
■ 18. Section 98.147 is amended by
revising the introductory text and
adding paragraph (d) to read as follows:
tkelley on DSK3SPTVN1PROD with RULES3
§ 98.147
Records that must be retained.
In addition to the information
required by § 98.3(g), you must retain
the records listed in paragraphs (a)
through (d) of this section.
*
*
*
*
*
(d) Verification software records. You
must keep a record of the file generated
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by the verification software specified in
§ 98.5(b) for the applicable data
specified in paragraphs (d)(1) through
(3) of this section. Retention of this file
satisfies the recordkeeping requirement
for the data in paragraphs (d)(1) through
(3) of this section.
(1) Annual average decimal mass
fraction of carbonate-based mineral in
each carbonate-based raw material for
each continuous glass melting furnace
(specify the default value, if used, or the
value determined according to § 98.144)
(percentage, expressed as a decimal)
(Equation N–1 of § 98.143).
(2) Annual amount of each carbonatebased raw material charged to each
continuous glass melting furnace (tons)
(Equation N–1).
(3) Decimal fraction of each
calcination achieved for carbonatebased raw material for each continuous
glass melting furnace (specify the
default value, if used, or the value
determined according to § 98.144)
(percentage, expressed as a decimal)
(Equation N–1).
Subpart O—HCFC–22 Production and
HFC–23 Destruction
19. Section 98.156 is amended by:
a. Removing and reserving paragraphs
(a)(2), (a)(7) through (10), and (b)(1) and
(2);
■ b. Revising paragraph (d) introductory
text; and
■ c. Removing and reserving paragraphs
(d)(1) and (5) and (e)(1).
The revisions read as follows:
■
■
§ 98.156
Data reporting requirements.
*
*
*
*
*
(d) If the HFC–23 concentration
measured pursuant to § 98.154(l) is
greater than that measured during the
performance test that is the basis for the
destruction efficiency (DE), the facility
shall report the following:
*
*
*
*
*
■ 20. Section 98.157 is amended by
adding paragraph (c) to read as follows:
§ 98.157
Records that must be retained.
*
*
*
*
*
(c) Verification software records. You
must keep a record of the file generated
by the verification software specified in
§ 98.5(b) for the applicable data
specified in paragraphs (c)(1) through
(16) of this section. Retention of this file
satisfies the recordkeeping requirement
for the data in paragraphs (c)(1) through
(16) of this section.
(1) Factor to account for the loss of
HCFC–22 upstream of the measurement
over the period, determined pursuant to
§ 98.154(e) (Equation O–3 of § 98.153).
(2) Mass of HCFC–22 that is measured
coming out of the production process
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over the period. A period can be one
year (kg) (Equation O–3).
(3) Mass of used HCFC–22 that is
added to the production process
upstream of the output measurement
over the period. A period can be one
year (kg) (Equation O–3).
(4) Mass of HFC–23 generated
annually per HCFC–22 production
process (metric tons) (Equation O–4 of
§ 98.153).
(5) Mass of HFC–23 sent off site for
sale annually per HCFC–22 production
process (metric tons) (Equation O–4).
(6) Mass of HFC–23 sent off site for
destruction annually per HCFC–22
production process (metric tons)
(Equation O–4).
(7) Mass of HFC–23 destroyed on site
per HCFC–22 production process
(metric tons) (Equation O–4).
(8) HFC–23 in storage at end of year
per HCFC–22 production process
(metric tons) (Equation O–4).
(9) HFC–23 in storage at beginning of
year per HCFC–22 production process
(metric tons) (Equation O–4).
(10) Mass of HFC–23 fed into each
destruction device annually per HCFC–
22 production process (metric tons)
(Equation O–9 of § 98.153 and the
calculation method in either
§ 98.154(l)(1) or (2)).
(11) Identify if each destruction
efficiency for each HCFC-22 production
process is entered directly, or is
calculated using § 98.154(l)(1), or is
calculated using § 98.154(l)(2) (Equation
O–9 and the calculation method in
either § 98.154(l)(1) or (2)).
(12) Destruction efficiency of each
destruction device for each HCFC-22
production process (decimal fraction)
(Equation O–9 and the calculation
method in either § 98.154(l)(1) or (2)).
(13) Volumetric flow rate at the inlet
of each destruction device for each
HCFC-22 production process from
previous test (kg/hr) (Equation O–9 and
the calculation method in either
§ 98.154(l)(1) or (2)).
(14) Volumetric flow rate at the inlet
of destruction device during test for
each HCFC-22 production process (kg/
hr) (Equation O–9 and the calculation
method in either § 98.154(l)(1) or (2)).
(15) Concentration of HFC-23 at the
inlet of destruction device for each
HCFC-22 production process from
previous test (weight fraction) (Equation
O–9 and the calculation method in
either § 98.154(l)(1) or (2)).
(16) Concentration of HFC-23 at the
inlet of destruction device for each
HCFC-22 production process during test
(weight fraction) (Equation O–9 and the
calculation method in either
§ 98.154(l)(1) or (2)).
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MVC = Molar volume conversion factor at
standard conditions, as defined in § 98.6.
Use 849.5 scf per kg mole if you select
68°F as standard temperature and 836.6
scf per kg mole if you select 60°F as
standard temperature.
Fl,i = Annual volume of the liquid fuel
combusted (‘‘(Fl)’’ included in Equation
Q–1) for each process unit (gallons).
Fs,i = Annual mass of the solid fuel
combusted (‘‘(Fs)’’ in Equation Q–1) for
each process unit (metric tons).
Where:
NFI = Annual mass of all non-fuel inputs (to
all process unit types) specified in
Equations Q–1 through Q–7 of § 98.173
(metric tons).
n = Number of process units, all process
types.
O = Annual mass of greenball (taconite)
pellets fed to the taconite furnace(s)
(metric tons).
§ 98.166
Data reporting requirements.
In addition to the information
required by § 98.3(c), each annual report
must contain the information specified
in paragraphs (a) or (b) of this section,
as appropriate, and paragraphs (c)
through (e) of this section:
*
*
*
*
*
(b) * * *
(7) Name and annual quantity (metric
tons) of each carbon-containing fuel and
feedstock.
*
*
*
*
*
(e) Annual methanol production
(metric tons) for each process unit.
■ 22. Section 98.167 is amended by
revising the introductory text and
adding paragraph (e) to read as follows:
tkelley on DSK3SPTVN1PROD with RULES3
§ 98.167
Records that must be retained.
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Subpart Q—Iron and Steel Production
23. Section 98.176 is amended by:
a. Revising paragraph (b);
b. Removing and reserving paragraphs
(e)(1), (3), and (4);
■ c. Adding paragraph (e)(6); and
■ c. Removing and reserving paragraphs
(f)(2) through (4) and (g).
The revisions and additions read as
follows:
■
■
■
§ 98.176
Data reporting requirements.
*
*
*
*
*
(b) If a CEMS is used to measure CO2
emissions, then you must report the
annual production quantity for the
production unit (in metric tons) for
taconite pellets, coke, sinter, iron, and
raw steel.
*
*
*
*
*
(e) * * *
(6) The information specified in
paragraphs (e)(6)(i) through (vi) of this
section aggregated for all process units
for which CO2 emissions were
determined using the mass balance
method in § 98.173(b)(1), except as
provided in § 98.174(b)(4).
(i) The annual mass (metric tons) of
all gaseous, liquid, and solid fuels
(combined) used in process units for
which CO2 emissions were determined
using Equations Q–1 through Q–7 of
§ 98.173, calculated as specified in
Equation Q–9 of this section.
rl,i = Density of the liquid fuel (kg/gallon).
0.001 = Conversion factor from kg to metric
tons.
(ii) The annual mass (metric tons) of
all non-fuel material inputs (combined)
specified in Equations Q–1 through Q–
7 of § 98.173, calculated as specified in
Equation Q–10 of this section.
Iron = Annual mass of molten iron charged
to the basic oxygen furnace(s) plus
annual mass of direct reduced iron
charged to the EAF(s) (metric tons).
E:\FR\FM\24OCR3.SGM
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ER24OC14.012
Where:
Fuel = Annual mass of all gaseous, liquid,
and solid fuels used in process units
(metric tons).
n = Number of process units where fuel is
used.
Fg,i = Annual volume of gaseous fuel
combusted (‘‘(Fg)’’ in Equations Q–1, Q–
4 and Q–7 of § 98.173) for each process
(scf).
MWi = Molecular weight of gaseous fuel used
in each process (kg/kg-mole).
21. Section 98.166 is amended by:
a. Revising the introductory text;
b. Removing and reserving paragraphs
(b)(2), (5), and (6); and
■ c. Adding paragraphs (b)(7) and (e).
The revisions and additions read as
follows:
■
■
■
(12) Average monthly carbon content
of the solid fuel or feedstock (kg C per
kg of fuel and feedstock) (Equation P–
3).
ER24OC14.011
In addition to the information
required by § 98.3(g), you must retain
the records specified in paragraphs (a)
through (e) of this section for each
hydrogen production facility.
*
*
*
*
*
(e) Verification software records. You
must keep a record of the file generated
by the verification software specified in
§ 98.5(b) for the applicable data
specified in paragraphs (e)(1) through
(12) of this section. Retention of this file
satisfies the recordkeeping requirement
for the data in paragraphs (e)(1) through
(12) of this section.
(1) Indicate whether the monthly
consumption of each gaseous fuel or
feedstock is measured as mass or
volume (Equation P–1 of § 98.163).
(2) Monthly volume of the gaseous
fuel or feedstock (scf at standard
conditions of 68 °F and atmospheric
pressure) (Equation P–1).
(3) Monthly mass of the gaseous fuel
or feedstock (kg of fuel or feedstock)
(Equation P–1).
(4) Average monthly carbon content of
the gaseous fuel or feedstock (kg C per
kg of fuel or feedstock) (Equation P–1).
(5) Average monthly molecular weight
of the gaseous fuel or feedstock (kg/kgmole) (Equation P–1).
(6) Indicate whether the monthly
consumption of each liquid fuel or
feedstock is measured as mass or
volume (Equation P–2 of § 98.163).
(7) Monthly volume of the liquid fuel
or feedstock (gallons of fuel or
feedstock) (Equation P–2).
(8) Monthly mass of the liquid fuel or
feedstock (kg of fuel or feedstock)
(Equation P–2).
(9) Average monthly carbon content of
the liquid fuel or feedstock (kg C per
gallon of fuel or feedstock) (Equation P–
2).
(10) Average monthly carbon content
of the liquid fuel or feedstock (kg C per
kg of fuel or feedstock) (Equation P–2).
(11) Monthly mass of solid fuel or
feedstock (kg of fuel and feedstock)
(Equation P–3 of § 98.163).
Subpart P—Hydrogen Production
63787
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Federal Register / Vol. 79, No. 206 / Friday, October 24, 2014 / Rules and Regulations
Other = Annual mass of other materials
charged to the direction reduction
furnace(s) (metric tons).
Feed = Annual mass of sinter feed material
charged to the sinter process(es) (metric
tons).
Electrode = Annual mass of carbon electrode
consumed in the EAF(s) (metric tons).
Steelin = Annual mass of molten steel charged
to the decarburization vessels (metric
tons).
Ore = Annual mass of iron ore or iron ore
pellets fed to the direct reduction
furnace(s) (metric tons).
Where:
Products = Annual mass of all solid and
liquid products and by-products (from
all process units) specified in Equations
Q–1 through Q–7 of § 98.173 (metric
tons).
n = Number of process units, all types.
P = Annual mass of fired pellets produced by
the taconite furnace (metric tons).
R = Annual mass of air pollution control
residue from all process units (metric
tons).
Steelout = Annual mass of steel produced by
the basic oxygen furnace(s), EAF(s) and
decarburization vessel(s) (metric tons).
Slag = Annual mass of slag produced by the
basic oxygen furnace(s) and EAF(s)
(metric tons).
Coke = Annual mass of coke produced by the
non-recovery coke batteries (metric tons).
Sinter = Annual mass of sinter produced
from the sinter process(es) (metric tons).
Iron = Annual mass of iron produced from
the direct reduction furnace (metric
tons).
Where:
CFavg = Weighted average carbon content of
all gaseous, liquid, and solid fuels
included in Equation Q–9 of this section
(weight fraction).
n = Number of gaseous, liquid, and solid fuel
input to each process unit as used in
Equation Q–9.
Cgf,i = Average carbon content of the gaseous
fuel used in each process, from the fuel
analysis results (kg C per kg of fuel).
Clf,i = Carbon content of the liquid fuel used
in each process, from the fuel analysis
results (kg C per gallon of fuel.
Csf = Carbon content of the solid fuel used
in each process, from the fuel analysis
(expressed as a decimal fraction, e.g.,
95% = 0.95).
Fuel = Annual mass of all gaseous, liquid,
and solid fuels used in process units
(metric tons), as calculated in Equation
Q–9.
(v) The weighted average carbon
content of all non-fuel inputs to all
process units (combined) included in
Equation Q–10 of this section,
calculated as specified in Equation Q–
13 of this section.
Where:
CIavg = Weighted average carbon content of
all non-fuel inputs to all process units
included in Equation Q–10 of this
section (weight fraction).
n = Number of non-fuel inputs to all process
units as used in Equation Q–10.
NFIi = Annual mass of each non-fuel input
used in Equation Q–10 (metric tons).
CNFIi = Average carbon content of each nonfuel input used in Equation Q–10
(expressed as a decimal fraction).
NFI = Total of all non-fuel inputs to all
process units (metric tons).
(vi) The weighted average carbon
content of all solid and liquid products
and byproducts from all process units
(combined) included in Equation Q–11
of this section, calculated as specified in
Equation Q–14 of this section.
Where:
CPavg = Weighted average carbon content of
all solid and liquid products and
byproducts from all process units
(weight fraction).
n = Number of products and byproducts from
each process unit as used in Equation Q–
11 of this section.
Producti = Annual mass of each product or
byproduct used in Equation Q–11
(metric tons).
Cp,i = Average carbon content of each product
or byproduct used in Equation Q–11
(expressed as a decimal fraction).
Products = Mass of all products and
byproducts from all process units,
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(iii) The annual mass (metric tons) of
all solid and liquid products and
byproducts (combined) specified in
Equations Q–1 through Q–7 of § 98.173,
calculated as specified in Equation Q–
11 of this section.
NM = Annual mass of non-metallic materials
produced by the direct reduction furnace
(metric tons).
*
*
*
*
*
24. Section 98.177 is amended by
revising the introductory text and
adding paragraph (f) to read as follows:
■
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calculated in Equation Q–11 (metric
tons).
ER24OC14.016
(iv) The weighted average carbon
content of all gaseous, liquid, and solid
fuels (combined) included in Equation
Q–9 of this section, calculated as
specified in Equation Q–12 of this
section.
ER24OC14.013
tkelley on DSK3SPTVN1PROD with RULES3
Scrap = Annual mass of ferrous scrap
charged to the basic oxygen furnace(s)
and EAF(s) (metric tons).
Flux = Annual mass of flux materials charged
to the basic oxygen furnace(s) and EAF(s)
(metric tons).
Carbon = Annual mass of carbonaceous
materials (e.g., coal, coke) charged to the
basic oxygen furnace(s), EAF(s), and
direct reduction furnace(s) (metric tons).
Coal = Annual mass of coal charged to the
coke oven battery(s) (metric tons).
Federal Register / Vol. 79, No. 206 / Friday, October 24, 2014 / Rules and Regulations
tkelley on DSK3SPTVN1PROD with RULES3
§ 98.177
Records that must be retained.
In addition to the records required by
§ 98.3(g), you must retain the records
specified in paragraphs (a) through (f) of
this section, as applicable. Facilities that
use CEMS to measure emissions must
also retain records of the verification
data required for the Tier 4 Calculating
Methodology in § 98.36(e).
*
*
*
*
*
(f) Verification software records. You
must keep a record of the file generated
by the verification software specified in
§ 98.5(b) for the applicable data
specified in paragraphs (f)(1) through (9)
of this section. Retention of this file
satisfies the recordkeeping requirement
for the data in paragraphs (f)(1) through
(9) of this section.
(1) The data in paragraphs (f)(1)(i)
through (xxv) of this section for each
applicable taconite indurating furnace
for which the carbon mass balance
method of reporting is used.
(i) Annual mass of each solid fuel
(metric tons) (Equation Q–1 of § 98.173).
(ii) Carbon content of each solid fuel,
from the fuel analysis (expressed as a
decimal fraction) (Equation Q–1).
(iii) Annual volume of each gaseous
fuel (scf) (Equation Q–1).
(iv) Average carbon content of each
gaseous fuel, from the fuel analysis
results (kg C per kg of fuel) (Equation
Q–1).
(v) Molecular weight of each gaseous
fuel (kg/kg-mole) (Equation Q–1).
(vi) Annual volume of each liquid fuel
(gallons) (Equation Q–1).
(vii) Carbon content of each liquid
fuel, from the fuel analysis results (kg C
per gallon of fuel) (Equation Q–1).
(viii) Annual mass of the greenball
(taconite) pellets fed to the furnace
(metric tons) (Equation Q–1).
(ix) Carbon content of the greenball
(taconite) pellets, from the carbon
analysis results (expressed as a decimal
fraction) (Equation Q–1).
(x) Annual mass of fired pellets
produced by the furnace (metric tons)
(Equation Q–1).
(xi) Carbon content of the fired
pellets, from the carbon analysis results
(expressed as a decimal fraction)
(Equation Q–1).
(xii) Annual mass of air pollution
control residue collected (metric tons)
(Equation Q–1).
(xiii) Carbon content of the air
pollution control residue, from the
carbon analysis results (expressed as a
decimal fraction) (Equation Q–1).
(xiv) Annual mass of each other solid
input containing carbon fed to each
furnace (metric tons) (Equation Q–1).
(xv) Carbon content of each other
solid input containing carbon fed to
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each furnace (expressed as a decimal
fraction) (Equation Q–1).
(xvi) Annual mass of each other solid
output containing carbon produced by
each furnace (metric tons) (Equation
Q–1).
(xvii) Carbon content of each other
solid output containing carbon
(expressed as a decimal fraction)
(Equation Q–1).
(xviii) Annual mass of each other
gaseous input containing carbon fed to
each furnace (metric tons) (Equation
Q–1).
(xix) Carbon content of each other
gaseous input containing carbon fed to
each furnace (expressed as a decimal
fraction) (Equation Q–1).
(xx) Annual mass of each other
gaseous output containing carbon
produced by each furnace (metric tons)
(Equation Q–1).
(xxi) Carbon content of each other
gaseous output containing carbon
produced by each furnace (expressed as
a decimal fraction) (Equation Q–1).
(xxii) Annual mass of each other
liquid input containing carbon fed to
each furnace (metric tons) (Equation
Q–1).
(xxiii) Carbon content of each other
liquid input containing carbon fed to
each furnace (expressed as a decimal
fraction) (Equation
Q–1).
(xxiv) Annual mass of each other
liquid output containing carbon
produced by each furnace (metric tons)
(Equation Q–1).
(xxv) Carbon content of each other
liquid output containing carbon
produced by each furnace (expressed as
a decimal fraction) (Equation Q–1).
(2) The data in paragraphs (f)(2)(i)
through (xxvi) of this section for each
applicable basic oxygen process furnace
for which the carbon mass balance
method of reporting is used.
(i) Annual mass of molten iron
charged to the furnace (metric tons)
(Equation Q–2 of § 98.173).
(ii) Carbon content of the molten iron
charged to the furnace, from the carbon
analysis results (expressed as a decimal
fraction) (Equation Q–2).
(iii) Annual mass of ferrous scrap
charged to the furnace (metric tons)
(Equation Q–2).
(iv) Carbon content of the ferrous
scrap charged to the furnace, from the
carbon analysis results (expressed as a
decimal fraction) (Equation Q–2).
(v) Annual mass of the flux materials
(e.g., limestone, dolomite) charged to
the furnace (metric tons) (Equation
Q–2).
(vi) Carbon content of the flux
materials charged to the furnace, from
the carbon analysis results (expressed as
a decimal fraction) (Equation Q–2).
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63789
(vii) Annual mass of the carbonaceous
materials (e.g., coal, coke) charged to the
furnace (metric tons) (Equation Q–2).
(viii) Carbon content of the
carbonaceous materials charged to the
furnace, from the carbon analysis results
(expressed as a decimal fraction)
(Equation Q–2).
(ix) Annual mass of molten raw steel
produced by the furnace (metric tons)
(Equation Q–2).
(x) Carbon content of the steel
produced by the furnace, from the
carbon analysis results (expressed as a
decimal fraction) (Equation Q–2).
(xi) Annual mass of slag produced by
the furnace (metric tons) (Equation
Q–2).
(xii) Carbon content of the slag
produced by the furnace, from the
carbon analysis (expressed as a decimal
fraction) (Equation Q–2).
(xiii) Annual mass of air pollution
control residue collected for the furnace
(metric tons) (Equation Q–2).
(xiv) Carbon content of the air
pollution control residue collected for
the furnace, from the carbon analysis
results (expressed as a decimal fraction)
(Equation Q–2).
(xv) Annual mass of each other solid
input containing carbon fed to each
furnace (metric tons) (Equation Q–2).
(xvi) Carbon content of each other
solid input containing carbon fed to
each furnace (expressed as a decimal
fraction) (Equation Q–2).
(xvii) Annual mass of each other solid
output containing carbon produced by
each furnace (metric tons) (Equation
Q–2).
(xviii) Carbon content of each other
solid output containing carbon
(expressed as a decimal fraction)
(Equation
Q–2).
(xix) Annual mass of each other
gaseous input containing carbon fed to
each furnace (metric tons) (Equation
Q–2).
(xx) Carbon content of each other
gaseous input containing carbon fed to
each furnace (expressed as a decimal
fraction) (Equation Q–2).
(xxi) Annual mass of each other
gaseous output containing carbon
produced by each furnace (metric tons)
(Equation Q–2).
(xxii) Carbon content of each other
gaseous output containing carbon
produced by each furnace (expressed as
a decimal fraction) (Equation Q–2).
(xxiii) Annual mass of each other
liquid input containing carbon fed to
each furnace (metric tons) (Equation Q–
2).
(xxiv) Carbon content of each other
liquid input containing carbon fed to
each furnace (expressed as a decimal
fraction) (Equation Q–2).
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Federal Register / Vol. 79, No. 206 / Friday, October 24, 2014 / Rules and Regulations
(xxv) Annual mass of each other
liquid output containing carbon
produced by each furnace (metric tons)
(Equation Q–2).
(xxvi) Carbon content of each other
liquid output containing carbon
produced by each furnace (expressed as
a decimal fraction) (Equation Q–2).
(3) The data in paragraphs (f)(3)(i)
through (xviii) of this section for each
applicable non-recovery coke oven
battery for which the carbon mass
balance method of reporting is used.
(i) Annual mass of coal charged to the
battery (metric tons) (Equation Q–3 of
§ 98.173).
(ii) Carbon content of the coal, from
the carbon analysis results (expressed as
a decimal fraction) (Equation Q–3).
(iii) Annual mass of coke produced by
the battery (metric tons) (Equation Q–3).
(iv) Carbon content of the coke, from
the carbon analysis results (expressed as
a decimal fraction) (Equation Q–3).
(v) Annual mass of air pollution
control residue collected (metric tons)
(Equation Q–3).
(vi) Carbon content of the air
pollution control residue, from the
carbon analysis results (expressed as a
decimal fraction) (Equation Q–3).
(vii) Annual mass of each other solid
input containing carbon fed to each
battery (metric tons) (Equation Q–3).
(viii) Carbon content of each other
solid input containing carbon fed to
each battery (expressed as a decimal
fraction) (Equation Q–3).
(ix) Annual mass of each other solid
output containing carbon produced by
each battery (metric tons) (Equation
Q–3).
(x) Carbon content of each other solid
output containing carbon (expressed as
a decimal fraction) (Equation Q–3).
(xi) Annual mass of each other
gaseous input containing carbon fed to
each battery (metric tons) (Equation
Q–3).
(xii) Carbon content of each other
gaseous input containing carbon fed to
each battery (expressed as a decimal
fraction) (Equation Q–3).
(xiii) Annual mass of each other
gaseous output containing carbon
produced by each battery (metric tons)
(Equation Q–3).
(xiv) Carbon content of each other
gaseous output containing carbon
produced by each battery (expressed as
a decimal fraction) (Equation Q–3).
(xv) Annual mass of each other liquid
input containing carbon fed to each
battery (metric tons) (Equation Q–3).
(xvi) Carbon content of each other
liquid input containing carbon fed to
each battery (expressed as a decimal
fraction) (Equation Q–3).
(xvii) Annual mass of each other
liquid output containing carbon
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produced by each battery (metric tons)
(Equation Q–3).
(xviii) Carbon content of each other
liquid output containing carbon
produced by each battery (expressed as
a decimal fraction) (Equation Q–3).
(4) The data in paragraphs (f)(4)(i)
through (xxi) of this section for each
applicable sinter process for which the
carbon mass balance method of
reporting is used.
(i) Annual volume of the gaseous fuel
(scf) (Equation Q–4 of § 98.173).
(ii) Carbon content of the gaseous fuel,
from the fuel analysis results (kg C per
kg of fuel) (Equation Q–4).
(iii) Molecular weight of the gaseous
fuel (kg/kg-mole) (Equation Q–4).
(iv) Annual mass of sinter feed
material (metric tons) (Equation Q–4).
(v) Carbon content of the mixed sinter
feed materials that form the bed entering
the sintering machine, from the carbon
analysis results (expressed as a decimal
fraction) (Equation Q–4).
(vi) Annual mass of sinter produced
(metric tons) (Equation Q–4).
(vii) Carbon content of the sinter
pellets, from the carbon analysis results
(expressed as a decimal fraction)
(Equation Q–4).
(viii) Annual mass of air pollution
control residue collected (metric tons)
(Equation Q–4).
(ix) Carbon content of the air
pollution control residue, from the
carbon analysis results (expressed as a
decimal fraction) (Equation Q–4).
(x) Annual mass of each other solid
input containing carbon fed to each
sinter process (metric tons) (Equation
Q–4).
(xi) Carbon content of each other solid
input containing carbon fed to each
sinter process (expressed as a decimal
fraction) (Equation Q–4).
(xii) Annual mass of each other solid
output containing carbon produced by
each sinter process (metric tons)
(Equation Q–4).
(xiii) Carbon content of each other
solid output containing carbon
(expressed as a decimal fraction)
(Equation Q–4).
(xiv) Annual mass of each other
gaseous input containing carbon fed to
each sinter process (metric tons)
(Equation Q–4).
(xv) Carbon content of each other
gaseous input containing carbon fed to
each sinter process (expressed as a
decimal fraction) (Equation Q–4).
(xvi) Annual mass of each other
gaseous output containing carbon
produced by each sinter process (metric
tons) (Equation Q–4).
(xvii) Carbon content of each other
gaseous output containing carbon
produced by each sinter process
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(expressed as a decimal fraction)
(Equation Q–4).
(xviii) Annual mass of each other
liquid input containing carbon fed to
each sinter process (metric tons)
(Equation Q–4).
(xix) Carbon content of each other
liquid input containing carbon fed to
each sinter process (expressed as a
decimal fraction) (Equation Q–4).
(xx) Annual mass of each other liquid
output containing carbon produced by
each sinter process (metric tons)
(Equation Q–4).
(xxi) Carbon content of each other
liquid output containing carbon
produced by each sinter process
(expressed as a decimal fraction)
(Equation Q–4).
(5) The data in paragraphs (f)(5)(i)
through (xxxi) of this section for each
applicable electric arc furnace for which
the carbon mass balance method of
reporting is used.
(i) Annual mass of direct reduced iron
(if any) charged to the furnace (metric
tons) (Equation Q–5 of § 98.173).
(ii) Carbon content of the direct
reduced iron, from the carbon analysis
results (expressed as a decimal fraction)
(Equation Q–5)
(iii) Annual mass of ferrous scrap
charged to the furnace (metric tons)
(Equation Q–5).
(iv) Carbon content of the ferrous
scrap, from the carbon analysis results
(expressed as a decimal fraction)
(Equation Q–5).
(v) Annual mass of flux materials
(e.g., limestone, dolomite) charged to
the furnace (metric tons) (Equation
Q–5).
(vi) Carbon content of the flux
materials, from the carbon analysis
results (expressed as a decimal fraction)
(Equation Q–5).
(vii) Annual mass of carbon electrode
consumed (metric tons) (Equation Q–5).
(viii) Carbon content of the carbon
electrode, from the carbon analysis
results (expressed as a decimal fraction)
(Equation Q–5).
(ix) Annual mass of carbonaceous
materials (e.g., coal, coke) charged to the
furnace (metric tons) (Equation Q–5).
(x) Carbon content of the
carbonaceous materials, from the carbon
analysis results (expressed as a decimal
fraction) (Equation Q–5).
(xi) Annual mass of molten raw steel
produced by the furnace (metric tons)
(Equation Q–5).
(xii) Carbon content of the steel, from
the carbon analysis results (expressed as
a decimal fraction) (Equation Q–5).
(xiii) Annual volume of the gaseous
fuel (scf at 60F and 1 atm) (Equation
Q–5).
(xiv) Average carbon content of the
gaseous fuel, from the fuel analysis
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results (kg C per kg of fuel) (Equation
Q–5).
(xv) Molecular weight of the gaseous
fuel (kg/kg-mole) (Equation Q–5).
(xvi) Annual mass of slag produced by
the furnace (metric tons) (Equation
Q–5).
(xvii) Carbon content of the slag, from
the carbon analysis (expressed as a
decimal fraction) (Equation Q–5).
(xviii) Annual mass of air pollution
control residue collected (metric tons)
(Equation Q–5).
(xix) Carbon content of the air
pollution control residue, from the
carbon analysis results (expressed as a
decimal fraction) (Equation Q–5).
(xx) Annual mass of each other solid
input containing carbon fed to each
furnace (metric tons) (Equation Q–5).
(xxi) Carbon content of each other
solid input containing carbon fed to
each furnace (expressed as a decimal
fraction) (Equation Q–5).
(xxii) Annual mass of each other solid
output containing carbon produced by
each furnace (metric tons) (Equation
Q–5).
(xxiii) Carbon content of each other
solid output containing carbon
(expressed as a decimal fraction)
(Equation
Q–5).
(xxiv) Annual mass of each other
gaseous input containing carbon fed to
each furnace (metric tons) (Equation
Q–5).
(xxv) Carbon content of each other
gaseous input containing carbon fed to
each furnace (expressed as a decimal
fraction) (Equation Q–5).
(xxvi) Annual mass of each other
gaseous output containing carbon
produced by each furnace (metric tons)
(Equation Q–5).
(xxvii) Carbon content of each other
gaseous output containing carbon
produced by each furnace (expressed as
a decimal fraction) (Equation Q–5).
(xxviii) Annual mass of each other
liquid input containing carbon fed to
each furnace (metric tons) (Equation
Q–5).
(xxix) Carbon content of each other
liquid input containing carbon fed to
each furnace (expressed as a decimal
fraction) (Equation Q–5).
(xxx) Annual mass of each other
liquid output containing carbon
produced by each furnace (metric tons)
(Equation Q–5).
(xxxi) Carbon content of each other
liquid output containing carbon
produced by each furnace (expressed as
a decimal fraction) (Equation Q–5).
(6) The data in paragraphs (f)(6)(i)
through (xvii) of this section for each
applicable decarburization vessel for
which the carbon mass balance method
of reporting is used.
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(i) Annual mass of molten steel
charged to the vessel (metric tons)
(Equation Q–6 of § 98.173).
(ii) Carbon content of the molten steel
before decarburization, from the carbon
analysis results (expressed as a decimal
fraction) (Equation Q–6).
(iii) Carbon content of the molten
steel after decarburization, from the
carbon analysis results (expressed as a
decimal fraction) (Equation Q–6).
(iv) Annual mass of air pollution
control residue collected (metric tons)
(Equation Q–6).
(v) Carbon content of the air pollution
control residue, from the carbon
analysis results (expressed as a decimal
fraction) (Equation Q–6).
(vi) Annual mass of each other solid
input containing carbon fed to each
decarburization vessel (metric tons)
(Equation Q–6).
(vii) Carbon content of each other
solid input containing carbon fed to
each decarburization vessel (expressed
as a decimal fraction) (Equation Q–6).
(viii) Annual mass of each other solid
output containing carbon produced by
each decarburization vessel (metric
tons) (Equation Q–6).
(ix) Carbon content of each other solid
output containing carbon (expressed as
a decimal fraction) (Equation Q–6).
(x) Annual mass of each other gaseous
input containing carbon fed to each
decarburization vessel (metric tons)
(Equation Q–6).
(xi) Carbon content of each other
gaseous input containing carbon fed to
each decarburization vessel (expressed
as a decimal fraction) (Equation Q–6).
(xii) Annual mass of each other
gaseous output containing carbon
produced by each decarburization
vessel (metric tons) (Equation Q–6).
(xiii) Carbon content of each other
gaseous output containing carbon
produced by each decarburization
vessel (expressed as a decimal fraction)
(Equation Q–6).
(xiv) Annual mass of each other liquid
input containing carbon fed to each
decarburization vessel (metric tons)
(Equation Q–6).
(xv) Carbon content of each other
liquid input containing carbon fed to
each decarburization vessel (expressed
as a decimal fraction) (Equation Q–6).
(xvi) Annual mass of each other liquid
output containing carbon produced by
each decarburization vessel (metric
tons) (Equation Q–6).
(xvii) Carbon content of each other
liquid output containing carbon
produced by each decarburization
vessel (expressed as a decimal fraction)
(Equation Q–6).
(7) The data in paragraphs (f)(7)(i)
through (xxvii) of this section for each
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applicable direct reduction furnace for
which the carbon mass balance method
of reporting is used.
(i) Annual volume of the gaseous fuel
(scf at 68F and 1 atm) (Equation Q–7 of
§ 98.173).
(ii) Average carbon content of the
gaseous fuel, from the fuel analysis
results (kg C per kg of fuel) (Equation
Q–7).
(iii) Molecular weight of the gaseous
fuel (kg/kg-mole) (Equation Q–7).
(iv) Annual mass of iron ore or iron
pellets fed to the furnace (metric tons)
(Equation Q–7).
(v) Carbon content of the iron ore or
iron pellets, from the carbon analysis
(expressed as a decimal fraction)
(Equation Q–7).
(vi) Annual mass of carbonaceous
materials (e.g., coal, coke) charged to the
furnace (metric tons) (Equation Q–7).
(vii) Carbon content of the
carbonaceous materials, from the carbon
analysis results (expressed as a decimal
fraction) (Equation Q–7).
(viii) Annual mass of each other
material charged to the furnace (metric
tons) (Equation Q–7).
(ix) Average carbon content of each
other material charged to the furnace,
from the carbon analysis results
(expressed as a decimal fraction)
(Equation Q–7).
(x) Annual mass of iron produced
(metric tons) (Equation Q–7).
(xi) Carbon content of the iron
produced, from the carbon analysis
results (expressed as a decimal fraction)
(Equation Q–7).
(xii) Annual mass of non-metallic
materials produced by the furnace
(metric tons) (Equation Q–7).
(xiii) Carbon content of the nonmetallic materials produced, from the
carbon analysis results (expressed as a
decimal fraction) (Equation Q–7).
(xiv) Annual mass of air pollution
control residue collected (metric tons)
(Equation Q–7).
(xv) Carbon content of the air
pollution control residue collected, from
the carbon analysis results (expressed as
a decimal fraction) (Equation Q–7).
(xvi) Annual mass of each other solid
input containing carbon fed to each
furnace (metric tons) (Equation Q–7).
(xvii) Carbon content of each other
solid input containing carbon fed to
each furnace (expressed as a decimal
fraction) (Equation Q–7).
(xviii) Annual mass of each other
solid output containing carbon
produced by each furnace (metric tons)
(Equation Q–7).
(xix) Carbon content of each other
solid output containing carbon
(expressed as a decimal fraction)
(Equation Q–7).
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(xx) Annual mass of each other
gaseous input containing carbon fed to
each furnace (metric tons) (Equation
Q–7).
(xxi) Carbon content of each other
gaseous input containing carbon fed to
each furnace (expressed as a decimal
fraction) (Equation Q–7).
(xxii) Annual mass of each other
gaseous output containing carbon
produced by each furnace (metric tons)
(Equation Q–7).
(xxiii) Carbon content of each other
gaseous output containing carbon
produced by each furnace (expressed as
a decimal fraction) (Equation Q–7).
(xxiv) Annual mass of each other
liquid input containing carbon fed to
each furnace (metric tons) (Equation
Q–7).
(xxv) Carbon content of each other
liquid input containing carbon fed to
each furnace (expressed as a decimal
fraction) (Equation
Q–7).
(xxvi) Annual mass of each other
liquid output containing carbon
produced by each furnace (metric tons)
(Equation Q–7).
(xxvii) Carbon content of each other
liquid output containing carbon
produced by each furnace (expressed as
a decimal fraction) (Equation Q–7).
(8) The data in paragraphs (f)(8)(i) and
(ii) of this section for each process unit
for which the site-specific emission
factor method was used.
(i) Average hourly feed or production
rate, as applicable, during the test
(metric tons/hour) (as used in
§ 98.173(b)(2)(iii)).
(ii) Annual total feed or production,
as applicable (metric tons) (as used in
§ 98.173(b)(2)(iv)).
(9) Total coal charged to the coke
ovens for each process (metric tons/
year)(as used in § 98.173(c)).
Subpart R—Lead Production
25. Section 98.186 is amended by
removing and reserving paragraphs
(b)(6) and (7) and revising paragraph
(b)(8) to read as follows:
■
§ 98.186
Data reporting procedures.
tkelley on DSK3SPTVN1PROD with RULES3
*
*
*
*
*
(b) * * *
(8) List the method used for the
determination of carbon content for
each material used for the calculation of
annual process CO2 emissions using
Equation R–1 of § 98.183 for each
smelting furnace (e.g., supplier provided
information, analyses of representative
samples you collected).
*
*
*
*
*
■ 26. Section 98.187 is amended by
revising the introductory text and
adding paragraph (d) to read as follows:
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§ 98.187
Records that must be retained.
In addition to the records required by
§ 98.3(g), you must retain the records of
the information specified in paragraphs
(a) through (d) of this section, as
applicable to the smelting furnaces at
your facility.
*
*
*
*
*
(d) Verification software records. You
must keep a record of the file generated
by the verification software specified in
§ 98.5(b) for the applicable data
specified in paragraphs (d)(1) through
(10) of this section. Retention of this file
satisfies the recordkeeping requirement
for the data in paragraphs (d)(1) through
(10) of this section.
(1) Annual mass of lead ore charged
to each smelting furnace (tons)
(Equation R–1 of § 98.183).
(2) Carbon content of the lead ore per
furnace, from the carbon analysis results
(percent by weight, expressed as a
decimal fraction) (Equation R–1).
(3) Annual mass of lead scrap charged
to each smelting furnace (tons)
(Equation R–1).
(4) Carbon content of the lead scrap
per furnace, from the carbon analysis
(percent by weight, expressed as a
decimal fraction) (Equation R–1).
(5) Annual mass of flux materials
(e.g., limestone, dolomite) charged to
each smelting furnace (tons) (Equation
R–1).
(6) Carbon content of the flux
materials per furnace, from the carbon
analysis (percent by weight, expressed
as a decimal fraction) (Equation R–1).
(7) Annual mass of carbonaceous
materials (e.g., coal, coke) charged to
each smelting furnace (tons) (Equation
R–1).
(8) Carbon content of the
carbonaceous materials per furnace,
from the carbon analysis (percent by
weight, expressed as a decimal fraction)
(Equation R–1).
(9) Annual mass of each other
material containing carbon, other than
fuel, fed, charged, or otherwise
introduced into the smelting furnace
(tons) (Equation R–1).
(10) Carbon content of each other
material, from the carbon analysis
results per furnace (percent by weight,
expressed as a decimal fraction)
(Equation R–1).
Subpart S—Lime Manufacturing
27. Section 98.196 is amended by:
a. Revising paragraph (b) introductory
text;
■ b. Removing and reserving paragraphs
(b)(2), (3), (5), (6), (8), (10), (11), and
(12); and
■ c. Adding paragraph (b)(18).
The revisions and addition read as
follows:
■
■
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§ 98.196
Data reporting requirements.
*
*
*
*
*
(b) If a CEMS is not used to measure
CO2 emissions, then you must report the
information listed in paragraphs (b)(1)
through (18) of this section.
*
*
*
*
*
(18) Annual quantity (tons) of lime
product sold, by type.
■ 28. Section 98.197 is amended by
revising the introductory text and
adding paragraph (c) to read as follows:
§ 98.197
Records that must be retained.
In addition to the records required by
§ 98.3(g), you must retain the records
specified in paragraphs (a) through (c) of
this section.
*
*
*
*
*
(c) Verification software records. You
must keep a record of the file generated
by the verification software specified in
§ 98.5(b) for the applicable data
specified in paragraphs (c)(1) through
(9) of this section. Retention of this file
satisfies the recordkeeping requirement
for the data in paragraphs (c)(1) through
(9) of this section.
(1) Monthly calcium oxide content for
each lime type, determined according to
§ 98.194(c) (metric tons CaO/metric ton
lime) (Equation S–1 of § 98.193).
(2) Monthly magnesium oxide content
for each lime type, determined
according to § 98.194(c) (metric tons
MgO/metric ton lime) (Equation S–1).
(3) Monthly calcium oxide content for
each calcined lime byproduct or waste
type sold (metric tons CaO/metric ton
lime) (Equation S–2 of § 98.193).
(4) Monthly magnesium oxide content
for each calcined lime byproduct or
waste type sold (metric tons MgO/
metric ton lime) (Equation S–2).
(5) Calcium oxide content for each
calcined lime byproduct or waste type
that is not sold (metric tons CaO/metric
ton lime) (Equation S–3 of § 98.193).
(6) Magnesium oxide content for each
calcined lime byproduct or waste type
that is not sold (metric tons MgO/metric
ton lime) (Equation S–3).
(7) Annual weight or mass of calcined
byproducts or wastes for lime type that
is not sold (tons) (Equation S–3).
(8) Monthly weight or mass of each
lime type produced (tons) (Equation S–
4 of § 98.193).
(9) Monthly weight or mass of each
calcined byproducts or wastes sold
(tons) (Equation S–4).
Subpart U—Miscellaneous Uses of
Carbonate
§ 98.216
[Amended]
29. Section 98.216 is amended by
removing and reserving paragraphs (b),
(e)(1) and (2), and (f).
■
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30. Section 98.217 is amended by
revising the introductory text and
adding paragraph (e) to read as follows:
■
§ 98.217
Records that must be retained.
In addition to the records required by
§ 98.3(g), you must retain the records
specified in paragraphs (a) through (e) of
this section:
*
*
*
*
*
(e) Verification software records. You
must keep a record of the file generated
by the verification software specified in
§ 98.5(b) for the applicable data
specified in paragraphs (e)(1) through
(4) of this section. Retention of this file
satisfies the recordkeeping requirement
for the data in paragraphs (e)(1) through
(4) of this section.
(1) Fraction calcination achieved for
each particular carbonate type. As an
alternative to measuring the calcination
fraction, a value of 1.0 can be used
(decimal fraction) (Equation U–1 of
§ 98.213).
(2) Annual mass of each carbonate
type consumed (tons) (Equation U–1).
(3) Annual mass of each input
carbonate type (tons) (Equation U–2 of
§ 98.213).
(4) Annual mass of each output
carbonate type (tons) (Equation U–2).
Subpart V—Nitric Acid Production
31. Section 98.226 is amended by:
a. Revising the introductory text;
b. Removing and reserving paragraphs
(c), (d), (i), (j), (m)(1), (m)(3), (m)(4),
(m)(5), (m)(6), and (p); and
■ c. Adding paragraph (q).
The revisions and addition read as
follows:
■
■
■
§ 98.226
Data reporting requirements.
In addition to the information
required by § 98.3(c), each annual report
must contain the information specified
in paragraphs (a) through (q) of this
section.
*
*
*
*
*
(q) Annual percent N2O emission
reduction for all nitric acid trains
combined.
■ 32. Section 98.227 is amended by
revising the introductory text and
adding paragraph (h) to read as follows:
tkelley on DSK3SPTVN1PROD with RULES3
§ 98.227
Records that must be retained.
17:25 Oct 23, 2014
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Subpart W—Petroleum and Natural
Gas Systems
33. Section 98.236 is amended by
revising paragraphs (c)(6)(i)(B), (D), (E),
and (F), (c)(8)(i)(F), and (c)(8)(ii)(A) and
adding paragraph (c)(20) to read as
follows:
■
§ 98.236
In addition to the information
required by § 98.3(g), you must retain
the records specified in paragraphs (a)
through (h) of this section for each nitric
acid production facility:
*
*
*
*
*
(h) Verification software records. You
must keep a record of the file generated
by the verification software specified in
§ 98.5(b) for the applicable data
VerDate Sep<11>2014
specified in paragraphs (h)(1) through
(10) of this section. Retention of this file
satisfies the recordkeeping requirement
for the data in paragraphs (h)(1) through
(10) of this section.
(1) Annual nitric acid produced from
each nitric acid train (tons nitric acid
produced, 100% acid basis).
(2) Indicate which equation was used
to calculate emissions for each nitric
acid train.
(3) N2O concentration per test run
during the performance test (ppm N2O)
(Equation V–1 of § 98.223).
(4) Volumetric flow rate of effluent
gas per test run during the performance
test (dscf/hr) (Equation V–1).
(5) Production rate per test run during
the performance test (tons nitric acid
produced per hour, 100 percent acid
basis) (Equation V–1).
(6) Annual nitric acid production
from each nitric acid train during which
each N2O abatement technology was
operational (tons nitric acid produced,
100 percent acid basis) (Equation V–2 of
§ 98.223).
(7) Destruction efficiency of N2O
abatement technology that is used on
each nitric acid train (decimal fraction
of N2O removed from vent stream)
(Equation V–3a of § 98.223).
(8) Destruction efficiency of each N2O
abatement technology that is used on
each nitric acid train (decimal fraction
of N2O removed from vent stream)
(Equation V–3b of § 98.223).
(9) Destruction efficiency of each N2O
abatement technology that is used on
each nitric acid train (decimal fraction
of N2O removed from vent stream)
(Equation V–3c of § 98.223).
(10) Fraction control factor of each
N2O abatement technology that is used
on each nitric acid train (decimal
fraction of total emissions from nitric
acid train ‘‘t’’ that are sent to abatement
technology ‘‘n’’) (Equation V–3c).
Data reporting requirements.
*
*
*
*
*
(c) * * *
(6) * * *
(i) * * *
(B) When using Equation W–10A of
§ 98.233, measured flow rate of
backflow during well completion in
standard cubic feet per hour. You may
delay the reporting of this data element
if you indicate in the annual report that
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63793
wildcat wells and/or delineation wells
are the only wells that can be used for
the measurement. If you elect to delay
reporting of this data element, you must
report by the date specified in
§ 98.236(c)(20) the measured flow rate of
backflow during well completion and
the API Well Number(s) for the wells
included in the measurement.
*
*
*
*
*
(D) When using Equation W–10A,
measured flow rate of backflow during
well workover in standard cubic feet per
hour. You may delay the reporting of
this data element if you indicate in the
annual report that wildcat wells and/or
delineation wells are the only wells that
can be used for the measurement. If you
elect to delay reporting of this data
element, you must report by the date
specified in § 98.236(c)(20) the flow rate
of backflow during well workover and
the API Well Number(s) for the well(s)
included in the measurement.
(E) When using Equation W–10A,
total number of days of backflow from
all wells during completions. You may
delay the reporting of this data element
if you indicate in the annual report that
wildcat wells and/or delineation wells
are the only wells included in this
number. If you elect to delay reporting
of this data element, you must report by
the date specified in § 98.236(c)(20) the
total number of days of backflow from
all wells during completions and the
API Well Number(s) for the well(s)
included in the number.
(F) When using Equation W–10A,
total number of days of backflow from
all wells during workovers. You may
delay the reporting of this data element
if you indicate in the annual report that
wildcat wells and/or delineation wells
are the only wells included in this
number. If you elect to delay reporting
of this data element, you must report by
the date specified in § 98.236(c)(20) the
total number of days of backflow from
all wells during workovers and the API
Well Number(s) for the well(s) included
in the number.
*
*
*
*
*
(8) * * *
(i) * * *
(F) Total volume of oil from all
wellhead separators sent to tank(s) in
barrels per year. You may delay the
reporting of this data element if you
indicate in the annual report that only
wildcat and delineation wells in the
sub-basin have wellhead separators. If
you elect to delay reporting the this data
element, you must report by the date
specified in § 98.236(c)(20) the total
volume of oil from all wellhead
separators sent to tank(s) and the API
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Well Number(s) for the well(s) included
in this volume.
*
*
*
*
*
(ii) * * *
(A) Total volume of sales oil from all
wells in barrels per year. You may delay
the reporting of this data element if you
indicate in the annual report that
wildcat wells and delineation wells are
the only wells in the sub-basin with oil
production greater than or equal to 10
barrels per day. If you elect to delay
reporting of this data element, you must
report by the date specified in
§ 98.3236(c)(20) the total volume of
sales oil from all wells and the API Well
Number(s) for the well(s) included in
this volume.
*
*
*
*
*
(20) If you elect to delay reporting the
information in paragraph (c)(6)(i)(B),
(D), (E), (F), (c)(8)(i)(F), or (c)(8)(ii)(A) of
this section, you must report the
information required in that paragraph
no later than the date specified in
paragraphs (c)(20)(i) through (iii) of this
section, as applicable.
(i) March 31, 2016, for reporting year
2013.
(ii) March 31, 2017, for reporting year
2014.
(iii) The date 2 years following the
date specified in § 98.3(b) introductory
text, for reporting year 2015 and
thereafter.
■ 34. Section 98.238 is amended by
adding definitions for ‘‘Delineation
well’’ and ‘‘Wildcat well’’ in
alphabetical order to read as follows:
§ 98.238
Definitions.
*
*
*
*
*
Delineation well means a well drilled
in order to determine the boundary of a
field or producing reservoir.
*
*
*
*
*
Wildcat well means a well outside
known fields or the first well drilled in
an oil or gas field where no other oil and
gas production exists.
Subpart X—Petrochemical Production
35. Section 98.246 is amended by:
a. Revising paragraph (a) introductory
text and paragraphs (a)(2) and (4);
■ b. Adding paragraphs (a)(12) and (13);
■ c. Revising paragraph (b) introductory
text; and
■ d. Adding paragraphs (b)(9) and (10).
The revisions and additions read as
follows:
tkelley on DSK3SPTVN1PROD with RULES3
■
■
§ 98.246
Data reporting requirements.
*
*
*
*
*
(a) If you use the mass balance
methodology in § 98.243(c), you must
report the information specified in
paragraphs (a)(1) through (13) of this
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section for each type of petrochemical
produced, reported by process unit.
*
*
*
*
*
(2) The type of petrochemical
produced, names of products, and
names of carbon-containing feedstocks.
*
*
*
*
*
(4) The temperature (in °F) at which
the gaseous feedstock and product
volumes used in Equation X–1 of
§ 98.243 were determined.
*
*
*
*
*
(12) Name and annual quantity (in
metric tons) of each carbon-containing
feedstock included in Equations X–1,
X–2, and X–3 of § 98.243.
(13) Name and annual quantity (in
metric tons) of each product included in
Equations X–1, X–2, and X–3.
(b) If you measure emissions in
accordance with § 98.243(b), then you
must report the information listed in
paragraphs (b)(1) through (10) of this
section.
*
*
*
*
*
(9) Name and annual quantity (in
metric tons) of each carbon-containing
feedstock.
(10) Name and annual quantity (in
metric tons) of each product.
*
*
*
*
*
■ 36. Section 98.247 is amended by
revising the introductory text and
adding paragraph (d) to read as follows:
§ 98.247
Records that must be retained.
In addition to the recordkeeping
requirements in § 98.3(g), you must
retain the records specified in
paragraphs (a) through (d) of this
section, as applicable.
*
*
*
*
*
(d) Verification software records. You
must keep a record of the file generated
by the verification software specified in
§ 98.5(b) for the applicable data
specified in paragraphs (d)(1) through
(30) of this section. Retention of this file
satisfies the recordkeeping requirement
for the data in paragraphs (d)(1) through
(30) of this section.
(1) Indicate whether the feedstock is
measured as mass or volume (Equation
X–1 of § 98.243).
(2) Indicate whether you used the
alternative to sampling and analysis
specified in § 98.243(c)(4) (Equation X–
1).
(3) Volume of gaseous feedstock
introduced per month (scf) (Equation X–
1).
(4) Mass of gaseous feedstock
introduced per month (kg) (Equation X–
1).
(5) Average carbon content of the
gaseous feedstock per month (kg C per
kg of feedstock) (Equation X–1).
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(6) Molecular weight of gaseous
feedstock per month (kg per kg-mole)
(Equation X–1).
(7) Indicate whether the gaseous
product is measured as mass or volume
(Equation X–1).
(8) Volume of gaseous product
produced per month (scf) (Equation X–
1).
(9) Mass of gaseous product produced
per month (kg) (Equation X–1).
(10) Average carbon content of
gaseous product (including streams
containing CO2 recovered for sale or use
in another process) per month (kg C per
kg of product) (Equation X–1).
(11) Molecular weight of gaseous
product per month (kg per kg-mole)
(Equation X–1).
(12) Molar volume conversion factor
of product (scf per kg-mole) (Equation
X–1).
(13) Indicate whether feedstock is
measured as mass or volume (Equation
X–2 of § 98.243).
(14) Indicate whether you used the
alternative to sampling and analysis
specified in § 98.243(c)(4) (Equation X–
2).
(15) Volume of liquid feedstock
introduced per month (gallons)
(Equation X–2).
(16) Mass of liquid feedstock
introduced per month (kg) (Equation X–
2).
(17) Average carbon content of liquid
feedstock per month (kg C per gallon)
(Equation X–2).
(18) Average carbon content of liquid
feedstock per month (kg C per kg of
feedstock) (Equation X–2).
(19) Indicate whether product is
measured as mass or volume per month
(Equation X–2).
(20) Volume of liquid product
produced per month (gallons) (Equation
X–2).
(21) Mass of liquid product produced
per month (kg) (Equation X–2).
(22) Average carbon content of liquid
product per month, including organic
liquid wastes (kg C per gallon) (Equation
X–2).
(23) Average carbon content of liquid
product, including organic liquid wastes
(kg C per kg of product) (Equation X–2).
(24) Indicate whether you used the
alternative to sampling and analysis
specified in § 98.243(c)(4) (Equation X–
3 of § 98.243).
(25) Mass of solid feedstock
introduced per month (kg) (Equation X–
3).
(26) Average carbon content of solid
feedstock per month (kg C per kg of
feedstock) (Equation X–3).
(27) Mass of solid product produced
per month (kg) (Equation X–3).
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(28) Average carbon content of solid
product per month (kg C per kg of
product) (Equation X–3).
(29) Records required in § 98.257(b)(1)
through (8) of this section for each flare
that burns ethylene process off-gas.
(30) Records required in § 98.37 for
each stationary fuel combustion unit (or
group of stationary sources with a
common pipe) that burns ethylene
process off-gas, except flares.
Subpart Y—Petroleum Refineries
37. Section 98.256 is amended by:
a. Revising paragraph (e)(6) and
paragraph (e)(7) introductory text;
■ b. Removing and reserving paragraph
(e)(7)(ii);
■ c. Revising paragraphs (e)(9) and (10);
■ d. Revising paragraphs (f)(7) and
(f)(10) through (13);
■ e. Removing and reserving paragraph
(h)(4);
■ f. Revising paragraphs (h)(5) and (i)(5),
(7), and (8);
■ g. Removing and reserving paragraph
(j)(2);
■ h. Revising paragraphs (j)(5) through
(9), (k)(3) and (4), (l)(5), and (m)(3);
■ i. Removing and reserving paragraphs
(o)(2)(ii) and (o)(4)(ii) through (iv);
■ j. Revising paragraph (o)(4)(v);
■ k. Removing and reserving paragraphs
(o)(6) and (7); and
■ l. Revising paragraph (p)(2).
The revisions read as follows:
■
■
§ 98.256
Data reporting requirements.
tkelley on DSK3SPTVN1PROD with RULES3
*
*
*
*
*
(e) * * *
(6) If you use Equation Y–1a of
§ 98.253, an indication of whether daily
or weekly measurement periods are
used, the annual volume of flare gas
combusted (in scf/year) and the annual
average molecular weight (in kg/kgmole), and annual average carbon
content of the flare gas (in kg carbon per
kg flare gas).
(7) If you use Equation Y–1b of
§ 98.253, an indication of whether daily
or weekly measurement periods are
used, the annual volume of flare gas
combusted (in scf/year), the annual
average CO2 concentration (volume or
mole percent), the number of carbon
containing compounds other than CO2
in the flare gas stream, and for each of
the carbon containing compounds other
than CO2 in the flare gas stream:
*
*
*
*
*
(9) If you use Equation Y–3 of
§ 98.253, the number of SSM events
exceeding 500,000 scf/day.
(10) The basis for the value of the
fraction of carbon in the flare gas
contributed by methane used in
Equation Y–4 of § 98.253.
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(f) * * *
(7) If you use Equation Y–6 of
§ 98.253, the annual average exhaust gas
flow rate, %CO2, and %CO.
*
*
*
*
*
(10) If you use Equation Y–8 of
§ 98.253, the basis for the value of the
average carbon content of coke.
(11) Indicate whether you use a
measured value, a unit-specific
emission factor, or a default for CH4
emissions. If you use a unit-specific
emission factor for CH4, report the basis
for the factor.
(12) Indicate whether you use a
measured value, a unit-specific
emission factor, or a default emission
factor for N2O emissions. If you use a
unit-specific emission factor for N2O,
report the basis for the factor.
(13) If you use Equation Y–11 of
§ 98.253, the number of regeneration
cycles or measurement periods during
the reporting year and the average coke
burn-off quantity per cycle or
measurement period.
*
*
*
*
*
(h) * * *
(5) If you recycle tail gas to the front
of the sulfur recovery plant, indicate
whether the recycled flow rate and
carbon content are included in the
measured data under § 98.253(f)(2) and
(3). Indicate whether a correction for
CO2 emissions in the tail gas was used
in Equation Y–12 of § 98.253. If so, then
report:
(i) Indicate whether you used the
default (95 percent) or a unit specific
correction, and if a unit-specific
correction was used, report the value of
the correction and the approach used.
(ii) If the following data are not used
to calculate the recycling correction
factor, report the information specified
in paragraphs (h)(5)(ii)(A) through (B) of
this section.
(A) The annual volume of recycled
tail gas (in scf/year) only.
(B) The annual average mole fraction
of carbon in the tail gas (in kg-mole C/
kg-mole gas).
*
*
*
*
*
(i) * * *
(5) If you use Equation Y–13 of
§ 98.253, an indication of whether coke
dust is recycled to the unit (e.g., all dust
is recycled, a portion of the dust is
recycled, or none of the dust is
recycled).
*
*
*
*
*
(7) Indicate whether you use a
measured value, a unit-specific
emission factor or a default emission
factor for CH4 emissions. If you use a
unit-specific emission factor for CH4,
report the basis for the factor.
(8) Indicate whether you use a
measured value, a unit-specific
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emission factor, or a default emission
factor for N2O emissions. If you use a
unit-specific emission factor for N2O,
report the basis for the factor.
(j) * * *
(5) If you use Equation Y–14 of
§ 98.253, the basis for the CO2 emission
factor used.
(6) If you use Equation Y–15 of
§ 98.253, the basis for the CH4 emission
factor used.
(7) If you use Equation Y–16a of
§ 98.253, the basis for the carbon
emission factor used.
(8) If you use Equation Y–16b of
§ 98.253, the basis for the CO2 emission
factor used and the basis for the carbon
emission factor used.
(9) If you use Equation Y–17 of
§ 98.253, the basis for the CH4 emission
factor used.
*
*
*
*
*
(k) * * *
(3) The total number of delayed
coking units at the facility; the total
number of delayed coking drums at the
facility; and, for each coke drum or
vessel, the typical drum outage (i.e. the
unfilled distance from the top of the
drum, in feet).
(4) For each set of coking drums that
are the same dimensions, the number of
coking drums in the set, and the mole
fraction of methane in coking gas (in kgmole CH4/kg-mole gas, wet basis).
*
*
*
*
*
(l) * * *
(5) The annual volumetric flow
discharged to the atmosphere (in scf),
and an indication of the measurement or
estimation method, annual average mole
fraction of each GHG above the
concentration threshold or otherwise
required to be reported and an
indication of the measurement or
estimation method, and for intermittent
vents, the number of venting events and
the cumulative venting time.
*
*
*
*
*
(m) * * *
(3) For uncontrolled blowdown
systems reporting under § 98.253(k), the
basis for the value of the methane
emission factor used for uncontrolled
blowdown systems.
*
*
*
*
*
(o) * * *
(4) * * *
(v) The basis for the mole fraction of
CH4 in vent gas from unstabilized crude
oil storage tanks.
*
*
*
*
*
(p) * * *
(2) The types of materials loaded that
have an equilibrium vapor-phase
concentration of methane of 0.5 volume
percent or greater, and the type of vessel
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(barge, tanker, marine vessel, etc.) in
which each type of material is loaded.
*
*
*
*
*
■ 38. Section 98.257 is amended to read
as follows:
tkelley on DSK3SPTVN1PROD with RULES3
§ 98.257
Records that must be retained.
In addition to the records required by
§ 98.3(g), you must retain the records
specified in paragraphs (a) and (b) of
this section.
(a) The records of all parameters
monitored under § 98.255. If you
comply with the combustion
methodology in § 98.252(a), then you
must retain under this subpart the
records required for the Tier 3 and/or
Tier 4 Calculation Methodologies in
§ 98.37 and you must keep records of
the annual average flow calculations.
(b) Verification software records. You
must keep a record of the file generated
by the verification software specified in
§ 98.5(b) for the applicable data
specified in paragraphs (b)(1) through
(67) of this section. Retention of this file
satisfies the recordkeeping requirement
for the data in paragraphs (b)(1) through
(67) of this section.
(1) Volume of flare gas combusted
during measurement period (scf)
(Equation Y–1b of § 98.253).
(2) Mole percent CO2 concentration in
the flare gas stream during the
measurement period (mole percent)
(Equation Y–1b).
(3) Mole percent concentration of
compound ‘‘x’’ in the flare gas stream
during the measurement period (mole
percent) (Equation Y–1b).
(4) Carbon mole number of compound
‘‘x’’ in the flare gas stream during the
measurement period (mole carbon
atoms per mole compound) (Equation
Y–1b).
(5) Molar volume conversion factor
(scf per kg-mole) (Equation Y–1b).
(6) Annual volume of flare gas
combusted for each flare during normal
operations from company records
(million (MM) standard cubic feet per
year, MMscf/year) (Equation Y–3 of
§ 98.253).
(7) Higher heating value for fuel gas
or flare gas for each flare from company
records (British thermal units per scf,
Btu/scf = MMBtu/MMscf) (Equation Y–
3).
(8) Volume of flare gas combusted
during indexed start-up, shutdown, or
malfunction event from engineering
calculations (scf) (Equation Y–3).
(9) Average molecular weight of the
flare gas, from the analysis results or
engineering calculations for the event
(kg/kg-mole) (Equation Y–3).
(10) Molar volume conversion factor
(scf per kg-mole) (Equation Y–3).
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(11) Average carbon content of the
flare gas, from analysis results or
engineering calculations for the event
(kg C per kg flare gas) (Equation Y–3).
(12) Weight fraction of carbon in the
flare gas prior to combustion in each
flare that is contributed by methane
from measurement values or
engineering calculations (kg C in
methane in flare gas/kg C in flare gas)
(Equation Y–4 of § 98.253).
(13) Annual throughput of unit from
company records for each catalytic
cracking unit or fluid coking unit
(barrels/year) (Equation Y–8 of
§ 98.253).
(14) Coke burn-off factor from
engineering calculations (default for
catalytic cracking units = 7.3; default for
fluid coking units = 11) (kg coke per
barrel of feed) (Equation Y–8).
(15) Carbon content of coke based on
measurement or engineering estimate
(kg C per kg coke) (Equation Y–8).
(16) Value of unit-specific CH4
emission factor, including the units of
measure, for each catalytic cracking
unit, traditional fluid coking unit,
catalytic reforming unit, and coke
calcining unit (calculation method in
§ 98.253(c)(4)).
(17) Annual activity data (e.g., input
or product rate), including the units of
measure, in units of measure consistent
with the emission factor, for each
catalytic cracking unit, traditional fluid
coking unit, catalytic reforming unit,
and coke calcining unit (calculation
method in § 98.253(c)(4)).
(18) Value of unit-specific N2O
emission factor, including the units of
measure, for each catalytic cracking
unit, traditional fluid coking unit,
catalytic reforming unit, and coke
calcining unit (calculation method in
§ 98.253(c)(5)).
(19) Annual activity data (e.g., input
or product rate), including the units of
measure, in units of measure consistent
with the emission factor, for each
catalytic cracking unit, traditional fluid
coking unit, catalytic reforming unit,
and coke calcining unit (calculation
method in § 98.253(c)(5)).
(20) Carbon content of coke based on
measurement or engineering estimate
(default = 0.94) (kg C per kg coke)
(Equation Y–11 of § 98.253).
(21) Volumetric flow rate of sour gas
(including sour water stripper gas) feed
sent off site for sulfur recovery in the
year (scf/year) (Equation Y–12 of
§ 98.253).
(22) Mole fraction of carbon in the
sour gas feed sent off site for sulfur
recovery (kg-mole C/kg-mole gas)
(Equation Y–12).
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(23) Molar volume conversion factor
for sour gas sent off site (scf per kgmole) (Equation Y–12).
(24) Volumetric flow rate of sour gas
(including sour water stripper gas) fed
to the onsite sulfur recovery plant (scf/
year) (Equation Y–12).
(25) Mole fraction of carbon in the
sour gas fed to the onsite sulfur recovery
plant (kg-mole C/kg-mole gas) (Equation
Y–12).
(26) Molar volume conversion factor
for onsite sulfur recovery plant (scf per
kg-mole) (Equation Y–12).
(27) Annual mass of green coke fed to
the coke calcining unit from facility
records (metric tons/year) (Equation Y–
13 of § 98.253).
(28) Annual mass of marketable
petroleum coke produced by the coke
calcining unit from facility records
(metric tons/year) (Equation Y–13).
(29) Annual mass of petroleum coke
dust removed from the process through
the dust collection system of the coke
calcining unit from facility records. For
coke calcining units that recycle the
collected dust, the mass of coke dust
removed from the process is the mass of
coke dust collected less the mass of coke
dust recycled to the process (metric
tons/year) (Equation Y–13).
(30) Average mass fraction carbon
content of green coke from facility
measurement data (metric tons C per
metric ton green coke) (Equation Y–13).
(31) Average mass fraction carbon
content of marketable petroleum coke
produced by the coke calcining unit
from facility measurement data (metric
tons C per metric ton petroleum coke
(Equation Y–13).
(32) Quantity of asphalt blown for
each asphalt blowing unit (million
barrels per year (MMbbl/year))
(Equation Y–14 of § 98.253).
(33) Emission factor for CO2 from
uncontrolled asphalt blowing from
facility-specific test data for each
asphalt blowing unit (metric tons CO2/
MMbbl asphalt blown) (Equation Y–14).
(34) Emission factor for CH4 from
uncontrolled asphalt blowing from
facility-specific test data for each
asphalt blowing unit (metric tons CH4/
MMbbl asphalt blown) (Equation Y–15
of § 98.253).
(35) Quantity of asphalt blown
(million barrels/year (MMbbl/year))
(Equation Y–16a of § 98.253).
(36) Carbon emission factor from
asphalt blowing from facility-specific
test data (metric tons C/MMbbl asphalt
blown) (Equation Y–16a).
(37) Quantity of asphalt blown for
each asphalt blowing unit (million
barrels per year (MMbbl/year))
(Equation Y–16b of § 98.253).
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(38) Emission factor for CO2 from
uncontrolled asphalt blowing from
facility-specific test data for each
asphalt blowing unit (metric tons CO2/
MMbbl asphalt blown) (Equation Y–
16b).
(39) Carbon emission factor from
asphalt blowing from facility-specific
test data for each asphalt blowing unit
(metric tons C/MMbbl asphalt blown)
(Equation Y–16b).
(40) Emission factor for CH4 from
uncontrolled asphalt blowing from
facility-specific test data for each
asphalt blowing unit (metric tons CH4/
MMbbl asphalt blown) (Equation Y–17
of § 98.253).
(41) Cumulative number of vessel
openings for all delayed coking unit
vessels of the same dimensions during
the year (Equation Y–18 of § 98.253).
(42) Height of coking unit vessel for
each set of coke drums or vessels of the
same size (feet) (Equation Y–18).
(43) Gauge pressure of the coking
vessel when opened to the atmosphere
prior to coke cutting or, if the alternative
method provided in § 98.253(i)(2) is
used, gauge pressure of the coking
vessel when depressurization gases are
first routed to the atmosphere for each
set of coke drums or vessels of the same
size (pounds per square inch gauge
(psig)) (Equation Y–18).
(44) Volumetric void fraction of
coking vessel prior to steaming for each
set of coke drums or vessels of the same
size (cf gas/cf of vessel) (Equation Y–
18).
(45) Diameter of coking unit vessel for
each set of coke drums or vessels of the
same size (feet) (Equation Y–18).
(46) Molar volume conversion factor
for each set of coke drums or vessels of
the same size (scf per kg-mole)
(Equation Y–18).
(47) Average volumetric flow rate of
process gas during the event from
measurement data, process knowledge,
or engineering estimates for each set of
coke drums or vessels of the same size
(scf per hour) (Equation Y–19 of
§ 98.253).
(48) Mole fraction of methane in
process vent during the event from
measurement data, process knowledge,
or engineering estimates for each set of
coke drums or vessels of the same size
(kg-mole CH4/kg-mole gas) (Equation Y–
19).
(49) Venting time for the event for
each set of coke drums or vessels of the
same size (hours) (Equation Y–19).
(50) Molar volume conversion factor
for each set of coke drums or vessels of
the same size (scf per kg-mole)
(Equation Y–19).
(51) Quantity of crude oil plus the
quantity of intermediate products
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received from off site that are processed
at the facility (MMbbl/year) (Equation
Y–20 of § 98.253).
(52) Molar volume conversion factor
(scf per kg-mole) (Equation Y–20).
(53) Methane emission factor for
uncontrolled blown systems (scf CH4/
MMbbl) (Equation Y–20).
(54) Quantity of crude oil plus the
quantity of intermediate products
received from off site that are processed
at the facility (MMbbl/year) (Equation
Y–22 of § 98.253).
(55) Quantity of unstabilized crude oil
received at the facility (MMbbl/year)
(Equation Y–23 of § 98.253).
(56) Pressure differential from the
previous storage pressure to
atmospheric pressure (psi) (Equation Y–
23).
(57) Average mole fraction of CH4 in
vent gas from the unstabilized crude oil
storage tanks from facility
measurements (kg-mole CH4/kg-mole
gas) (Equation Y–23).
(58) Molar volume conversion factor
(scf per kg-mole) (Equation Y–23).
(59) Specify whether the calculated or
default loading factor L specified in
§ 98.253(n) is entered, for each liquid
loaded to each (methods specified in
§ 98.253(n)).
(60) Saturation factor specified in
§ 98.253(n), for each liquid loaded to
each vessel (methods specified in
§ 98.253(n)).
(61) True vapor pressure of liquid
loaded, for each liquid loaded to each
vessel (psia) (methods specified in
§ 98.253(n)).
(62) Molecular weight of vapors (lb
per lb-mole), for each liquid loaded to
each vessel (methods specified in
§ 98.253(n)).
(63) Temperature of bulk liquid
loaded, for each liquid loaded to each
vessel (°R, degrees Rankine) (methods
specified in § 98.253(n)).
(64) Total loading loss (without
efficiency correction), for each liquid
loaded to each vessel (pounds per 1000
gallons loaded) (methods specified in
§ 98.253(n)).
(65) Overall emission control system
reduction efficiency, including the
vapor collection system efficiency and
the vapor recovery or destruction
efficiency (enter zero if no emission
controls), for each liquid loaded to each
vessel (percent) (methods specified
§ 98.253(n)).
(66) Vapor phase concentration of
methane in liquid loaded, for each
liquid loaded to each vessel (percent by
volume) (methods specified in
§ 98.253(n)).
(67) Quantity of material loaded, for
each liquid loaded to each vessel
(thousand gallon per year) (methods
specified in § 98.253(n)).
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Subpart Z—Phosphoric Acid
Production
§ 98.266
[Amended]
39. Section 98.266 is amended by
removing and reserving paragraphs (f)(5)
and (6).
■ 40. Section 98.267 is amended by
revising the introductory text and
adding paragraph (d) to read as follows:
■
§ 98.267
Records that must be retained.
In addition to the records required by
§ 98.3(g), you must retain the records
specified in paragraphs (a) through (d)
of this section for each wet-process
phosphoric acid production facility.
*
*
*
*
*
(d) Verification software records. You
must keep a record of the file generated
by the verification software specified in
§ 98.5(b) for the applicable data
specified in paragraphs (d)(1) through
(4) of this section. Retention of this file
satisfies the recordkeeping requirement
for the data in paragraphs (d)(1) through
(4) of this section.
(1) Inorganic carbon content of a grab
sample batch of phosphate rock by
origin obtained during month by wetprocess phosphoric acid process line,
from the carbon analysis results (percent
by weight, expressed as a decimal
fraction) (Equation Z–1a of § 98.263).
(2) Mass of phosphate rock by origin
consumed in month by wet-process
phosphoric acid process line (tons)
(Equation Z–1a).
(3) Carbon dioxide content of a grab
sample batch of phosphate rock by
origin obtained during month by wetprocess phosphoric acid process line
(percent by weight, expressed as a
decimal fraction) (Equation Z–1b of
§ 98.263).
(4) Mass of phosphate rock by origin
consumed in month by wet-process
phosphoric acid process line (tons)
(Equation Z–1b).
Subpart AA—Pulp and Paper
Manufacturing
41. Section 98.276 is amended by:
a. Revising the introductory
paragraph;
■ b. Removing and reserving paragraph
(b);
■ c. Revising paragraph (c);
■ d. Removing and reserving paragraphs
(d), (f), (g), (h) and (i); and
■ e. Adding paragraph (l).
The revisions and addition read as
follows:
■
■
§ 98.276
Data reporting requirements.
In addition to the information
required by § 98.3(c) and the applicable
information required by § 98.36, each
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annual report must contain the
information in paragraphs (a) through (l)
of this section as applicable:
*
*
*
*
*
(c) Basis for determining the annual
mass of the spent liquor solids
combusted (whether based on T650 om05 Solids Content of Black Liquor,
TAPPI (incorporated by reference, see
§ 98.7) or an online measurement
system).
*
*
*
*
*
(l) For each pulp mill lime kiln, report
the information specified in paragraphs
(l)(1) and (2) of this section.
(1) The quantity of calcium oxide
(CaO) produced (metric tons).
(2) The percent of annual heat input,
individually for each fossil fuel type.
■ 42. Section 98.277 is amended by
revising the introductory text and
adding paragraph (g) to read as follows:
tkelley on DSK3SPTVN1PROD with RULES3
§ 98.277
Records that must be retained.
In addition to the information
required by § 98.3(g), you must retain
the records in paragraphs (a) through (g)
of this section.
*
*
*
*
*
(g) Verification software records. You
must keep a record of the file generated
by the verification software specified in
§ 98.5(b) for the applicable data
specified in paragraphs (g)(1) through
(27) of this section. Retention of this file
satisfies the recordkeeping requirement
for the data in paragraphs (g)(1) through
(27) of this section.
(1) Mass of the solid fuel combusted
(tons/year) (Equation C–1 of § 98.33).
(2) Volume of the liquid fuel
combusted (gallons/year) (Equation C–
1).
(3) Volume of the gaseous fuel
combusted (scf/year) (Equation C–1).
(4) Annual natural gas usage (therms/
year) (Equation C–1a of § 98.33).
(5) Annual natural gas usage (mmBtu/
year) (Equation C–1b of § 98.33).
(6) Mass of the solid fuel combusted
(tons/year) (Equation C–2a of § 98.33).
(7) Volume of the liquid fuel
combusted (gallons/year) (Equation C–
2a).
(8) Volume of the gaseous fuel
combusted (scf/year) (Equation C–2a).
(9) Annual mass of the solid fuel
combusted (short tons/year) (Equation
C–3 of § 98.33).
(10) Annual average carbon content of
the solid fuel (percent by weight,
expressed as a decimal fraction)
(Equation C–3).
(11) Annual volume of the liquid fuel
combusted (gallons/year) (Equation C–4
of § 98.33).
(12) Annual average carbon content of
the liquid fuel (kg C per gallon of fuel)
(Equation C–4).
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(13) Annual volume of the gaseous
fuel combusted (scf/year) (Equation C–
5 of § 98.33).
(14) Annual average carbon content of
the gaseous fuel (kg C per kg of fuel)
(Equation C–5).
(15) Annual average molecular weight
of the gaseous fuel (kg/kg-mole)
(Equation C–5).
(16) Molar volume conversion factor
at standard conditions, as defined in
§ 98.6 (scf per kg-mole) (Equation C–5).
(17) Identify if you will use the
default high heat value from Table C–1
of subpart C of this part, or actual HHV
data (Equation C–8 of § 98.33).
(18) High heat value of the fuel
(mmBTU/tons) (Equation C–8).
(19) High heat value of the fuel
(mmBTU/gallons) (Equation C–8).
(20) High heat value of the fuel
(mmBTU/scf) (Equation C–8).
(21) Mass of spent liquor solids
combusted from each chemical recovery
furnace located at a kraft or soda
facility, in short tons in year,
determined according to § 98.274(b)
(tons/year) (Equation AA–1 of § 98.273).
(22) Annual high heat value of the
spent liquor solids from each chemical
recovery furnace located at a kraft or
soda facility determined according to
§ 98.274(b) (mmBtu per kilogram)
(Equation AA–1).
(23) Annual high heat value of the
spent liquor solids from each chemical
recovery combustion unit located at a
sulfite or stand-alone semichemical
facility, determined according to
§ 98.274(b) (mmBtu per kilogram)
(Equation AA–1).
(24) Mass of the spent liquor solids
combusted in short tons per year
determined according to § 98.274(b)
(tons/year) (Equation AA–2 of § 98.273).
(25) Annual carbon content of the
spent liquor solids, determined
according to § 98.274(b) (percent by
weight, expressed as a decimal fraction
(e.g., 95% = 0.95)) (Equation AA–2).
(26) Make-up quantity of CaCO3 used
for the reporting year (metric tons/year)
(Equation AA–3 of § 98.273).
(27) Make-up quantity of Na2CO3 used
for the reporting year metric tons/year)
(Equation AA–3).
Subpart BB—Silicon Carbide
Production
§ 98.286
[Amended]
43. Section 98.286 is amended by
removing and reserving paragraphs
(b)(1), (4), and (6).
■ 44. Section 98.287 is amended by
revising the introductory text and
adding paragraph (c) to read as follows:
■
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§ 98.287
Records that must be retained.
In addition to the records required by
§ 98.3(g), you must retain the records
specified in paragraphs (a) through (c) of
this section for each silicon carbide
production facility.
*
*
*
*
*
(c) Verification software records. You
must keep a record of the file generated
by the verification software specified in
§ 98.5(b) for the applicable data
specified in paragraphs (c)(1) and (2) of
this section. Retention of this file
satisfies the recordkeeping requirement
for the data in paragraphs (c)(1) and (2)
of this section.
(1) Carbon content factor for
petroleum coke consumed in month
from the supplier or as measured by the
applicable method (percent by weight
expressed as a decimal fraction)
(Equation BB–1 of § 98.283).
(2) Petroleum coke consumption in
month (tons) (Equation BB–2 of
§ 98.283).
Subpart CC—Soda Ash Manufacturing
45. Section 98.296 is amended by
removing and reserving paragraphs
(b)(5) through (7) and adding paragraphs
(b)(10)(v) and (vi) to read as follows:
■
§ 98.296
Data reporting requirements.
*
*
*
*
*
(b) * * *
(10) * * *
(v) Average process vent flow from
mine water stripper/evaporator during
performance test (pounds/hour).
(vi) Annual process vent flow rate
from mine water stripper/evaporator
(thousand pounds/hour).
*
*
*
*
*
■ 46. Section 98.297 is amended by
revising the introductory text and
adding paragraph (c) to read as follows:
§ 98.297
Records that must be retained.
In addition to the records required by
§ 98.3(g), you must retain the records
specified in paragraphs (a) through (c) of
this section for each soda ash
manufacturing line.
*
*
*
*
*
(c) Verification software records. You
must keep a record of the file generated
by the verification software specified in
§ 98.5(b) for the applicable data
specified in paragraphs (c)(1) through
(4) of this section. Retention of this file
satisfies the recordkeeping requirement
for the data in paragraphs (c)(1) through
(4) of this section
(1) Inorganic carbon content in trona
input, from the carbon analysis results
for month (percent by weight, expressed
as a decimal fraction) (Equation CC–1 of
§ 98.293).
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(2) Mass of trona input in month
(tons) (Equation CC–1).
(3) Inorganic carbon content in soda
ash output, from the carbon analysis
results for month (percent by weight,
expressed as a decimal fraction)
(Equation CC–2 of § 98.293).
(4) Mass of soda ash output in month
(tons) (Equation CC–2).
Subpart EE—Titanium Dioxide
Production
§ 98.316
[Amended]
47. Section 98.316 is amended by
removing and reserving paragraphs
(b)(6) and (9).
■ 48. Section 98.317 is amended by
revising the introductory text and
adding paragraph (c) to read as follows:
■
§ 98.317
Records that must be retained.
In addition to the records required by
§ 98.3(g), you must retain the records
specified in paragraphs (a) through (c) of
this section for each titanium dioxide
production facility.
*
*
*
*
*
(c) Verification software records. You
must keep a record of the file generated
by the verification software specified in
§ 98.5(b) for the applicable data
specified in paragraphs (c)(1) and (2) of
this section. Retention of this file
satisfies the recordkeeping requirement
for the data in paragraphs (c)(1) and (2)
of this section.
(1) Carbon content factor for
petroleum coke consumed in month
from the supplier or as measured by the
applicable method incorporated by
reference in § 98.7 according to
§ 98.314(c) (percent by weight,
expressed as a decimal fraction)
(Equation EE–2 of § 98.313).
(2) Calcined petroleum coke
consumption for process line in month
(tons) (Equation EE–2).
Subpart GG—Zinc Production
§ 98.336
[Amended]
49. Section 98.336 is amended by
removing and reserving paragraphs
(b)(6), (7), and (10).
■ 50. Section 98.337 is amended by
revising the introductory text and
adding paragraph (c) to read as follows:
tkelley on DSK3SPTVN1PROD with RULES3
■
VerDate Sep<11>2014
17:25 Oct 23, 2014
Jkt 235001
§ 98.337
Records that must be retained.
In addition to the records required by
§ 98.3(g), you must retain the records
specified in paragraphs (a) through (c) of
this section for each zinc production
facility.
*
*
*
*
*
(c) Verification software records. You
must keep a record of the file generated
by the verification software specified in
§ 98.5(b) for the applicable data
specified in paragraphs (c)(1) through
(9) of this section. Retention of this file
satisfies the recordkeeping requirement
for the data in paragraphs (c)(1) through
(9) of this section.
(1) Annual mass of zinc bearing
material charged to kiln or furnace
(tons) (Equation GG–1 of § 98.333).
(2) Carbon content of the zinc bearing
material, from the annual carbon
analysis for kiln or furnace (percent by
weight, expressed as a decimal fraction)
(Equation GG–1).
(3) Annual mass of flux materials
(e.g., limestone, dolomite) charged to
each kiln or furnace (tons) (Equation
GG–1).
(4) Carbon content of the flux
materials charged to each kiln or
furnace, from the annual carbon
analysis (percent by weight, expressed
as a decimal fraction) (Equation GG–1).
(5) Annual mass of carbon electrode
consumed in each furnace (tons)
(Equation GG–1).
(6) Carbon content of the carbon
electrode consumed in each furnace,
from the annual carbon analysis
(percent by weight, expressed as a
decimal fraction) (Equation GG–1).
(7) Annual mass of carbonaceous
materials (e.g., coal, coke) charged to
each kiln or furnace (tons) (Equation
GG–1).
(8) Carbon content of the
carbonaceous materials charged to each
kiln or furnace, from the annual carbon
analysis (percent by weight, expressed
as a decimal fraction) (Equation GG–1).
(9) Identify whether each unit is a
Waelz kiln or an electrothermic furnace.
Subpart TT—Industrial Waste Landfills
51. Section 98.466 is amended by:
a. Removing and reserving paragraph
(c)(3)(i);
■
■
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63799
b. Revising paragraph (c)(3)(ii); and
■ c. Removing and reserving paragraph
(c)(3)(iii).
The revisions read as follows:
■
§ 98.466
Data reporting requirements.
*
*
*
*
*
(c) * * *
(3) * * *
(ii) The year of the data used in
Equation TT–2 of § 98.463 for the waste
disposal quantity and production
quantity, for each year used in Equation
TT–2 to calculate the average waste
disposal factor (WDF).
*
*
*
*
*
52. Section 98.467 is amended to read
as follows:
■
§ 98.467
Records that must be retained.
In addition to the information
required by § 98.3(g), you must retain:
(a) The calibration records for all
monitoring equipment, including the
method or manufacturer’s specification
used for calibration, and all
measurement data used for the purposes
of § 98.460(c)(2)(xii) or (xiii) or used to
determine waste stream-specific DOCX
values for use in Equation TT–1 of
§ 98.463.
(b) Verification software records. You
must keep a record of the file generated
by the verification software specified in
§ 98.5(b) for the applicable data
specified in paragraphs (b)(1) and (2) of
this section. Retention of this file
satisfies the recordkeeping requirement
for the data in paragraphs (b)(1) and (2)
of this section.
(1) Quantity of each product produced
or feedstock entering the process or
facility per waste stream per year, from
measurement data and/or other
company records. You must use the
same basis for all years in the
calculation (i.e., based on production or
based on quantity of feedstock) (metric
tons) (Equation TT–2 of § 98.463).
(2) [Reserved]
[FR Doc. 2014–23780 Filed 10–23–14; 8:45 am]
BILLING CODE 6560–50–P
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Agencies
[Federal Register Volume 79, Number 206 (Friday, October 24, 2014)]
[Rules and Regulations]
[Pages 63749-63799]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2014-23780]
[[Page 63749]]
Vol. 79
Friday,
No. 206
October 24, 2014
Part III
Environmental Protection Agency
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40 CFR Part 98
Revisions to Reporting and Recordkeeping Requirements, and
Confidentiality Determinations Under the Greenhouse Gas Reporting
Program; Final Rule
Federal Register / Vol. 79 , No. 206 / Friday, October 24, 2014 /
Rules and Regulations
[[Page 63750]]
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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 98
[EPA-HQ-OAR-2010-0929; FRL-9916-76-OAR]
RIN 2060-AQ81
Revisions to Reporting and Recordkeeping Requirements, and
Confidentiality Determinations Under the Greenhouse Gas Reporting
Program; Final Rule
AGENCY: Environmental Protection Agency.
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: The Environmental Protection Agency (EPA) is amending the
reporting and recordkeeping requirements of the Greenhouse Gas
Reporting Program. These amendments include an alternative verification
approach in lieu of collecting certain data elements for which the EPA
has identified disclosure concerns and for which the reporting deadline
was deferred until March 31, 2015. The alternative verification
approach includes the addition of new verification, recordkeeping, and
reporting requirements while maintaining the EPA's ability to verify
emissions and ensure compliance with the Greenhouse Gas Reporting
Program. In conjunction with the amendments, the EPA is establishing
final confidentiality determinations for the new data elements added in
this action.
DATES: This final rule is effective on November 24, 2014.
ADDRESSES: All documents in the docket are listed in the https://www.regulations.gov index. Although listed in the index, some
information is not publicly available, e.g., confidential business
information (CBI) or other information whose disclosure is restricted
by statute. Certain other material, such as copyrighted material, will
be publicly available only in hard copy. Publicly available docket
materials are available either electronically in https://www.regulations.gov or in hard copy at the Air Docket, EPA/DC, William
Jefferson Clinton Building West, Room B102, 1301 Constitution Ave. NW.,
Washington, DC. This Docket Facility is open from 8:30 a.m. to 4:30
p.m., Monday through Friday, excluding legal holidays. The telephone
number for the Public Reading Room is (202) 566-1744, and the telephone
number for the Air Docket is (202) 566-1742.
FOR FURTHER GENERAL INFORMATION CONTACT: Carole Cook, Climate Change
Division, Office of Atmospheric Programs (MC-6207J), Environmental
Protection Agency, 1200 Pennsylvania Ave. NW., Washington, DC 20460;
telephone number: (202) 343-9263; fax number: (202) 343-2342; email
address: GHGreporting@epa.gov. For technical information, contact the
Greenhouse Gas Reporting Rule Helpline at: https://www.epa.gov/climatechange/emissions/ghgrule_contactus.htm. Alternatively, contact
Carole Cook at 202-343-9263.
Worldwide Web (WWW). In addition to being available in the docket,
an electronic copy of this final rule, memoranda to the docket, and all
other related information will also be available through the WWW on the
EPA's greenhouse gas reporting rule Web site at https://www.epa.gov/climatechange/emissions/ghgrulemaking.html.
SUPPLEMENTARY INFORMATION:
Regulated Entities. This final rule revision on reporting and
recordkeeping requirements and verification procedures affects entities
that must submit annual greenhouse gas (GHG) reports under the
Greenhouse Gas Reporting Program (GHGRP) (40 CFR part 98). The
Administrator has determined that 40 CFR part 98 is subject to the
provisions of Clean Air Act (CAA) section 307(d). See CAA section
307(d)(1)(V) (the provisions of CAA section 307(d) apply to ``such
other actions as the Administrator may determine''). Entities affected
by this final rule are owners and operators of facilities that are
direct emitters of GHGs, which include those listed in Table 1 of this
preamble:
Table 1--Examples of Affected Entities by Category
----------------------------------------------------------------------------------------------------------------
Category NAICS Examples of affected facilities
----------------------------------------------------------------------------------------------------------------
General Stationary Fuel Combustion .............................. Facilities operating boilers, process
Sources. heaters, incinerators, turbines, and
internal combustion engines.
321........................... Manufacturers of lumber and wood
products.
322........................... Pulp and paper mills.
325........................... Chemical manufacturers.
324........................... Petroleum refineries and manufacturers
of coal products.
316, 326, 339................. Manufacturers of rubber and
miscellaneous plastic products.
331........................... Steel works, blast furnaces.
332........................... Electroplating, plating, polishing,
anodizing, and coloring.
336........................... Manufacturers of motor vehicle parts and
accessories.
221........................... Electric, gas, and sanitary services.
622........................... Health services.
611........................... Educational services.
325193........................ Ethyl alcohol manufacturing facilities.
311611........................ Meat processing facilities.
311411........................ Frozen fruit, juice, and vegetable
manufacturing facilities.
311421........................ Fruit and vegetable canning facilities.
Adipic Acid Production................ 325199........................ Adipic acid manufacturing facilities.
Aluminum Production................... 331312........................ Primary aluminum production facilities.
Ammonia Manufacturing................. 325311........................ Anhydrous and aqueous ammonia production
facilities.
Cement Production..................... 327310........................ Portland cement manufacturing plants.
Ferroalloy Production................. 331112........................ Ferroalloys manufacturing facilities.
Glass Production...................... 327211........................ Flat glass manufacturing facilities.
327213........................ Glass container manufacturing
facilities.
327212........................ Other pressed and blown glass and
glassware manufacturing facilities.
HCFC-22 Production and HFC-23 325120........................ Chlorodifluoromethane manufacturing
Destruction. facilities.
Hydrogen Production................... 325120........................ Hydrogen production facilities.
Iron and Steel Production............. 331111........................ Integrated iron and steel mills, steel
companies, sinter plants, blast
furnaces, basic oxygen process furnace
shops.
[[Page 63751]]
Lead Production....................... 331419........................ Primary lead smelting and refining
facilities.
331492........................ Secondary lead smelting and refining
facilities.
Lime Production....................... 327410........................ Calcium oxide, calcium hydroxide,
dolomitic hydrates manufacturing
facilities.
Nitric Acid Production................ 325311........................ Nitric acid production facilities.
Petrochemical Production.............. 32511......................... Ethylene dichloride production
facilities.
325199........................ Acrylonitrile, ethylene oxide, methanol
production facilities.
325110........................ Ethylene production facilities.
325182........................ Carbon black production facilities.
Petroleum and Natural Gas Systems..... 486210........................ Pipeline transportation of natural gas.
221210........................ Natural gas distribution facilities.
211........................... Extractors of crude petroleum and
natural gas.
211112........................ Natural gas liquid extraction
facilities.
Petroleum Refineries.................. 324110........................ Petroleum refineries.
Phosphoric Acid Production............ 325312........................ Phosphoric acid manufacturing
facilities.
Pulp and Paper Manufacturing.......... 322110........................ Pulp mills.
322121........................ Paper mills.
322130........................ Paperboard mills.
Silicon Carbide Production............ 327910........................ Silicon carbide abrasives manufacturing
facilities.
Soda Ash Manufacturing................ 325181........................ Alkalies and chlorine manufacturing
facilities.
212391........................ Soda ash, natural, mining and/or
beneficiation.
Titanium Dioxide Production........... 325188........................ Titanium dioxide manufacturing
facilities.
Zinc Production....................... 331419........................ Primary zinc refining facilities.
331492........................ Zinc dust reclaiming facilities,
recovering from scrap and/or alloying
purchased metals.
311411........................ Frozen fruit, juice and vegetable
manufacturing facilities.
311421........................ Fruit and vegetable canning facilities.
Wastewater Treatment \a\.............. 322110........................ Pulp mills.
322121........................ Paper mills.
322122........................ Newsprint mills.
322130........................ Paperboard mills.
311611........................ Meat processing facilities.
311411........................ Frozen fruit, juice and vegetable
manufacturing facilities.
311421........................ Fruit and vegetable canning facilities.
325193........................ Ethanol manufacturing facilities.
----------------------------------------------------------------------------------------------------------------
\a\ The inputs to emission equations (for which reporting was deferred to 2015) in these categories were
evaluated following the four-step process set forth in the memorandum entitled ``Process for Evaluating and
Potentially Amending Part 98 Inputs to Emission Equations'' (Docket ID No. EPA-HQ-OAR-2010-0929). Refer to
Section 1.B of the proposal preamble (78 FR 55994, September 11, 2013) for further information regarding this
evaluation. No amendment to the subpart affecting this industry category was proposed as a result of the
evaluation. Accordingly, this final action does not include any amendment to this subpart. Refer to Section
II.B of this preamble for further discussion of the EPA's decision.
Table 1 of this preamble is not intended to be exhaustive, but
rather provides a guide for readers regarding facilities and suppliers
likely to be affected by this action. Types of facilities other than
those listed in this table might also be affected by this action. To
determine whether you are affected by this action, you should carefully
examine the applicability criteria found in 40 CFR part 98, subpart A
or the relevant criteria in the subparts. If you have questions
regarding the applicability of this action to a particular facility or
supplier, consult the person listed in the preceding FOR FURTHER
GENERAL INFORMATION CONTACT section.
Many facilities that are affected by 40 CFR part 98 have GHG
emissions from multiple source categories listed in Table 1 of this
preamble.
Judicial Review. Under CAA section 307(b)(1), judicial review of
this final rule is available only by filing a petition for review in
the U.S. Court of Appeals for the District of Columbia Circuit (the
Court) by December 23, 2014. 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. Section 307(d)(7)(B) of the CAA also provides a
mechanism for the EPA to convene a proceeding for reconsideration,
``[i]f the person raising an objection can demonstrate to EPA that it
was impracticable to raise such objection within [the period for public
comment] or if the grounds for such objection arose after the period
for public comment (but within the time specified for judicial review)
and if such objection is of central relevance to the outcome of the
rule.'' Any person seeking to make such a demonstration to us should
submit a Petition for Reconsideration to the Office of the
Administrator, Environmental Protection Agency, Room 3000, William
Jefferson Clinton Building, 1200 Pennsylvania Ave. NW., Washington, DC
20460, with a copy to the person listed in the preceding FOR FURTHER
GENERAL 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 20004. Note that 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.
Acronyms and Abbreviations. The following acronyms and
abbreviations are used in this document.
CAA Clean Air Act
CaO Calcium oxide
CAR Climate Action Reserve
CBI Confidential business information
CEMS continuous emissions monitoring system
CFR Code of Federal Regulations
CKD Cement kiln dust
CO2 Carbon dioxide
[[Page 63752]]
e-GGRT Electronic Greenhouse Gas Reporting Tool
EPA U.S. Environmental Protection Agency
FISMA Federal Information Security Management Act of 2002
FR Federal Register
FTC Federal Trade Commission
GHG Greenhouse gas
GHGRP Greenhouse Gas Reporting Program
HCFC-22 Chlorodifluoromethane
HFC Hydrofluorocarbons
HTML Hypertext markup language
ICR Information Collection Request
IVT Inputs Verification Tool
KA Ketone-alcohol oil (or cyclohexanol)
lb Pound
MMBtu Million British thermal units
N2O Nitrous oxide
NAICS North American Industry Classification System
NIST National Institute of Standards and Technology
NTTAA National Technology Transfer and Advancement Act
OMB Office of Management & Budget
PUC Public utility commission
RFA Regulatory Flexibility Act
SSM Startup, shutdown, and malfunction
TLS Transport Layer Security
TRI Toxics Release Inventory
UMRA Unfunded Mandates Reform Act
U.S. United States
WWW Worldwide Web
XML Extensible markup language
Organization of This Document. The following outline is provided to
aid in locating information in this preamble.
I. Executive Summary, Background, and Overview
A. How is this preamble organized?
B. Executive Summary
C. Background on the Action
D. Subparts Covered in the Final Rule
E. Legal Authority
II. Summary of Final Amendments to Part 98
A. Addition of a Requirement for Certain Reporters To Use an
Inputs Verification Tool (IVT) to Enter Certain Data Elements
B. Removal of the Requirement To Report Certain Data Elements
C. Revision of Recordkeeping Requirements for Facilities
Required To Use IVT
D. Addition of Reporting Requirements for Certain Facilities
Required To Use IVT
III. Summary of Final Confidentiality Determinations for New Data
Elements
A. Summary of Final CBI Determinations
B. Response to Public Comments
IV. Impacts of the Final Rule
A. How were the costs of this final rule estimated?
B. Do the final confidentiality determinations change the
impacts of the final amendments?
V. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory Planning and Review and
Executive Order 13563: Improving Regulation and Regulatory Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act (RFA)
D. Unfunded Mandates Reform Act (UMRA)
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation and Coordination With
Indian Tribal Governments
G. Executive Order 13045: Protection of Children From
Environmental Health Risks and Safety Risks
H. Executive Order 13211: Actions That Significantly Affect
Energy Supply, Distribution, or Use
I. National Technology Transfer and Advancement Act
J. Executive Order 12898: Federal Actions To Address
Environmental Justice in Minority Populations and Low-Income
Populations
K. Congressional Review Act
I. Executive Summary, Background, and Overview
A. How is this preamble organized?
Section I of this preamble provides background information
regarding the origin of the final amendments. Section I also discusses
the EPA's legal authority under the CAA to promulgate and amend the
Greenhouse Gas Reporting Rule (40 CFR part 98, hereinafter referred to
as ``Part 98'') and the EPA's legal authority to make confidentiality
determinations for new data elements required by this amendment.
Section II of this preamble describes the final amendments to Part 98,
which includes the EPA's proposed alternative verification approach.
Section II of this preamble also describes the major changes made since
proposal to the alternative verification approach and provides brief
summaries of significant public comments and the EPA's responses
thereto. Section III of this preamble finalizes the confidentiality
determinations for the new data reporting elements being added to Part
98 in this action. Section IV of this preamble discusses the impacts of
the final amendments. Section V of this preamble describes the
statutory and executive order requirements applicable to this action.
B. Executive Summary
The EPA is finalizing the proposed alternative verification
approach for the GHGRP, with some changes made in response to public
comments. The alternative verification approach includes amendments to
reporting and recordkeeping requirements of Part 98, as follows:
Adding a requirement for certain reporters under 23
subparts to use an EPA-provided inputs verification tool (IVT). For
these subparts, 324 inputs to emission equations for which reporting
was deferred to 2015 and for which disclosure concerns have been
identified must be entered into IVT.\1\ IVT will perform electronic
verification on the entered inputs to emission equations and use the
entered inputs to calculate the emission equation results. IVT will not
retain the entered inputs (i.e., the inputs are not reporting
requirements under Part 98); instead, IVT will conduct certain checks
(e.g., accuracy of the inputs and the calculated emissions values) at
the time of data entry and generate a verification summary. The EPA
will not have access to the entered inputs either during the time of
entry or any time thereafter. However, the verification summary, which
will be accessible to the EPA once the reporter has completed using IVT
and the annual report is submitted, will provide the EPA with
information to conduct further verification if necessary.
---------------------------------------------------------------------------
\1\ Under this final action, IVT would not be required to be
used by reporters for any reported GHG for which the reporter uses a
continuous emissions monitoring system (CEMS) or an EPA-approved
alternative method--as allowed under 40 CFR 98.33(a)(5),
98.53(a)(2), and 98.223(a)(2) to calculate the reported GHG value,
rather than using inputs to emission equations (for which reporting
was deferred to 2015) and the associated EPA-provided calculation
methodologies to calculate the reported GHG value.
---------------------------------------------------------------------------
For 23 subparts, removing the requirement to report 378
inputs to emission equations for which reporting was deferred to 2015
and for which disclosure concerns have been identified.\2\
---------------------------------------------------------------------------
\2\ As mentioned above, there are 378 equation inputs for which
reporting was deferred to 2015 and for which the EPA determined
there are disclosure concerns, and 324 of these equation inputs must
be entered into IVT. Fifty-four of the 378 equation inputs do not
need to be entered into IVT because these equation inputs are
redundant to other equations inputs being entered into IVT or are
otherwise not needed for verification.
---------------------------------------------------------------------------
For reporters required to use IVT, specifying the format
for maintaining records of data entered into IVT so that all such
records are maintained in a consistent format; and for each facility
subject to the IVT requirement, lengthening the record retention period
from 3 to 5 years for all data entered into IVT and for other records
maintained by the reporting facility under Part 98 (including subparts
not required to use IVT).
For certain reporters required to use IVT, adding new data
elements to be reported.
The EPA is not amending the reporting requirements for 151 inputs
to emission equations for which reporting was deferred, but for which
disclosure concerns were not identified and the data remain useful. For
these inputs to emission equations, the deferral will
[[Page 63753]]
expire on March 31, 2015, by which date these inputs must be
reported.\3\
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\3\ In this action, the EPA is providing an option for Subpart W
reporters to delay reporting of six inputs to emission equations for
two reporting years in specific situations. Refer to section III.A.3
of this preamble for further discussion on this topic.
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This alternative verification approach builds on the EPA's
experience and success with electronic reporting and verification
during the first 4 years of the GHGRP. This alternative verification
approach, which includes additional verification checks that IVT will
conduct on data entered into IVT (during the data entry process),
provides the EPA with information necessary to identify facilities with
potential reporting errors and conduct further verification following
the submission of annual reports. This alternative verification
approach, including its associated revisions to recordkeeping and
reporting requirements, provides an alternative to collecting certain
data elements for which disclosure concerns have been identified, while
maintaining the EPA's ability to verify data and ensure compliance with
the GHGRP.
Also, in conjunction with the amendments, the EPA is establishing
confidentiality determinations for the new data elements finalized in
this action.
C. Background on the Action
On October 30, 2009, the EPA published the Greenhouse Gas Reporting
Rule, 40 CFR part 98, requiring annual reporting of GHG data from a
broad range of industry sectors (74 FR 56260). Under Part 98, the EPA
requires annual reporting of data from certain facilities and suppliers
above specified emission or quantity-supplied thresholds. On July 7,
2010 (75 FR 39094) and subsequent proposals (77 FR 1434, January 10,
2012; 77 FR 10434, February 22, 2012), we proposed confidentiality
determinations for the data elements required to be reported. The
confidentiality of each reported data element was determined using a
two-step approach: (1) Grouping data elements into 22 data categories
(e.g., inputs to emission equations, emissions, and unit/process
operating characteristics that are not inputs to emission equations for
direct emitter source categories) and (2) making confidentiality
determinations either categorically or on the basis of individual data
elements. Refer to both the July 7, 2010 proposal (75 FR 39097) and the
May 26, 2011 final rule (76 FR 30785-30786) for more detailed
descriptions of this process. Refer to the May 26, 2011 final rule also
for a discussion of individual data element confidentiality
determinations. The EPA has established final confidentiality
determinations for part 98 data elements except those in the ``inputs
to emission equations'' category (May 26, 2011, 76 FR 30782; August 13,
2012, 77 FR 48072; and August 24, 2012, 77 FR 51477).\4\ We proposed
that ``inputs to emission equations'' meet the definition of ``emission
data'' under 40 CFR 2.301(a)(2)(i). Because, under section 114(c) of
the CAA, emission data are not entitled to confidential treatment, we
did not evaluate whether such data elements would qualify as CBI,
including whether disclosure would likely cause substantial competitive
harm to the reporting facilities (75 FR 39105 and 39108, July 7, 2010).
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\4\ There are a small number of data elements (besides data
elements categorized as ``inputs to emission equations'') for which
we have not made final confidentiality determinations because we
concluded that a determination of confidentiality for the data
element should be made on a case-by-case facility basis. For
example, annual ferroalloy product production capacity in subpart K
(ferroalloy production), was not assigned a confidentiality
determination; see 76 FR 30782, May 26, 2011.
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Following our proposal, we received numerous industry comments
expressing concerns regarding potential disclosure of many of these
data elements. In light of the comments, the EPA expressed that ``these
concerns warranted an in-depth evaluation of the potential impact from
the release of inputs to emission equations'' and that the EPA would
``complete this evaluation and take appropriate final actions regarding
inputs to equations before these data elements are reported to EPA and
potentially be subject to release.'' (76 FR 53060, August 25, 2011). In
a document published on December 27, 2010, we issued a call for
information (75 FR 81366) requesting additional information to assist
us in conducting our evaluation. To allow sufficient time to complete
this evaluation through notice and comment, we deferred the reporting
deadline for data elements assigned to the ``inputs to emission
equation'' category. Reporting of certain of these data elements was
deferred to March 31, 2013, as specified in Table A-6 to subpart A; and
reporting of the remainder of these data elements was deferred to March
31, 2015, as specified in Table A-7 to subpart A (see the August 25,
2011 final rule, 76 FR 53057).
Our process for the abovementioned evaluation was documented in the
final deferral document (76 FR 53057, August 25, 2011) and the
accompanying memorandum entitled ``Process for Evaluating and
Potentially Amending Part 98 Inputs to Emission Equations'' (Docket ID
No. EPA-HQ-OAR-2010-0929). As discussed in the final deferral document
and memorandum, our evaluation involved a four-step process, as
follows:
Step 1: Determine whether each data element assigned to
the ``inputs to emission equations'' category is already publicly
available.
Step 2: For data elements assigned to the ``inputs to
emission equations'' category that are not publicly available,
evaluate whether disclosure of the information is likely to result
in substantial competitive harm.
Step 3: For data elements assigned to the ``inputs to
emission equations'' category that are likely to cause substantial
competitive harm if disclosed, evaluate potential alternative
calculation methods.
Step 4: For data elements assigned to the ``inputs to
emission equations'' category that are likely to cause substantial
competitive harm if disclosed, evaluate potential alternative
verification methods.
Using each step of the four-step evaluation process, the EPA
evaluated data elements for which reporting was deferred to March 31,
2015.\5\ The results of the evaluation were documented in the four
following memoranda available in the EPA's Docket ID No. EPA-HQ-OAR-
2010-0929:
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\5\ Based on the same four-step process, we also evaluated all
data elements for which reporting was deferred to March 31, 2013
(Table A-6 to Part 98), which did not result in amendments to Part
98. Accordingly, affected facilities were required to report by
April 1, 2013 these data elements for reporting years 2010 through
2012 and must include them in annual reports for subsequent
reporting years, as required by Part 98. For a discussion of this
evaluation, refer to the EPA's memorandum ``Summary of Evaluation of
Greenhouse Gas Reporting Program (GHGRP) Part 98 ``Inputs to
Emission Equations'' Data Elements Deferred Until 2013'' (December
17, 2012), available at https://www.epa.gov/ghgreporting/documents/pdf/2012/documents/2013-inputs-memo.pdf. In addition, the reporting
of the inputs to emission equations in subpart I was addressed by
amendments published on November 13, 2013 (77 FR 68162).
``Evaluation of Public Availability of Inputs to
Emission Equations for which Reporting was Deferred to March 31,
2015,'' August 2013.
``Evaluation of Competitive Harm from Disclosure of
`Inputs to Equations' Data Elements Deferred to March 31, 2015,''
August 2013.
``Evaluation of Alternative Calculation Methods,''
August 2013.
``Evaluation of Alternative Verification Approaches For
Greenhouse Gas Reporting Rule Subparts for which Reporting of Inputs
to Emission Equations was Deferred to March 31, 2015,'' August 2013.
Based on the results of this evaluation, the EPA proposed on
September 11, 2013 (78 FR 55994) amendments to the recordkeeping and
reporting provisions for 24 subparts of Part 98, including an
alternative
[[Page 63754]]
verification approach, to address the inputs to emission equations for
which disclosure concerns were identified in these subparts. The public
comment period for the proposed rule amendments was initially scheduled
to end on November 12, 2013. The EPA received requests to extend the
public comment period, and the EPA published a document in the Federal
Register on November 6, 2013 (78 FR 66674) extending the public comment
period to November 26, 2013.
In this action, the EPA is finalizing the proposed alternative
verification approach for 23 subparts of the GHGRP with some changes
from the proposed rule. The EPA had proposed amendments but is not
taking final action on subpart L inputs to emission equations. Final
action on subpart L inputs to emission equations will be addressed in a
separate rulemaking.\6\ Responses to comments submitted on the proposed
amendments can be found in both Section II of this preamble and the
document ``Greenhouse Gas Reporting Rule--Revisions to Reporting and
Recordkeeping Requirements, and Proposed Confidentiality Determinations
Under the Greenhouse Gas Reporting Program: EPA's Responses to Public
Comments'' (see Docket ID No. EPA-HQ-OAR-2010-0929).
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\6\ Accordingly, comments received covering solely topics
related to subpart L will be addressed in a separate rulemaking.
---------------------------------------------------------------------------
D. Subparts Covered in the Final Rule
The final amendments remove certain reporting requirements and add
certain verification requirements for all subparts listed in Table 2 of
this preamble. Table 2 of this preamble includes most of the subparts
of Part 98 with inputs to emission equations for which the reporting
deadline was deferred until 2015. Subpart I is not included in Table 2
of this preamble because reporting of the inputs to emission equations
for subpart I was addressed by amendments published on November 13,
2013 (77 FR 68162). As mentioned above, subpart L is not included in
Table 2 of this preamble because the EPA's final decision on reporting
of the inputs to emission equations for subpart L will be addressed in
a separate rulemaking. Subpart II is not listed in Table 2 of this
preamble because no subpart II inputs to emission equations were
determined to have disclosure concerns, so no subpart II inputs are
removed from reporting under this amendment. Subpart W is excluded from
Table 2 of this preamble as well, because no inputs to emission
equations in subpart W are being removed from reporting. Refer to the
memorandum ``Final Evaluation of Competitive Harm from Disclosure of
`Inputs to Equations' Data Elements Deferred to March 31, 2015,''
September 2014 (refer to Docket ID No. EPA-HQ-OAR-2010-0929) for
discussions about the EPA's harm analysis results for subparts W and
II. Refer to Section II.B of this preamble for a discussion of
amendments to subpart W. Additionally, parts of these final rule
amendments affect subparts not listed in Table 2 of this preamble.
Specifically, for owners or operators of facilities subject to both a
subpart listed in Table 2 of this preamble and a subpart of Part 98 not
listed in Table 2 of this preamble, the amended recordkeeping duration
applies to the facility's records required for all Part 98 subparts (to
which the reporter is subject). Refer to Sections II.C and III.B of the
proposal preamble for further discussion of this recordkeeping
amendment (78 FR 55994, September 11, 2013). Additionally, owners or
operators of facilities reporting under subparts E, H, O, Q, W, Y, AA,
CC, and II, as well as certain owners and operators reporting under
subpart C, must report inputs to emission equations for which reporting
was deferred to 2015 and disclosure concerns were not identified for
reporting years 2010 through 2013 in the reporting year 2014 annual
report.\7\ Refer to Section III.A.3 of the proposal preamble for
further discussion of this reporting amendment (78 FR 55994, September
11, 2013).
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\7\ For six data elements in subpart W, reporting of the data
for reporting year 2013 may be delayed until reporting year 2015 in
specific cases. Refer to section II.B.2 of this preamble for further
discussion of this optional reporting delay. Further, final action
on the inputs to emission equations whose reporting deadline was
deferred until 2015 in Subpart L will be addressed in a separate
rulemaking.
Table 2--Subparts Affected by the Final Amendments Removing Certain
Reporting and Adding Certain Verification Requirements \a\
------------------------------------------------------------------------
Subpart
-------------------------------------------------------------------------
C--General Stationary Fuel Combustion--Stationary fuel combustion
sources (e.g., individual units, aggregations of units, common pipes,
or common stacks) excluding those that contain at least one combustion
unit connected to a fuel-fired electric generator owned or operated by
an entity that is subject to regulation of customer billing rates by
the public utility commission (PUC) (excluding generators connected to
combustion units subject to 40 CFR part 98, subpart D) and that are
located at a facility for which the sum of the nameplate capacities for
all such electric generators is greater than or equal to 1 megawatt
electric output.b c
E--Adipic Acid Production.
F--Aluminum Production.
G--Ammonia Manufacturing.
H--Cement Production.
K--Ferroalloy Production.
N--Glass Production.
O--HCFC-22 Production and HFC-23 Destruction.
P--Hydrogen Production.
Q--Iron and Steel Production.
R--Lead Production.
S--Lime Manufacturing.
U--Miscellaneous Uses of Carbonate.
V--Nitric Acid Production.
X--Petrochemical Production.
Y--Petroleum Refineries.
Z--Phosphoric Acid Production.
AA--Pulp and Paper Manufacturing.
BB--Silicon Carbide Production.
CC--Soda Ash Manufacturing.
EE--Titanium Dioxide Production.
[[Page 63755]]
GG--Zinc Production.
TT--Industrial Waste Landfills.
------------------------------------------------------------------------
\a\ This final action does not remove reporting requirements or require
use of IVT for any reported GHG value for which the reporter uses a
continuous emissions monitoring system (CEMS) or an EPA-approved
alternative method--as allowed under 40 CFR 98.33(a)(5), 98.53(a)(2),
and 98.223(a)(2)--to calculate the reported GHG value, rather than
using inputs to emission equations for which reporting was deferred to
March 31, 2015, and the associated EPA-provided calculation
methodologies to calculate the reported GHG value.
\b\ Includes one deferred input to an emission equations, 40 CFR
98.3(d)(3)(v), which is specified in subpart A of Part 98 and applies
to only certain reporters under subpart C.
\c\ These subpart C sources may elect to report inputs to emission
equations rather than use IVT.
E. Legal Authority
The EPA is amending Part 98 under its existing CAA authority
provided in CAA section 114. As stated in the preamble to the 2009
final GHG reporting rule (74 FR 56260, October 30, 2009), CAA section
114(a)(1) provides the EPA broad authority to require the information
to be reported by this rule because such data would inform and are
relevant to the EPA's carrying out a wide variety of CAA provisions.
See the preambles to the proposed (74 FR 16448, April 10, 2009) and
final Part 98 (74 FR 56260, October 30, 2009) for further information.
In addition, pursuant to sections 114, 301, and 307 of the CAA, the
EPA has established final confidentiality determinations for the new
data elements required by this amendment. Section 114(c) of the CAA
requires that the EPA make publicly available information obtained
under CAA section 114, except for information (excluding emission data)
that qualifies for confidential treatment. The Administrator has
determined that this action (Part 98 amendment and confidentiality
determinations) is subject to the provisions of CAA section 307(d).
II. Summary of Final Amendments to Part 98
The EPA is finalizing the proposed alternative verification
approach for the GHGRP, with some changes made in response to public
comments. A detailed description of the alternative verification
approach is available in the preamble to the proposed rule (78 FR
55994, September 11, 2013). Additionally, the EPA is finalizing its CBI
determinations for the new reporting elements added to Part 98 in this
action, with changes made in response to public comments.
This section of the preamble describes the final amendments to Part
98, organized according to the following four general areas:
Addition of a requirement for facilities subject to the
subparts listed in Table 2 of this preamble to use IVT to enter 324
inputs to emission equations into IVT for which reporting was
deferred to 2015 and for which disclosure concerns were identified.
Removal of the requirement to report 378 inputs to
emission equations for which reporting was deferred to 2015 and for
which disclosure concerns were identified.\8\
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\8\ As mentioned above, there are 378 equation inputs for which
reporting was deferred to 2015 and for which the EPA determined
there are disclosure concerns, and 324 of these equation inputs must
be entered into IVT. Fifty-four of the 378 equation inputs do not
need to be entered into IVT because these equation inputs are
redundant to other equations inputs being entered into IVT or are
otherwise not needed for verification.
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Revision of recordkeeping requirements for facilities
required to use IVT.
Addition of new reporting elements for certain
facilities required to use IVT.
These four areas of final amendments are described in more detail
in Sections II.A through II.D of this preamble. Specifically, each of
these sections includes a summary of final amendments, a summary of
major changes since proposal, and a summary of the major comments and
the EPA's responses thereto. The comment response document (Docket ID.
No. EPA-HQ-OAR-2010-0929) includes a complete listing of all comments
received on the proposed rule (78 FR 55994, September 11, 2013) and the
EPA's responses.
Additional rationale for these amendments is available in the
preamble to the proposed rule (78 FR 55994, September 11, 2013).
The final amendments also include minor changes from the proposed
rule that harmonize regulatory text to be consistent with other
provisions in 40 CFR part 98, clarify regulatory text, and correct
minor errors in the proposal. These changes are described in the
memorandum ``Summary and Explanation of Minor Changes Since the
Proposed Rule'' (Docket ID No. EPA-HQ-OAR-2010-0929).
A. Addition of a Requirement for Certain Reporters To Use an Inputs
Verification Tool (IVT) To Enter Certain Data Elements
1. Summary of Final Amendments to Part 98
The EPA is finalizing the proposed requirement that IVT be used by
facilities subject to the subparts listed in Table 2 of this preamble,
with some exceptions for certain subpart C sources, as further
discussed in Section II.A.2 of this preamble. Most commenters generally
supported use of IVT as an effective method for verifying emissions.
Using entered inputs to emission equations, IVT calculates the equation
results, conducts electronic verification checks on the inputs, and
generates a verification summary, as follows. IVT will be deployed
within the Electronic Greenhouse Gas Reporting Tool (e-GGRT) and will
be integrated without interrupting the current electronic reporting
process. Reporters will enter data into e-GGRT that are required to be
reported in the annual report, and will also enter into e-GGRT (via
IVT) the inputs to emission equations for which reporting is no longer
required under the amendments. IVT will use these entered data to
calculate the equation results, conduct electronic verification checks
on the entered inputs to emission equations, and generate a
verification summary that informs the EPA about the verification
results without specifying the entered inputs to emission equations.
IVT will not retain the entered inputs to emission equations, which
will not be electronically accessible to the EPA during their entry or
anytime thereafter. Instead, the EPA will rely on the verification
summary, which will become accessible to the EPA after annual report
submittal, and other follow-up verification procedures described in the
proposed rule for conducting verification. Sources subject to multiple
subparts under Part 98 are required to use IVT for only those subparts
listed in Table 2 of this
[[Page 63756]]
preamble. Reporters must use IVT starting with reporting year 2014. A
detailed description of IVT and these requirements is provided in the
proposal preamble (78 FR 55994, September 11, 2013), the memorandum
``Technical Approach and Design for Inputs Verification Tool,'' August
2013 (refer to Docket ID No. EPA-HQ-OAR-2010-0929), and Section II.A.3
of this preamble.
The inputs to emission equations required to be entered into IVT
are specified in the ``verification software records'' provisions in
the recordkeeping section of each subpart specified in Table 2 of this
preamble.
Subpart C sources (e.g., individual units, aggregations of units,
common pipes, or common stacks) that do not meet the following criteria
have the option to use IVT or to report these deferred inputs to
emission equations for which reporting was deferred to 2015: Contain at
least one combustion unit connected to a fuel-fired electric generator
owned or operated by an entity that is subject to regulation of
customer billing rates by the public utility commission (PUC)
(excluding generators connected to combustion units subject to 40 CFR
part 98, subpart D) and are located at a facility for which the sum of
the nameplate capacities for all such electric generators is greater
than or equal to 1 megawatt electric output. For those sources who
choose to report their inputs to emission equations, e-GGRT will
require the reporters to waive the right to make confidentiality claims
before they can be reported via e-GGRT.
2. Summary of Changes Since Proposal
This section provides a brief summary of changes to the requirement
to use IVT since proposal. The EPA's rationale for these changes is
provided in Section II.A.3 of this preamble as part of the EPA's
response to the related comment(s).
The changes to the proposed requirement to use IVT are as follows:
The EPA has revised one of the criteria in 40 CFR
98.36(f) that specifies which stationary fuel combustion sources
(e.g., individual units, aggregations of units, common pipes, or
common stacks) subject to subpart C of part 98 are required to
report inputs to emission equations for which reporting was deferred
to 2015. At proposal, 40 CFR 98.36(f)(1) stated that the stationary
combustion source contains at least one combustion unit connected to
a fuel-fired electric generator granted access by the Public
Utilities Commission to deliver power to the local or regional power
grid (excluding generators that are connected to combustion units
that are subject to subpart D of the part). In the final rule, this
criterion is revised to state that the stationary fuel combustion
source contains at least one combustion unit connected to a fuel-
fired electric generator that is owned or operated by an entity that
is subject to regulation of customer billing rates by the public
utility commission (excluding generators that are connected to
combustion units that are subject to subpart D of the part).
For sources that do not meet the criteria specified in
40 CFR 98.36(f), the EPA has added an option in 40 CFR 98.3(d)(3)(v)
and 40 CFR 98.36(a) to either elect to use IVT or, if potential
disclosure is not a concern to the reporters, to report these inputs
to emission equations. For reporting year 2014, if a subpart C
source elects not to use IVT, the source is required to report their
subpart C inputs to emission equations for which reporting was
deferred to 2015 for reporting years 2010 through 2014 in the
reporting year 2014 annual report. If this source is not required to
use IVT for other subparts listed in Table 2 of this preamble, the
source would not be subject to the extended recordkeeping
requirements of 5 years.\9\
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\9\ If the source is required to use IVT for other subparts, the
source must retain records for all subparts (including subpart C)
for a period of 5 years.
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The EPA has revised the proposed amendments to 40 CFR
98.5(b) to add an option for reporters subject to using IVT to enter
an explanation into IVT in cases where IVT has produced a warning
message for an entered data value (e.g., the value is outside the
EPA's expected range), but the reporter believes that the data value
is accurate as entered.
The EPA has revised its method for specifying which
inputs to emission equations must be entered into IVT. At proposal,
40 CFR 98.5(b) indicated which inputs to emission equations must be
entered into IVT by referring to equations specified in proposed
Table A-8 of Part 98. In the final rule, the EPA identifies the
inputs to emission equations that must be entered into IVT in a
``verification software records'' provision in the recordkeeping
section of each affected subpart. Therefore, proposed Table A-8 is
not included in the final rule. Refer to Section II.C of this
preamble for further discussion of these ``verification software
records'' provisions.
Additionally, in response to public comments, the EPA is making
changes related to implementation of the alternative verification
approach. These changes do not involve regulatory amendments to Part
98, but do improve the design and use of the IVT and address questions
and concerns raised by commenters. A summary of these changes follows.
IVT Testing. The EPA will provide an opportunity well in advance of
the March 2015 reporting deadline for stakeholders to test and provide
feedback to the EPA on IVT for the 23 subparts addressed in this final
action via a compliance assistance open testing period, or ``sandbox.''
Refer to Section II.A.3 of this preamble for a description of
``sandbox'' testing and further discussion of this opportunity. The EPA
encourages all stakeholders to participate in the sandbox testing
because this testing will provide a valuable opportunity for reporters
to preview and familiarize themselves with the new application for all
applicable subparts before the open reporting period begins, typically
in mid-February. The EPA intends to offer sandbox testing from October
through December 2014, providing testing by subpart on a rolling basis.
Participants who identify an error in IVT will have the opportunity to
provide feedback to the EPA regarding their IVT testing experience.
Such feedback will ensure a higher quality IVT for reporting in early
2015 and subsequent years. For details on the sandbox testing,
including a schedule of when testing will occur for each of the 23
subparts, please see https://www.epa.gov/ghgreporting/reporters/training/inputs-verifier.html.
IVT Design. In response to commenter input, the EPA has revised the
IVT design to improve the ease of use and the efficiency of the data
entry process, instructions, help screens, warnings, and error
messages. Refer to Section II.A.3 of this preamble for further
discussion of these revisions. See the EPA's comment response document
in Docket ID No. EPA-HQ-OAR-2010-0929 for a list of all public comments
regarding additional improvements to IVT and the EPA's responses,
including revisions to address errors identified by commenters.
3. Summary of Comments and Responses
This section provides a brief summary of the significant comments
received in response to the proposed requirement to use IVT, and the
EPA's responses. The EPA's comment response document in Docket ID No.
EPA-HQ-OAR-2010-0929 provides a complete listing of all related
comments and the EPA's responses.
Comment: One commenter asserted that the verification approach that
the EPA has used during the deferral period has been successful, is
efficient, and should be adopted as EPA's permanent approach for
verification, rather than requiring facilities to use IVT. The
commenter asserted that, during this deferral period, verification
checks have been conducted through e-GGRT on data that have been
reported to the EPA. The commenter believes that while the EPA has
identified reporting errors during these years, such concerns will
become increasingly rare as reporters become more familiar with and are
able
[[Page 63757]]
to streamline the reporting process. The commenter asserted that in
situations where the EPA is not able to verify the data, the EPA can
continue to follow-up with facilities. The commenter also asserted that
the interim verification approach used by the EPA has strong parallels
to other ``certification'' requirements that the EPA has long deemed
sufficient to ensure compliance in similar circumstances. Finally, the
commenter asserted that because the interim verification approach has
been successful, the risk of entering CBI into an unproven system that
has the potential to be insecure is not justified.
Response: As the commenter notes, the EPA has been conducting
verification checks using data other than inputs to emission equations.
Although the checks to date gave us some confidence in the submitted
data, the verification approach being finalized in this action allows
for more precise checks to be conducted and therefore a more robust
verification approach. Specifically, requiring that the inputs to
emission equations (for which disclosure concerns were identified) be
entered into IVT allows the tool to verify reported emissions by
calculating the emission equation results as well as conducting
verification checks on the entered inputs to emission equations. These
checks are designed to ensure that calculations are performed correctly
by the reporter and that appropriate data were used to calculate
emissions. While the EPA agrees that over time, commenters will become
more familiar with e-GGRT and IVT and the increased familiarity may
help to reduce reporting errors, it is important that the Agency's
verification process is as robust as it can be to ensure the accuracy
of the submitted data. The verification approach finalized in this
action will accomplish that goal while at the same time addressing the
concerns regarding potential disclosure of sensitive information.
Regarding the comment that the verification approach used during
the deferral period is similar to ``other certification requirements
that the EPA has long deemed sufficient to ensure compliance in similar
circumstances,'' it is not clear which programs to which the commenter
is referring. As the EPA stated in the memorandum ``Evaluation of
Alternative Verification Approaches For Greenhouse Gas Reporting Rule
Subparts for which Reporting of Inputs to Emission Equations was
Deferred to March 31, 2015'' (EPA-HQ-OAR-2010-0929-0048), the EPA
considered the verification approach used by the EPA's Toxics Release
Inventory (TRI) program, which requires self-certification that the
information reported is accurate, and includes electronic data checks
and follow-up conducted by the EPA. However, the TRI is a different
type of program than the GHGRP in that it does not require specific
monitoring and calculation approaches, but rather requires that
estimates be based on the best available information. In contrast, the
GHGRP prescribes a set of specific calculation methods, or equations,
for individual source categories, processes, and emission units, so
that data collected from multiple facilities are consistent and
comparable. Given the additional specification required by the GHGRP,
the EPA concluded that the more precise checks that will be conducted
by IVT are warranted.
The EPA addresses the comment about IVT's security and the
assertion that the system is unproven later in this section of the
preamble.
Comment: One commenter expressed concern regarding the language
used in 40 CFR 98.36(f)(1), indicating that the language is vague and
confusing. The commenter stated that the phrase ``granted access by the
Public Utilities Commission (PUC) to deliver power to the local or
regional electric power grid'' could result in confusion or overly-
broad reporting of CBI. The commenter explained that some jurisdictions
impose only registration and other ministerial requirements on units
granted access; whereas some jurisdictions ``engage in direct price and
other regulation of vertically integrated and other utility operations
that grant or restrict franchise rights.'' The commenter cautioned that
it is not clear what level of regulation constitutes a ``grant of
access'' under the rule, explaining that all units, regardless of type
or regulatory regime, require ``access'' to a local or regional grid in
some form to make off-site sales of power.
The commenter recommended that the EPA avoid misinterpretation of
40 CFR 98.36(f) by clarifying in the final rule that only units subject
to regulation as ``public utilities under the laws and regulations of a
given state'' (as opposed to those under other Federal regulations or
not otherwise subject to State utility commission oversight of
operations and rates as ``public utilities'') should be considered as
having been ``granted access by the Public Utilities Commission to
deliver power to the local or regional electric power grid.'' The
commenter also stated that it is incorrect to assume that information
provided to PUCs or similar institutions is also disclosed publicly,
and that the EPA should clarify how it will address such information if
the PUC treats that information as CBI or it is otherwise not available
to the public.
Response: For the reasons stated below, the EPA agrees that the
proposed 40 CFR 98.36(f)(1) does not clearly define the combustion
units that must report subpart C inputs to emission equations for which
reporting was deferred to 2015. Proposed 40 CFR 98.36(f) specified
that: (1) The stationary combustion source contains at least one
combustion unit connected to a fuel-fired electric generator that has
been granted access by the Public Utilities Commission to deliver power
to the local or regional electric power grid (excluding generators that
are connected to combustion units that are subject to subpart D of the
part); and (2) The stationary fuel combustion source is located at a
facility for which the sum of the nameplate capacities for all electric
generators specified in paragraph (f)(1) of the section is greater than
or equal to 1 megawatt electric output.\10\ As indicated in the
memorandum, ``Evaluation of Competitive Harm from Disclosure of `Inputs
to Equations' Data Elements Deferred to March 31, 2015,'' August 2013
(refer to Docket ID No. EPA-HQ-OAR-2010-0929), the EPA had found no
disclosure concerns for any combustion source meeting the proposed
criteria in 40 CFR 98.36(f)(1), including combustion sources owned or
operated both by power producers whose primary purpose is selling
electricity and by power producers whose primary purpose is not selling
electricity. It was the EPA's understanding at the time that both types
of power producers are granted access to the grid by the PUC, that such
grant requires that the associated consumer billing rates be regulated
by PUCs and that, therefore, the power producers experience a high
level of transparency due to the practice of the owner or operator
disclosing fuel costs to the PUC through ratemaking procedures. Based
on the above understanding, the EPA had concluded that releasing these
data would not reveal any proprietary information about facility or
process performance, design, and operation; cost to do business; raw
material usage; or production.
---------------------------------------------------------------------------
\10\ We received no comment on the proposed criterion (2), and
we are therefore finalizing that criterion as proposed.
---------------------------------------------------------------------------
In light of the comment above, the EPA further investigated the
reporting obligations of the owner or operators of power producers to
PUCs. Based on these investigations, the EPA established that the PUC
does not
[[Page 63758]]
typically grant access to the grid, but sometimes requires utilities to
grant other power producers access to the grid. The EPA recognized that
not all power producers that are granted access to the grid are subject
to regulation of rates by PUCs, and therefore some of these power
producers do not experience the high level of transparency that would
be associated with the disclosure of fuel costs to the PUC through
ratemaking procedures. As a result, the EPA cannot conclude that there
would be no disclosure concerns associated with the release of these
data for power producers based on their connectivity to the grid, given
that some power producers connected to the grid are not subject to
regulation of rates by the PUC. The new understanding and resulting
harm analysis described above are also reflected in the memorandum
``Final Evaluation of Competitive Harm from Disclosure of `Inputs to
Equations' Data Elements Deferred to March 31, 2015,'' September 2014
(refer to Docket ID No. EPA-HQ-OAR-2010-0929). Given that the EPA found
no disclosure concerns with respect to those power producers subject to
regulatory oversight of consumer billing rates by a PUC, the EPA has
changed proposed 40 CFR 98.36(f)(1) in the final rule to more clearly
and accurately describe the combustion units that must report as those
units owned or operated by an entity that is subject to regulation of
customer billing rates by the public utility commission. Power
producers subject to regulatory oversight of consumer billing rates by
a PUC include investor-owned utilities (IOUs) (i.e., the most common
type of utility regulated by PUCs), non-utility generators, and
consumer-owned utilities (COUs) that are subject to regulation of
customer billing rates by a PUC. Because industrial plants that
generate electricity are not subject to regulation of customer billing
rates by a PUC, power producers owned or operated by industrial plants
would not meet this revised reporting criterion in 40 CFR 98.36(f)(1).
The commenter recommended replacing the proposed language ``granted
access by the PUC to deliver power to the grid'' with ``subject to
regulation as a public utility under the laws and regulations of a
given state.'' The terminology ``public utility'' could be interpreted
to refer only to COUs, which are sometimes called ``public power,'' but
excluding IOUs, which would not be appropriate because IOUs are subject
to regulatory oversight of consumer billing rates by a PUC and
therefore experience a high level of transparency. Also, the
commenter's suggested phrase ``under the laws and regulations of a
given state'' could be interpreted as meaning any state law or
regulation, regardless of whether they are associated with PUCs. Given
that virtually all facilities generating electricity are governed to
some degree by other state laws and regulations, and those regulated by
the PUC might not be regulated for ratemaking purposes, this suggested
text would expand the reporting requirement beyond those facilities
subject to regulation of rates by the PUC, which is the basis for our
finding of transparency. Accordingly, the EPA has determined that the
rule text suggested by the commenter was overly broad. The EPA has
determined that the text ``owned by an entity subject to regulation of
customer billing rates by a public utility commission'' more accurately
describes the power producers for which we found no disclosure concerns
and therefore must report the subpart C inputs to emission equations
for which reporting was deferred until 2015.
The EPA agrees with the comment that not all information that is
provided to PUCs may necessarily be made available to the public;
however, the EPA believes that power producers subject to regulation of
rates by PUCs generally experience a high level of transparency. The
EPA has received no comment refuting the high level of transparency or
stating that there are disclosure concerns associated with these
subpart C inputs to emission equations. The final criterion (``subject
to regulation of customer billing rates by PUCs'') was formulated to
capture power producers that are utilities in states with so-called
``regulated'' electricity markets. In these states, power producers are
generally owned by vertically integrated utilities, which operate as
monopolies and sell power to customers at rates that are established
through PUC proceedings. Given this monopolistic market for power
producers subject to regulation of rates by PUCs, the EPA does not
identify any disclosure concerns with reporting the inputs to emission
equations in subpart C for reporters that meet the final criterion. In
contrast, in ``deregulated'' or ``restructured'' states that have
unbundled generation and delivery, independent power producers may
compete to sell electricity, which is then delivered through a
regulated distribution utility. These independent producers are not
subject to PUC ratemaking procedures, and they will therefore not be
required to report subpart C inputs to emission equation data for their
combustion units. For the reasons stated above, the EPA concludes that
clarifying the scope of the criteria to be those power producers that
are subject to regulation of customer billing rates by PUCs accurately
specifies facilities identified as having no disclosure concerns with
the release of these data.
Specifically, the final 40 CFR 98.36(f) provides the following
criteria to indicate which stationary fuel combustion sources (e.g.,
individual unit, aggregation of units, common pipe, or common stack)
must report their inputs to emission equations for which reporting was
deferred to 2015: (1) The stationary fuel combustion source contains at
least one combustion unit connected to a fuel-fired electric generator
owned or operated by an entity that is subject to regulation of
customer billing rates by the public utility commission (excluding
generators that are connected to combustion units that are subject to
subpart D of the part); and (2) The stationary fuel combustion source
is located at a facility for which the sum of the nameplate capacities
for all electric generators specified in paragraph (f)(1) of the
section is greater than or equal to 1 megawatt electric output. For any
stationary fuel combustion source subject to subpart C that does not
meet these criteria, the final rule provides an option for the source
either to use IVT starting in reporting year 2014 or to report these
data to the EPA, including reporting the data specified in revised
Table A-7 for reporting years 2010 through 2013.\11\ Refer to the
comment summary and the EPA's response immediately following this
response for further discussion about this new option.
---------------------------------------------------------------------------
\11\ As discussed above, the e-GGRT will require that such
reporter waive any confidentiality claim for its facility's inputs
to emission equations before such data can be entered into e-GGRT.
---------------------------------------------------------------------------
Comment: Three commenters asserted that the EPA not require them to
use IVT. They asserted that reporters under subpart HH (municipal solid
waste landfills) have not expressed disclosure concerns regarding
inputs to equations during comment periods for previous rulemakings,
and that the proposal did not take this into consideration as it did
not include an option to allow reporters to submit data to the EPA
rather than use IVT. They further asserted that under the proposal,
they would be required to use IVT for only a single equation input
(quantity of fuel combusted under subpart C, Tier 1), and that the
burden to their industry associated with use of IVT is not warranted,
given that the single
[[Page 63759]]
equation input is associated with less than 1 percent of reported GHG
emissions from the industry. The commenters expressed concern that
imposing the proposed requirements associated with IVT on landfills
would be burdensome, and indicated that they would be willing to report
the single data element to the EPA. They recommended that the EPA
exclude Tier 1 reporters from being required to use IVT.
Response: The IVT requirements in the final amendments for subpart
C, which covers a wide range of industries, address disclosure concerns
identified for certain ``inputs to emission equations'' data elements.
However, these commenters expressed that they do not have disclosure
concerns with their fuel use data, the single input required for Tier 1
reporting under subpart C. For these commenters who are not concerned
with reporting their fuel use quantity under subpart C, the EPA sees no
reason to insist that they use IVT instead of reporting such data. In
addition, the fact that these commenters have not identified disclosure
concerns with any inputs to equations suggests that it is likely that
landfills using other subpart C calculation methods besides Tier 1 may
similarly prefer to report inputs to emission equations data elements
under subpart C instead of using the IVT. Further, given the wide range
of industries reporting under subpart C, it is possible that there are
other industries that do not have disclosure concerns with fuel
quantity and other equation inputs for subpart C calculation methods.
For any such subpart C reporter, the EPA similarly sees no reason to
insist that it use IVT instead of reporting such data. Accordingly, the
EPA is revising 40 CFR 98.36 to make it optional for subpart C sources
that do not meet the criteria for electric generators in 40 CFR
98.36(f) \12\ to use IVT. As such, under the final rule, a subpart C
reporter, except for those meeting the criteria of 40 CFR 98.36(f), who
does not have disclosure concerns for the subpart C inputs to emission
equation data elements may waive confidentiality claims and report such
data instead of using IVT. Before e-GGRT will accept entry of these
inputs to emission equations data, it will require that the reporter
waive confidentiality claims of such data.
---------------------------------------------------------------------------
\12\ Sources meeting the criteria in 40 CFR 98.36(f) must report
their subpart C inputs to emission equations that were deferred from
reporting until 2015.
---------------------------------------------------------------------------
If a subpart C source elects to report these data for reporting
year 2014, the source is required to report these data for reporting
years 2010 through 2013 as part of the reporting year 2014 annual
report. If a source elects to use IVT in reporting year 2014, and then
the source elects in a future year to report these data, the reporter
will not be obligated to report these data for any prior year.
Comment: Six commenters recommended that the EPA allow reporters
time to test IVT prior to the start of reporting for reporting year
2014, using a fully functional ``sandbox'' testing environment similar
to that used previously for e-GGRT testing. These commenters urged the
EPA to allow sandbox testing for each affected subpart, arguing that
the subpart X prototype developed for commenter review at proposal
allowed them to review only the design and functionality of the
prototype for subpart X. They stressed that additional testing is
necessary to ensure IVT works for all affected subparts. Two commenters
noted that sandbox testing would allow errors in the software to be
found and corrected prior to implementation. Commenters also noted that
sandbox testing of each subpart would enable them to determine whether
IVT calculates emission equation results correctly and stated that
sandbox testing would provide an opportunity for reporters to compare
results of the calculations in IVT against the values calculated using
the optional calculation spreadsheets. Other commenters requested
sandbox testing because it would allow them to review and comment on
the verification ranges incorporated in IVT. One commenter stated that
testing could provide important information that may result in
improvements to IVT that obviate the need for reporters to over-ride
error messages. Other commenters expressed concern about protection of
CBI and concluded that rigorous testing of each affected subpart is
critical to ensuring confidential data are protected.
Four commenters recommended that the EPA allow sandbox testing of
the XML version of IVT. These commenters noted that the pilot IVT
provided very limited testing for reporters using the XML option. They
noted that the testing was limited to only one subpart, that only one
sample XML file was provided for testing, and that the EPA did not
provide the XML schema. Two commenters requested that the EPA provide
additional time for reporters to review and test the XML IVT for each
subpart. The complexity of the XML option, they argue, makes thorough
testing of any XML schema essential.
Eight commenters asserted that the pilot tool available during the
comment period for the subpart X mass balance methodology was too
limited, and as a result provided limited value in assessing the burden
of the tool for the other methodologies and subparts that would be
required to use the tool. Two of these commenters noted that because
subpart X has different inputs to equation data elements and equations
than other subparts, they were unable to provide adequate feedback on
the tool during the comment period. Two of these commenters suggested
that the EPA develop a pilot reporting tool for their subpart of
interest, and re-propose the verification tool for that subpart to
provide ample opportunity to provide public comment on the burden
associated with the use of the tool. Three of these commenters asserted
that because the pilot testing for subpart X was limited to the mass
balance methodology, it provided limited value to assess the ease of
use and burden of the tool for the other methodologies within subpart
X.
Two commenters indicated that reporters need more time in 2015 to
complete their annual reports than in previous years. One commenter
stated that in the past, the EPA has provided industry just a handful
of weeks before the reporting deadline to update all of its data
systems, input all of its data into e-GGRT, correct any errors,
complete internal reviews of the reports, and to submit the reports.
The commenter noted that the short timeframe was extremely challenging
in past years. Both commenters indicated that it would be unacceptable
for the EPA to provide another short timeframe in 2015, considering the
new requirements to back-report 2010 through 2013 data and use the new
IVT. One commenter requested that the inputs verification tool be fully
functional by January 1, 2015 to allow reporters to undergo the
required software development so that their systems accurately ``sync''
with the new version of e-GGRT. The commenter suggested that the EPA
include language in Subpart A to indicate that for each day past
January 1, 2015 that the upgraded e-GGRT is not available, the
reporting deadline will be extended by one day.
Response: During the public comment period, the EPA provided a
subpart X prototype for testing and comment. This prototype allowed
reporters to review the overall design, structure, and functionality of
IVT, which applies to all subparts that are to use the tool. It was not
necessary to have a prototype for every subpart during the open comment
period because the overall design of IVT is the same irrespective of
the specific methodologies, or
[[Page 63760]]
equations, in each subpart. Specifically, the tool demonstrated the
following functions that apply to all subparts that are to use the
tool: How IVT functions within e-GGRT, how to navigate from e-GGRT to
IVT and vice versa, how inputs are entered into IVT, how IVT calculates
equation results based on the inputs to emission equations entered, how
an emission equation result calculated in IVT is transferred to the
annual reporting form in e-GGRT, how the reporter may override an
emission value calculated by IVT, how the results of the verification
checks conducted in IVT appear in the verification summary, how a
reporter may enter inputs to emission equations into IVT over multiple
e-GGRT sessions without having to start over each time the reporter
logs out of e-GGRT (by saving them on their local computer), and how to
use the XML bulk upload feature rather than using webforms. Reporters
were also able to generate the list of inputs entered into IVT that
must be kept as a record, view the format of the records file created,
and test the downloading of the records file for recordkeeping
purposes. These features that were available for testing represent all
of the key functions of IVT. Comments on any of the above features
received during the public comment period would apply to all subparts
that are required to use IVT and not just the subpart X prototype. The
feedback assisted the EPA in determining improvements to the design and
functionality of IVT for all subparts with the IVT requirement.
Although providing IVT for all subparts during the comment period
was not necessary, the EPA agrees with the commenters that both the EPA
and reporters would benefit from the opportunity to test IVT for all
applicable subparts prior to the beginning of reporting for reporting
year 2014. Accordingly, the EPA will offer reporters an opportunity
prior to the beginning of the reporting year 2014 open reporting period
(which is typically in mid-February) to view and provide feedback on
the IVT modules for all 23 subparts listed in Table 2 of this preamble.
The EPA will use a sandbox testing environment similar to that used
previously for e-GGRT testing. The EPA intends to offer sandbox testing
from October through December 2014, providing testing by subpart on a
rolling basis. For details on the sandbox testing, including a schedule
of when testing will occur for each of the 23 subparts, please see
https://www.epa.gov/ghgreporting/reporters/training/inputs-verifier.html. We are confident that this sandbox testing period will
provide reporters the time needed to sync their systems with IVT prior
to the open reporting period for reporting year 2014, and submit their
reports by March 31, 2015.
As previously provided for in the 2010 sandbox for testing of e-
GGRT, the sandbox environment for IVT will provide participants an
opportunity to try IVT functions for all 23 subparts, including
navigating between IVT screens, entering data, testing the XML
uploading option (saving XML files to local drives, and uploading XML
files to IVT), checking the built-in calculation algorithms, and
accessing Help content. Participants will be assigned a test facility
for which they will be able to enter mock data for any IVT subpart
module they wish to test.
Sandbox participants may notify the EPA should they identify an
error, bug, or technical glitch in IVT. The EPA plans to conduct
extensive testing to ensure that IVT calculates the emissions correctly
for all subparts; however, should any calculation or other subpart-
specific errors remain, these can be detected during the sandbox period
and addressed prior to the open reporting period. Because extensive
internal testing will have been conducted prior to the compliance
assistance ``sandbox'' being made available, the EPA does not
anticipate major issues during the sandbox period that cannot be
addressed prior to the open reporting period.
Regarding the comment that additional time is needed due to the
back-reporting of a significant amount of information, the EPA notes
that, with the exception of subpart W, only a handful of inputs to
equations in each subpart must be back-reported for years 2010 through
2013 (i.e., reporters typically will have no more than 10 inputs to
equations in each of these subparts to report for these years.)
Further, as discussed above, because the system will have gone through
extensive testing followed by an IVT sandbox period for reporters to
sync their systems with IVT before it is opened for reporting, we are
confident that the reporters will have sufficient time to submit their
reports, including back reporting a small number of inputs for
reporting years 2010 through 2013. For subpart W, which has a
substantial number of inputs to be back-reported to the EPA for these
years, the EPA plans to use a spreadsheet to collect this data, and
anticipates publishing the spreadsheet in October 2014. This will allow
facilities to begin data entry into the spreadsheet prior to the open
reporting period. The spreadsheet can then be uploaded to e-GGRT during
the open reporting season. Refer to Section II.B.1 of this preamble for
a discussion of the timing of entering inputs to emission equations for
reporting years 2011 through 2013 for subpart W. In light of the
extensive testing and the sandbox period, which will allow reporters to
sync their systems with IVT prior to the open reporting period, and the
EPA's plans to make the subpart W spreadsheet for 2010 through 2013
available in October, we have determined that the typical reporting
period of approximately six weeks is sufficient.
As requested by commenters, sandbox participants may provide input
on the ranges that the EPA has identified for the reasonable range
verification checks on the inputs entered into IVT. As is the case for
all expected range checks used as part of the electronic verification
process, the EPA will set initial ranges and will continually refine
ranges as additional information is obtained. Should the EPA receive
feedback on expected range checks during the sandbox period, the EPA
will review the feedback and adjust the ranges prior to the open
reporting period as appropriate. Also, as is the case for all expected
range checks conducted in e-GGRT, the reporter may enter any value into
IVT regardless of the reasonable range. The expected ranges are not
used by the EPA as a final determination regarding data quality or
compliance; rather, they are used as a first step of the verification
process and are further investigated. Finally, as is discussed in more
detail later in this section of this preamble, during the reporting
process, the reporter will have the opportunity to add a comment to the
EPA associated with individual verification warnings in IVT. As a
result, if reporters feel that an explanation is needed as to why a
particular range was exceeded or that the range within IVT needs to be
adjusted, they may do so as part of the annual reporting process.
Regarding the comments on the XML upload reporting option, the EPA
notes that during the public comment period, we published an XML schema
for the IVT prototype, as well as two sample files to be used with the
prototype, an XML Inputs Verifier file and an XML Annual Report File.
The sandbox that will be available for IVT will also include this XML
upload reporting option. For subparts with XML reporters, the EPA will
provide the XML schema for the inputs to equations data entered into
IVT and example XML files to use for testing the XML upload approach.
The EPA agrees that changes to the XML schema need to be
[[Page 63761]]
thoroughly tested, and the EPA plans to do so prior to releasing the
XML schema for e-GGRT and IVT.
The EPA disagrees with the comments that the pilot verification
tool provided at proposal for the mass balance methodology in subpart X
was of limited value for assessing the burden of use for other
methodologies and subparts required to use IVT. As discussed in detail
above, the overall design of the IVT is the same irrespective of the
differences in methodologies and subparts. Accordingly, the subpart X
prototype allowed reporters to review the overall design, structure,
and functionality of IVT for all subparts that are to use the tool.
Based on their experience with the subpart X prototype, reporters may
assess the burden associated with other subparts by comparing the
number and complexity of equations in other subparts to the equations
in subpart X. Further, in the proposed Impacts Analysis, ``Assessment
of Cost Impacts of 2015 Inputs Proposal--Revisions to Reporting,
Recordkeeping, and Verification Requirements Under the Greenhouse Gas
Reporting Program,'' August 2013 (available in the EPA's Docket ID No.
EPA-HQ-OAR-2010-0929), the EPA stated that the burden for entering
inputs to equations into IVT is no different than it would be to enter
them into e-GGRT for reporting to the EPA. The EPA did not receive
comments on the proposed Impacts analysis. For the reasons stated
above, we do not believe that it is necessary to re-propose the tool
with all subparts to provide an opportunity to comment on the burden of
using the tool for all subparts, as suggested by several commenters.
Refer to the next comment and response for additional detail on the
specific comments provided to the EPA on IVT design and functionality
and how the EPA is addressing those comments.
Regarding the comment that rigorous testing of each affected
subpart is critical to ensuring that data are adequately protected,
refer to comments and responses later in this section on how the EPA is
ensuring that inputs entered into IVT are not retained by the EPA.
Comment: Many commenters provided useful suggestions for
improvements to IVT. For example, some commenters recommended IVT
include functions that allow reporters to automatically populate web
form fields in situations where the data are reported on a recurring
basis (e.g., weekly, monthly, etc.) and are likely to remain constant
over time. Other commenters recommended IVT allow data to be copied
from external spreadsheets or other data files instead of being entered
individually into IVT. These commenters noted that this approach would
save time and avoid unnecessary transcription errors. Three commenters
recommended that IVT flag any data entry errors related to the data
being outside an acceptable range directly following data entry, rather
than on a separate screen. One of these commenters requested that IVT
should provide more information regarding the error triggered (e.g.,
whether the entered data are above or below the expected range). These
commenters stressed that alerting reporters to errors at the moment of
data entry would help reporters identify errors more quickly. Three
commenters recommended an additional comment field be added to IVT that
allows reporters to respond to IVT error messages. They maintained that
this approach would streamline the verification process and save time
for both the EPA and reporters by potentially avoiding follow-up after
the report has been submitted to the EPA.
Response: The EPA has reviewed the commenters' suggested
improvements to IVT and, with the exception of one suggestion described
below, has incorporated these improvements in IVT. The EPA agrees with
the suggestion that reporters should have the ability to automatically
populate web form fields in situations where the data required to be
entered were collected on a recurring basis (e.g., weekly, monthly,
etc.). For example, in subpart X, for the gas stream entry fields,
reporters will be able to automatically populate the monthly carbon
content and molecular weight of the feedstock with the first month's
values since those values may remain constant in many cases. The EPA
anticipates that this change in IVT will improve the efficiency of the
data entry process and reduce chances for errors associated with manual
entry. Regarding the recommendation to allow data to be copied from
external spreadsheets or other data files instead of being entered
individually into IVT, the EPA agrees with commenters that this
capability would reduce burden and errors associated with manual data
entry. For each data element for which the reporter is required to
enter values collected at a frequency greater than monthly, the EPA is
providing an off-line tool to convert spreadsheets to the XML input
format, for use with IVT.
The EPA has evaluated commenters' concerns regarding the flagging
of data errors when they are entered into IVT. As discussed in the
proposed rule, IVT provides ``real-time'' checks as data are entered
into IVT, similar to checks in e-GGRT. The results of these checks,
called validation messages in IVT, will be easily accessible within e-
GGRT at the time of entry. Although such warnings will be on a separate
screen, there are direct links to such screens to ensure that it is
easy to navigate to IVT to revise data as needed. This is the same for
all validation checks that are currently conducted and displayed within
e-GGRT for all reporters. Although we recognize the potential
usefulness of this suggestion, this type of design change would require
a significant amount of resources, and cannot be done prior to the
reporting period for reporting year 2014. The EPA is always open to
making changes to e-GGRT and IVT over time, and may consider whether it
is feasible to show validation messages on the same screen on which the
data are being entered and, if so, whether to make such adjustment in
IVT.
The EPA agrees with commenters that IVT should provide more
information regarding the error triggered (e.g., whether entered data
are above or below the expected range). Accordingly, in response to
these comments, IVT will include an ``out of range'' message in the
verification summary that indicates the range being used for each data
element entered as well as whether the value entered was above or below
the range. We anticipate that this additional information will make the
verification process more efficient by reducing the amount of follow-up
required for verification.
Finally, the EPA has considered commenter recommendations for
addition of a comment field allowing reporters to respond to IVT error
messages, explaining why a potential error may not be an error, such as
when an entered equation input is found to be out of range or has
otherwise triggered a message on the verification summary. The EPA
recognizes that, in some cases, reporters may have inputs to emission
equations that are legitimately outside of identified ranges due to
unique circumstances. In cases such as these, we agree with commenters
that this option will reduce the amount of follow-up required of the
EPA and reporters. As such, we have implemented this change in IVT.
Comment: Eight commenters raised security concerns regarding data
entered into IVT. These commenters wanted additional information on how
IVT would protect sensitive data and assurances that the data would not
be inadvertently disclosed. One commenter stated that the security of
IVT was particularly important to facilities that are required to
comply with certain U.S.
[[Page 63762]]
export control requirements. Four commenters were concerned about
security during the period of transient storage while the user is
logged into IVT of data. Some commenters asked for clarification on
where the data will reside during this period, while other commenters
wanted the EPA to demonstrate that data would only be stored
temporarily and that no data would be retained during a system crash.
Some commenters wanted additional information about who would have
access to the data during this transient storage of the data. One
commenter wanted the EPA to confirm that data with disclosure concerns
entered into IVT would not be accessible to EPA personnel. Two
commenters were concerned that outside vendors would have access to
data in the transient storage area. Three commenters were concerned
about the security of data transmitted over the Internet. Two
commenters were concerned that data could be intercepted during
transmission by proxy servers and that data may still be stored in
these proxy servers after the session ends. One commenter expressed
concern that use of XML files to input data into IVT raises security
concerns because the format is easily readable, containing the
definitions needed to decipher the data values. This commenter was also
concerned that malicious or inadvertent HTML codes can be inserted into
XML files thereby causing other security vulnerabilities. Other
commenters wanted the EPA to confirm that IVT will not submit
confidential information over the Internet.
Response: IVT is designed to operate securely within e-GGRT, as a
transient process, such that data entered into IVT would be temporarily
housed in the IVT system while the reporter is actively using IVT. The
IVT system is designed so that entered inputs data are placed only in
session (server memory). The entered inputs will not be saved to the
underlying EPA database, nor will they be saved to the server's file
system. The EPA has taken the following steps to ensure that inputs
data are not mistakenly appended to data that are saved (e.g., when
saving validation and verification summary records to the database) and
to ensure that information saved to the server logs does not contain
user-entered inputs data. IVT has not been configured to use the
server's file system to temporarily save files. Instead, IVT is
configured only to use memory for transient housing of inputs data
while the reporter is actively using IVT. This configuration applies to
inputs data entered into IVT webforms or data uploaded from a local
`inputs' file through the IVT webforms, as well as inputs data uploaded
through the XML upload process. As with data entered through the
webform, IVT will not save uploaded XML files to the underlying EPA
database or to the server's file system, but will only retain the data
in server memory for the duration of the session. Uploaded XML files
will be validated against a published schema definition (i.e.,
published document prescribing the required format of the file), so in
many cases XML files containing ``malicious or inadvertent HTML codes''
would be rejected by the system as not being well-formed. If
``malicious or inadvertent HTML codes'' were inserted into an XML in a
manner that did not render it invalid, the file would be rejected by a
process that inspects uploaded files for script tags. Therefore, the
system is not vulnerable to any potential HTML code appended to these
files. The entered inputs to emission equations are then erased when
the user's session with e-GGRT ends.
Regarding the comments that unauthorized persons may be able to
access data that are temporarily in session while the reporter is
actively using IVT and the concerns with transmission of data over the
Internet and potential data interception, the EPA complies with the
strict security procedures and guidance governing access to federal
data servers established by the National Institutes of Standards and
Technology (NIST) and in accordance with the Federal Information
Security Management Act of 2002 (FISMA). All EPA information systems
must meet the security requirements defined in the NIST Special
Publication 800-53.\13\ Adherence to the NIST Federal Information
Systems requirements are intended to protect EPA information systems,
including e-GGRT, from a diverse set of threats including hostile
cyber-attacks, natural disasters, structural failures, and human
errors. As such, the program keeps a security plan up to date and
conducts annual reviews of the security controls. Furthermore, in order
to address the security concerns noted by the commenter regarding
unauthorized access to data while it is in session on the server, the
EPA has identified an additional security layer beyond the NIST
requirements to encrypt the transient session data used by the server
while the reporter is actively using IVT. The session data will be
encrypted with a key unique to that user's session. As a result, the
EPA has concluded that this suite of protections is sufficient to
address concerns raised regarding the possibility of unauthorized
persons accessing data in the transient housing area while the reporter
is actively using IVT.
---------------------------------------------------------------------------
\13\ https://csrc.nist.gov/publications/PubsSPs.html.
---------------------------------------------------------------------------
Regarding the comments expressing concern over transmission of data
over the Internet and potential data interception, the inputs data
entered by a reporter in the web form are encrypted via Transport Layer
Security (TLS) security protocol. TLS is a standard security protocol
providing an encrypted link between the client (the user's browser) and
the EPA's servers. TLS encryption ensures that entered data are secure
from the browser to the EPA server. Normal Internet HTTP communication
sends data between the client and the server in plain text. Application
of the TLS protocol to HTTP communication (HTTPS) will ensure that the
inputs data are encrypted rather than in plain text while in transit.
TLS encryption ensures that data are completely secure from the user's
browser to the e-GGRT servers. Although data are transferred over the
Internet through proxy servers, due to TLS encryption, the inputs data
would never be in plain text and could not be deciphered by
intermediate or proxy servers. TLS is the standard security protocol
used to protect the transfer of many types of sensitive data, including
credit card numbers, banking data, and similar information requiring
maximum protection. The EPA does not use proxy servers for its e-GGRT
database, but relies completely on dedicated server space at the
National Computer Center. Therefore, TLS termination takes place only
on secured e-GGRT servers. The EPA will always use these secure servers
(identified with the ``https'' prefix), which identify that the TLS
security protocol is applied, and IVT will not incorporate inputs to
emission equations data into URLs. This also applies to data
transferred through XML upload. XML data uploaded by a user will also
be encrypted via TLS security protocol and will not be in plain text
while in transit. If intercepted while in transit, the XML data would
be encrypted and therefore indecipherable. These encrytion procedures
will protect data as they are transferred between the client's browser
and the EPA's servers.
IVT is also designed to protect data in the instance of a system
malfunction. In the event of a system crash, all session data are lost,
including the session key that would be capable of decrypting that
data. There are no processes in place to save any information during a
system crash. Therefore, if a reporter enters data
[[Page 63763]]
into IVT and the IVT system malfunctions, the reporter's data are not
stored in any way and cannot be recovered.
Regarding an earlier comment that IVT is an unproven system, the
EPA disagrees with this comment. The EPA designed a prototype to
demonstrate the functionality of the tool. As stated earlier in this
preamble, this prototype allowed reporters to review the overall
design, structure, and functionality of IVT, which applies to all
subparts required to use the tool. For additional information on this
topic, please see the discussion earlier in this preamble on the
prototype and ``sandbox'' testing.
In summary, the EPA has taken several steps to add safeguards and
to build multiple security ``layers'' into the system to prevent
release of the data as they are transmitted to the EPA's servers and
temporarily housed while the user is actively using IVT, but are not
retained in the server memory after the user's e-GGRT session ends. The
EPA is confident that the described security procedures will adequately
protect the data entered into IVT.
Comment: Six commenters stated that they consider equation input
data required to be entered into IVT to be CBI and expressed concern
that the EPA has not gone far enough to legally protect these data from
public disclosure. Four commenters described how these data meet the
five-part criteria specified in 40 CFR 2.208 for confidential
treatment. The commenters asserted that the EPA recognized in its
proposed rule that these data are entitled to protection from public
disclosure. The commenters questioned why, given this recognition, the
EPA has not afforded these data CBI protection under the CAA. Two
commenters questioned why the EPA was silent in its proposal as to
whether these data are to be afforded CBI protection, instead focusing
on revising reporting and recordkeeping requirements for these data.
Five of the commenters referred to a continued risk associated with
the proposed verification approach that equation inputs entered into
IVT will be available to the public or subject to disclosure under the
CAA. Four commenters noted that section 114(c) requires that the EPA
must provide ``emission data'' to the public, if requested. One of
these commenters described the continued risk as related to the EPA's
inspection of facility records, indicating that the EPA did not include
provisions in the proposal explaining whether or how records of
equation input data entered into IVT are to be afforded CBI protection
or otherwise protected from public disclosure as a result of Agency
review of records. The commenter further stated that the proposed rule
does not set forth a requirement that the EPA can access these data
only through an official enforcement-related action that might afford
the information privileged status and provide some security from public
release, nor, according to the commenter, are there provisions to
ensure that non-enforcement staff or EPA contractors cannot access the
data and inadvertently release these data or otherwise render the
information unprotected.
Three commenters further expressed concern that by retaining any
residual risk of disclosure of equation input data entered into IVT, 40
CFR part 98 could potentially subject reporters to antitrust liability.
The commenters explained that equation input data required to be
entered into IVT include cost- and output-related information that is a
significant determinant of prices, including information regarding fuel
production and distribution, which provides details about plant
operations and inputs, nature, and location of sources.
The six commenters contended that the EPA must take further steps
to address the remaining ``residual risk'' of disclosure under the CAA
of equation input data required to be entered into IVT. Five of the
commenters urged the EPA to provide CBI protection to equation inputs
entered into IVT. Four of the commenters urged the EPA to address their
concerns about disclosure by explicitly stating in the final rule that
data entered into IVT qualify for confidential treatment under the
EPA's regulations and should not be deemed ``emission data.'' One
commenter requested that the EPA address their concerns about
disclosure by including in the final rule language expressly
recognizing the CBI status of these data. One commenter urged the EPA
to further address concerns about the residual risk of disclosure by
clarifying, in the preamble to the final rule, that equation input data
entered into IVT remain at all times in the possession of the company
entering the data and thus are not subject to disclosure under any
other Federal law as a result of entry into IVT.
Response: As explained below, the EPA has not determined either in
this rulemaking or any other final action that the equation input data
entered into IVT are entitled to CBI protection. The EPA previously
amended Part 98 to defer the reporting of inputs to emission equations
data elements to allow the Agency time to evaluate concerns raised by
some reporters regarding potential public disclosure of some of these
data elements and to take appropriate action (76 FR 53057, August 25,
2011). The four-step evaluation, which was designed to inform the
Agency whether and what further action may be appropriate, includes
discussions of potential disclosure scenarios as well as consideration
of alternative emission calculation and verification methods.\14\ The
evaluation does not include establishing confidentiality status for any
data that the EPA assigns to the inputs to emission equations category.
Any such determination must be made in accordance with the CAA and the
EPA's implementing regulations under 40 CFR part 2, subpart B. Based on
the evaluation,\15\ we had proposed, and are now taking final action,
to replace the requirement to report certain inputs to emission
equations by 2015 with a requirement to enter these data into IVT.
Although the final rule addresses potential disclosure concerns with
respect to certain inputs by providing an alternative verification tool
(i.e., IVT) instead of requiring reporting of these inputs, it does not
include final confidentiality determinations for any equation input
data required to be entered into IVT, nor has the EPA stated anywhere
in the rulemaking record that such data are entitled to CBI protection.
The EPA therefore has not concluded that any such data (inputs to
emission equations) are entitled to CBI protection.
---------------------------------------------------------------------------
\14\ For a description of the evaluation process, please see the
memorandum titled ``Process for Evaluating and Potentially Amending
Part 98 Inputs to Emission Equations'' (Docket ID No. EPA-HQ-OAR-
2010-0929).
\15\ The results of the evaluation were documented in the four
following memoranda available in the EPA's Docket ID No. EPA-HQ-OAR-
2010-0929: ``Evaluation of Public Availability of Inputs to Emission
Equations for which Reporting was Deferred to March 31, 2015,''
August 2013; ``Evaluation of Competitive Harm from Disclosure of
`Inputs to Equations' Data Elements Deferred to March 31, 2015,''
August 2013; ``Evaluation of Alternative Calculation Methods,''
August 2013; ``Evaluation of Alternative Verification Approaches For
Greenhouse Gas Reporting Rule Subparts for which Reporting of Inputs
to Emission Equations was Deferred to March 31, 2015,'' August 2013.
---------------------------------------------------------------------------
Regarding the comments that expressed concern about the EPA's
ability to protect equation input data entered into IVT, the concern
may have stemmed from a mistaken belief that the EPA will have
possession of such data. That is not the case as explained in detail
here, as well as in the response to comment immediately above, Section
II.A of the preamble to the proposed rule (78 FR 55994, September 11,
2013), and the memorandum ``Technical Approach and Design for Inputs
Verification Tool,'' August 2013 (refer to Docket ID No. EPA-HQ-OAR-
2010-
[[Page 63764]]
0929). During the time period that a reporter is entering data (i.e.,
inputs to emissions equations) into IVT, the EPA will have no access to
the data being entered. Further, when a reporter logs out of IVT, none
of the data entered into IVT are retained in the EPA's electronic
systems. To address concerns about potential release of these data via
the Internet, the EPA provides further clarifications regarding the
security of IVT elsewhere in this section of the preamble. Given that
the EPA will have no access to, nor possession of, data entered into
IVT, such data will not be considered to be agency records as defined
by the Freedom of Information Act or the Federal Records Act, and the
EPA cannot conceive, and the commenters did not explain, which federal
law would require the EPA to release information that it does not have.
For the same reason, the EPA also rejects any suggestion that the
Agency is legally required to protect or make confidentiality
determinations for equation input data entered into IVT. The commenters
have not identified any law or regulation that requires the EPA to
protect data not in the EPA's possession, nor do we believe that any
such duty exists. For the reasons stated above, we disagree with the
comments that the EPA must provide CBI protection to equation input
data entered into IVT.
With respect to the commenter's inquiry on how records of equation
input data entered into IVT, which are required to be kept on-site, are
protected from public disclosure as a result of Agency review of
records, we describe below the verification process, including follow-
up on-site visits. As described below, we do not envision that an
onsite review of records for purposes of verifying emissions reported
using inputs that are entered into IVT would necessitate or typically
involve collection of those records. Rather, visual inspections would
likely suffice to determine whether or not a facility is in compliance.
As described below, the EPA has developed a robust electronic
verification and communication system in order to ensure high quality
data are reported under the GHGRP, and the verification summaries from
IVT will be integrated into that process. This electronic verification
approach helps to minimize the need for on-site review which helps to
reduce the burden and costs to the EPA and reporters. Likely scenarios
under which a GHGRP inspection could occur due to information received
from the IVT verification summaries are described below. As described
below, none of these activities typically involve the EPA's collection
of the inputs entered into the IVT.
As explained in the proposed rule, the first step of the
verification process will include review of the verification summary
generated by the IVT in conjunction with the results of the
verification checks that are currently used on the annual report data.
In the event that the EPA's review results in remaining questions
regarding data quality, the EPA plans to follow-up with the facility
initially via email or phone to determine whether a reporting error has
occurred. For example, if the EPA learns from the facility that the
facility's production doubled in a given year due to unusually high
demand, the EPA may then understand the increase in emissions, certain
out of range warnings, and determine that there is not a data quality
issue. If the EPA is unable to resolve the issue via phone and email,
an on-site visit may be needed. The EPA anticipates that these visits
would likely include a review of the records required to be kept which,
as mentioned above, include the record of the inputs to emission
equations that were entered into IVT as well as an examination of the
monitoring equipment. Depending on the results of the verification
summary for a particular facility, the EPA envisions two general
scenarios for these on-site visits. One scenario would be that the
verification summary produced by IVT for a particular facility
indicates that the reported emissions values matched the values
calculated by IVT but other verification checks show that certain
inputs are outside the EPA's expected range(s). In that scenario, the
EPA anticipates that if a site visit is needed, the site visit would
focus on the accuracy of the inputs entered into IVT. To verify the
accuracy of the inputs entered into IVT, the EPA would likely check
whether data entered into IVT are consistent with other records
required to be kept by the facility. For example, if an input to an
equation is a monthly average of a value that is measured daily by a
particular on-site monitor and the daily measured values are also
required records, the EPA may confirm that the input entered into IVT
is in fact the average of the daily values. In addition, the EPA may
confirm that the on-site monitor meets the specifications prescribed in
Part 98, such as calibration and accuracy specifications. If
calibration and accuracy specifications do not comply with Part 98
requirements, then a substantive error \16\ would likely be identified,
and the facility would need to resubmit their report. If the inputs at
issue comport with the on-site records, then there would be no further
action necessary by either the EPA or the reporter. As described above,
because we envision that verification would be completed while on-site,
we do not expect that there would be a need to collect inputs records.
---------------------------------------------------------------------------
\16\ 40 CFR 98.3(h)(3) defines substantive error as an error
that impacts the quantity of GHG emissions reported or otherwise
prevents the reported data from being validated or verified. 40 CFR
98.3(h) states that once a substantive error is identified, an owner
or operator shall, within 45 days of receipt of the notification,
either resubmit the report that, for each identified substantive
error, corrects the identified substantive error (in accordance with
the applicable requirements of this part) or provide information
demonstrating that the previously submitted report does not contain
the identified substantive error or that the identified error is not
a substantive error.
---------------------------------------------------------------------------
In the second scenario, an on-site visit that is conducted in a
situation when the verification summary produced by IVT indicates a
discrepancy between the reported emissions and the emission equation
results calculated by IVT, the EPA anticipates that the visit would
focus on determining the root cause of the discrepancy. The EPA would
ask the facility to demonstrate how their emissions calculations
yielded a result different from the one calculated through the use of
IVT. The EPA expects that such discrepancy is likely a result of
mathematical error(s), which would likely constitute a substantive
error, and the facility would need to resubmit their report.
In both of these scenarios, the EPA envisions that the
discrepancies would be resolved on-site and that collecting the on-site
records of inputs would not be necessary. Despite the above, we do not
rule out the possibility that collection of certain records could be
necessary under unique circumstances not contemplated above. However,
the EPA does not know at this point what records would be removed, the
specific circumstances under which they would be collected and the
reasons for such collection, and therefore we cannot address at this
time how such records would be treated. Should that occur, the EPA will
treat the collected information according to applicable laws and
regulations.
Regarding the comments asserting that 40 CFR part 98 could
potentially subject reporters to antitrust liability, the EPA
reiterates that information entered into IVT is not reported to or
collected by the EPA. As a result, it does not become an agency record
and, therefore, it is not subject to Freedom of
[[Page 63765]]
Information Act or other required disclosures related to agency
records.
B. Removal of the Requirement To Report Certain Data Elements
1. Summary of Final Amendments to Part 98
The EPA is removing the requirement to report 396 data elements in
the 23 subparts listed in Table 2 of this preamble. Of these 396 data
elements removed from reporting, 378 data elements are removed due to
disclosure concerns and 18 data elements are removed because these data
elements are redundant to other inputs being reported or are no longer
useful to be reported to the EPA in the absence of other inputs to
emission equations that will no longer be reported (refer to the
discussion below for further explanation). Of the 378 data elements
removed from reporting due to disclosure concerns, 324 data elements
will be entered into IVT.\17\ We are finalizing the proposed amendments
to remove reporting requirements and require entry of these data
elements into IVT, with changes specified in Section II.B.2 of this
preamble.
---------------------------------------------------------------------------
\17\ As mentioned above, there are 378 equation inputs for which
reporting was deferred to 2015 and for which the EPA determined
there are disclosure concerns, and 324 of these equation inputs must
be entered into IVT. Fifty-four of the 378 equation inputs do not
need to be entered into IVT because these equation inputs are
redundant to other equations inputs being entered into IVT or are
otherwise not needed for verification.
---------------------------------------------------------------------------
Table 3 of this preamble provides a summary of the number of data
elements removed from reporting for each subpart. Refer to Table 1 in
the memorandum ``Data Elements Deferred to March 31, 2015: Final List
of `Inputs to Equations' Data Elements Not To Be Reported,'' September
2014, (refer to Docket ID No. EPA-HQ-OAR-2010-0929) for a list of these
396 data elements removed from reporting.
Table 3--Subparts for Which Reporting Requirements Are Removed
------------------------------------------------------------------------
Number of inputs
to emission Number of
equations for deferred inputs
Subpart which reporting for which
was deferred to reporting is
2015 (``deferred removed
inputs'')
------------------------------------------------------------------------
C--General Stationary Fuel \b\ 26 \b\ 26
Combustion--Stationary fuel
combustion sources excluding
sources that contain at least one
combustion unit connected to a
fuel-fired electric generator
owned or operated by an entity
that is subject to regulation of
customer billing rates by the
public utility commission
(excluding generators connected
to combustion units subject to 40
CFR part 98, subpart D) and that
are located at a facility for
which the sum of the nameplate
capacities for all such electric
generators is greater than or
equal to 1 megawatt electric
output \a\.......................
E--Adipic Acid Production......... 21 11
F--Aluminum Production............ 29 29
G--Ammonia Manufacturing.......... 8 8
H--Cement Production.............. 16 14
K--Ferroalloy Production.......... 13 13
N--Glass Production............... 3 3
O--HCFC-22 Production and HFC-23 15 12
Destruction......................
P--Hydrogen Production............ 7 7
Q--Iron and Steel Production...... 86 85
R--Lead Production................ 10 10
S--Lime Manufacturing............. 9 9
U--Miscellaneous Uses of Carbonate 6 6
V--Nitric Acid Production......... 21 21
X--Petrochemical Production....... \c\ 19 \c\ 19
Y--Petroleum Refineries........... 75 70
Z--Phosphoric Acid Production..... 4 4
AA--Pulp and Paper Manufacturing.. 31 28
BB--Silicon Carbide Production.... 3 3
CC--Soda Ash Manufacturing........ 10 4
EE--Titanium Dioxide Production... 2 2
GG--Zinc Production............... 8 8
TT--Industrial Waste Landfills.... 4 4
------------------------------------------------------------------------
\a\ These subpart C sources may elect to report inputs to emission
equations rather than use IVT. Additionally, the reporting
requirements are not amended for stationary fuel combustion sources
that contain at least one combustion unit connected to a fuel-fired
electric generator owned or operated by an entity that is subject to
regulation of customer billing rates by the PUC (excluding generators
connected to combustion units subject to 40 CFR part 98, subpart D)
and that are located at a facility for which the sum of the nameplate
capacities for all such electric generators is greater than or equal
to 1 megawatt electric output.
\b\ Includes one deferred input to an emission equations, 40 CFR
98.3(d)(3)(v), which is specified in subpart A of part 98 and applies
to only certain reporters under 40 CFR part 98, subpart C.
\c\ There were 2 additional inputs to emission equations for which
reporting was deferred to 2015; however, these two inputs are not
reflected in this table because the inputs were removed from Part 98
by a previous rulemaking (78 FR 71904, November 29, 2013).
The EPA is finalizing the proposed amendments to exclude from
reporting 18 deferred inputs to emission equations for which no
disclosure concerns have been identified. As explained in the preamble
to the proposed rule (78 FR 56005, September 11, 2013), while posing no
disclosure concerns, these data elements are redundant to other inputs
being reported or are no longer useful to be reported in the absence of
other inputs to emission equations that will no longer be reported;
they are not needed to be reported to the EPA for data verification and
they are also not helpful in informing future GHG policy development.
For further information
[[Page 63766]]
on these 18 data elements, please see the memorandum ``Data Elements
Deferred to March 31, 2015: Final List of Data Elements Not To Be
Reported,'' September 2014 (refer to Docket ID No. EPA-HQ-OAR-2010-
0929).
For the remaining inputs to emission equations for which reporting
was deferred to 2015 for the 23 subparts listed in Table 2 of this
preamble, the EPA is not amending the reporting requirements because
the EPA has not identified disclosure concerns associated with their
public release, and reporting of these data elements remains useful to
the EPA for data verification as well as for informing future GHG
policy development. Deferral of reporting of these inputs to emission
equations expires on March 31, 2015. As a result, by March 31, 2015,
151 inputs to emission equations must be reported for reporting year
2014 and all prior reporting years, except as described below for six
inputs to emission equations in subpart W of part 98. These 151 data
inputs must also be reported in the annual report for all future
reporting years, except as specified below for the six inputs to
emission equations in subpart W. Refer to Section III.A.3 of the
preamble to the proposed rule (78 FR 56005, September 11, 2013) for
further discussion about how 2010 through 2014 data will be included in
the 2014 annual report. For a list of these 151 deferred inputs to
emission equations that will be reported, refer to Table 2 of the
memorandum cited above. Additionally, to clarify which data elements
must be reported for previous reporting years 2010 through 2013, the
EPA is finalizing its proposed revision of Table A-7 of Part 98, ``Data
Elements That Are Inputs To Emission Equations And For Which The
Reporting Deadline Is March 31, 2015'', which includes these 151 inputs
to emission equations that must be reported.
For the purposes of reporting the subpart W inputs for reporting
years 2011 through 2014, the EPA plans to use a spreadsheet format that
will be uploaded to e-GGRT. Recognizing the substantial amount of
information that facilities will be entering into the spreadsheet, the
EPA anticipates publishing the spreadsheet in October 2014. This will
allow facilities to begin data entry into the spreadsheet prior to the
open reporting period. The spreadsheet can then be uploaded to e-GGRT
during the open reporting season.
For subpart W, the EPA is finalizing the proposed decision to
require subpart W facilities to report all inputs to emission equations
for which reporting was deferred to 2015; however, in the final rule,
in response to comment, the EPA is providing an option for reporters to
delay reporting of six of these inputs to emission equations for two
reporting years for specific situations related to two types of
exploratory wells, delineation and wildcat wells (as defined in this
final rule in 40 CFR 98.238), starting with reporting year 2013.
2. Summary of Changes Since Proposal
This section provides a brief summary of changes since proposal to
the proposed requirement to use IVT. The EPA's rationale for these
changes is provided in Section II.A.3 as part of the EPA's response to
the related comment(s).
The changes to the list of data elements removed from reporting and
required to be entered into IVT are as follows:
The proposed amendments, specifically at 40 CFR
98.5(b), required that the inputs to emission equations for the
calculation methods listed in the proposed Table A-8, ``Calculation
Methods For Which Inputs To the Calculation Methods Must be Entered
Into Verification Software Specified By the Administrator,'' be
entered into IVT. In the final rule, the EPA removed the proposed
Table A-8 of part 98, replacing it with a new ``verification
software records'' provision in the recordkeeping section of each
affected subpart, which lists for each subpart each equation input
that must be entered into IVT.
The proposed amendments required that the data element
in 40 CFR 98.196(b)(8) be entered into IVT. After proposal, we
discovered that this data element is not an input to an emission
equation. Further, it is no longer needed for verification because
the proposed new data element (40 CFR 98.196(b)(18)), which is being
finalized in this action, will be sufficient for verification
purposes. Therefore, in the final rule, we are removing the
reporting requirement for this data element.
The proposed amendments did not require that the input
to Equation F-4 be entered into IVT, because this input is not
required to be reported under Part 98. Based on a suggestion from a
commenter, in the final rule we are requiring that the input to
Equation F-4 be entered into IVT. Although part 98 does not require
reporting of this input, the commenter stated that this input should
be entered into IVT, and we agree that it is needed for calculating
and verifying emissions in subpart F.
The EPA is replacing eight reporting elements, which
were incorrectly identified in the final deferral rulemaking (76 FR
53057, August 25, 2011) as inputs to Equations F-2 and F-3 and were,
therefore, incorrectly proposed (78 FR 55994, September 11, 2013) to
be entered into IVT (instead of the correct inputs to Equations F-2
and F-3). As a result of a comment received, the EPA discovered that
it had previously misidentified eight data elements as inputs to
Equations F-2 and F-3, mistakenly required and then deferred their
reporting under part 98, and recently mistakenly proposed their
entry into IVT. These misidentified data elements are annual values;
whereas the inputs to these two equations are monthly values, which
are not required to be reported under Part 98. In light of the
error, the EPA is requiring in this final rule that the correct
inputs (monthly values) for Equations F-2 and F-3 be entered into
IVT. Further, given that the EPA had previously incorrectly required
the reporting of these eight annual values as inputs to Equations F-
2 and F-3, and given that the actual inputs (i.e., the monthly
values) for Equations F-2 and F-3 will be entered into IVT, the EPA
does not need these eight annual values for verification. The EPA is
therefore finalizing the removal of reporting of these eight annual
values for Equations F-2 and F-3. Refer to the EPA's comment
response document in Docket ID No. EPA-HQ-OAR-2010-0929 for further
discussion of this comment supporting entry into IVT of monthly
input data for Equations F-2 through F-4 and the EPA's response.
For a given sub-basin, in the following situations, the
EPA is providing the option to delay for two reporting years the
reporting of six data elements associated with delineation or
wildcat wells starting in reporting year 2013:
--For gas well completions or workovers with hydraulic fracturing,
where wildcat wells and/or delineation wells are the only wells in a
sub-basin that can be used for the measurement; and
--for onshore production storage tanks, where wildcat wells and/or
delineation wells are the only wells in a sub-basin.
These six data elements are: (1) Measured flow rate of backflow
during well completion (40 CFR 98.236(c)(6)(i)(B)); (2) measured
flow rate of backflow during well workover (40 CFR 98.236
(c)(6)(i)(D)); (3) total number of days of backflow from all wells
during completions (40 CFR 98.236 (c)(6)(i)(E)); (4) total number of
days of backflow from all wells during workovers (40 CFR 98.236
(c)(6)(i)(F)); (5) total volume of oil from all wellhead separators
sent to tank(s) in barrels per year (40 CFR 98.236(c)(8)(i)(F)); and
(6) total volume of sales oil from all wells in barrels per year (40
CFR 98.236(c)(8)(ii)(A)). For reporting years 2011 and 2012, the two
year delay would still require reporting by March 31, 2015. As a
result, there is no need to delay reporting for these two reporting
years. Refer to Section II.B.3 of this preamble for the EPA's
rationale for this decision. If the 2-year delay in reporting is
used, the reporter must report the following information in the
current reporting year: indicate for each delayed reporting element
that one of the two situations listed above is true (e.g., for gas
well completions or workovers with hydraulic fracturing, wildcat
wells and/or delineation wells are the only wells in a sub-basin
that can be used for the measurement). In addition, when reporters
report the delayed inputs to emission equations after the 2 year
delay, they must also report the API well ID numbers for the
applicable wildcat and/or delineation wells in the sub-basin for
which the reporting element was delayed.
For purposes of part 98, the EPA has added to 40 CFR
90.238 definitions of
[[Page 63767]]
``delineation well'' and ``wildcat well.'' ``Delineation well'' is
defined as a well drilled in order to determine the boundary of a
field or producing reservoir. ``Wildcat well'' is defined as a well
outside known fields or the first well drilled in an oil or gas
field where no other oil and gas production exists. These
definitions are consistent with the definitions of ``delineation
well'' and ``wildcat well'' in 40 CFR part 60, subpart OOOO. Refer
to Section II.B.2 of this preamble for the EPA's rationale for this
decision.
The EPA has removed from reporting the inputs to
emission equations in 40 CFR 98.226(i), (j), (m)(4), (m)(5), and
(p). These data must be entered into IVT, except for 40 CFR
98.226(j). Refer to Section II.B.3 of this preamble for the EPA's
rationale for this decision.
3. Summary of Comments and Responses
This section summarizes the significant comments and responses
related to the proposed amendments to remove reporting requirements and
require entry of data into IVT. The EPA's comment response document in
Docket ID No. EPA-HQ-OAR-2010-0929 provides a complete listing of all
comments related to this topic and the EPA's responses.
Comment: One commenter asserted that all 9 inputs to emission
equations reported under 40 CFR 98.226(i), (j), (m)(4) and (5), and (p)
would reveal process design, process performance, and operational
efficiencies data regarding a nitric acid train. The commenter further
noted that the EPA indicated in section 2.2 of its memorandum,
``Evaluation of Competitive Harm from Disclosure of `Inputs to
Equations' Data Elements Deferred to March 31, 2015,'' August 2013
(refer to Docket ID No. EPA-HQ-OAR-2010-0929), that these types of data
could be used to determine facility operational conditions and would,
therefore, have disclosure concerns.
Response: In the EPA's proposed harm analysis cited above in the
comment summary, the EPA stated that the 9 inputs to emission equations
reported under 40 CFR 98.226(i), (j), (m)(4) and (5), and (p) would not
reveal any proprietary information about cost to do business, raw
material usage, production, or facility or process performance, design,
and operation, as long as the emission factors required to be reported
in 40 CFR 98.226(m)(1) are not reported. As a result of this comment,
the EPA further investigated the operational conditions at current
nitric acid facilities, and considered the specific case when there are
nitric acid facilities that have non-operational nitric acid trains and
others that are in the process of installing or upgrading
NOX control devices, some of which can also serve as
N2O abatement (i.e., non-selective catalytic reduction). In
light of this, the data reported under 40 CFR 98.226(i), (j), (m)(4),
(m)(5), and (p), if reported over a multiple-year period where
facilities are making changes to the operational status of their trains
and/or abatement systems, could be used to determine train-specific
conditions at the facility, such as efficiency losses, equipment
degradation, changes in nitric acid demand, and/or the installation of
N2O abatement technology. As a result, the EPA agrees with
the commenter that the deferred inputs to emission equations reported
under 40 CFR 98.226(i), (j), (m)(4), (m)(5), and (p) (destruction
efficiency and fraction control factor of the abatement technology,
abatement utilization factor, and nitrous oxide (N2O)
concentration and volumetric flow rate per test run during performance
test of each train) would reveal information about process design,
process performance, and operational efficiencies of a nitric acid
train, regardless of whether the emission factors required to be
reported in 40 CFR 98.226(m)(1) are not reported. Therefore, the EPA
has concluded that these data have disclosure concerns, and the EPA is
removing these data from the reporting requirements in the final rule.
Reporters will be required to enter these data into IVT, except 40 CFR
98.226(j), which is not needed to be entered into IVT for verification
purposes because IVT generates this value using the inputs entered into
Equation V-2 and Equation V-2.
Comment: One commenter expressed concern about reporting
information on exploratory wells in Subpart W, especially when the
wells are located in step-out areas where no prior reporting exists for
a given sub-basin (including vertical or horizontal wells). The
commenter explained that the problem occurs when an exploratory well is
the sole well in a sub-basin (including vertical or horizontal wells)
and is not reported in combination with other wells, thereby shielding
any individual well's contribution. The commenter noted that its
concerns are related to the timing of releasing the information to the
public, as the commenter stated that the information is most sensitive
if it is made available too early during the exploration or initial
development stages. The commenter stated that the success of a well in
exploratory areas could be inferred if detailed data are provided to
the public too soon during the exploration and assessment period. The
commenter provided an example of such an occurrence: An exploratory
well completed in December of the reporting year, data reported to the
EPA by end of March of the following year and then released by the EPA
to the public within a few months during the same year. The commenter
stated that early release of data regarding operating characteristics
of such wells, including postflowback flaring/venting volumes, could
cause competitive harm if made publicly available too early.
The commenter noted that Federal law and State codes allow
companies to designate as confidential the data obtained from
exploratory wells, especially in new discovery areas or areas that are
being explored for development. The commenter further noted that the
original intent of State oil and gas commissions to allow withholding
of select drilling and production information from early release to the
public was to allow competitive exploration by searching for new
pockets of oil or gas and experimenting with new tools and techniques.
The commenter stated that releasing data on such wells through the
GHGRP--despite the fact that they are held confidential by other
regulatory bodies--could cause substantial competitive harm and lead to
a loss of investment value. The commenter explained that competitive
harm could occur if the public could obtain detailed high-resolution
operational information on a well-by-well basis and on a daily or
weekly basis.
The commenter requested that the EPA categorically determine that
all information associated with exploratory wells, with the exception
of well ID and location, be classified as CBI for a period of at least
24 months from the start of exploration. The commenter recommended
either of two suggested approaches under the GHGRP: (1) Companies would
report all data to the EPA as mandated by subpart W, but the EPA would
hold the reported data as CBI and not include it in its public data
release for at least 24 months (this could be accomplished by a
flagging system (or a ``radio button'') in e-GGRT that could also allow
for a short informative text on why that particular well information is
to be maintained confidential); or (2) the EPA could set up a deferral
system where initial data on exploratory wells will be well ID and
location information and the remaining data would be backfilled by
companies after a period of 24 months. The commenter added that neither
option would require case-by-case review of companies' information, and
both are consistent with the approach taken by state oil and gas
commissions and are
[[Page 63768]]
protective of companies' commercial investment interests.
Response: The EPA reviewed the types of data identified by the
commenter as having disclosure concerns for exploratory wells: ``data
regarding operating characteristics . . . including post-flowback
flaring/venting volumes.'' In our proposed memorandum ``Evaluation of
Competitive Harm from Disclosure of `Inputs to Equations' Data Elements
Deferred to March 31, 2015,'' August 2013 (refer to Docket ID No. EPA-
HQ-OAR-2010-0929), the EPA stated regarding exploratory wells, that
because onshore production data are reported under the GHGRP at a sub-
basin level, as defined by county boundaries, the data are aggregated
to a large enough scale that disclosure of the data collected under
subpart W would not reveal any proprietary information about the
facility or cost to do business. After further investigation in
response to the comment received, and review of the state laws
protecting these types of data, the EPA has determined that, in the
following situations which were not specifically considered in the
proposed rule, early public disclosure of certain deferred inputs to
emission equations associated with wildcat wells and/or delineation
wells could reveal the well productivity, thereby resulting in the loss
of investment value:
For gas well completions or workovers with hydraulic
fracturing, where wildcat wells and/or delineation wells are the
only wells in a sub-basin that can be used for the measurement; and
For onshore production storage tanks, where wildcat
wells and/or delineation wells are the only wells in a sub-basin.
The inputs to emission equations (for which reporting was deferred
to 2015) that could reveal well productivity for wildcat and/or
delineation wells in the applicable situations listed above are as
follows:
For gas well completions or workovers with hydraulic
fracturing, the measured flow rate of backflow during well
completion (40 CFR 98.236(c)(6)(i)(B));
For gas well completions or workovers with hydraulic
fracturing, the measured flow rate of backflow during well workover
(40 CFR 98.236(c)(6)(i)(D));
For gas well completions or workovers with hydraulic
fracturing, the total number of days of backflow from all wells
during completions (40 CFR 98.236(c)(6)(i)(E));
For gas well completions or workovers with hydraulic
fracturing, the total number of days of backflow from all wells
during workovers (40 CFR 98.236(c)(6)(i)(F));
For onshore production storage tanks, the total volume
of oil from all wellhead separators with wellhead gas-liquid
separator oil throughput greater than or equal to 10 barrels per day
sent to tank(s) in barrels per year (40 CFR 98.236(c)(8)(i)(F)); and
For onshore production storage tanks, the total volume
of sales oil from all wells with oil production greater than or
equal to 10 barrels/day in barrels per year (40 CFR
98.236(c)(8)(ii)(A)).
These six inputs to emission equations data elements are themselves
a small subset of the inputs to emission equations data elements (for
which reporting was deferred to 2015) collected in subpart W, as there
are 90 such inputs to emission equations in subpart W. Further, wildcat
and delineation wells represent a relatively small percentage of the
wells being reported under the GHGRP for these data elements. As such,
in the interim period before these data are reported to the EPA, the
EPA will be able to verify the majority of the emissions using the
inputs to equations that will be reported to the EPA. For the six
inputs to emission equations that may be delayed for 2 years, the EPA
will verify emissions using other data reported to the EPA, and will
conclude verification upon receipt of the data. The EPA agrees with the
commenter that a 2-year delay of reporting is sufficient to prevent
early public disclosure of these data and will provide sufficient time
for the reporter to thoroughly conduct an assessment of the well. Given
the results of this evaluation, the EPA determined that, for these six
inputs to emission equations, in those cases where a reporter has
wildcat wells or delineation wells in a sub-basin and these wells meet
one of the two situations described above, reporters should be provided
an option to delay reporting of the given input for two reporting years
starting in reporting year 2013. There is no early public disclosure
concern for these inputs for reporting years 2011 and 2012 because 2
years would already have passed before they are to be reported in March
31, 2015. As a result, there is no need to delay reporting for these
two reporting years. For reporting years 2013 and thereafter, this
delay will prevent early public disclosure of information regarding
well productivity. In such cases, if the 2-year delay in reporting is
used, the reporter must report the following information in the current
reporting year: indicate for each delayed reporting element that one of
the two situations listed above is true (e.g., for gas well completions
or workovers with hydraulic fracturing, wildcat wells and/or
delineation wells are the only wells in a sub-basin that can be used
for the measurement). In addition, when reporters report the delayed
inputs to emission equations after the 2 year delay, they must also
report the API well ID numbers for the applicable wildcat and/or
delineation wells in the sub-basin for which the reporting element was
delayed.
The EPA also determined that additional definitions are necessary
in order to clarify and specify the types of exploratory wells
(delineation and wildcat wells) covered by the 2-year delay of
reporting option. The EPA is adopting the terms and definitions used to
describe delineation wells and wildcat wells in the new source
performance standards for the oil and gas sector under 40 CFR part 60,
subpart OOOO, as reporters under 40 CFR part 98, subpart W are also
complying with 40 CFR part 60, subpart OOOO requirements. To minimize
confusion for reporters and be consistent with 40 CFR part 60, subpart
OOOO, the final rule includes the terms and definitions of a
``delineation well'' and ``wildcat well,'' as used in 40 CFR part 60,
subpart OOOO. ``Delineation well'' is defined as a well drilled in
order to determine the boundary of a field or producing reservoir.
``Wildcat well'' is defined as a well outside known fields or the first
well drilled in an oil or gas field where no other oil and gas
production exists.
C. Revision of Recordkeeping Requirements for Facilities Required To
Use IVT
1. Summary of Final Amendments to Part 98
The EPA is finalizing the proposed revisions to recordkeeping
requirements for facilities required to use IVT. For each facility
required to use IVT, the facility is required to retain all records
starting with records for reporting year 2010, including records for
subparts not subject to using IVT, for 5 years, rather than the 3-year
record retention period required for non-IVT users. In other words, if
any facility subject to using IVT is also subject to a subpart of Part
98 not listed in Table 2 of this preamble, the facility is required to
maintain the records required for those other subparts for 5 years.
Facilities subject to IVT are also required to maintain a record of all
inputs to emission equations entered into IVT, in the format provided
by IVT. At the time the reporter completes entry of data into IVT, the
facility is required to download from IVT a file that lists the entered
data and maintain a copy of the file as a record of the entered inputs.
As specified in 40 CFR 98.3(g), subpart A, this file may be maintained
in electronic or hard copy format. Refer to Sections II.C and III.B of
the proposal preamble (78 FR 55994, September 11, 2013) for further
discussion of these
[[Page 63769]]
amendments to the Part 98 recordkeeping requirements being finalized in
this action.
The EPA has added a new ``verification software records'' provision
to the recordkeeping section of each subpart listed in Table 2 of this
preamble to list all inputs to emission equations required to be
entered into IVT. As mentioned above, a list of the entered inputs must
be downloaded from IVT and maintained as records.
We are also revising an error in 40 CFR 98.3(g), as proposed. As
discussed in Section III.B of the proposal preamble (78 FR 55994,
September 11, 2013), in a previous action amending this paragraph (76
FR 73866, November 29, 2011), our intention was to amend the second
sentence of the paragraph regarding record retention duration; however,
the third sentence regarding record format was inadvertently amended.
As a result, as proposed, we are removing the second sentence of 40 CFR
98.3(g) and reinstating the previous third sentence of 40 CFR 98.3(g)
(regarding format of records). Refer to Section II.B of this preamble
for further discussion of this new provision.
2. Summary of Changes Since Proposal
The EPA is making no changes to the proposed revisions to
recordkeeping requirements for IVT users. To clarify which data are
entered into IVT and must be kept as records (i.e., the data included
in the file generated by IVT to be maintained as a record), the EPA is
adding a ``verification software records'' provision to the
recordkeeping section of each subpart specified in Table 2 of this
preamble. Each ``verification software records'' provision lists the
inputs to equations required to be entered into IVT and required to be
maintained as a record.
3. Summary of Comments and Responses
This section summarizes the significant comments and responses
related to the proposed amendments to the recordkeeping requirements
for IVT users. The EPA's comment response document in Docket ID No.
EPA-HQ-OAR-2010-0929 provides a complete listing of all comments and
responses related to this topic.
Comment: Three commenters supported the EPA's extension of the
records retention period. Eight commenters opposed the EPA's proposal
to extend the record retention time from 3 to 5 years. Five of the
eight commenters indicated that this proposed requirement would add
significantly more burden to owners with multiple reporting facilities,
where some facilities would be subject to a 3-year record retention
schedule and some of which would be subject to a 5-year record
retention period. Three of these commenters presented this argument in
the context of landfills, where one owner would have multiple
landfills, and only certain of the landfills would be subject to using
IVT due to being subject to subpart C. One of the five commenters
explained that owners of multiple facilities in remote locations (e.g.,
offshore production platforms, compressor stations, fuel supply
terminals) rely on data centers and centralized archiving procedures to
maintain accurate records and back-up documentation for demonstrating
compliance for some records. The commenter provided one example of a
scenario where an owner of multiple facilities subject to subparts C,
W, and NN would be subject to use of IVT due to subpart C. The
commenter indicated that this requirement would create confusion by
requiring that data maintained in the central data centers be organized
according to two different record retention periods. Additionally, the
commenter asserted, for a given reporter (e.g., gas processing plant
subject to subparts C and W), some records are maintained on site and
other are maintained in a central data exchange. The commenter added
that the requirement to keep records according to two different
retention periods would substantially increase the volume of records
required. Another commenter also pointed out the increased confusion
associated with maintaining records for multiple record duration
periods.
Two commenters contended that this revision conflicts with the
justification the EPA previously made for requiring 3 years in the 2009
promulgated GHGRP rule, citing that the EPA determined it was
sufficient time to audit and review, reduces recordkeeping burden, and
is consistent with recordkeeping requirements in other Federal
programs. Two of the commenters stated that the EPA did not provide
sufficient justification for extending the record retention time. Two
of the commenters disagreed with the EPA's rationale that the extra
time is needed for follow-up with reporters because IVT would generate
an immediate flag on a real-time basis of any input errors and follow-
up could be immediate. One of these commenters further disagreed with
the EPA's rationale that the extra time would allow the EPA inspectors
time for appropriate assessment of compliance, because the EPA could
accomplish this with timely inspections that do not need the extra
time.
One commenter expressed concern that the proposed extra retention
time would be an unfair burden because it only applies to those sources
using IVT and not all sources. The commenter added that sources using
IVT would be unfairly subjected to potential additional fines and
penalties for noncompliance for an extra 2 years, while other sources
would not be subject to this noncompliance issue. The commenter
concluded that requiring the verification IVT users to retain
information longer would lead to unjustified prejudices against these
source categories.
Six of the eight commenters that opposed the EPA's proposal to
extend the record retention time from 3 to 5 years also opposed the
EPA's proposal that this 5-year record retention requirement for IVT
users be extended to all subparts applicable to a reporter. The six
commenters opposed this additional requirement for the same reasons
they opposed the 5-year retention period.
Response: The EPA is finalizing in this action this proposed
amendment to recordkeeping requirements for IVT users as part of the
alternative verification approach included in these amendments. As
previously stated in the proposal preamble (September 11, 2013, 78 FR
55994), the EPA considered whether the current record retention period
and record format requirements would be sufficient to allow the EPA to
perform data verification under this alternative verification approach.
We considered:
The time we would need to follow up with reporters to
further verify reported GHG emissions.
The desirability of retaining multiple years of data
records to allow for appropriate assessment of compliance and for
analyses of trends for policy analysis purposes.
The format of records, and whether the current format
would be adequate for our verification process. For example, we
considered whether records of inputs to emission equations (for
which reporting was deferred to 2015) contained in multiple separate
documents (as currently allowed under Part 98) would allow an EPA
inspector to efficiently analyze the consistency of the data
elements and use the data elements to perform calculations to
confirm reported GHG emissions.
This revision to the recordkeeping timeframe is part of the new
verification approach using IVT that is being finalized today. Given
the large number of reporters under the subparts identified in Table 2
of this preamble (over 2,000 facilities) and the likely increase in
follow-up activities under
[[Page 63770]]
the new approach, it is important that relevant records are available
to the EPA for follow-up activities with facilities, including on-site
audits if necessary, regarding potential errors, discrepancies, or
questions. When an EPA employee visits a facility, it is important that
the employee be able to examine not only the current year's records but
those from previous years as well, because previous years' data will
provide year-to-year comparisons, which are useful for verifying the
current year's data. A 5-year record retention period ensures the
availability of relevant records for the follow-up activities described
above.
Regarding the general comment that this proposed 5-year record
retention requirement would add significantly more burden to owners
with multiple reporting facilities, the EPA disagrees with this
assertion. Given that reporters are already required to maintain
records for 3 years, the reporter is not required to do anything more
than keep the records for an additional 2 years. Only one commenter
provided a description of the additional burden for these types of
owners. The commenter referred to a scenario where one parent company
has multiple facilities subject to different combinations of subparts
NN, C, and W (where some facilities are in remote locations, such as
offshore production platforms, compressor stations, and fuel supply
terminals). As such, the parent company is subject to both a 3-year
record duration for some facilities and a 5-year record duration for
other facilities. The commenter described the burden as being
associated with the need for their records that are maintained in their
central data centers to be organized according to two different record
retention periods. However, the commenter did not provide any
additional information or data to support their claim that the
increased burden associated with this scenario would be significant,
and the EPA does not understand how saving data electronically for an
additional 2 years would require significant additional burden. The EPA
received no comments on its proposed impacts analysis, which concluded
that there is no additional burden imposed on keeping records for 2
additional years (refer to Section V of the proposal preamble,
September 11, 2013, 78 FR 55994). Lastly, if a parent company does not
want to maintain some facilities' records for 3 years and others for 5
years, there is nothing in this rulemaking that prevents owners from
maintaining all records for a period of 5 years.
Regarding the comment that this 5-year record duration requirement
conflicts with the EPA's justification in the 2009 promulgated GHGRP
rule that the 3-year duration is adequate, the EPA's rationales for
extending the recordkeeping period under the new verification approach
using IVT do not conflict with the previous justification for the 3-
year recordkeeping requirement in the 2009 rulemaking because the 2009
GHGRP rule (74 FR 56260) did not include the alternative verification
approach being finalized today. Since the IVT approach was not part of
the 2009 rulemaking, the previous consideration did not take into
account this new approach that is being finalized today. Further, at
the time the previous justification was made, not only was there no IVT
approach, the inputs to equations, which were necessary for verifying
emissions under the 2009 rule, were required to be reported timely with
the annual reports. In light of the subsequent changes to the
verification approach and input reporting, it is unreasonable to
suggest that the previous justification for a 3-year recordkeeping
period still applies. The commenter did not identify or explain any
deficiency in the EPA's rationales for extending the record keeping
period to accommodate the IVT approach.
Regarding the comment that this 5-year record duration requirement
is inconsistent with recordkeeping requirements in other Federal
programs, the other Federal programs referred to by the commenter
(i.e., Department of Energy (DOE) and Acid Rain Program (ARP)) are not
using the alternative verification approach associated with this
action. As such, comparison to DOE or ARP reporting programs is not
appropriate. The EPA also notes that the EPA's National Emission
Standards for Hazardous Air Pollutants require 5-year record retention
(see 40 CFR 63.10(b)).
Regarding the comment that the EPA does not need extra time to
allow for follow-up with reporters because IVT would generate an
immediate flag on a real-time basis of any input errors and follow-up
could be immediate, based on its experience with data verification for
reporting years 2010 through 2012, the EPA anticipates situations where
the verification summary will indicate discrepancies between reported
GHG emissions and the GHG emission equation results calculated by IVT
as well as other verification results that will require further
attention. In certain situations, the EPA will need additional time to
follow up with these reporters to resolve discrepancies, as further
described above.
Regarding the comment that the EPA does not need extra time because
the EPA could accomplish this alternative verification approach with
``timely inspections,'' as further described above, the EPA anticipates
more direct follow-up activities under the alternative verification
approach associated with this action. Given the large number of sources
reporting to the GHGRP and limited resources, any direct follow-up with
facilities would be more effective with the ability to access 5 years
of data.
In response to the comment that the proposed extra retention time
would be an unfair burden because certain sources would be unfairly
subjected to potential additional fines and penalties for noncompliance
for an extra 2 years, it is important to note that different facilities
within the Greenhouse Gas Reporting Program are subject to different
verifications approaches (reporting inputs to emissions equations
versus using IVT). Different verification approaches necessitate
different reporting and record keeping requirements to ensure the
success of the individual verification approach. Further, we do not
believe that the 5-year record retention period is complex or otherwise
difficult or burdensome to implement; if a facility uses IVT, it must
keep all of its record for 5 years. Given that a reporter is already
required to maintain records for 3 years, this 5-year recordkeeping
requirement does not require any action beyond keeping these records
for an additional 2 years. In any event, the commenters did not provide
any information to support the claim that 2 additional years of record
maintenance would somehow trigger additional fines and penalties.
Further, the commenter provided no comment on the EPA's proposed
impacts analysis, which concluded that there is no additional burden
imposed on keeping records for 2 additional years (refer to Section V
of the proposal preamble, September 11, 2013, 78 FR 55994).
Regarding the comments opposing extending the 5-year record
retention requirement to all subparts for IVT users, the EPA proposed
this provision because during a site visit, if questions arise
regarding the accuracy of equation inputs entered into IVT, it may be
necessary to examine other recordkeeping information not entered into
IVT, such as a monitoring plan or recordkeeping information in a
different subpart, in order to fully investigate the accuracy of the
data at issue. For example, a lime production facility with natural
gas-fired kilns may report combustion emissions under subpart C,
CO2 process emissions from lime kilns
[[Page 63771]]
under subpart S, and CO2 supply under subpart PP. As part of
the site visit, the EPA may check for inconsistencies in the quantities
of CO2 collected and transferred off site (reported under
subpart PP) compared with the CO2 process emissions reported
under subpart S. Specifically, if a facility reported collecting 32,000
metric tons under subpart PP but reported generating only 30,000 metric
tons of CO2 in their lime kilns, then the EPA may need to
check the records and review the monitoring plan for both subpart S and
PP to determine why this inconsistency occurred. If this facility also
elected to report the natural gas combusted (i.e., the facility elects
not to use IVT for subpart C), then the EPA would also use the fuel
quantity data to check for unexpected inconsistencies in the subpart S
data using parameters such as the ratio of CO2 emissions to
fuel consumption and looking for significant changes in such parameters
when compared to data from previous years. As part of this process, the
EPA may examine the monitoring plan associated with all of the subparts
reported by this facility to ensure that the correct monitoring was
conducted by the facility. In this example, if facilities were allowed
to retain records for only 3 years for subparts for which IVT was not
used, the EPA's verification and compliance activities would be
impacted by incomplete records for subparts C and PP when compared with
subpart S. As the above example illustrates, records necessary to
verify data submitted by a facility using IVT may include that
facility's data from subparts not subject to IVT. It is therefore
necessary to ensure that all data necessary for verification are
available, and this 5-year record retention period requirement will
provide assurance of on-site data availability. The EPA received no
additional rationale opposing this provision beyond the rationales
presented against the 5-year record duration requirement. The EPA
received no details to contradict the EPA's proposed impacts analysis,
which concluded that this proposed requirement would impose no
additional burden (refer to Section V of the proposal preamble,
September 11, 2013, 78 FR 55994). As such, the EPA is finalizing the
proposed requirement for IVT users to maintain records for all subparts
for a period of 5 years.
Comment: One commenter suggested that the recordkeeping section of
each subpart be modified to clearly specify which records related to
IVT must be maintained. The commenter argued that e-GGRT is a reporting
tool, but not a regulation, such that it would not be appropriate for
IVT to dictate which records must be maintained.
Response: The EPA had requested comment on whether additional
specificity within the recordkeeping requirements of each subpart would
improve the clarity of the specific records that are required to be
retained. After considering the commenter's request, the EPA agrees
with the recommendation to specify each record that reporters must
maintain. In the final rule, each subpart listed in Table 2 of this
preamble includes, in the recordkeeping section, a new ``verification
software records'' provision that specifies each data element in that
subpart that must be entered into IVT and maintained as a record.
D. Addition of Reporting Requirements for Certain Facilities Required
To Use IVT
1. Summary of Final Amendments to Part 98
The EPA is finalizing the proposed addition of new reporting
requirements for facilities required to use IVT for subparts E, G, H,
P, Q, S, V, X, and AA of part 98, with changes to the proposed
amendments for subparts E, V, Y, and AA, as discussed in Section II.D.2
of this preamble. The final list of new data elements being added in
this action is in Table 4 of this preamble.
Table 4--New Data Elements Being Finalized in Today's Action for Subparts E, G, H, P, Q, S, V, X, and AA of Part
98
----------------------------------------------------------------------------------------------------------------
Subpart Subpart name New data element description
----------------------------------------------------------------------------------------------------------------
E..................................... Adipic Acid Production........ If only cyclohexane is oxidized to
produce adipic acid: the annual
quantity of cyclohexane (tons) used to
produce adipic acid. If materials other
than cyclohexane are oxidized to
produce adipic acid: the annual
quantity of cyclohexanone and
cyclohexanol mixture (metric tons) used
to produce adipic acid.
Annual percent nitrous oxide (N2O)
emission reduction for all production
units combined.
G..................................... Ammonia Production............ Annual ammonia production (metric tons,
sum of all process units reported
within subpart G).
Annual methanol production (metric tons)
for each process unit.
H..................................... Cement Production............. Annual clinker production (metric tons).
Annual average clinker carbon dioxide
(CO2) emission factor for the facility,
averaged across all kilns (metric tons
CO2/metric ton clinker produced).
Annual average cement kiln dust (CKD)
CO2 emission factor for the facility,
averaged across all kilns (metric tons
CO2/metric ton CKD produced).
P..................................... Hydrogen Production........... Name and annual quantity (metric tons)
of each carbon-containing fuel and
feedstock.
Annual methanol production (metric tons)
for each process unit.
[[Page 63772]]
Q..................................... Iron and Steel Production..... If you use the carbon mass balance
method in 40 CFR 98.173(b)(1) to
determine CO2 emissions: The annual
mass (metric tons) of all gaseous,
liquid, and solid fuels (combined) used
in process units specified in Equations
Q-1 through Q-7 of subpart Q,
calculated as specified in Equation Q-9
of subpart Q being finalized in this
action. Do not include fuel used in a
stationary combustion unit where
emissions are reported under subpart C.
If you use the carbon mass balance
method in 40 CFR 98.173(b)(1) to
determine CO2 emissions: The annual
mass (metric tons) of all non-fuel
material inputs (combined) specified in
Equations Q-1 through Q-7 of subpart Q,
calculated as specified in Equation Q-
10 of subpart Q being finalized in this
action.
If you use the carbon mass balance
method in 40 CFR 98.173(b)(1) to
determine CO2 emissions: The annual
mass (metric tons) of all solid and
liquid products and byproducts
(combined) specified in Equations Q-1
through Q-7 of subpart Q, calculated as
specified in Equation Q-11 of subpart Q
being finalized in this action.
If you use the carbon mass balance
method in 40 CFR 98.173(b)(1) to
determine CO2 emissions: The weighted
average carbon content of all gaseous,
liquid, and solid fuels (combined)
included in Equation Q-9 of subpart Q
being finalized in this action,
calculated as specified in Equation Q-
12 of subpart Q being finalized in this
action.
If you use the carbon mass balance
method in 40 CFR 98.173(b)(1) to
determine CO2 emissions: The weighted
average carbon content of all non-fuel
inputs to all furnaces (combined)
included in Equation Q-10 of subpart Q
being finalized in this action,
calculated as specified in Equation Q-
13 of subpart Q being finalized in this
action.
If you use the carbon mass balance
method in 40 CFR 98.173(b)(1) to
determine CO2 emissions: The weighted
average carbon content of all solid and
liquid products and byproducts from all
furnaces (combined) included in
Equation Q-11 of subpart Q being
finalized in this action, calculated as
specified in Equation Q-14 of subpart Q
being finalized in this action.
S..................................... Lime Manufacturing............ Annual quantity (tons) of lime product
sold, by type.
V..................................... Nitric Acid Production........ Annual percent N2O emission reduction
for all nitric acid trains combined.
X..................................... Petrochemical Production...... If using the CEMS method to calculate
GHG emissions: Name and annual quantity
(in metric tons) of each product. If
using the mass balance method to
calculate GHG emissions: Name and
annual quantity (in metric tons) of
each product used in Equations X-1, X-
2, and X-3 of subpart X.
If using the CEMS method to calculate
GHG emissions: Name and annual quantity
(in metric tons) of each carbon-
containing feedstock. If using the mass
balance method to calculate GHG
emissions: Name and annual quantity (in
metric tons) of each carbon-containing
feedstock used in Equations X-1, X-2,
and X-3 of subpart X.
AA.................................... Pulp and Paper Manufacturing.. For each pulp mill lime kiln: Quantity
of calcium oxide (CaO) produced (metric
tons).
For each pulp mill lime kiln: Percentage
of annual heat input, individually for
each fossil fuel type.
----------------------------------------------------------------------------------------------------------------
The EPA is also adding six new equations (Equations Q-9 through Q-
14 of part 98) to subpart Q, as proposed, to specify how to calculate
and report each of the six new data elements added to subpart Q in this
action. Final confidentiality determinations for the data elements
specified in Table 4 are presented in Section III of this preamble.
2. Summary of Changes Since Proposal
This section provides a brief summary of changes since proposal.
The EPA's rationale for these changes is provided in Section II.D.3 of
this preamble as part of the EPA's response to the related comment(s).
In cases where the EPA is making a change that was not related to a
public comment, a summary of the rationale is included in this section.
The changes to the proposed addition of new reporting requirements
for facilities required to use IVT are as follows:
In the final rule, the new data element for subpart E,
40 CFR 98.56(m), specifies that if only cyclohexane is oxidized to
produce adipic acid, the reporter must report the annual quantity of
cyclohexane used to produce adipic acid; otherwise, if materials
other than cyclohexane are oxidized to produce adipic acid, the
reporter must report the annual quantity of cyclohexanone and
cyclohexanol mixture used to produce adipic acid. Refer to Section
II.D.3 of this preamble for the rationale for this revision.
[[Page 63773]]
The EPA is not finalizing the proposed addition of two
new data elements to subpart AA: The annual mass of steam generated
(proposed as 40 CFR 98.276(m)(1)) and the ratio of the unit's
maximum rated heat input capacity to its design rated steam output
capacity (proposed as 40 CFR 98.276(m)(2)). Refer to Section II.D.3
of this preamble for the rationale for this revision.
The EPA is revising the new data element added to
subpart V (40 CFR 98.226(q)) to read ``annual percent N2O
emission reduction for all nitric acid trains combined.'' The text
``nitric acid trains'' replaces proposed text ``production units''
to be consistent with the terminology used elsewhere in subpart V.
This rationale is documented in ``Summary and Explanation of Minor
Changes Since the Proposed Rule'' (Docket ID No. EPA-HQ-OAR-2010-
0929).
The EPA is not finalizing the proposed addition of the
following three new data elements to subpart Y, which were proposed
to be required to be reported when Equation Y-3 is used to calculate
flare CO2 emissions: Annual quantity of flare gas
combusted, annual average molecular weight of flare gas combusted,
and annual average carbon content of flare gas combusted, all for
normal operations and startup, shutdown, and malfunction (SSM)
events combined. The EPA included these new elements in the proposal
to supplement the IVT verification approach by minimizing the need
for potential follow-up activities (e.g., phone calls, emails, site
visits, etc.) to verify reported GHG emissions from flares using
Equation Y-3 to calculate emissions. Specifically, such information
would allow the EPA to verify and reconcile potential differences
between reported emissions and emissions equation results calculated
by IVT, and therefore minimize the need for follow-up via phone,
email or site visits. At the time of proposal, the EPA did not
consider the proposed new reporting elements in conjunction with the
monitoring requirements associated with Equation Y-1a and Y-1b. In
the process of finalizing this rulemaking, the EPA realized that,
under the current rule, if the flare gas composition (which
determines molecular weight and carbon content) is measured weekly
or more frequently, reporters are required to use either Equation Y-
1a or Y-1b to calculate flare CO2 emissions. Reporters
that either do not measure the composition of flare gas or conduct
such measurements but less frequently than weekly may use Equation
Y-3, which does not require such values to calculate routine flare
gas emissions. As a result, requiring reporters to report annual
averages of molecular weight and carbon content when using Equation
Y-3 would undermine the purpose of Equation Y-3 by requiring
facilities that do not currently measure these values to now have to
determine and report these values. These facilities would now have
to conduct such measurements or provide the values through other
means. In the case where reporters do not measure these values, they
would likely report the values determined for the subset of flare
emissions related to SSM events, which would not be representative
of the annual average, and therefore would not be useful for
verification. As a result, the EPA is not finalizing the proposed
reporting of the annual average molecular weight of flare gas
combusted and annual average carbon content of flare gas combusted,
both for normal operations and SSM events combined. Further, given
that the three proposed data elements were to be used together to
provide an alternative method of estimating emissions, requiring
reporting of the annual quantity of flare gas combusted would not be
useful in the absence of the other two data elements. The EPA is
therefore not requiring the reporting of these three data elements
in the final rule and will continue to rely on the general IVT
verification approach for verifying flare CO2 emissions
using Equation Y-3.
3. Summary of Comments and Responses
This section summarizes the significant comments and responses
related to the proposed addition of new reporting requirements for
facilities required to use IVT. See the EPA's comment response document
in Docket ID No. EPA-HQ-OAR-2010-0929 for a complete listing of all
comments and responses related to this topic.
Comment: One commenter suggested that the amount of cyclohexanone
and cyclohexanol combined (also called ketone-alcohol oil or (KA) used
to manufacture adipic acid should be substituted for cyclohexane for
the verification of N2O emissions from adipic acid
manufacturing. The commenter indicated that they use an EPA-approved
alternate method, as allowed under 40 CFR 98.53(a)(2) to report
N2O emissions, and the proposed new data element would not
fairly represent emissions from their manufacturing facility. The
commenter explained that the EPA is assuming that adipic acid is
manufactured wholly via the oxidation of cyclohexane to KA, which is
then further oxidized with nitric acid to adipic acid. The commenter
stated that this assumes that all the KA used in the nitric acid
oxidation comes from cyclohexane oxidation and all the KA produced is
used to produce adipic acid. However, the commenter stated that, in
reality, KA can be purchased or sold commercially as well as produced
using materials other than cyclohexane. The commenter noted that they
operate an alternate process to produce KA in addition to the
cyclohexane-based KA production.
Response: The EPA agrees with the commenter that the proposed new
data element for subpart E (i.e., 40 CFR 98.56(m), the annual quantity
of cyclohexane fed to all production lines, combined) will be useful to
the EPA for verification purposes for only those reporters that are
producing all adipic acid from cyclohexane. At proposal, the EPA had
assumed that all KA used to produce adipic acid was produced by the
reporting facility using cyclohexane. Based on this commenter input and
further consideration, the EPA has determined that there are cases
where either the KA used by the reporting facility to create adipic
acid is purchased from another KA producer or the reporting facility
uses materials other than cyclohexane to produce KA (such as the
facility represented by the commenter). In a case where the KA used by
the reporting facility to create adipic acid is purchased from another
KA producer, the reporting facility may not know whether and how much
cyclohexane was used to produce the KA. Likewise, in cases where the
reporting facility uses materials other than cyclohexane to produce KA
(which may then be used to produce adipic acid), the reported annual
quantity of cyclohexane used to produce adipic acid would not be
applicable and, therefore, not useful to EPA for verification of
reported GHG emissions (representing all adipic acid produced) because
this quantity of cyclohexane would represent only part (or none, if no
cyclohexane is used) of the KA used to produce adipic acid. In cases
where a reporter is producing KA using materials other than
cyclohexane, or where a reporter is purchasing KA, the EPA has changed
the new data element to be the quantity of KA fed to adipic acid
production lines. In the final rule, the EPA has revised the new data
element to specify that if only cyclohexane is oxidized to produce
adipic acid, the reporter must report the annual quantity of
cyclohexane used to produce adipic acid; otherwise, the reporter must
report the annual quantity of KA used to produce adipic acid. Regarding
the comment that some adipic acid producers are selling some of the KA
produced, these adipic acid producers will be required to report a
corrected quantity of cyclohexane or KA, as applicable, used to produce
adipic acid to account for any KA sold. Regarding the comment that some
adipic acid producers purchase KA to produce adipic acid, these
reporters will be required to report the annual quantity of KA used to
produce adipic acid under 40 CFR 98.56(m)(2).
Comment: One commenter supported the reporting for two new data
elements proposed to be reported for subpart AA: (1) Quantity of
calcium oxide (CaO) produced (metric tons), and (2) percent of annual
heat input, individually for each fossil fuel type. The commenter
opposed the reporting of two other data
[[Page 63774]]
elements proposed to be reported for subpart AA for each chemical
recovery furnace and chemical recovery combustion unit for which
Equation C-2c of subpart C is not used to calculate CO2
emissions: (1) Annual mass of steam generated (pound (lb) steam),
individually for each fossil fuel type and for spent liquor solids, and
(2) Ratio of the unit's maximum rated heat input capacity to its design
rated steam output capacity (MMBtu/lb steam), individually for each
fossil fuel type and for spent liquor solids. The commenter contended
that these requirements are unclear and unnecessary and should be
removed from the final rule. The commenter asserted that these proposed
reporting requirements for pulp mills directly contradict the
requirement in 40 CFR 98.36(e)(2)(ii)(D) that requires stationary fuel
combustion units to report the steam and heat/steam ratio only if
Equation C-2c is used. Regarding recovery units not using Equation C-
2c, the commenter indicated that determining these two data elements
would be overly burdensome because determining steam generation by fuel
type would be very difficult. The commenter explained that most
recovery furnaces only use spent pulping liquor as their fuel and some
may use other fuels for either start-up or for flame stabilization,
but, generally, the fuels are liquid; and, other than using a percent
of fuel to estimate the amount of steam generation per fuel type, the
commenter did not know of any other method to determine the amount of
steam generation per fuel type. As such, the commenter requested that
these two proposed new data elements (annual mass of steam generated
and ratio of the unit's maximum rated heat input capacity to its design
rated steam output capacity) be eliminated in the final rule.
Response: The EPA thanks the commenter for their support for
reporting the quantity of CaO produced, and percent of annual heat
input, individually for each fossil fuel type. These two data elements
are added as proposed. Regarding the other two data elements (annual
mass of steam generated (lb steam), individually for each fossil fuel
type and for spent liquor solids, and ratio of the unit's maximum rated
heat input capacity to its design rated steam output capacity (MMBtu/lb
steam), individually for each fossil fuel type and for spent liquor
solids), the EPA included these new elements in the proposal to
supplement the IVT verification approach because having such
information would allow the EPA to verify and reconcile potential
differences between reported emissions and emissions equation results
calculated by IVT and therefore minimize the need for follow-up via
phone, email or on-site visit. However, as the EPA stated in the
proposal preamble (September 11, 2013), the proposal to collect these
two data elements was also based in part on the EPA's incorrect
assumption that the proposed new reporting elements would be readily
available for affected facilities, or easily calculated using data
already required to be collected. In light of the comment, and after
further investigation of the method available to reporters to calculate
steam generated by fuel type, the EPA has learned that generating these
two new data reporting elements would require a significant investment
in time. Upon further consideration, the EPA concludes that any
potential time saved from the reduced follow-up activities due to
collection of these two data elements is outweighed by the significant
resources and time required for the facilities to generate these data.
The EPA is therefore not requiring the reporting of these two data
elements in the final rule and will continue to rely on the general IVT
verification approach for verifying chemical recovery furnace and
chemical recovery combustion unit emissions. For the reasons stated
above, the EPA is not finalizing these two new data elements in this
final action.
III. Summary of Final Confidentiality Determinations for New Data
Elements
A. Summary of Final CBI Determinations
The EPA is finalizing the proposed data category assignment and
confidentiality determination for each new data element added in this
final rule \18\ except 40 CFR 98.226(q). For 40 CFR 98.226(q), the EPA
is finalizing the proposed data category assignment, but is not making
any final confidentiality determination. The EPA's rationale for this
change is provided in Section III.B of this preamble.
---------------------------------------------------------------------------
\18\ EPA is not finalizing the addition of all the data elements
proposed to be added to the rule. Five data elements are not being
added to the rule. The EPA's rationale for this change is provided
in Section III.B of this preamble.
---------------------------------------------------------------------------
For the 16 new data elements listed in Table 5 of this preamble,
the EPA has determined that they are entitled to confidential
treatment, as proposed. Specifically, the EPA is finalizing the
proposed category assignments of these data elements to the
``Production/Throughput Data that are Not Inputs to Emission
Equations'' and ``Raw Materials Consumed that are Not Inputs to
Emission Equations'' data categories and the application of the
categorical confidentiality determinations made for these categories in
the 2011 final CBI rule (76 FR 30782, May 26, 2011) to these data
elements.
Table 5--Data Elements Assigned to the ``Production/Throughput Data That Are Not Inputs to Emission Equations''
and ``Raw Materials Consumed That Are Not Inputs to Emission Equations'' Data Categories
----------------------------------------------------------------------------------------------------------------
Subpart Final citation Data element
----------------------------------------------------------------------------------------------------------------
``Production/Throughput Data That Are Not Inputs to Emission Equations'' Data Category
----------------------------------------------------------------------------------------------------------------
G--Ammonia Production................... 40 CFR 98.76(b)(14)........ Annual ammonia production (metric tons,
sum of all process lines reported within
subpart G).
40 CFR 98.76(b)(15)........ Annual methanol production (metric tons)
for each process unit.
H--Cement Kilns......................... 40 CFR 98.86(b)(16)........ Annual clinker production (metric tons).
P--Hydrogen Production.................. 40 CFR 98.166(e)........... Annual methanol production (metric tons)
for each process unit.
S--Lime Manufacturing................... 40 CFR 98.196(b)(18)....... Annual quantity (tons) of lime product
sold, by type.
X--Petrochemical........................ 40 CFR 98.246(a)(13) and If using the CEMS method to calculate GHG
(b)(10). emissions: Name and annual quantity (in
metric tons) of each product. If using
the mass balance method to calculate GHG
emissions: Name and annual quantity (in
metric tons) of each product used in
Equations X-1, X-2, and X-3 of subpart
X.
[[Page 63775]]
AA--Pulp and Paper...................... 40 CFR 98.276(l)(1)........ For each pulp mill lime kiln: Quantity of
calcium oxide (CaO) produced (metric
tons).
----------------------------------------------------------------------------------------------------------------
``Raw Materials Consumed That Are Not Inputs to Emission Equations'' Data Category
----------------------------------------------------------------------------------------------------------------
E--Adipic Acid Production............... 40 CFR 98.56(m)............ If only cyclohexane is oxidized to
produce adipic acid, report the annual
quantity of cyclohexane (tons) used to
produce adipic acid. If materials other
than cyclohexane are oxidized to produce
adipic acid, report the annual quantity
of cyclohexanone and cyclohexanol
mixture (tons) used to produce adipic
acid.
P--Hydrogen Production.................. 40 CFR 98.166(b)(7)........ Name and annual quantity (metric tons) of
each carbon-containing fuel and
feedstock.
Q--Iron and Steel....................... 40 CFR 98.176(e)(6)(i)..... If you use the carbon mass balance method
in 40 CFR 98.173(b)(1) to determine CO2
emissions: The annual mass (metric tons)
of all gaseous, liquid, and solid fuels
(combined) used in process units
specified in Equations Q-1 through Q-7,
calculated as specified in a new
Equation Q-9 of subpart Q in the final
rule amendments. Does not include fuel
used in a stationary combustion unit
where emissions are reported under
subpart C.
40 CFR 98.176(e)(6)(ii).... If you use the carbon mass balance method
in 40 CFR 98.173(b)(1) to determine CO2
emissions: The annual mass (metric tons)
of all non-fuel material inputs
(combined) specified in Equations Q-1
through Q-7 of subpart Q, calculated as
specified in a new Equation Q-10 of
subpart Q in the final rule amendments.
40 CFR 98.176(e)(6)(iii)... If you use the carbon mass balance method
in 40 CFR 98.173(b)(1) to determine CO2
emissions: The annual mass (metric tons)
of all solid and liquid products and
byproducts (combined) specified in
Equations Q-1 through Q-7, calculated as
specified in a new Equation Q-11 of
subpart Q in the final rule amendments.
40 CFR 98.176(e)(6)(iv).... If you use the carbon mass balance method
in 40 CFR 98.173(b)(1) to determine CO2
emissions: The weighted average carbon
content of all gaseous, liquid, and
solid fuels (combined) included in
Equation Q-9 of subpart Q, calculated as
specified in a new Equation Q-12 of
subpart Q in the final rule amendments.
40 CFR 98.176(e)(6)(v)..... If you use the carbon mass balance method
in 40 CFR 98.173(b)(1) to determine CO2
emissions: The weighted average carbon
content of all non-fuel inputs to all
furnaces (combined) included in Equation
Q-10 of subpart Q, calculated as
specified in a new Equation Q-13 of
subpart Q in the final rule amendments.
40 CFR 98.176(e)(6)(vi).... If you use the carbon mass balance method
in 40 CFR 98.173(b)(1) to determine CO2
emissions: The weighted average carbon
content of all solid and liquid products
and byproducts from all furnaces
(combined) included in a new Equation Q-
11 of subpart Q in the final rule
amendments, calculated as specified in
new Equation Q-14 of subpart Q in the
final rule amendments.
X--Petrochemical........................ 40 CFR 98.246(a)(12) and If using the CEMS method to calculate GHG
(b)(9). emissions: Name and annual quantity (in
metric tons) of each carbon-containing
feedstock. If using the mass balance
method to calculate GHG emissions: Name
and annual quantity (in metric tons) of
each carbon-containing feedstock used in
Equations X-1, X-2, and X-3 of subpart
X.
----------------------------------------------------------------------------------------------------------------
The five new data elements listed below in Table 6 of this preamble
were proposed to be assigned to the ``Unit Process Operating
Characteristics that are Not Inputs to Emission Equations'' category,
for which EPA has not established a categorical confidentiality
determination. Individual confidentiality determinations were proposed
for these data elements, which are shown in Table 6 below. In this
action, the EPA is finalizing the categorical assignments and
confidentiality determinations for four of the five new data elements
listed in Table 6, as proposed. The EPA revised the confidentiality
determination for the new data element in subpart V, as shown in Table
6.
[[Page 63776]]
Table 6--Final Confidentiality Determinations for New Data Elements Assigned to the ``Unit/Process Operating
Characteristics That Are Not Inputs to Emission Equations''
----------------------------------------------------------------------------------------------------------------
Final rationale for
Subpart Citation Data element Confidentiality confidentiality
determination determination
----------------------------------------------------------------------------------------------------------------
E--Adipic Acid Production..... 40 CFR 98.56(n). Annual percent N2O Not CBI......... The annual facility
emission reduction percent N2O
for all production reduction could not
units combined. be used to calculate
adipic acid
production. The
level of N2O
reductions varies by
the type of
abatement
technology, the
environment in which
the abatement
technology is
operating, the age
of the abatement
technology, the age
of the catalyst
used, and the
maintenance level of
the abatement
technology.
H--Cement Kilns............... 40 CFR Annual average CBI............. This data element
98.86(b)(17). clinker CO2 emission could be used to
factor for the back calculate a
facility, averaged facility's clinker
across all kilns production data,
(metric tons CO2/ which would result
metric ton clinker in competitive
produced). disadvantage.
40 CFR Annual average cement CBI............. This data element
98.86(b)(18). kiln dust (CKD) CO2 could provide
emission factor for information about
the facility, the efficiency of
averaged across all the operation, which
kilns (metric tons would result in
CO2/metric ton CKD competitive
produced). disadvantage.
V--Nitric Acid Production..... 40 CFR 98.226(q) Annual percent N2O ND \a\.......... Refer to Section
emission reduction III.B of this
for all nitric acid preamble for the
trains combined. rationale for this
determination.
AA--Pulp and Paper............ 40 CFR For each pulp mill Non-CBI......... Release of this data
98.276(l)(2). lime kiln: Percent would not result in
of annual heat competitive harm
input, individually because lime kiln
for each fossil fuel fossil fuel use as a
type. fraction of design
heat input was
reported to the EPA
as part of a 2011
ICR survey, and
facilities reporting
via the survey made
no CBI claims
regarding fuel type
and percent of
design heat input.
----------------------------------------------------------------------------------------------------------------
\a\ ND = No determination is being finalized.
B. Response to Public Comments
The EPA received several comments related to the proposed
confidentiality determinations for new data elements. Several
commenters provided support for the EPA's proposed confidentiality
determinations for new data elements proposed to be reported in
subparts G, H, S, P, Y, and AA. These comments may be found in the
EPA's comment response document in Docket ID No. EPA-HQ-OAR-2010-0929.
We received several comments questioning the proposed confidentiality
determination of several new data elements, including requests that the
data elements be treated as confidential, or that the confidentiality
be determined on a case-by-case basis, and summaries of these comments
and EPA's responses thereto are provided below. Additional comments and
the EPA's responses may be found in the comment response document noted
above.
Comment: One commenter provided comments on confidentiality
determinations for new data elements proposed for subpart V (Nitric
Acid Production). The commenter expressed support for the inclusion of
the data element ``annual percent nitrous oxide emissions reduction for
all production units combined'' (40 CFR 98.226(q)) in the ``Unit/
Process `Operating' Characteristics That Are Not Inputs to Emission
Equations'' data category. However, the commenter disagreed with the
EPA's proposed determination that the data element is considered not
confidential. The commenter disagreed with the EPA's assertion that the
data could not be used to calculate nitric acid production for an
individual train because it is an aggregate number, stating that for
facility with only a single nitric acid train with N2O
abatement, this would not hold true. The commenter further asserted
that the EPA was incorrect to assume that the data are publicly
available through the voluntary Climate Action Reserve (CAR). The
commenter stated that although some industry members participate in the
CAR and release the information, several do not. The commenter
contested that it is inappropriate for the EPA to base part of its
decision on the voluntary reporting of some facilities. As an
alternative, the commenter requested that the EPA not make a
confidentiality determination for this data element as it has done for
other data elements and, instead, allow individual reporters to assert
CBI claims for the data element.
Response: The EPA agrees with the commenter that the annual percent
nitrous oxide emissions reduction for all production units combined is
not publicly available on an annual basis through the CAR for all
facilities reporting under this subpart, and notes that the EPA did not
indicate such was the case in the proposed rule. At proposal, the EPA
did not specifically consider the situation where a facility has only
one nitric acid train. After further investigation in response to the
comment received, the EPA agrees that, in cases where a facility has
only one nitric acid train with N2O, the data element
``annual percent nitrous oxide emissions reduction for all production
units combined'' (40 CFR 98.226(q)) could be used to calculate nitric
acid production. For facilities with only one nitric acid train with
N2O abatement, the reporting of annual percent
N2O emissions reductions, together with annual
N2O emissions from nitric acid
[[Page 63777]]
production (as required to be reported in 40 CFR 98.3(c)(4)), the
destruction efficiency (as required to be reported in 40 CFR
98.226(i)), and the abatement utilization factor (as required to be
reported in 40 CFR 98.226(j)), could be used to back-calculate the mass
of nitric acid produced. Further, the EPA cannot conclude that in
specific situations, if a facility adds a nitric acid train from one
year to the next, and the EPA publishes this data for the year that the
facility has two nitric acid trains, that data revealing the annual
percent nitrous oxide emissions reductions for all production units
combined could not be back-calculated or estimated for the previous
year (when the facility had one nitric acid train.)
However, if a facility reports this information to the CAR and it
is publicly available, the EPA sees no reason why the same data could
not be published through the Greenhouse Gas Reporting Program,
regardless of the number of nitric acid trains at the facility. In
light of the above, the EPA cannot make a confidentiality determination
that applies to all facilities required to report this data element.
Therefore, the EPA is not finalizing a confidentiality determination
for this data element. In Table 6 of this preamble, the determination
for this data element is designated as ``ND,'' which means that no
determination has been made. The EPA will make a confidentiality
determination for this data element on a case by case basis.
Comment: One commenter provided support for the confidentiality
determinations for three new data elements proposed in subpart Y:
Annual quantity of flare gas combusted (40 CFR 98.256(e)(11)(i));
annual average molecular weight of flare gas combusted (40 CFR
98.256(e)(11)(ii)); and annual average carbon content of flare gas
combusted (40 CFR 98.256(e)(11)(iii)). The three data elements, which
are only required when using Equation Y-3 of subpart Y, were assigned
to the ``Unit/Process `Operating' Characteristics that Are Not Inputs
to Emission Equations'' Data Category'' and were not classified as CBI
in the proposal. Another commenter disagreed with the EPA's
determination that these data are not confidential. The commenter
explained that the flared gases are process gases, and would reveal
characteristics of iron and steel processes. The commenter stated that
the data elements may reveal operating efficiency, provide information
that would allow competitors to infer production costs and process
characteristics, and enable them to gain a competitive advantage. The
commenter asserted that the data elements are CBI and must be
considered CBI in the final rule.
Response: The EPA proposed to collect these three data elements to
assist the EPA in verifying reported GHG emissions associated with
flaring gas when Equation Y-3 is used. The EPA is not finalizing the
reporting of these data elements. Refer to Section II.D.2 of this
preamble for further discussion of the EPA's rationale for this
decision.
IV. Impacts of the Final Rule
The EPA has determined that the cost associated with this final
action will be $438,000 in the first year of implementation and $55,000
in each subsequent year, as further summarized below. A full discussion
of the impacts may be found in the memorandum, ``Assessment of Cost
Impacts of 2015 Inputs Proposal--Revisions to Reporting, Recordkeeping,
and Verification Requirements Under the Greenhouse Gas Reporting
Program,'' August 2013, available in the EPA's Docket ID No. EPA-HQ-
OAR-2010-0929.
A. How were the costs of this final rule estimated?
1. Inputs Verification Tool
The data elements required to be used for calculating the annual
GHG emissions values, and the cost associated with collecting these
data elements, have not changed from the estimate made during the
original rulemaking process. The time associated with entry of these
inputs to emission equations into e-GGRT (including into the new IVT)
is expected to be equivalent to the time originally anticipated for
data entry. Prior to using IVT, as currently required, reporters must
use their own calculation tool (e.g., calculator, calculation software)
to calculate the annual GHG emissions values, using the same sets of
equations and entering the same data elements that they would enter
into the tool.
The EPA does recognize however that there may be some time
associated with learning the new procedures for IVT and we have
estimated a cost of approximately $67 per facility, or $383,000 for the
first year for all affected facilities. During their first session
using IVT, reporters would need to spend approximately one hour to
become familiar with how the tool operates within e-GGRT. The
requirement to use IVT would not result in any change in the respondent
activity of entering these data into e-GGRT. Once the reporter has
become familiar with the tool, the EPA does not anticipate any
additional burden. The cost includes technical, clerical, and
managerial labor hours. For further information about this cost
estimate, refer to the memorandum ``Assessment of Cost Impacts of 2015
Inputs Final Rule--Revisions to Reporting, Recordkeeping, and
Verification Requirements Under the Greenhouse Gas Reporting Program''
September 2014 and the supporting statement for the information
collection request, ``Supporting Statement, Environmental Protection
Agency: Revisions to Reporting and Recordkeeping Requirements, and
Final Confidentiality Determinations Under the Greenhouse Gas Reporting
Program, Office of Management and Budget (OMB) Control Number 2060-
0629, ICR Number 2300.12,'' both available in Docket ID No. EPA-HQ-OAR-
2010-0929.
2. New Data Elements
We are adding 21 new data elements that were not previously
required to be reported under Part 98 (see Section II.D of this
preamble for further discussion). These data elements must be reported
by facilities in certain subparts that are required to use IVT. Of
these 21 data elements, seven data elements are related to annual
production or raw material usage, which are collected by a facility as
a routine part of conducting business. For these data elements, we are
not requiring that reporters comply with specific data collection or
monitoring requirements beyond the methods commonly used for accounting
purposes. The other 14 data elements to be reported are calculated
values using data currently required to be collected to perform
emissions calculations. For all of these additional data elements, the
EPA has estimated a nominal additional cost to report the data element
and fulfill the recordkeeping requirements. The total costs associated
with reporting and recordkeeping for the 21 data elements in 9 subparts
is $55,000. These costs represent the cost for all affected facilities
in the first year.
B. Do the final confidentiality determinations change the impacts of
the final amendments?
The final confidentiality determinations for the new data elements
would not affect whether and how data are reported and, therefore,
would not impose any additional burden on sources. Whether a data
reporting element is determined to be CBI, not CBI, or emission data,
the reporting element is reported to the EPA through e-GGRT in the same
manner.
[[Page 63778]]
V. Statutory and Executive Order Reviews
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'' under the
terms of Executive Order 12866 (58 FR 51735, October 4, 1993) and is
therefore not subject to review under Executive Orders 12866 and 13563
(76 FR 3821, January 21, 2011).
B. Paperwork Reduction Act
The information collection requirements in this final rule have
been submitted for approval to the OMB under the Paperwork Reduction
Act, 44 U.S.C. 3501 et seq. The Information Collection Request (ICR)
document prepared by the EPA has been assigned EPA ICR number 2300.12.
The information collection requirements are not enforceable until OMB
approves them.
This action finalizes amendments to reporting and recordkeeping
requirements and verification procedures for the GHGRP. In addition,
the EPA is publishing confidentiality determinations for the new data
elements added in this action. The amendments to the reporting
requirements in the source category-specific subparts are not
anticipated to result in significant burden for reporters. The data
elements required to be reported are expected to be readily available
for affected facilities, or easily calculated using data already
required to be collected (e.g., a monthly value was previously reported
and an annual value is to be reported).
Impacts associated with the changes to the reporting requirements
in each subpart are detailed in the memorandum ``Assessment of Cost
Impacts of 2015 Inputs Final Rule--Revisions to Reporting,
Recordkeeping, and Verification Requirements under the Greenhouse Gas
Reporting Program,'' September 2014, (see Docket ID No. EPA-HQ-OAR-
2010-0929). Burden is defined at 5 CFR 1320.3(b).
An agency may not conduct or sponsor, and a person is not required
to respond to, a collection of information unless it displays a
currently valid OMB control number. The OMB control numbers for the
EPA's regulations in 40 CFR are listed in 40 CFR part 9. When this ICR
is approved by OMB, the Agency will publish a technical amendment to 40
CFR part 9 in the Federal Register to display the OMB control number
for the approved information collection requirements contained in this
final rule.
C. Regulatory Flexibility Act (RFA)
The RFA generally requires an agency to prepare a regulatory
flexibility analysis of any rule subject to notice and comment
rulemaking requirements under the Administrative Procedure Act or any
other statute unless the agency certifies that the rule will not have a
significant economic impact on a substantial number of small entities.
Small entities include small businesses, small organizations, and small
governmental jurisdictions.
For purposes of assessing the impacts of these final rule
amendments and confidentiality determinations on small entities, small
entity is defined as: (1) A small business as defined by the Small
Business Administration's (SBA) regulations at 13 CFR 121.201; (2) a
small governmental jurisdiction that is a government of a city, county,
town, school district or special district with a population of less
than 50,000; or (3) a small organization that is any not-for-profit
enterprise which is independently owned and operated and is not
dominant in its field. After considering the economic impacts of these
final amendments on small entities, I certify that this action will not
have a significant economic impact on a substantial number of small
entities. The small entities directly regulated by these final rule
amendments include small businesses across all sectors of the economy
encompassed by Part 98, small governmental jurisdictions, and small
non-profits. We have determined that these facilities will experience
impacts of roughly a first-year cost of $67 per facility for learning
new procedures for the verification tool and an annual cost of $93 per
facility for the recordkeeping and reporting of 21 new data elements.
Although these final rule amendments will not have a significant
economic impact on a substantial number of small entities, the EPA
nonetheless has tried to reduce the impact of this rule on small
entities. The EPA supports a ``help desk'' for the GHGRP, which will be
available to answer questions on the provisions in this final
rulemaking.
D. Unfunded Mandates Reform Act (UMRA)
The final amendments and confidentiality determinations do not
contain a Federal mandate that may result in expenditures of $100
million or more for State, local, and tribal governments, in the
aggregate, or the private sector in any one year. This action finalizes
the following requirements: (1) Requirements for certain reporters
under 23 subparts to use an EPA-provided IVT instead of reporting
certain data elements for which disclosure concerns have been
identified, (2) lengthening the record retention time for reporters
required to use IVT, and (3) new data elements to be reported for
certain reporters using IVT and confidentiality determinations for
these new data element. As discussed in Section IV of this preamble,
for the first year, the total collective impact on regulated entities
is (1) $383,000, or $67 per entity, for using IVT; and (2) $55,000, or
$93 per entity, for the final new data elements to be reported. Thus,
the final amendments and confidentiality determinations are not subject
to the requirements of sections 202 or 205 of UMRA.
This final rule is also not subject to the requirements of section
203 of UMRA because it contains no regulatory requirements that might
significantly or uniquely affect small governments. This action amends
reporting and recordkeeping requirements and verification procedures
for certain reporters in the GHGRP. In addition, the EPA is finalizing
confidentiality determinations for the new data elements added in this
action. As discussed in Section IV of this preamble, the total
collective impact on regulated entities is $438,000 in the first year,
and $55,000 annually thereafter. Because this impact on each individual
facility is estimated to be approximately $67-$160 in the first year
and $93 annually thereafter, the EPA has determined that the provisions
in this action will not significantly impact small governments. In
addition, because none of the provisions apply specifically to small
governments, the EPA has determined that the provisions in this action
will not uniquely impact small governments. Therefore, this action is
not subject to the requirements of section 203 of the UMRA.
E. Executive Order 13132: Federalism
The final rule 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,
as specified in Executive Order 13132. The final amendments and
confidentiality determinations apply to facilities that directly emit
greenhouses gases and fuel and chemicals suppliers. These changes do
not apply to governmental entities unless the government entity owns a
facility that directly emits GHGs above threshold levels (such as a
large
[[Page 63779]]
stationary combustion device), so relatively few government facilities
will be affected. Moreover, for government facilities that are subject
to the rule, the final revisions will not have a significant cost
impact. This final rule also does not limit the power of States or
localities to collect GHG data and/or regulate GHG emissions. Thus,
Executive Order 13132 does not apply to this rule.
F. Executive Order 13175: Consultation and Coordination With Indian
Tribal Governments
This final rule does not have tribal implications, as specified in
Executive Order 13175 (65 FR 67249, November 9, 2000). The final
amendments and confidentiality determinations apply directly to
facilities that directly emit GHGs or that are suppliers of GHGs. They
will not have tribal implications unless the tribal entity owns a
facility that directly emits GHGs above threshold levels (such as a
landfill or large combustion device). Relatively few tribal facilities
would be affected. Thus, Executive Order 13175 does not apply to this
action.
G. Executive Order 13045: Protection of Children From Environmental
Health Risks and Safety Risks
The EPA interprets Executive Order 13045 (62 FR 19885, April 23,
1997) as applying only to those regulatory actions that concern health
or safety risks, such that the analysis required under section 5-501 of
the Executive Order has the potential to influence the regulation. This
final rule is not subject to Executive Order 13045 because it does not
establish an environmental standard intended to mitigate health or
safety risks.
H. Executive Order 13211: Actions That Significantly Affect Energy
Supply, Distribution, or Use
This final rule is not a ``significant energy action'' as defined
in Executive Order 13211 (66 FR 28355, May 22, 2001), because it is not
likely to have a significant adverse effect on the supply,
distribution, or use of energy. Part 98 relates to monitoring,
reporting, and recordkeeping and does not impact energy supply,
distribution, or use. This final rule amends reporting and
recordkeeping requirements and verification procedures for the GHGRP.
In addition, the EPA is finalizing confidentiality determinations for
the new data elements added in this rulemaking. These final amendments
and confidentiality determinations do not make any changes to the
existing monitoring, recordkeeping, or reporting requirements under
Part 98 that affect the supply, distribution, or use of energy.
I. National Technology Transfer and Advancement Act
Section 12(d) of the National Technology Transfer and Advancement
Act of 1995 (NTTAA), Public Law No. 104-113, 12(d) (15 U.S.C. 272 note)
directs the EPA to use voluntary consensus standards in its regulatory
activities unless to do so would be inconsistent with applicable law or
otherwise impractical. Voluntary consensus standards are technical
standards (e.g., materials specifications, test methods, sampling
procedures, and business practices) that are developed or adopted by
voluntary consensus standards bodies. NTTAA directs the EPA to provide
Congress, through the OMB, explanations when the Agency decides not to
use available and applicable voluntary consensus standards.
This final rulemaking does not involve any new technical standards.
Therefore, the EPA is not considering the use of any voluntary
consensus standards.
J. Executive Order 12898: Federal Actions To Address Environmental
Justice in Minority Populations and Low-Income Populations
Executive Order 12898 (59 FR 7629, February 16, 1994) establishes
Federal executive policy on environmental justice. Its main provision
directs Federal agencies, to the greatest extent practicable and
permitted by law, to make environmental justice part of their mission
by identifying and addressing, as appropriate, disproportionately high
and adverse human health or environmental effects of their programs,
policies, and activities on minority populations and low-income
populations in the United States.
The EPA has determined that these final rule amendments and
confidentiality determinations will not have disproportionately high
and adverse human health or environmental effects on minority or low-
income populations because the amendments do not affect the level of
protection provided to human health or the environment. This is because
the final amendments address information collection and reporting and
verification procedures.
K. Congressional Review Act
The Congressional Review Act, 5 U.S.C. 801 et seq., as added by the
Small Business Regulatory Enforcement Fairness Act of 1996, generally
provides that before a rule may take effect, the agency promulgating
the rule must submit a rule report, which includes a copy of the rule,
to each House of the Congress and to the Comptroller General of the
United States. The EPA will submit a report containing this rule and
other required information to the U.S. Senate, the U.S. House of
Representatives, and the Comptroller General of the United States prior
to publication of the rule in the Federal Register. A major rule cannot
take effect until 60 days after it is published in the Federal
Register. This action is not a ``major rule'' as defined by 5 U.S.C.
804(2). This rule will be effective on November 24, 2014.
List of Subjects 40 CFR Part 98
Environmental protection, Administrative practice and procedure,
Greenhouse gases, Reporting and recordkeeping requirements.
Dated: September 26, 2014.
Gina McCarthy,
Administrator.
For the reasons stated in the preamble, the Environmental
Protection Agency amends title 40, chapter I, of the Code of Federal
Regulations as follows:
PART 98--MANDATORY GREENHOUSE GAS REPORTING
0
1. The authority citation for part 98 continues to read as follows:
Authority: 42 U.S.C. 7401, et seq.
Subpart A--General Provision
0
2. Section 98.3 is amended by revising paragraphs (c)(4)(vii),
(d)(3)(v), (g) introductory text, and (g)(2)(i) to read as follows:
Sec. 98.3 What are the general monitoring, reporting, recordkeeping
and verification requirements of this part?
* * * * *
(c) * * *
(4) * * *
(vii) The owner or operator of a facility is not required to report
the data elements specified in Table A-6 of this subpart for calendar
years 2010 through 2011 until March 31, 2013. The owner or operator of
a facility is not required to report the data elements specified in
Table A-7 of this subpart for calendar years 2010 through 2013 until
March 31, 2015 (as part of the annual report for reporting year 2014),
except as otherwise specified in Table A-7 of this subpart.
* * * * *
(d) * * *
(3) * * *
[[Page 63780]]
(v) For each stationary fuel combustion source that meets the
criteria specified in Sec. 98.36(f), report any facility operating
data or process information used for the GHG emission calculations. A
stationary fuel combustion source that does not meet the criteria
specified in Sec. 98.36(f) must either report the data specified in
this paragraph (d)(3)(v) in the annual report or use verification
software according to Sec. 98.5(b) in lieu of reporting the data
specified in this paragraph.
* * * * *
(g) Recordkeeping. An owner or operator that is required to report
GHGs under this part must keep records as specified in this paragraph
(g). Except as otherwise provided in this paragraph, retain all
required records for at least 3 years from the date of submission of
the annual GHG report for the reporting year in which the record was
generated. The records shall be kept in an electronic or hard-copy
format (as appropriate) and recorded in a form that is suitable for
expeditious inspection and review. If the owner or operator of a
facility is required under Sec. 98.5(b) to use verification software
specified by the Administrator, then all records required for the
facility under this part must be retained for at least 5 years from the
date of submission of the annual GHG report for the reporting year in
which the record was generated, starting with records for reporting
year 2010. Upon request by the Administrator, the records required
under this section must be made available to EPA. Records may be
retained off site if the records are readily available for expeditious
inspection and review. For records that are electronically generated or
maintained, the equipment or software necessary to read the records
shall be made available, or, if requested by EPA, electronic records
shall be converted to paper documents. You must retain the following
records, in addition to those records prescribed in each applicable
subpart of this part:
* * * * *
(2) * * *
(i) The GHG emissions calculations and methods used. For data
required by Sec. 98.5(b) to be entered into verification software
specified in Sec. 98.5(b), maintain the entered data in the format
generated by the verification software according to Sec. 98.5(b).
* * * * *
0
3. Section 98.5 is revised to read as follows:
Sec. 98.5 How is the report submitted?
(a) Each GHG report and certificate of representation for a
facility or supplier must be submitted electronically in accordance
with the requirements of Sec. 98.4 and in a format specified by the
Administrator.
(b) For reporting year 2014 and thereafter, you must enter into
verification software specified by the Administrator the data specified
in the verification software records provision in each applicable
recordkeeping section. For each data element entered into the
verification software, if the software produces a warning message for
the data value and you elect not to revise the data value, you may
provide an explanation in the verification software of why the data
value is not being revised.
0
4. Table A-7 to Subpart A of Part 98 is revised to read as follows:
Table A-7 to Subpart A of Part 98--Data Elements That Are Inputs to
Emission Equations and for Which the Reporting Deadline Is March 31,
2015
------------------------------------------------------------------------
Specific data
elements for which
reporting date is
March 31, 2015
Rule citation (40 (``All'' means all
Subpart CFR part 98) data elements in the
cited paragraph are
not required to be
reported until March
31, 2015)
------------------------------------------------------------------------
A............................. 98.3(d)(3)(v).... All.\a\
C............................. 98.36(b)(9)(iii). Only estimate of the
heat input.\a\
C............................. 98.36(c)(2)(ix).. Only estimate of the
heat input from each
type of fuel listed
in Table C-2 of
subpart C of this
part.\a\
C............................. 98.36(e)(2)(i)... All.\a\
C............................. 98.36(e)(2)(ii)(A All.\a\
).
C............................. 98.36(e)(2)(ii)(C Only HHV value for
). each calendar month
in which HHV
determination is
required.\a\
C............................. 98.36(e)(2)(ii)(D All.\a\
).
C............................. 98.36(e)(2)(iv)(A All.\a\
).
C............................. 98.36(e)(2)(iv)(C All.\a\
).
C............................. 98.36(e)(2)(iv)(F All.\a\
).
C............................. 98.36(e)(2)(ix)(D All.\a\
).
C............................. 98.36(e)(2)(ix)(E All.\a\
).
C............................. 98.36(e)(2)(ix)(F All.\a\
).
E............................. 98.56(g)......... All.
E............................. 98.56(h)......... All.
E............................. 98.56(j)(4)...... All.
E............................. 98.56(j)(5)...... All.
E............................. 98.56(j)(6)...... All.
E............................. 98.56(l)......... All.
H............................. 98.86(b)(11)..... All.
H............................. 98.86(b)(13)..... Name of raw kiln feed
or raw material.
L............................. 98.126(b)(1)..... Only data used in
calculating the
absolute errors and
data used in
calculating the
relative errors.
L............................. 98.126(b)(2)..... All.
L............................. 98.126(b)(6)..... Only mass of each
fluorine-containing
reactant fed into
the process.
L............................. 98.126(b)(7)..... Only mass of each
fluorine-containing
product produced by
the process.
L............................. 98.126(b)(8)(i).. Only mass of each
fluorine-containing
product that is
removed from the
process and fed into
the destruction
device.
[[Page 63781]]
L............................. 98.126(b)(8)(ii). Only mass of each
fluorine-containing
by-product that is
removed from the
process and fed into
the destruction
device.
L............................. 98.126(b)(8)(iii) Only mass of each
fluorine-containing
reactant that is
removed from the
process and fed into
the destruction
device.
L............................. 98.126(b)(8)(iv). Only mass of each
fluorine-containing
by-product that is
removed from the
process and
recaptured.
L............................. 98.126(b)(8)(v).. All.
L............................. 98.126(b)(9)(i).. All.
L............................. 98.126(b)(9)(ii). All.
L............................. 98.126(b)(9)(iii) All.
L............................. 98.126(b)(10).... All.
L............................. 98.126(b)(11).... All.
L............................. 98.126(b)(12).... All.
L............................. 98.126(c)(1)..... Only quantity of the
process activity
used to estimate
emissions.
L............................. 98.126(c)(2)..... All.
L............................. 98.126(d)........ Only estimate of
missing data.
L............................. 98.126(f)(1)..... All.
L............................. 98.126(g)(1)..... All.
L............................. 98.126(h)(2)..... All.
O............................. 98.156(d)(2)..... All.
O............................. 98.156(d)(3)..... All.
O............................. 98.156(d)(4)..... All.
Q............................. 98.176(f)(1)..... All.
W............................. 98.236(c)(1)(i).. All.
W............................. 98.236(c)(1)(ii). All.
W............................. 98.236(c)(1)(iii) All.
W............................. 98.236(c)(2)(i).. All.
W............................. 98.236(c)(3)(i).. All.
W............................. 98.236(c)(3)(ii). Only Calculation
Methodology 2 of
Sec. 98.233(d).
W............................. 98.236(c)(3)(iii) All.
W............................. 98.236(c)(3)(iv). All.
W............................. 98.236(c)(4)(i)(A All.
).
W............................. 98.236(c)(4)(i)(B All.
).
W............................. 98.236(c)(4)(i)(C All.
).
W............................. 98.236(c)(4)(i)(D All.
).
W............................. 98.236(c)(4)(i)(E All.
).
W............................. 98.236(c)(4)(i)(F All.
).
W............................. 98.236(c)(4)(i)(G All.
).
W............................. 98.236(c)(4)(i)(H All.
).
W............................. 98.236(c)(4)(ii)( All.
A).
W............................. 98.236(c)(5)(i)(D All.
).
W............................. 98.236(c)(5)(ii)( All.
C).
W............................. 98.236(c)(6)(i)(B All.\b\
).
W............................. 98.236(c)(6)(i)(D All.\b\
).
W............................. 98.236(c)(6)(i)(E All.\b\
).
W............................. 98.236(c)(6)(i)(F All.\b\
).
W............................. 98.236(c)(6)(i)(G Only the amount of
). natural gas
required.
W............................. 98.236(c)(6)(i)(H Only the amount of
). natural gas
required.
W............................. 98.236(c)(6)(ii)( All.
A).
W............................. 98.236(c)(6)(ii)( All.
B).
W............................. 98.236(c)(7)(i)(A Only for Equation W-
). 14A of Sec.
98.233.
W............................. 98.236(c)(8)(i)(F All.\b\
).
W............................. 98.236(c)(8)(i)(K All.
).
W............................. 98.236(c)(8)(ii)( All.\b\
A).
W............................. 98.236(c)(8)(ii)( All.
H).
W............................. 98.236(c)(8)(iii) All.
(A).
W............................. 98.236(c)(8)(iii) All.
(B).
W............................. 98.236(c)(8)(iii) All.
(G).
W............................. 98.236(c)(12)(ii) All.
W............................. 98.236(c)(12)(v). All.
W............................. 98.236(c)(13)(i)( All.
E).
W............................. 98.236(c)(13)(i)( All.
F).
W............................. 98.236(c)(13)(ii) All.
(A).
W............................. 98.236(c)(13)(ii) All.
(B).
W............................. 98.236(c)(13)(iii All.
)(A).
W............................. 98.236(c)(13)(iii All.
)(B).
[[Page 63782]]
W............................. 98.236(c)(13)(v)( All.
A).
W............................. 98.236(c)(14)(i)( All.
B).
W............................. 98.236(c)(14)(ii) All.
(A).
W............................. 98.236(c)(14)(ii) All.
(B).
W............................. 98.236(c)(14)(iii All.
)(A).
W............................. 98.236(c)(14)(iii All.
)(B).
W............................. 98.236(c)(14)(v)( All.
A).
W............................. 98.236(c)(15)(ii) All.
(A).
W............................. 98.236(c)(15)(ii) All.
(B).
W............................. 98.236(c)(16)(vii All.
i).
W............................. 98.236(c)(16)(ix) All.
W............................. 98.236(c)(16)(x). All.
W............................. 98.236(c)(16)(xi) All.
W............................. 98.236(c)(16)(xii All.
).
W............................. 98.236(c)(16)(xii All.
i).
W............................. 98.236(c)(16)(xiv All.
).
W............................. 98.236(c)(16)(xv) All.
W............................. 98.236(c)(16)(xvi All.
).
W............................. 98.236(c)(17)(ii) All.
W............................. 98.236(c)(17)(iii All.
).
W............................. 98.236(c)(17)(iv) All.
W............................. 98.236(c)(18)(i). All.
W............................. 98.236(c)(18)(ii) All.
W............................. 98.236(c)(19)(iv) All.
W............................. 98.236(c)(19)(vii All.
).
Y............................. 98.256(h)(5)(i).. Only value of the
correction.
Y............................. 98.256(k)(4)..... Only mole fraction of
methane in coking
gas.
Y............................. 98.256(n)(3)..... All (if used in
Equation Y-21 of
Sec. 98.253 to
calculate emissions
from equipment
leaks).
Y............................. 98.256(o)(4)(vi). Only tank-specific
methane composition
data and gas
generation rate
data.
AA............................ 98.276(e)........ All.
CC............................ 98.296(b)(10)(i). All.
CC............................ 98.296(b)(10)(ii) All.
CC............................ 98.296(b)(10)(iii All.
).
CC............................ 98.296(b)(10)(iv) All.
CC............................ 98.296(b)(10)(v). All.
CC............................ 98.296(b)(10)(vi) All.
II............................ 98.356(d)(2)..... All (if conducting
weekly sampling).
II............................ 98.356(d)(3)..... All (if conducting
weekly sampling).
II............................ 98.356(d)(4)..... Only weekly average
temperature (if
conducting weekly
sampling).
II............................ 98.356(d)(5)..... Only weekly average
moisture content (if
conducting weekly
sampling).
II............................ 98.356(d)(6)..... Only weekly average
pressure (if
conducting weekly
sampling).
------------------------------------------------------------------------
\a\ Required to be reported only by: (1) Stationary fuel combustion
sources (e.g., individual units, aggregations of units, common pipes,
or common stacks) subject to subpart C of this part that contain at
least one combustion unit connected to a fuel-fired electric generator
owned or operated by an entity that is subject to regulation of
customer billing rates by the PUC (excluding generators connected to
combustion units subject to 40 CFR part 98, subpart D) and that are
located at a facility for which the sum of the nameplate capacities
for all such electric generators is greater than or equal to 1
megawatt electric output; and (2) stationary fuel combustion sources
(e.g., individual units, aggregations of units, common pipes, or
common stacks) subject to subpart C of this part that do not meet the
criteria in (1) of this footnote that elect to report these data
elements, as provided in Sec. 98.36(a), for reporting year 2014.
\b\ This rule citation provides an option to delay reporting of this
data element for certain wildcat wells and/or delineation wells.
Subpart C--General Stationary Fuel Combustion Sources
0
5. Section 98.36 is amended by:
0
a. Revising paragraph (a);
0
b. Revising paragraph (b)(9)(iii) and adding paragraph (b)(9)(iv);
0
c. Revising paragraphs (c)(2)(ix) and (x);
0
d. Revising paragraph (e)(2)(ii)(C) and adding paragraph (e)(2)(ii)(E);
and
0
e. Adding paragraph (f).
0
The revisions and additions read as follows:
Sec. 98.36 Data reporting requirements.
(a) In addition to the facility-level information required under
Sec. 98.3, the annual GHG emissions report shall contain the unit-
level or process-level data specified in paragraphs (b) through (f) of
this section, as applicable, for each stationary fuel combustion source
(e.g., individual unit, aggregation of units, common pipe, or common
stack) except as otherwise provided in this paragraph (a). For the data
specified in paragraphs (b)(9)(iii), (c)(2)(ix), (e)(2)(i),
(e)(2)(ii)(A), (e)(2)(ii)(C), (e)(2)(ii)(D), (e)(2)(iv)(A),
(e)(2)(iv)(C), (e)(2)(iv)(F), and (e)(2)(ix)(D) through (F) of this
section, the owner or operator of a stationary fuel combustion source
that does not meet the criteria specified in paragraph
[[Page 63783]]
(f) of this section may elect either to report the data specified in
this sentence in the annual report or to use verification software
according to Sec. 98.5(b) in lieu of reporting these data. If you
elect to use this verification software, you must use the verification
software according to Sec. 98.5(b) for all of these data that apply to
the stationary fuel combustion source.
(b) * * *
(9) * * *
(iii) An estimate of the heat input from each type of fuel listed
in Table C-2 of this subpart that was combusted in the unit during the
report year.
(iv) The annual CH4 and N2O emissions for
each type of fuel listed in Table C-2 of this subpart that was
combusted in the unit during the report year, expressed in metric tons
of each gas and in metric tons of CO2e.
* * * * *
(c) * * *
(2) * * *
(ix) An estimate of the heat input from each type of fuel listed in
Table C-2 of this subpart that was combusted in the units sharing the
common stack or duct during the report year.
(x) For each type of fuel listed in Table C-2 of this subpart that
was combusted during the report year in the units sharing the common
stack or duct during the report year, the annual CH4 and
N2O mass emissions from the units sharing the common stack
or duct, expressed in metric tons of each gas and in metric tons of
CO2e.
* * * * *
(e) * * *
(2) * * *
(ii) * * *
(C) The high heat values used in the CO2 emissions
calculations for each type of fuel combusted during the reporting year,
in mmBtu per short ton for solid fuels, mmBtu per gallon for liquid
fuels, and mmBtu per scf for gaseous fuels. Report a HHV value for each
calendar month in which HHV determination is required. If multiple
values are obtained in a given month, report the arithmetic average
value for the month.
* * * * *
(E) For each HHV used in the CO2 emissions calculations
for each type of fuel combusted during the reporting year, indicate
whether the HHV is a measured value or a substitute data value.
* * * * *
(f) Each stationary fuel combustion source (e.g., individual unit,
aggregation of units, common pipe, or common stack) subject to
reporting under paragraph (b) or (c) of this section must indicate if
both of the following two conditions are met:
(1) The stationary fuel combustion source contains at least one
combustion unit connected to a fuel-fired electric generator owned or
operated by an entity that is subject to regulation of customer billing
rates by the public utility commission (excluding generators that are
connected to combustion units that are subject to subpart D of this
part).
(2) The stationary fuel combustion source is located at a facility
for which the sum of the nameplate capacities for all electric
generators specified in paragraph (f)(1) of this section is greater
than or equal to 1 megawatt electric output.
0
6. Section 98.37 is revised to read as follows:
Sec. 98.37 Records that must be retained.
In addition to the requirements of Sec. 98.3(g), you must retain:
(a) The applicable records specified in Sec. Sec. 98.34(f) and
(g), 98.35(b), and 98.36(e).
(b) Verification software records. For each stationary fuel
combustion source that elects to use the verification software
specified in Sec. 98.5(b) rather than report data specified in
paragraphs (b)(9)(iii), (c)(2)(ix), (e)(2)(i), (e)(2)(ii)(A),
(e)(2)(ii)(C), (e)(2)(ii)(D), (e)(2)(iv)(A), (e)(2)(iv)(C),
(e)(2)(iv)(F), and (e)(2)(ix)(D) through (F) of this section, you must
keep a record of the file generated by the verification software for
the applicable data specified in paragraphs (b)(1) through (36) of this
section. Retention of this file satisfies the recordkeeping requirement
for the data in paragraphs (b)(1) through (36) of this section.
(1) Mass of each solid fuel combusted (tons/year) (Equation C-1 of
Sec. 98.33).
(2) Volume of each liquid fuel combusted (gallons/year) (Equation
C-1).
(3) Volume of each gaseous fuel combusted (scf/year) (Equation C-
1).
(4) Annual natural gas usage (therms/year) (Equation C-1a of Sec.
98.33).
(5) Annual natural gas usage (mmBtu/year) (Equation C-1b of Sec.
98.33).
(6) Mass of each solid fuel combusted (tons/year) (Equation C-2a of
Sec. 98.33).
(7) Volume of each liquid fuel combusted (gallons/year) (Equation
C-2a).
(8) Volume of each gaseous fuel combusted (scf/year) (Equation C-
2a).
(9) Measured high heat value of each solid fuel, for month (which
may be the arithmetic average of multiple determinations), or, if
applicable, an appropriate substitute data value (mmBtu per ton)
(Equation C-2b of Sec. 98.33).
(10) Measured high heat value of each liquid fuel, for month (which
may be the arithmetic average of multiple determinations), or, if
applicable, an appropriate substitute data value (mmBtu per gallons)
(Equation C-2b).
(11) Measured high heat value of each gaseous fuel, for month
(which may be the arithmetic average of multiple determinations), or,
if applicable, an appropriate substitute data value (mmBtu per scf)
(Equation C-2b).
(12) Mass of each solid fuel combusted during month (tons)
(Equation C-2b).
(13) Volume of each liquid fuel combusted during month (gallons)
(Equation C-2b).
(14) Volume of each gaseous fuel combusted during month (scf)
(Equation C-2b).
(15) Total mass of steam generated by municipal solid waste or each
solid fuel combustion during the reporting year (pounds steam)
(Equation C-2c of Sec. 98.33).
(16) Ratio of the boiler's maximum rated heat input capacity to its
design rated steam output capacity (MMBtu/pounds steam) (Equation C-
2c).
(17) Annual mass of each solid fuel combusted (short tons/year)
(Equation C-3 of Sec. 98.33).
(18) Annual average carbon content of each solid fuel (percent by
weight, expressed as a decimal fraction) (Equation C-3).
(19) Annual volume of each liquid fuel combusted (gallons/year)
(Equation C-4 of Sec. 98.33).
(20) Annual average carbon content of each liquid fuel (kg C per
gallon of fuel) (Equation C-4).
(21) Annual volume of each gaseous fuel combusted (scf/year)
(Equation C-5 of Sec. 98.33).
(22) Annual average carbon content of each gaseous fuel (kg C per
kg of fuel) (Equation C-5).
(23) Annual average molecular weight of each gaseous fuel (kg/kg-
mole) (Equation C-5).
(24) Molar volume conversion factor at standard conditions, as
defined in Sec. 98.6 (scf per kg-mole) (Equation C-5).
(25) Identify for each fuel if you will use the default high heat
value from Table C-1 of this subpart, or actual high heat value data
(Equation C-8 of Sec. 98.33).
(26) High heat value of each solid fuel (mmBtu/tons) (Equation C-
8).
(27) High heat value of each liquid fuel (mmBtu/gallon) (Equation
C-8).
(28) High heat value of each gaseous fuel (mmBtu/scf) (Equation C-
8).
[[Page 63784]]
(29) Cumulative annual heat input from combustion of each fuel
(mmBtu) (Equation C-10 of Sec. 98.33).
(30) Total quantity of each solid fossil fuel combusted in the
reporting year, as defined in Sec. 98.6 (pounds) (Equation C-13 of
Sec. 98.33).
(31) Total quantity of each liquid fossil fuel combusted in the
reporting year, as defined in Sec. 98.6 (gallons) (Equation C-13).
(32) Total quantity of each gaseous fossil fuel combusted in the
reporting year, as defined in Sec. 98.6 (scf) (Equation C-13).
(33) High heat value of the each solid fossil fuel (Btu/lb)
(Equation C-13).
(34) High heat value of the each liquid fossil fuel (Btu/gallons)
(Equation C-13).
(35) High heat value of the each gaseous fossil fuel (Btu/scf)
(Equation C-13).
(36) Fuel-specific carbon based F-factor per fuel (scf
CO2/mmBtu) (Equation C-13).
Subpart E--Adipic Acid Production
0
7. Section 98.56 is amended by:
0
a. Revising the introductory text;
0
b. Removing and reserving paragraphs (b), (c), and (j)(1) and (3); and
0
c. Adding paragraphs (m) and (n).
The revisions and additions read as follows:
Sec. 98.56 Data reporting requirements.
In addition to the information required by Sec. 98.3(c), each
annual report must contain the information specified in paragraphs (a)
through (n) of this section at the facility level.
* * * * *
(m) If only cyclohexane is oxidized to produce adipic acid and the
quantity is known, report the information specified in paragraph (m)(1)
of this section. If materials other than cyclohexane are oxidized to
produce adipic acid, report the information specified in paragraph
(m)(2) of this section.
(1) Annual quantity of cyclohexane (tons) used to produce adipic
acid.
(2) Annual quantity of cyclohexanone and cyclohexanol mixture
(tons) used to produce adipic acid.
(n) Annual percent N2O emission reduction for all
production units combined.
0
8. Section 98.57 is amended by revising the introductory text and
adding paragraph (i) to read as follows:
Sec. 98.57 Records that must be retained.
In addition to the information required by Sec. 98.3(g), you must
retain the records specified in paragraphs (a) through (i) of this
section at the facility level:
* * * * *
(i) Verification software records. You must keep a record of the
file generated by the verification software specified in Sec. 98.5(b)
for the applicable data specified in paragraphs (i)(1) through (3) of
this section. Retention of this file satisfies the recordkeeping
requirement for the data in paragraphs (i)(1) through (3) of this
section.
(1) Annual adipic acid production from each adipic acid production
unit (tons) (Equations E-2, E-3a, E-3b, E-3c, and E-3d of Sec. 98.53).
(2) Production rate per test run during the performance test for
each production unit test run (tons adipic acid produced/hr) (Equation
E-1 of Sec. 98.53).
(3) Annual adipic acid production per N2O abatement
technology during which N2O abatement technology was used
(tons adipic acid produced) (Equation E-2).
Subpart F--Aluminum Production
0
9. Section 98.66 is amended by:
0
a. Removing and reserving paragraphs (a) and (c)(2);
0
b. Revising paragraphs (c)(3), (e)(1), and (f)(1); and
0
c. Removing and reserving paragraph (g).
The revisions read as follows:
Sec. 98.66 Data reporting requirements.
* * * * *
(c) * * *
(3) The last date when the smelter-specific-slope coefficients (or
overvoltage emission factors) were measured.
* * * * *
(e) * * *
(1) Annual anode consumption if using the method in Sec. 98.63(g).
* * * * *
(f) * * *
(1) Annual paste consumption if using the method in Sec. 98.63(g).
* * * * *
0
10. Section 98.67 is amended by adding paragraph (i) to read as
follows:
Sec. 98.67 Records that must be retained.
* * * * *
(i) Verification software records. You must keep a record of the
file generated by the verification software specified in Sec. 98.5(b)
for the applicable data specified in paragraphs (i)(1) through (30) of
this section. Retention of this file satisfies the recordkeeping
requirement for the data in paragraphs (i)(1) through (30) of this
section.
(1) Slope coefficient per potline per month (kg CF4/
metric ton Al)/(AE-Mins/cell-day)) (Equation F-2 of Sec. 98.63).
(2) Anode effect minutes per cell-day per potline per month (AE-
Mins/cell-day) (Equation F-2).
(3) Anode effect frequency per potline per month (AE/
cell[hyphen]day) (Equation F-2).
(4) Anode effect duration per potline per month (minutes) (Equation
F-2).
(5) Metal production of aluminum per potline per month (metric
tons) (Equation F-2).
(6) Overvoltage emission factor per potline per month (kg CF4/
metric ton Al) (Equation F-3 of Sec. 98.63).
(7) Metal production of aluminum per potline per month (metric
tons) (Equation F-3).
(8) Weight fraction of C2F6/CF4 per potline
per month (kg C2F6/kg CF4) (Equation
F-4 of Sec. 98.63).
(9) Net annual prebaked anode consumption (metric tons C/metric
tons Al) (Equation F-5 of Sec. 98.63).
(10) Annual metal production of aluminum (metric tons) (Equation F-
5).
(11) Sulfur content in baked anode (weight percent) (Equation F-5).
(12) Ash content in baked anode (weight percent) (Equation F-5).
(13) Annual paste consumption (metric ton/metric ton Al) (Equation
F-6 of Sec. 98.63).
(14) Annual metal production of aluminum (metric tons) (Equation F-
6).
(15) Annual emissions of cyclohexane soluble matter (kg/metric ton
Al) (Equation F-6).
(16) Binder content of paste (weight percent) (Equation F-6).
(17) Sulfur content of pitch (weight percent) (Equation F-6).
(18) Ash content of pitch (weight percent) (Equation F-6).
(19) Hydrogen content of pitch (weight percent) (Equation F-6).
(20) Sulfur content in calcined coke (weight percent) (Equation F-
6).
(21) Ash content in calcined coke (weight percent) (Equation F-6).
(22) Carbon in skimmed dust from S[oslash]derberg cells (metric ton
C/metric ton Al) (Equation F-6).
(23) Initial weight of green anodes (metric tons) (Equation F-7 of
Sec. 98.63).
(24) Annual hydrogen content in green anodes (metric tons)
(Equation F-7).
(25) Annual baked anode production (metric tons) (Equation F-7).
(26) Annual waste tar collected (metric tons) (Equation F-7).
(27) Annual packing coke consumption (metric tons/metric ton baked
anode) (Equation F-8 of Sec. 98.63).
(28) Annual baked anode production (metric tons) (Equation F-8).
(29) Sulfur content in packing coke (weight percent) (Equation F-
8).
(30) Ash content in packing coke (weight percent) (Equation F-8).
[[Page 63785]]
Subpart G--Ammonia Manufacturing
0
11. Section 98.76 is amended by removing and reserving paragraphs
(b)(2) and (b)(7) through (11) and adding paragraphs (b)(14) and (15)
to read as follows:
Sec. 98.76 Data reporting requirements.
* * * * *
(b) * * *
(14) Annual ammonia production (metric tons, sum of all process
units reported within subpart G).
(15) Annual methanol production for each process unit (metric
tons).
0
12. Section 98.77 is amended by revising the introductory text and
adding paragraph (c) to read as follows:
Sec. 98.77 Records that must be retained.
In addition to the records required by Sec. 98.3(g), you must
retain the following records specified in paragraphs (a) through (c) of
this section for each ammonia manufacturing unit.
* * * * *
(c) Verification software records. You must keep a record of the
file generated by the verification software specified in Sec. 98.5(b)
for the applicable data specified in paragraphs (c)(1) through (7) of
this section. Retention of this file satisfies the recordkeeping
requirement for the data in paragraphs (c)(1) through (7) of this
section.
(1) Volume of each gaseous feedstock used in month (scf of
feedstock) (in Equation G-1 of Sec. 98.73).
(2) Carbon content of each gaseous feedstock, for month (kg C per
kg of feedstock) (in Equation G-1).
(3) Molecular weight of each gaseous feedstock per ammonia
manufacturing unit with gaseous feedstock (kg/kg-mole) (Equation G-1).
(4) Volume of each liquid feedstock used in month (gallons of
feedstock) (Equation G-2 of Sec. 98.73).
(5) Carbon content of each liquid feedstock, for month (kg C per
gallon of feedstock) (Equation G-2).
(6) Mass of each solid feedstock used in month (kg of feedstock)
(Equation G-3 of Sec. 98.73).
(7) Carbon content of each solid feedstock, for month (kg C per kg
of feedstock) (Equation G-3).
Subpart H--Cement Production
0
13. Section 98.86 is amended by:
0
a. Removing and reserving paragraphs (b)(2), (5), (6), (8), (10), and
(12);
0
b. Revising paragraphs (b)(13) and (15); and
0
c. Adding paragraphs (b)(16) through (18).
The revisions and additions read as follows:
Sec. 98.86 Data reporting requirements.
* * * * *
(b) * * *
(13) Name of raw kiln feed or raw material.
* * * * *
(15) Method used to determine the monthly clinker production from
each kiln.
(16) Annual clinker production (metric tons).
(17) Annual average clinker CO2 emission factor for the
facility, averaged across all kilns (metric tons CO2/metric
ton clinker produced).
(18) Annual average CKD CO2 emission factor for the
facility, averaged across all kilns (metric tons CO2/metric
ton CKD produced).
0
14. Section 98.87 is amended by adding paragraph (c) to read as
follows:
Sec. 98.87 Records that must be retained.
* * * * *
(c) Verification software records. You must keep a record of the
file generated by the verification software specified in Sec. 98.5(b)
for the applicable data specified in paragraphs (c)(1) through (17) of
this section. Retention of this file satisfies the recordkeeping
requirement for the data in paragraphs (c)(1) through (17) of this
section.
(1) Identify per kiln per month if clinker is measured directly, or
is calculated from raw feed (Equation H-2 of Sec. 98.83 and the method
in Sec. 98.84(d)).
(2) Quantity of raw kiln feed in month from kiln (tons) (Equation
H-2 and the method in Sec. 98.84(d)).
(3) Kiln-specific factor per kiln per month (ton clinker per ton
raw feed) (Equation H-2 and the method in Sec. 98.84(d)).
(4) Quantity of clinker produced in month from kiln (tons)
(Equation H-2 and the method in Sec. 98.84(d)).
(5) Cement kiln dust (CKD) not recycled to the kiln in quarter from
kiln (tons) (Equation H-2 and the method in Sec. 98.84(d)).
(6) Monthly total CaO content of clinker per kiln (weight fraction)
(Equation H-3 of Sec. 98.83).
(7) Monthly non-calcined CaO content of clinker per kiln (weight
fraction) (Equation H-3).
(8) Monthly total MgO content of clinker per kiln (weight fraction)
(Equation H-3).
(9) Monthly non-calcined MgO content of clinker per kiln (weight
fraction) (Equation H-3).
(10) Quarterly total CaO content of cement kiln dust not recycled
to each kiln (weight fraction) (Equation H-4 of Sec. 98.83).
(11) Quarterly non-calcined CaO content of cement kiln dust not
recycled to each kiln (weight fraction) (Equation H-4).
(12) Quarterly total MgO content of cement kiln dust not recycled
to each kiln (weight fraction) (Equation H-4).
(13) Quarterly non-calcined MgO content of cement kiln dust not
recycled to each kiln (weight fraction) (Equation H-4).
(14) The amount of each raw material consumed annually per kiln
(tons/yr (dry basis)) (Equation H-5 of Sec. 98.83).
(15) The amount of each raw kiln feed consumed annually per kiln
(tons/yr (dry basis)) (Equation H-5).
(16) Organic carbon content of each raw material per kiln, as
determined in Sec. 98.84(c). Default value is 0.002 weight fraction
(Equation H-5).
(17) Organic carbon content of combined raw kiln feed per kiln, as
determined in Sec. 98.84(c). Default value is 0.002 weight fraction
(Equation H-5).
Subpart K--Ferroalloy Production
0
15. Section 98.116 is amended by:
0
a. Revising paragraph (b).
0
b. Removing and reserving paragraphs (e)(4) and (5); and
0
c. Revising paragraph (e)(6).
The revisions read as follows:
Sec. 98.116 Data reporting requirements.
* * * * *
(b) If a CEMS is used to measure CO2 emissions, report
the annual production for each ferroalloy product identified in Sec.
98.110, from each EAF (tons).
* * * * *
(e) * * *
(6) List the method used for the determination of carbon content
for each material included for the calculation of annual process
CO2 emissions for each EAF (e.g., supplier provided
information, analyses of representative samples you collected).
* * * * *
0
16. Section 98.117 is amended by revising the introductory text and
adding paragraph (e) to read as follows:
Sec. 98.117 Records that must be retained.
In addition to the records required by Sec. 98.3(g), you must
retain the records specified in paragraphs (a) through (e) of this
section for each EAF, as applicable.
* * * * *
(e) Verification software records. You must keep a record of the
file generated by the verification software specified in Sec. 98.5(b)
for the applicable data specified in paragraphs (e)(1) through (13) of
this section. Retention of this file satisfies the recordkeeping
requirement for the data in paragraphs (e)(1) through (13) of this
section.
[[Page 63786]]
(1) Carbon content in reducing agent (percent by weight, expressed
as a decimal fraction) (Equation K-1 of Sec. 98.113).
(2) Annual mass of reducing agent fed, charged, or otherwise
introduced into the EAF (tons) (Equation K-1).
(3) Carbon content of carbon electrode (percent by weight,
expressed as a decimal fraction) (Equation K-1).
(4) Annual mass of carbon electrode consumed in the EAF (tons)
(Equation K-1).
(5) Carbon content in ore (percent by weight, expressed as a
decimal fraction) (Equation K-1).
(6) Annual mass of ore charged to the EAF (tons) (Equation K-1).
(7) Carbon content in flux material (percent by weight, expressed
as a decimal fraction) (Equation K-1).
(8) Annual mass of flux material fed, charged, or otherwise
introduced into the EAF to facilitate slag formation (tons) (Equation
K-1).
(9) Carbon content in alloy product (percent by weight, expressed
as a decimal fraction) (Equation K-1).
(10) Annual mass of alloy product produced/tapped in the EAF (tons)
(Equation K-1).
(11) Carbon content in non-product outgoing material (percent by
weight, expressed as a decimal fraction) (Equation K-1).
(12) Annual mass of non-product outgoing material removed from EAF
(tons) (Equation K-1).
(13) CH4 emission factor selected from Table K-1 of this
subpart for each product (kg of CH4 emissions/metric ton of
alloy product) (Equation K-3 of Sec. 98.113).
Subpart N--Glass Production
0
17. Section 98.146 is amended by revising paragraph (b)(2) and removing
and reserving paragraphs (b)(4) and (6) to read as follows:
Sec. 98.146 Data reporting requirements.
* * * * *
(b) * * *
(2) Annual quantity of each carbonate-based raw material charged
(tons) to all furnaces combined.
* * * * *
0
18. Section 98.147 is amended by revising the introductory text and
adding paragraph (d) to read as follows:
Sec. 98.147 Records that must be retained.
In addition to the information required by Sec. 98.3(g), you must
retain the records listed in paragraphs (a) through (d) of this
section.
* * * * *
(d) Verification software records. You must keep a record of the
file generated by the verification software specified in Sec. 98.5(b)
for the applicable data specified in paragraphs (d)(1) through (3) of
this section. Retention of this file satisfies the recordkeeping
requirement for the data in paragraphs (d)(1) through (3) of this
section.
(1) Annual average decimal mass fraction of carbonate-based mineral
in each carbonate-based raw material for each continuous glass melting
furnace (specify the default value, if used, or the value determined
according to Sec. 98.144) (percentage, expressed as a decimal)
(Equation N-1 of Sec. 98.143).
(2) Annual amount of each carbonate-based raw material charged to
each continuous glass melting furnace (tons) (Equation N-1).
(3) Decimal fraction of each calcination achieved for carbonate-
based raw material for each continuous glass melting furnace (specify
the default value, if used, or the value determined according to Sec.
98.144) (percentage, expressed as a decimal) (Equation N-1).
Subpart O--HCFC-22 Production and HFC-23 Destruction
0
19. Section 98.156 is amended by:
0
a. Removing and reserving paragraphs (a)(2), (a)(7) through (10), and
(b)(1) and (2);
0
b. Revising paragraph (d) introductory text; and
0
c. Removing and reserving paragraphs (d)(1) and (5) and (e)(1).
The revisions read as follows:
Sec. 98.156 Data reporting requirements.
* * * * *
(d) If the HFC-23 concentration measured pursuant to Sec.
98.154(l) is greater than that measured during the performance test
that is the basis for the destruction efficiency (DE), the facility
shall report the following:
* * * * *
0
20. Section 98.157 is amended by adding paragraph (c) to read as
follows:
Sec. 98.157 Records that must be retained.
* * * * *
(c) Verification software records. You must keep a record of the
file generated by the verification software specified in Sec. 98.5(b)
for the applicable data specified in paragraphs (c)(1) through (16) of
this section. Retention of this file satisfies the recordkeeping
requirement for the data in paragraphs (c)(1) through (16) of this
section.
(1) Factor to account for the loss of HCFC-22 upstream of the
measurement over the period, determined pursuant to Sec. 98.154(e)
(Equation O-3 of Sec. 98.153).
(2) Mass of HCFC-22 that is measured coming out of the production
process over the period. A period can be one year (kg) (Equation O-3).
(3) Mass of used HCFC-22 that is added to the production process
upstream of the output measurement over the period. A period can be one
year (kg) (Equation O-3).
(4) Mass of HFC-23 generated annually per HCFC-22 production
process (metric tons) (Equation O-4 of Sec. 98.153).
(5) Mass of HFC-23 sent off site for sale annually per HCFC-22
production process (metric tons) (Equation O-4).
(6) Mass of HFC-23 sent off site for destruction annually per HCFC-
22 production process (metric tons) (Equation O-4).
(7) Mass of HFC-23 destroyed on site per HCFC-22 production process
(metric tons) (Equation O-4).
(8) HFC-23 in storage at end of year per HCFC-22 production process
(metric tons) (Equation O-4).
(9) HFC-23 in storage at beginning of year per HCFC-22 production
process (metric tons) (Equation O-4).
(10) Mass of HFC-23 fed into each destruction device annually per
HCFC-22 production process (metric tons) (Equation O-9 of Sec. 98.153
and the calculation method in either Sec. 98.154(l)(1) or (2)).
(11) Identify if each destruction efficiency for each HCFC-22
production process is entered directly, or is calculated using Sec.
98.154(l)(1), or is calculated using Sec. 98.154(l)(2) (Equation O-9
and the calculation method in either Sec. 98.154(l)(1) or (2)).
(12) Destruction efficiency of each destruction device for each
HCFC-22 production process (decimal fraction) (Equation O-9 and the
calculation method in either Sec. 98.154(l)(1) or (2)).
(13) Volumetric flow rate at the inlet of each destruction device
for each HCFC-22 production process from previous test (kg/hr)
(Equation O-9 and the calculation method in either Sec. 98.154(l)(1)
or (2)).
(14) Volumetric flow rate at the inlet of destruction device during
test for each HCFC-22 production process (kg/hr) (Equation O-9 and the
calculation method in either Sec. 98.154(l)(1) or (2)).
(15) Concentration of HFC-23 at the inlet of destruction device for
each HCFC-22 production process from previous test (weight fraction)
(Equation O-9 and the calculation method in either Sec. 98.154(l)(1)
or (2)).
(16) Concentration of HFC-23 at the inlet of destruction device for
each HCFC-22 production process during test (weight fraction) (Equation
O-9 and the calculation method in either Sec. 98.154(l)(1) or (2)).
[[Page 63787]]
Subpart P--Hydrogen Production
0
21. Section 98.166 is amended by:
0
a. Revising the introductory text;
0
b. Removing and reserving paragraphs (b)(2), (5), and (6); and
0
c. Adding paragraphs (b)(7) and (e).
The revisions and additions read as follows:
Sec. 98.166 Data reporting requirements.
In addition to the information required by Sec. 98.3(c), each
annual report must contain the information specified in paragraphs (a)
or (b) of this section, as appropriate, and paragraphs (c) through (e)
of this section:
* * * * *
(b) * * *
(7) Name and annual quantity (metric tons) of each carbon-
containing fuel and feedstock.
* * * * *
(e) Annual methanol production (metric tons) for each process unit.
0
22. Section 98.167 is amended by revising the introductory text and
adding paragraph (e) to read as follows:
Sec. 98.167 Records that must be retained.
In addition to the information required by Sec. 98.3(g), you must
retain the records specified in paragraphs (a) through (e) of this
section for each hydrogen production facility.
* * * * *
(e) Verification software records. You must keep a record of the
file generated by the verification software specified in Sec. 98.5(b)
for the applicable data specified in paragraphs (e)(1) through (12) of
this section. Retention of this file satisfies the recordkeeping
requirement for the data in paragraphs (e)(1) through (12) of this
section.
(1) Indicate whether the monthly consumption of each gaseous fuel
or feedstock is measured as mass or volume (Equation P-1 of Sec.
98.163).
(2) Monthly volume of the gaseous fuel or feedstock (scf at
standard conditions of 68[emsp14][deg]F and atmospheric pressure)
(Equation P-1).
(3) Monthly mass of the gaseous fuel or feedstock (kg of fuel or
feedstock) (Equation P-1).
(4) Average monthly carbon content of the gaseous fuel or feedstock
(kg C per kg of fuel or feedstock) (Equation P-1).
(5) Average monthly molecular weight of the gaseous fuel or
feedstock (kg/kg-mole) (Equation P-1).
(6) Indicate whether the monthly consumption of each liquid fuel or
feedstock is measured as mass or volume (Equation P-2 of Sec. 98.163).
(7) Monthly volume of the liquid fuel or feedstock (gallons of fuel
or feedstock) (Equation P-2).
(8) Monthly mass of the liquid fuel or feedstock (kg of fuel or
feedstock) (Equation P-2).
(9) Average monthly carbon content of the liquid fuel or feedstock
(kg C per gallon of fuel or feedstock) (Equation P-2).
(10) Average monthly carbon content of the liquid fuel or feedstock
(kg C per kg of fuel or feedstock) (Equation P-2).
(11) Monthly mass of solid fuel or feedstock (kg of fuel and
feedstock) (Equation P-3 of Sec. 98.163).
(12) Average monthly carbon content of the solid fuel or feedstock
(kg C per kg of fuel and feedstock) (Equation P-3).
Subpart Q--Iron and Steel Production
0
23. Section 98.176 is amended by:
0
a. Revising paragraph (b);
0
b. Removing and reserving paragraphs (e)(1), (3), and (4);
0
c. Adding paragraph (e)(6); and
0
c. Removing and reserving paragraphs (f)(2) through (4) and (g).
The revisions and additions read as follows:
Sec. 98.176 Data reporting requirements.
* * * * *
(b) If a CEMS is used to measure CO2 emissions, then you
must report the annual production quantity for the production unit (in
metric tons) for taconite pellets, coke, sinter, iron, and raw steel.
* * * * *
(e) * * *
(6) The information specified in paragraphs (e)(6)(i) through (vi)
of this section aggregated for all process units for which
CO2 emissions were determined using the mass balance method
in Sec. 98.173(b)(1), except as provided in Sec. 98.174(b)(4).
(i) The annual mass (metric tons) of all gaseous, liquid, and solid
fuels (combined) used in process units for which CO2
emissions were determined using Equations Q-1 through Q-7 of Sec.
98.173, calculated as specified in Equation Q-9 of this section.
[GRAPHIC] [TIFF OMITTED] TR24OC14.011
Where:
Fuel = Annual mass of all gaseous, liquid, and solid fuels used in
process units (metric tons).
n = Number of process units where fuel is used.
Fg,i = Annual volume of gaseous fuel combusted
(``(Fg)'' in Equations Q-1, Q-4 and Q-7 of Sec. 98.173)
for each process (scf).
MWi = Molecular weight of gaseous fuel used in each
process (kg/kg-mole).
MVC = Molar volume conversion factor at standard conditions, as
defined in Sec. 98.6. Use 849.5 scf per kg mole if you select
68[deg]F as standard temperature and 836.6 scf per kg mole if you
select 60[deg]F as standard temperature.
Fl,i = Annual volume of the liquid fuel combusted
(``(Fl)'' included in Equation Q-1) for each process unit
(gallons).
Fs,i = Annual mass of the solid fuel combusted
(``(Fs)'' in Equation Q-1) for each process unit (metric
tons).
[rho]l,i = Density of the liquid fuel (kg/gallon).
0.001 = Conversion factor from kg to metric tons.
(ii) The annual mass (metric tons) of all non-fuel material inputs
(combined) specified in Equations Q-1 through Q-7 of Sec. 98.173,
calculated as specified in Equation Q-10 of this section.
[GRAPHIC] [TIFF OMITTED] TR24OC14.012
Where:
NFI = Annual mass of all non-fuel inputs (to all process unit types)
specified in Equations Q-1 through Q-7 of Sec. 98.173 (metric
tons).
n = Number of process units, all process types.
O = Annual mass of greenball (taconite) pellets fed to the taconite
furnace(s) (metric tons).
Iron = Annual mass of molten iron charged to the basic oxygen
furnace(s) plus annual mass of direct reduced iron charged to the
EAF(s) (metric tons).
[[Page 63788]]
Scrap = Annual mass of ferrous scrap charged to the basic oxygen
furnace(s) and EAF(s) (metric tons).
Flux = Annual mass of flux materials charged to the basic oxygen
furnace(s) and EAF(s) (metric tons).
Carbon = Annual mass of carbonaceous materials (e.g., coal, coke)
charged to the basic oxygen furnace(s), EAF(s), and direct reduction
furnace(s) (metric tons).
Coal = Annual mass of coal charged to the coke oven battery(s)
(metric tons).
Feed = Annual mass of sinter feed material charged to the sinter
process(es) (metric tons).
Electrode = Annual mass of carbon electrode consumed in the EAF(s)
(metric tons).
Steelin = Annual mass of molten steel charged to the
decarburization vessels (metric tons).
Ore = Annual mass of iron ore or iron ore pellets fed to the direct
reduction furnace(s) (metric tons).
Other = Annual mass of other materials charged to the direction
reduction furnace(s) (metric tons).
(iii) The annual mass (metric tons) of all solid and liquid
products and byproducts (combined) specified in Equations Q-1 through
Q-7 of Sec. 98.173, calculated as specified in Equation Q-11 of this
section.
[GRAPHIC] [TIFF OMITTED] TR24OC14.013
Where:
Products = Annual mass of all solid and liquid products and by-
products (from all process units) specified in Equations Q-1 through
Q-7 of Sec. 98.173 (metric tons).
n = Number of process units, all types.
P = Annual mass of fired pellets produced by the taconite furnace
(metric tons).
R = Annual mass of air pollution control residue from all process
units (metric tons).
Steelout = Annual mass of steel produced by the basic
oxygen furnace(s), EAF(s) and decarburization vessel(s) (metric
tons).
Slag = Annual mass of slag produced by the basic oxygen furnace(s)
and EAF(s) (metric tons).
Coke = Annual mass of coke produced by the non-recovery coke
batteries (metric tons).
Sinter = Annual mass of sinter produced from the sinter process(es)
(metric tons).
Iron = Annual mass of iron produced from the direct reduction
furnace (metric tons).
NM = Annual mass of non-metallic materials produced by the direct
reduction furnace (metric tons).
(iv) The weighted average carbon content of all gaseous, liquid,
and solid fuels (combined) included in Equation Q-9 of this section,
calculated as specified in Equation Q-12 of this section.
[GRAPHIC] [TIFF OMITTED] TR24OC14.014
Where:
CFavg = Weighted average carbon content of all gaseous,
liquid, and solid fuels included in Equation Q-9 of this section
(weight fraction).
n = Number of gaseous, liquid, and solid fuel input to each process
unit as used in Equation Q-9.
Cgf,i = Average carbon content of the gaseous fuel used
in each process, from the fuel analysis results (kg C per kg of
fuel).
Clf,i = Carbon content of the liquid fuel used in each
process, from the fuel analysis results (kg C per gallon of fuel.
Csf = Carbon content of the solid fuel used in each
process, from the fuel analysis (expressed as a decimal fraction,
e.g., 95% = 0.95).
Fuel = Annual mass of all gaseous, liquid, and solid fuels used in
process units (metric tons), as calculated in Equation Q-9.
(v) The weighted average carbon content of all non-fuel inputs to
all process units (combined) included in Equation Q-10 of this section,
calculated as specified in Equation Q-13 of this section.
[GRAPHIC] [TIFF OMITTED] TR24OC14.015
Where:
CIavg = Weighted average carbon content of all non-fuel
inputs to all process units included in Equation Q-10 of this
section (weight fraction).
n = Number of non-fuel inputs to all process units as used in
Equation Q-10.
NFIi = Annual mass of each non-fuel input used in
Equation Q-10 (metric tons).
CNFIi = Average carbon content of each non-fuel input
used in Equation Q-10 (expressed as a decimal fraction).
NFI = Total of all non-fuel inputs to all process units (metric
tons).
(vi) The weighted average carbon content of all solid and liquid
products and byproducts from all process units (combined) included in
Equation Q-11 of this section, calculated as specified in Equation Q-14
of this section.
[GRAPHIC] [TIFF OMITTED] TR24OC14.016
Where:
CPavg = Weighted average carbon content of all solid and
liquid products and byproducts from all process units (weight
fraction).
n = Number of products and byproducts from each process unit as used
in Equation Q-11 of this section.
Producti = Annual mass of each product or byproduct used
in Equation Q-11 (metric tons).
Cp,i = Average carbon content of each product or
byproduct used in Equation Q-11 (expressed as a decimal fraction).
Products = Mass of all products and byproducts from all process
units, calculated in Equation Q-11 (metric tons).
* * * * *
0
24. Section 98.177 is amended by revising the introductory text and
adding paragraph (f) to read as follows:
[[Page 63789]]
Sec. 98.177 Records that must be retained.
In addition to the records required by Sec. 98.3(g), you must
retain the records specified in paragraphs (a) through (f) of this
section, as applicable. Facilities that use CEMS to measure emissions
must also retain records of the verification data required for the Tier
4 Calculating Methodology in Sec. 98.36(e).
* * * * *
(f) Verification software records. You must keep a record of the
file generated by the verification software specified in Sec. 98.5(b)
for the applicable data specified in paragraphs (f)(1) through (9) of
this section. Retention of this file satisfies the recordkeeping
requirement for the data in paragraphs (f)(1) through (9) of this
section.
(1) The data in paragraphs (f)(1)(i) through (xxv) of this section
for each applicable taconite indurating furnace for which the carbon
mass balance method of reporting is used.
(i) Annual mass of each solid fuel (metric tons) (Equation Q-1 of
Sec. 98.173).
(ii) Carbon content of each solid fuel, from the fuel analysis
(expressed as a decimal fraction) (Equation Q-1).
(iii) Annual volume of each gaseous fuel (scf) (Equation Q-1).
(iv) Average carbon content of each gaseous fuel, from the fuel
analysis results (kg C per kg of fuel) (Equation Q-1).
(v) Molecular weight of each gaseous fuel (kg/kg-mole) (Equation Q-
1).
(vi) Annual volume of each liquid fuel (gallons) (Equation Q-1).
(vii) Carbon content of each liquid fuel, from the fuel analysis
results (kg C per gallon of fuel) (Equation Q-1).
(viii) Annual mass of the greenball (taconite) pellets fed to the
furnace (metric tons) (Equation Q-1).
(ix) Carbon content of the greenball (taconite) pellets, from the
carbon analysis results (expressed as a decimal fraction) (Equation Q-
1).
(x) Annual mass of fired pellets produced by the furnace (metric
tons) (Equation Q-1).
(xi) Carbon content of the fired pellets, from the carbon analysis
results (expressed as a decimal fraction) (Equation Q-1).
(xii) Annual mass of air pollution control residue collected
(metric tons) (Equation Q-1).
(xiii) Carbon content of the air pollution control residue, from
the carbon analysis results (expressed as a decimal fraction) (Equation
Q-1).
(xiv) Annual mass of each other solid input containing carbon fed
to each furnace (metric tons) (Equation Q-1).
(xv) Carbon content of each other solid input containing carbon fed
to each furnace (expressed as a decimal fraction) (Equation Q-1).
(xvi) Annual mass of each other solid output containing carbon
produced by each furnace (metric tons) (Equation Q-1).
(xvii) Carbon content of each other solid output containing carbon
(expressed as a decimal fraction) (Equation Q-1).
(xviii) Annual mass of each other gaseous input containing carbon
fed to each furnace (metric tons) (Equation Q-1).
(xix) Carbon content of each other gaseous input containing carbon
fed to each furnace (expressed as a decimal fraction) (Equation Q-1).
(xx) Annual mass of each other gaseous output containing carbon
produced by each furnace (metric tons) (Equation Q-1).
(xxi) Carbon content of each other gaseous output containing carbon
produced by each furnace (expressed as a decimal fraction) (Equation Q-
1).
(xxii) Annual mass of each other liquid input containing carbon fed
to each furnace (metric tons) (Equation Q-1).
(xxiii) Carbon content of each other liquid input containing carbon
fed to each furnace (expressed as a decimal fraction) (Equation Q-1).
(xxiv) Annual mass of each other liquid output containing carbon
produced by each furnace (metric tons) (Equation Q-1).
(xxv) Carbon content of each other liquid output containing carbon
produced by each furnace (expressed as a decimal fraction) (Equation Q-
1).
(2) The data in paragraphs (f)(2)(i) through (xxvi) of this section
for each applicable basic oxygen process furnace for which the carbon
mass balance method of reporting is used.
(i) Annual mass of molten iron charged to the furnace (metric tons)
(Equation Q-2 of Sec. 98.173).
(ii) Carbon content of the molten iron charged to the furnace, from
the carbon analysis results (expressed as a decimal fraction) (Equation
Q-2).
(iii) Annual mass of ferrous scrap charged to the furnace (metric
tons) (Equation Q-2).
(iv) Carbon content of the ferrous scrap charged to the furnace,
from the carbon analysis results (expressed as a decimal fraction)
(Equation Q-2).
(v) Annual mass of the flux materials (e.g., limestone, dolomite)
charged to the furnace (metric tons) (Equation Q-2).
(vi) Carbon content of the flux materials charged to the furnace,
from the carbon analysis results (expressed as a decimal fraction)
(Equation Q-2).
(vii) Annual mass of the carbonaceous materials (e.g., coal, coke)
charged to the furnace (metric tons) (Equation Q-2).
(viii) Carbon content of the carbonaceous materials charged to the
furnace, from the carbon analysis results (expressed as a decimal
fraction) (Equation Q-2).
(ix) Annual mass of molten raw steel produced by the furnace
(metric tons) (Equation Q-2).
(x) Carbon content of the steel produced by the furnace, from the
carbon analysis results (expressed as a decimal fraction) (Equation Q-
2).
(xi) Annual mass of slag produced by the furnace (metric tons)
(Equation Q-2).
(xii) Carbon content of the slag produced by the furnace, from the
carbon analysis (expressed as a decimal fraction) (Equation Q-2).
(xiii) Annual mass of air pollution control residue collected for
the furnace (metric tons) (Equation Q-2).
(xiv) Carbon content of the air pollution control residue collected
for the furnace, from the carbon analysis results (expressed as a
decimal fraction) (Equation Q-2).
(xv) Annual mass of each other solid input containing carbon fed to
each furnace (metric tons) (Equation Q-2).
(xvi) Carbon content of each other solid input containing carbon
fed to each furnace (expressed as a decimal fraction) (Equation Q-2).
(xvii) Annual mass of each other solid output containing carbon
produced by each furnace (metric tons) (Equation Q-2).
(xviii) Carbon content of each other solid output containing carbon
(expressed as a decimal fraction) (Equation Q-2).
(xix) Annual mass of each other gaseous input containing carbon fed
to each furnace (metric tons) (Equation Q-2).
(xx) Carbon content of each other gaseous input containing carbon
fed to each furnace (expressed as a decimal fraction) (Equation Q-2).
(xxi) Annual mass of each other gaseous output containing carbon
produced by each furnace (metric tons) (Equation Q-2).
(xxii) Carbon content of each other gaseous output containing
carbon produced by each furnace (expressed as a decimal fraction)
(Equation Q-2).
(xxiii) Annual mass of each other liquid input containing carbon
fed to each furnace (metric tons) (Equation Q-2).
(xxiv) Carbon content of each other liquid input containing carbon
fed to each furnace (expressed as a decimal fraction) (Equation Q-2).
[[Page 63790]]
(xxv) Annual mass of each other liquid output containing carbon
produced by each furnace (metric tons) (Equation Q-2).
(xxvi) Carbon content of each other liquid output containing carbon
produced by each furnace (expressed as a decimal fraction) (Equation Q-
2).
(3) The data in paragraphs (f)(3)(i) through (xviii) of this
section for each applicable non-recovery coke oven battery for which
the carbon mass balance method of reporting is used.
(i) Annual mass of coal charged to the battery (metric tons)
(Equation Q-3 of Sec. 98.173).
(ii) Carbon content of the coal, from the carbon analysis results
(expressed as a decimal fraction) (Equation Q-3).
(iii) Annual mass of coke produced by the battery (metric tons)
(Equation Q-3).
(iv) Carbon content of the coke, from the carbon analysis results
(expressed as a decimal fraction) (Equation Q-3).
(v) Annual mass of air pollution control residue collected (metric
tons) (Equation Q-3).
(vi) Carbon content of the air pollution control residue, from the
carbon analysis results (expressed as a decimal fraction) (Equation Q-
3).
(vii) Annual mass of each other solid input containing carbon fed
to each battery (metric tons) (Equation Q-3).
(viii) Carbon content of each other solid input containing carbon
fed to each battery (expressed as a decimal fraction) (Equation Q-3).
(ix) Annual mass of each other solid output containing carbon
produced by each battery (metric tons) (Equation Q-3).
(x) Carbon content of each other solid output containing carbon
(expressed as a decimal fraction) (Equation Q-3).
(xi) Annual mass of each other gaseous input containing carbon fed
to each battery (metric tons) (Equation Q-3).
(xii) Carbon content of each other gaseous input containing carbon
fed to each battery (expressed as a decimal fraction) (Equation Q-3).
(xiii) Annual mass of each other gaseous output containing carbon
produced by each battery (metric tons) (Equation Q-3).
(xiv) Carbon content of each other gaseous output containing carbon
produced by each battery (expressed as a decimal fraction) (Equation Q-
3).
(xv) Annual mass of each other liquid input containing carbon fed
to each battery (metric tons) (Equation Q-3).
(xvi) Carbon content of each other liquid input containing carbon
fed to each battery (expressed as a decimal fraction) (Equation Q-3).
(xvii) Annual mass of each other liquid output containing carbon
produced by each battery (metric tons) (Equation Q-3).
(xviii) Carbon content of each other liquid output containing
carbon produced by each battery (expressed as a decimal fraction)
(Equation Q-3).
(4) The data in paragraphs (f)(4)(i) through (xxi) of this section
for each applicable sinter process for which the carbon mass balance
method of reporting is used.
(i) Annual volume of the gaseous fuel (scf) (Equation Q-4 of Sec.
98.173).
(ii) Carbon content of the gaseous fuel, from the fuel analysis
results (kg C per kg of fuel) (Equation Q-4).
(iii) Molecular weight of the gaseous fuel (kg/kg-mole) (Equation
Q-4).
(iv) Annual mass of sinter feed material (metric tons) (Equation Q-
4).
(v) Carbon content of the mixed sinter feed materials that form the
bed entering the sintering machine, from the carbon analysis results
(expressed as a decimal fraction) (Equation Q-4).
(vi) Annual mass of sinter produced (metric tons) (Equation Q-4).
(vii) Carbon content of the sinter pellets, from the carbon
analysis results (expressed as a decimal fraction) (Equation Q-4).
(viii) Annual mass of air pollution control residue collected
(metric tons) (Equation Q-4).
(ix) Carbon content of the air pollution control residue, from the
carbon analysis results (expressed as a decimal fraction) (Equation Q-
4).
(x) Annual mass of each other solid input containing carbon fed to
each sinter process (metric tons) (Equation Q-4).
(xi) Carbon content of each other solid input containing carbon fed
to each sinter process (expressed as a decimal fraction) (Equation Q-
4).
(xii) Annual mass of each other solid output containing carbon
produced by each sinter process (metric tons) (Equation Q-4).
(xiii) Carbon content of each other solid output containing carbon
(expressed as a decimal fraction) (Equation Q-4).
(xiv) Annual mass of each other gaseous input containing carbon fed
to each sinter process (metric tons) (Equation Q-4).
(xv) Carbon content of each other gaseous input containing carbon
fed to each sinter process (expressed as a decimal fraction) (Equation
Q-4).
(xvi) Annual mass of each other gaseous output containing carbon
produced by each sinter process (metric tons) (Equation Q-4).
(xvii) Carbon content of each other gaseous output containing
carbon produced by each sinter process (expressed as a decimal
fraction) (Equation Q-4).
(xviii) Annual mass of each other liquid input containing carbon
fed to each sinter process (metric tons) (Equation Q-4).
(xix) Carbon content of each other liquid input containing carbon
fed to each sinter process (expressed as a decimal fraction) (Equation
Q-4).
(xx) Annual mass of each other liquid output containing carbon
produced by each sinter process (metric tons) (Equation Q-4).
(xxi) Carbon content of each other liquid output containing carbon
produced by each sinter process (expressed as a decimal fraction)
(Equation Q-4).
(5) The data in paragraphs (f)(5)(i) through (xxxi) of this section
for each applicable electric arc furnace for which the carbon mass
balance method of reporting is used.
(i) Annual mass of direct reduced iron (if any) charged to the
furnace (metric tons) (Equation Q-5 of Sec. 98.173).
(ii) Carbon content of the direct reduced iron, from the carbon
analysis results (expressed as a decimal fraction) (Equation Q-5)
(iii) Annual mass of ferrous scrap charged to the furnace (metric
tons) (Equation Q-5).
(iv) Carbon content of the ferrous scrap, from the carbon analysis
results (expressed as a decimal fraction) (Equation Q-5).
(v) Annual mass of flux materials (e.g., limestone, dolomite)
charged to the furnace (metric tons) (Equation Q-5).
(vi) Carbon content of the flux materials, from the carbon analysis
results (expressed as a decimal fraction) (Equation Q-5).
(vii) Annual mass of carbon electrode consumed (metric tons)
(Equation Q-5).
(viii) Carbon content of the carbon electrode, from the carbon
analysis results (expressed as a decimal fraction) (Equation Q-5).
(ix) Annual mass of carbonaceous materials (e.g., coal, coke)
charged to the furnace (metric tons) (Equation Q-5).
(x) Carbon content of the carbonaceous materials, from the carbon
analysis results (expressed as a decimal fraction) (Equation Q-5).
(xi) Annual mass of molten raw steel produced by the furnace
(metric tons) (Equation Q-5).
(xii) Carbon content of the steel, from the carbon analysis results
(expressed as a decimal fraction) (Equation Q-5).
(xiii) Annual volume of the gaseous fuel (scf at 60F and 1 atm)
(Equation Q-5).
(xiv) Average carbon content of the gaseous fuel, from the fuel
analysis
[[Page 63791]]
results (kg C per kg of fuel) (Equation Q-5).
(xv) Molecular weight of the gaseous fuel (kg/kg-mole) (Equation Q-
5).
(xvi) Annual mass of slag produced by the furnace (metric tons)
(Equation Q-5).
(xvii) Carbon content of the slag, from the carbon analysis
(expressed as a decimal fraction) (Equation Q-5).
(xviii) Annual mass of air pollution control residue collected
(metric tons) (Equation Q-5).
(xix) Carbon content of the air pollution control residue, from the
carbon analysis results (expressed as a decimal fraction) (Equation Q-
5).
(xx) Annual mass of each other solid input containing carbon fed to
each furnace (metric tons) (Equation Q-5).
(xxi) Carbon content of each other solid input containing carbon
fed to each furnace (expressed as a decimal fraction) (Equation Q-5).
(xxii) Annual mass of each other solid output containing carbon
produced by each furnace (metric tons) (Equation Q-5).
(xxiii) Carbon content of each other solid output containing carbon
(expressed as a decimal fraction) (Equation Q-5).
(xxiv) Annual mass of each other gaseous input containing carbon
fed to each furnace (metric tons) (Equation Q-5).
(xxv) Carbon content of each other gaseous input containing carbon
fed to each furnace (expressed as a decimal fraction) (Equation Q-5).
(xxvi) Annual mass of each other gaseous output containing carbon
produced by each furnace (metric tons) (Equation Q-5).
(xxvii) Carbon content of each other gaseous output containing
carbon produced by each furnace (expressed as a decimal fraction)
(Equation Q-5).
(xxviii) Annual mass of each other liquid input containing carbon
fed to each furnace (metric tons) (Equation Q-5).
(xxix) Carbon content of each other liquid input containing carbon
fed to each furnace (expressed as a decimal fraction) (Equation Q-5).
(xxx) Annual mass of each other liquid output containing carbon
produced by each furnace (metric tons) (Equation Q-5).
(xxxi) Carbon content of each other liquid output containing carbon
produced by each furnace (expressed as a decimal fraction) (Equation Q-
5).
(6) The data in paragraphs (f)(6)(i) through (xvii) of this section
for each applicable decarburization vessel for which the carbon mass
balance method of reporting is used.
(i) Annual mass of molten steel charged to the vessel (metric tons)
(Equation Q-6 of Sec. 98.173).
(ii) Carbon content of the molten steel before decarburization,
from the carbon analysis results (expressed as a decimal fraction)
(Equation Q-6).
(iii) Carbon content of the molten steel after decarburization,
from the carbon analysis results (expressed as a decimal fraction)
(Equation Q-6).
(iv) Annual mass of air pollution control residue collected (metric
tons) (Equation Q-6).
(v) Carbon content of the air pollution control residue, from the
carbon analysis results (expressed as a decimal fraction) (Equation Q-
6).
(vi) Annual mass of each other solid input containing carbon fed to
each decarburization vessel (metric tons) (Equation Q-6).
(vii) Carbon content of each other solid input containing carbon
fed to each decarburization vessel (expressed as a decimal fraction)
(Equation Q-6).
(viii) Annual mass of each other solid output containing carbon
produced by each decarburization vessel (metric tons) (Equation Q-6).
(ix) Carbon content of each other solid output containing carbon
(expressed as a decimal fraction) (Equation Q-6).
(x) Annual mass of each other gaseous input containing carbon fed
to each decarburization vessel (metric tons) (Equation Q-6).
(xi) Carbon content of each other gaseous input containing carbon
fed to each decarburization vessel (expressed as a decimal fraction)
(Equation Q-6).
(xii) Annual mass of each other gaseous output containing carbon
produced by each decarburization vessel (metric tons) (Equation Q-6).
(xiii) Carbon content of each other gaseous output containing
carbon produced by each decarburization vessel (expressed as a decimal
fraction) (Equation Q-6).
(xiv) Annual mass of each other liquid input containing carbon fed
to each decarburization vessel (metric tons) (Equation Q-6).
(xv) Carbon content of each other liquid input containing carbon
fed to each decarburization vessel (expressed as a decimal fraction)
(Equation Q-6).
(xvi) Annual mass of each other liquid output containing carbon
produced by each decarburization vessel (metric tons) (Equation Q-6).
(xvii) Carbon content of each other liquid output containing carbon
produced by each decarburization vessel (expressed as a decimal
fraction) (Equation Q-6).
(7) The data in paragraphs (f)(7)(i) through (xxvii) of this
section for each applicable direct reduction furnace for which the
carbon mass balance method of reporting is used.
(i) Annual volume of the gaseous fuel (scf at 68F and 1 atm)
(Equation Q-7 of Sec. 98.173).
(ii) Average carbon content of the gaseous fuel, from the fuel
analysis results (kg C per kg of fuel) (Equation Q-7).
(iii) Molecular weight of the gaseous fuel (kg/kg-mole) (Equation
Q-7).
(iv) Annual mass of iron ore or iron pellets fed to the furnace
(metric tons) (Equation Q-7).
(v) Carbon content of the iron ore or iron pellets, from the carbon
analysis (expressed as a decimal fraction) (Equation Q-7).
(vi) Annual mass of carbonaceous materials (e.g., coal, coke)
charged to the furnace (metric tons) (Equation Q-7).
(vii) Carbon content of the carbonaceous materials, from the carbon
analysis results (expressed as a decimal fraction) (Equation Q-7).
(viii) Annual mass of each other material charged to the furnace
(metric tons) (Equation Q-7).
(ix) Average carbon content of each other material charged to the
furnace, from the carbon analysis results (expressed as a decimal
fraction) (Equation Q-7).
(x) Annual mass of iron produced (metric tons) (Equation Q-7).
(xi) Carbon content of the iron produced, from the carbon analysis
results (expressed as a decimal fraction) (Equation Q-7).
(xii) Annual mass of non-metallic materials produced by the furnace
(metric tons) (Equation Q-7).
(xiii) Carbon content of the non-metallic materials produced, from
the carbon analysis results (expressed as a decimal fraction) (Equation
Q-7).
(xiv) Annual mass of air pollution control residue collected
(metric tons) (Equation Q-7).
(xv) Carbon content of the air pollution control residue collected,
from the carbon analysis results (expressed as a decimal fraction)
(Equation Q-7).
(xvi) Annual mass of each other solid input containing carbon fed
to each furnace (metric tons) (Equation Q-7).
(xvii) Carbon content of each other solid input containing carbon
fed to each furnace (expressed as a decimal fraction) (Equation Q-7).
(xviii) Annual mass of each other solid output containing carbon
produced by each furnace (metric tons) (Equation Q-7).
(xix) Carbon content of each other solid output containing carbon
(expressed as a decimal fraction) (Equation Q-7).
[[Page 63792]]
(xx) Annual mass of each other gaseous input containing carbon fed
to each furnace (metric tons) (Equation Q-7).
(xxi) Carbon content of each other gaseous input containing carbon
fed to each furnace (expressed as a decimal fraction) (Equation Q-7).
(xxii) Annual mass of each other gaseous output containing carbon
produced by each furnace (metric tons) (Equation Q-7).
(xxiii) Carbon content of each other gaseous output containing
carbon produced by each furnace (expressed as a decimal fraction)
(Equation Q-7).
(xxiv) Annual mass of each other liquid input containing carbon fed
to each furnace (metric tons) (Equation Q-7).
(xxv) Carbon content of each other liquid input containing carbon
fed to each furnace (expressed as a decimal fraction) (Equation Q-7).
(xxvi) Annual mass of each other liquid output containing carbon
produced by each furnace (metric tons) (Equation Q-7).
(xxvii) Carbon content of each other liquid output containing
carbon produced by each furnace (expressed as a decimal fraction)
(Equation Q-7).
(8) The data in paragraphs (f)(8)(i) and (ii) of this section for
each process unit for which the site-specific emission factor method
was used.
(i) Average hourly feed or production rate, as applicable, during
the test (metric tons/hour) (as used in Sec. 98.173(b)(2)(iii)).
(ii) Annual total feed or production, as applicable (metric tons)
(as used in Sec. 98.173(b)(2)(iv)).
(9) Total coal charged to the coke ovens for each process (metric
tons/year)(as used in Sec. 98.173(c)).
Subpart R--Lead Production
0
25. Section 98.186 is amended by removing and reserving paragraphs
(b)(6) and (7) and revising paragraph (b)(8) to read as follows:
Sec. 98.186 Data reporting procedures.
* * * * *
(b) * * *
(8) List the method used for the determination of carbon content
for each material used for the calculation of annual process
CO2 emissions using Equation R-1 of Sec. 98.183 for each
smelting furnace (e.g., supplier provided information, analyses of
representative samples you collected).
* * * * *
0
26. Section 98.187 is amended by revising the introductory text and
adding paragraph (d) to read as follows:
Sec. 98.187 Records that must be retained.
In addition to the records required by Sec. 98.3(g), you must
retain the records of the information specified in paragraphs (a)
through (d) of this section, as applicable to the smelting furnaces at
your facility.
* * * * *
(d) Verification software records. You must keep a record of the
file generated by the verification software specified in Sec. 98.5(b)
for the applicable data specified in paragraphs (d)(1) through (10) of
this section. Retention of this file satisfies the recordkeeping
requirement for the data in paragraphs (d)(1) through (10) of this
section.
(1) Annual mass of lead ore charged to each smelting furnace (tons)
(Equation R-1 of Sec. 98.183).
(2) Carbon content of the lead ore per furnace, from the carbon
analysis results (percent by weight, expressed as a decimal fraction)
(Equation R-1).
(3) Annual mass of lead scrap charged to each smelting furnace
(tons) (Equation R-1).
(4) Carbon content of the lead scrap per furnace, from the carbon
analysis (percent by weight, expressed as a decimal fraction) (Equation
R-1).
(5) Annual mass of flux materials (e.g., limestone, dolomite)
charged to each smelting furnace (tons) (Equation R-1).
(6) Carbon content of the flux materials per furnace, from the
carbon analysis (percent by weight, expressed as a decimal fraction)
(Equation R-1).
(7) Annual mass of carbonaceous materials (e.g., coal, coke)
charged to each smelting furnace (tons) (Equation R-1).
(8) Carbon content of the carbonaceous materials per furnace, from
the carbon analysis (percent by weight, expressed as a decimal
fraction) (Equation R-1).
(9) Annual mass of each other material containing carbon, other
than fuel, fed, charged, or otherwise introduced into the smelting
furnace (tons) (Equation R-1).
(10) Carbon content of each other material, from the carbon
analysis results per furnace (percent by weight, expressed as a decimal
fraction) (Equation R-1).
Subpart S--Lime Manufacturing
0
27. Section 98.196 is amended by:
0
a. Revising paragraph (b) introductory text;
0
b. Removing and reserving paragraphs (b)(2), (3), (5), (6), (8), (10),
(11), and (12); and
0
c. Adding paragraph (b)(18).
The revisions and addition read as follows:
Sec. 98.196 Data reporting requirements.
* * * * *
(b) If a CEMS is not used to measure CO2 emissions, then
you must report the information listed in paragraphs (b)(1) through
(18) of this section.
* * * * *
(18) Annual quantity (tons) of lime product sold, by type.
0
28. Section 98.197 is amended by revising the introductory text and
adding paragraph (c) to read as follows:
Sec. 98.197 Records that must be retained.
In addition to the records required by Sec. 98.3(g), you must
retain the records specified in paragraphs (a) through (c) of this
section.
* * * * *
(c) Verification software records. You must keep a record of the
file generated by the verification software specified in Sec. 98.5(b)
for the applicable data specified in paragraphs (c)(1) through (9) of
this section. Retention of this file satisfies the recordkeeping
requirement for the data in paragraphs (c)(1) through (9) of this
section.
(1) Monthly calcium oxide content for each lime type, determined
according to Sec. 98.194(c) (metric tons CaO/metric ton lime)
(Equation S-1 of Sec. 98.193).
(2) Monthly magnesium oxide content for each lime type, determined
according to Sec. 98.194(c) (metric tons MgO/metric ton lime)
(Equation S-1).
(3) Monthly calcium oxide content for each calcined lime byproduct
or waste type sold (metric tons CaO/metric ton lime) (Equation S-2 of
Sec. 98.193).
(4) Monthly magnesium oxide content for each calcined lime
byproduct or waste type sold (metric tons MgO/metric ton lime)
(Equation S-2).
(5) Calcium oxide content for each calcined lime byproduct or waste
type that is not sold (metric tons CaO/metric ton lime) (Equation S-3
of Sec. 98.193).
(6) Magnesium oxide content for each calcined lime byproduct or
waste type that is not sold (metric tons MgO/metric ton lime) (Equation
S-3).
(7) Annual weight or mass of calcined byproducts or wastes for lime
type that is not sold (tons) (Equation S-3).
(8) Monthly weight or mass of each lime type produced (tons)
(Equation S-4 of Sec. 98.193).
(9) Monthly weight or mass of each calcined byproducts or wastes
sold (tons) (Equation S-4).
Subpart U--Miscellaneous Uses of Carbonate
Sec. 98.216 [Amended]
0
29. Section 98.216 is amended by removing and reserving paragraphs (b),
(e)(1) and (2), and (f).
[[Page 63793]]
0
30. Section 98.217 is amended by revising the introductory text and
adding paragraph (e) to read as follows:
Sec. 98.217 Records that must be retained.
In addition to the records required by Sec. 98.3(g), you must
retain the records specified in paragraphs (a) through (e) of this
section:
* * * * *
(e) Verification software records. You must keep a record of the
file generated by the verification software specified in Sec. 98.5(b)
for the applicable data specified in paragraphs (e)(1) through (4) of
this section. Retention of this file satisfies the recordkeeping
requirement for the data in paragraphs (e)(1) through (4) of this
section.
(1) Fraction calcination achieved for each particular carbonate
type. As an alternative to measuring the calcination fraction, a value
of 1.0 can be used (decimal fraction) (Equation U-1 of Sec. 98.213).
(2) Annual mass of each carbonate type consumed (tons) (Equation U-
1).
(3) Annual mass of each input carbonate type (tons) (Equation U-2
of Sec. 98.213).
(4) Annual mass of each output carbonate type (tons) (Equation U-
2).
Subpart V--Nitric Acid Production
0
31. Section 98.226 is amended by:
0
a. Revising the introductory text;
0
b. Removing and reserving paragraphs (c), (d), (i), (j), (m)(1),
(m)(3), (m)(4), (m)(5), (m)(6), and (p); and
0
c. Adding paragraph (q).
The revisions and addition read as follows:
Sec. 98.226 Data reporting requirements.
In addition to the information required by Sec. 98.3(c), each
annual report must contain the information specified in paragraphs (a)
through (q) of this section.
* * * * *
(q) Annual percent N2O emission reduction for all nitric
acid trains combined.
0
32. Section 98.227 is amended by revising the introductory text and
adding paragraph (h) to read as follows:
Sec. 98.227 Records that must be retained.
In addition to the information required by Sec. 98.3(g), you must
retain the records specified in paragraphs (a) through (h) of this
section for each nitric acid production facility:
* * * * *
(h) Verification software records. You must keep a record of the
file generated by the verification software specified in Sec. 98.5(b)
for the applicable data specified in paragraphs (h)(1) through (10) of
this section. Retention of this file satisfies the recordkeeping
requirement for the data in paragraphs (h)(1) through (10) of this
section.
(1) Annual nitric acid produced from each nitric acid train (tons
nitric acid produced, 100% acid basis).
(2) Indicate which equation was used to calculate emissions for
each nitric acid train.
(3) N2O concentration per test run during the
performance test (ppm N2O) (Equation V-1 of Sec. 98.223).
(4) Volumetric flow rate of effluent gas per test run during the
performance test (dscf/hr) (Equation V-1).
(5) Production rate per test run during the performance test (tons
nitric acid produced per hour, 100 percent acid basis) (Equation V-1).
(6) Annual nitric acid production from each nitric acid train
during which each N2O abatement technology was operational
(tons nitric acid produced, 100 percent acid basis) (Equation V-2 of
Sec. 98.223).
(7) Destruction efficiency of N2O abatement technology
that is used on each nitric acid train (decimal fraction of
N2O removed from vent stream) (Equation V-3a of Sec.
98.223).
(8) Destruction efficiency of each N2O abatement
technology that is used on each nitric acid train (decimal fraction of
N2O removed from vent stream) (Equation V-3b of Sec.
98.223).
(9) Destruction efficiency of each N2O abatement
technology that is used on each nitric acid train (decimal fraction of
N2O removed from vent stream) (Equation V-3c of Sec.
98.223).
(10) Fraction control factor of each N2O abatement
technology that is used on each nitric acid train (decimal fraction of
total emissions from nitric acid train ``t'' that are sent to abatement
technology ``n'') (Equation V-3c).
Subpart W--Petroleum and Natural Gas Systems
0
33. Section 98.236 is amended by revising paragraphs (c)(6)(i)(B), (D),
(E), and (F), (c)(8)(i)(F), and (c)(8)(ii)(A) and adding paragraph
(c)(20) to read as follows:
Sec. 98.236 Data reporting requirements.
* * * * *
(c) * * *
(6) * * *
(i) * * *
(B) When using Equation W-10A of Sec. 98.233, measured flow rate
of backflow during well completion in standard cubic feet per hour. You
may delay the reporting of this data element if you indicate in the
annual report that wildcat wells and/or delineation wells are the only
wells that can be used for the measurement. If you elect to delay
reporting of this data element, you must report by the date specified
in Sec. 98.236(c)(20) the measured flow rate of backflow during well
completion and the API Well Number(s) for the wells included in the
measurement.
* * * * *
(D) When using Equation W-10A, measured flow rate of backflow
during well workover in standard cubic feet per hour. You may delay the
reporting of this data element if you indicate in the annual report
that wildcat wells and/or delineation wells are the only wells that can
be used for the measurement. If you elect to delay reporting of this
data element, you must report by the date specified in Sec.
98.236(c)(20) the flow rate of backflow during well workover and the
API Well Number(s) for the well(s) included in the measurement.
(E) When using Equation W-10A, total number of days of backflow
from all wells during completions. You may delay the reporting of this
data element if you indicate in the annual report that wildcat wells
and/or delineation wells are the only wells included in this number. If
you elect to delay reporting of this data element, you must report by
the date specified in Sec. 98.236(c)(20) the total number of days of
backflow from all wells during completions and the API Well Number(s)
for the well(s) included in the number.
(F) When using Equation W-10A, total number of days of backflow
from all wells during workovers. You may delay the reporting of this
data element if you indicate in the annual report that wildcat wells
and/or delineation wells are the only wells included in this number. If
you elect to delay reporting of this data element, you must report by
the date specified in Sec. 98.236(c)(20) the total number of days of
backflow from all wells during workovers and the API Well Number(s) for
the well(s) included in the number.
* * * * *
(8) * * *
(i) * * *
(F) Total volume of oil from all wellhead separators sent to
tank(s) in barrels per year. You may delay the reporting of this data
element if you indicate in the annual report that only wildcat and
delineation wells in the sub-basin have wellhead separators. If you
elect to delay reporting the this data element, you must report by the
date specified in Sec. 98.236(c)(20) the total volume of oil from all
wellhead separators sent to tank(s) and the API
[[Page 63794]]
Well Number(s) for the well(s) included in this volume.
* * * * *
(ii) * * *
(A) Total volume of sales oil from all wells in barrels per year.
You may delay the reporting of this data element if you indicate in the
annual report that wildcat wells and delineation wells are the only
wells in the sub-basin with oil production greater than or equal to 10
barrels per day. If you elect to delay reporting of this data element,
you must report by the date specified in Sec. 98.3236(c)(20) the total
volume of sales oil from all wells and the API Well Number(s) for the
well(s) included in this volume.
* * * * *
(20) If you elect to delay reporting the information in paragraph
(c)(6)(i)(B), (D), (E), (F), (c)(8)(i)(F), or (c)(8)(ii)(A) of this
section, you must report the information required in that paragraph no
later than the date specified in paragraphs (c)(20)(i) through (iii) of
this section, as applicable.
(i) March 31, 2016, for reporting year 2013.
(ii) March 31, 2017, for reporting year 2014.
(iii) The date 2 years following the date specified in Sec.
98.3(b) introductory text, for reporting year 2015 and thereafter.
0
34. Section 98.238 is amended by adding definitions for ``Delineation
well'' and ``Wildcat well'' in alphabetical order to read as follows:
Sec. 98.238 Definitions.
* * * * *
Delineation well means a well drilled in order to determine the
boundary of a field or producing reservoir.
* * * * *
Wildcat well means a well outside known fields or the first well
drilled in an oil or gas field where no other oil and gas production
exists.
Subpart X--Petrochemical Production
0
35. Section 98.246 is amended by:
0
a. Revising paragraph (a) introductory text and paragraphs (a)(2) and
(4);
0
b. Adding paragraphs (a)(12) and (13);
0
c. Revising paragraph (b) introductory text; and
0
d. Adding paragraphs (b)(9) and (10).
The revisions and additions read as follows:
Sec. 98.246 Data reporting requirements.
* * * * *
(a) If you use the mass balance methodology in Sec. 98.243(c), you
must report the information specified in paragraphs (a)(1) through (13)
of this section for each type of petrochemical produced, reported by
process unit.
* * * * *
(2) The type of petrochemical produced, names of products, and
names of carbon-containing feedstocks.
* * * * *
(4) The temperature (in [deg]F) at which the gaseous feedstock and
product volumes used in Equation X-1 of Sec. 98.243 were determined.
* * * * *
(12) Name and annual quantity (in metric tons) of each carbon-
containing feedstock included in Equations X-1, X-2, and X-3 of Sec.
98.243.
(13) Name and annual quantity (in metric tons) of each product
included in Equations X-1, X-2, and X-3.
(b) If you measure emissions in accordance with Sec. 98.243(b),
then you must report the information listed in paragraphs (b)(1)
through (10) of this section.
* * * * *
(9) Name and annual quantity (in metric tons) of each carbon-
containing feedstock.
(10) Name and annual quantity (in metric tons) of each product.
* * * * *
0
36. Section 98.247 is amended by revising the introductory text and
adding paragraph (d) to read as follows:
Sec. 98.247 Records that must be retained.
In addition to the recordkeeping requirements in Sec. 98.3(g), you
must retain the records specified in paragraphs (a) through (d) of this
section, as applicable.
* * * * *
(d) Verification software records. You must keep a record of the
file generated by the verification software specified in Sec. 98.5(b)
for the applicable data specified in paragraphs (d)(1) through (30) of
this section. Retention of this file satisfies the recordkeeping
requirement for the data in paragraphs (d)(1) through (30) of this
section.
(1) Indicate whether the feedstock is measured as mass or volume
(Equation X-1 of Sec. 98.243).
(2) Indicate whether you used the alternative to sampling and
analysis specified in Sec. 98.243(c)(4) (Equation X-1).
(3) Volume of gaseous feedstock introduced per month (scf)
(Equation X-1).
(4) Mass of gaseous feedstock introduced per month (kg) (Equation
X-1).
(5) Average carbon content of the gaseous feedstock per month (kg C
per kg of feedstock) (Equation X-1).
(6) Molecular weight of gaseous feedstock per month (kg per kg-
mole) (Equation X-1).
(7) Indicate whether the gaseous product is measured as mass or
volume (Equation X-1).
(8) Volume of gaseous product produced per month (scf) (Equation X-
1).
(9) Mass of gaseous product produced per month (kg) (Equation X-1).
(10) Average carbon content of gaseous product (including streams
containing CO2 recovered for sale or use in another process)
per month (kg C per kg of product) (Equation X-1).
(11) Molecular weight of gaseous product per month (kg per kg-mole)
(Equation X-1).
(12) Molar volume conversion factor of product (scf per kg-mole)
(Equation X-1).
(13) Indicate whether feedstock is measured as mass or volume
(Equation X-2 of Sec. 98.243).
(14) Indicate whether you used the alternative to sampling and
analysis specified in Sec. 98.243(c)(4) (Equation X-2).
(15) Volume of liquid feedstock introduced per month (gallons)
(Equation X-2).
(16) Mass of liquid feedstock introduced per month (kg) (Equation
X-2).
(17) Average carbon content of liquid feedstock per month (kg C per
gallon) (Equation X-2).
(18) Average carbon content of liquid feedstock per month (kg C per
kg of feedstock) (Equation X-2).
(19) Indicate whether product is measured as mass or volume per
month (Equation X-2).
(20) Volume of liquid product produced per month (gallons)
(Equation X-2).
(21) Mass of liquid product produced per month (kg) (Equation X-2).
(22) Average carbon content of liquid product per month, including
organic liquid wastes (kg C per gallon) (Equation X-2).
(23) Average carbon content of liquid product, including organic
liquid wastes (kg C per kg of product) (Equation X-2).
(24) Indicate whether you used the alternative to sampling and
analysis specified in Sec. 98.243(c)(4) (Equation X-3 of Sec.
98.243).
(25) Mass of solid feedstock introduced per month (kg) (Equation X-
3).
(26) Average carbon content of solid feedstock per month (kg C per
kg of feedstock) (Equation X-3).
(27) Mass of solid product produced per month (kg) (Equation X-3).
[[Page 63795]]
(28) Average carbon content of solid product per month (kg C per kg
of product) (Equation X-3).
(29) Records required in Sec. 98.257(b)(1) through (8) of this
section for each flare that burns ethylene process off-gas.
(30) Records required in Sec. 98.37 for each stationary fuel
combustion unit (or group of stationary sources with a common pipe)
that burns ethylene process off-gas, except flares.
Subpart Y--Petroleum Refineries
0
37. Section 98.256 is amended by:
0
a. Revising paragraph (e)(6) and paragraph (e)(7) introductory text;
0
b. Removing and reserving paragraph (e)(7)(ii);
0
c. Revising paragraphs (e)(9) and (10);
0
d. Revising paragraphs (f)(7) and (f)(10) through (13);
0
e. Removing and reserving paragraph (h)(4);
0
f. Revising paragraphs (h)(5) and (i)(5), (7), and (8);
0
g. Removing and reserving paragraph (j)(2);
0
h. Revising paragraphs (j)(5) through (9), (k)(3) and (4), (l)(5), and
(m)(3);
0
i. Removing and reserving paragraphs (o)(2)(ii) and (o)(4)(ii) through
(iv);
0
j. Revising paragraph (o)(4)(v);
0
k. Removing and reserving paragraphs (o)(6) and (7); and
0
l. Revising paragraph (p)(2).
The revisions read as follows:
Sec. 98.256 Data reporting requirements.
* * * * *
(e) * * *
(6) If you use Equation Y-1a of Sec. 98.253, an indication of
whether daily or weekly measurement periods are used, the annual volume
of flare gas combusted (in scf/year) and the annual average molecular
weight (in kg/kg-mole), and annual average carbon content of the flare
gas (in kg carbon per kg flare gas).
(7) If you use Equation Y-1b of Sec. 98.253, an indication of
whether daily or weekly measurement periods are used, the annual volume
of flare gas combusted (in scf/year), the annual average CO2
concentration (volume or mole percent), the number of carbon containing
compounds other than CO2 in the flare gas stream, and for
each of the carbon containing compounds other than CO2 in
the flare gas stream:
* * * * *
(9) If you use Equation Y-3 of Sec. 98.253, the number of SSM
events exceeding 500,000 scf/day.
(10) The basis for the value of the fraction of carbon in the flare
gas contributed by methane used in Equation Y-4 of Sec. 98.253.
(f) * * *
(7) If you use Equation Y-6 of Sec. 98.253, the annual average
exhaust gas flow rate, %CO2, and %CO.
* * * * *
(10) If you use Equation Y-8 of Sec. 98.253, the basis for the
value of the average carbon content of coke.
(11) Indicate whether you use a measured value, a unit-specific
emission factor, or a default for CH4 emissions. If you use
a unit-specific emission factor for CH4, report the basis
for the factor.
(12) Indicate whether you use a measured value, a unit-specific
emission factor, or a default emission factor for N2O
emissions. If you use a unit-specific emission factor for
N2O, report the basis for the factor.
(13) If you use Equation Y-11 of Sec. 98.253, the number of
regeneration cycles or measurement periods during the reporting year
and the average coke burn-off quantity per cycle or measurement period.
* * * * *
(h) * * *
(5) If you recycle tail gas to the front of the sulfur recovery
plant, indicate whether the recycled flow rate and carbon content are
included in the measured data under Sec. 98.253(f)(2) and (3).
Indicate whether a correction for CO2 emissions in the tail
gas was used in Equation Y-12 of Sec. 98.253. If so, then report:
(i) Indicate whether you used the default (95 percent) or a unit
specific correction, and if a unit-specific correction was used, report
the value of the correction and the approach used.
(ii) If the following data are not used to calculate the recycling
correction factor, report the information specified in paragraphs
(h)(5)(ii)(A) through (B) of this section.
(A) The annual volume of recycled tail gas (in scf/year) only.
(B) The annual average mole fraction of carbon in the tail gas (in
kg-mole C/kg-mole gas).
* * * * *
(i) * * *
(5) If you use Equation Y-13 of Sec. 98.253, an indication of
whether coke dust is recycled to the unit (e.g., all dust is recycled,
a portion of the dust is recycled, or none of the dust is recycled).
* * * * *
(7) Indicate whether you use a measured value, a unit-specific
emission factor or a default emission factor for CH4
emissions. If you use a unit-specific emission factor for
CH4, report the basis for the factor.
(8) Indicate whether you use a measured value, a unit-specific
emission factor, or a default emission factor for N2O
emissions. If you use a unit-specific emission factor for
N2O, report the basis for the factor.
(j) * * *
(5) If you use Equation Y-14 of Sec. 98.253, the basis for the
CO2 emission factor used.
(6) If you use Equation Y-15 of Sec. 98.253, the basis for the
CH4 emission factor used.
(7) If you use Equation Y-16a of Sec. 98.253, the basis for the
carbon emission factor used.
(8) If you use Equation Y-16b of Sec. 98.253, the basis for the
CO2 emission factor used and the basis for the carbon
emission factor used.
(9) If you use Equation Y-17 of Sec. 98.253, the basis for the
CH4 emission factor used.
* * * * *
(k) * * *
(3) The total number of delayed coking units at the facility; the
total number of delayed coking drums at the facility; and, for each
coke drum or vessel, the typical drum outage (i.e. the unfilled
distance from the top of the drum, in feet).
(4) For each set of coking drums that are the same dimensions, the
number of coking drums in the set, and the mole fraction of methane in
coking gas (in kg-mole CH4/kg-mole gas, wet basis).
* * * * *
(l) * * *
(5) The annual volumetric flow discharged to the atmosphere (in
scf), and an indication of the measurement or estimation method, annual
average mole fraction of each GHG above the concentration threshold or
otherwise required to be reported and an indication of the measurement
or estimation method, and for intermittent vents, the number of venting
events and the cumulative venting time.
* * * * *
(m) * * *
(3) For uncontrolled blowdown systems reporting under Sec.
98.253(k), the basis for the value of the methane emission factor used
for uncontrolled blowdown systems.
* * * * *
(o) * * *
(4) * * *
(v) The basis for the mole fraction of CH4 in vent gas
from unstabilized crude oil storage tanks.
* * * * *
(p) * * *
(2) The types of materials loaded that have an equilibrium vapor-
phase concentration of methane of 0.5 volume percent or greater, and
the type of vessel
[[Page 63796]]
(barge, tanker, marine vessel, etc.) in which each type of material is
loaded.
* * * * *
0
38. Section 98.257 is amended to read as follows:
Sec. 98.257 Records that must be retained.
In addition to the records required by Sec. 98.3(g), you must
retain the records specified in paragraphs (a) and (b) of this section.
(a) The records of all parameters monitored under Sec. 98.255. If
you comply with the combustion methodology in Sec. 98.252(a), then you
must retain under this subpart the records required for the Tier 3 and/
or Tier 4 Calculation Methodologies in Sec. 98.37 and you must keep
records of the annual average flow calculations.
(b) Verification software records. You must keep a record of the
file generated by the verification software specified in Sec. 98.5(b)
for the applicable data specified in paragraphs (b)(1) through (67) of
this section. Retention of this file satisfies the recordkeeping
requirement for the data in paragraphs (b)(1) through (67) of this
section.
(1) Volume of flare gas combusted during measurement period (scf)
(Equation Y-1b of Sec. 98.253).
(2) Mole percent CO2 concentration in the flare gas
stream during the measurement period (mole percent) (Equation Y-1b).
(3) Mole percent concentration of compound ``x'' in the flare gas
stream during the measurement period (mole percent) (Equation Y-1b).
(4) Carbon mole number of compound ``x'' in the flare gas stream
during the measurement period (mole carbon atoms per mole compound)
(Equation Y-1b).
(5) Molar volume conversion factor (scf per kg-mole) (Equation Y-
1b).
(6) Annual volume of flare gas combusted for each flare during
normal operations from company records (million (MM) standard cubic
feet per year, MMscf/year) (Equation Y-3 of Sec. 98.253).
(7) Higher heating value for fuel gas or flare gas for each flare
from company records (British thermal units per scf, Btu/scf = MMBtu/
MMscf) (Equation Y-3).
(8) Volume of flare gas combusted during indexed start-up,
shutdown, or malfunction event from engineering calculations (scf)
(Equation Y-3).
(9) Average molecular weight of the flare gas, from the analysis
results or engineering calculations for the event (kg/kg-mole)
(Equation Y-3).
(10) Molar volume conversion factor (scf per kg-mole) (Equation Y-
3).
(11) Average carbon content of the flare gas, from analysis results
or engineering calculations for the event (kg C per kg flare gas)
(Equation Y-3).
(12) Weight fraction of carbon in the flare gas prior to combustion
in each flare that is contributed by methane from measurement values or
engineering calculations (kg C in methane in flare gas/kg C in flare
gas) (Equation Y-4 of Sec. 98.253).
(13) Annual throughput of unit from company records for each
catalytic cracking unit or fluid coking unit (barrels/year) (Equation
Y-8 of Sec. 98.253).
(14) Coke burn-off factor from engineering calculations (default
for catalytic cracking units = 7.3; default for fluid coking units =
11) (kg coke per barrel of feed) (Equation Y-8).
(15) Carbon content of coke based on measurement or engineering
estimate (kg C per kg coke) (Equation Y-8).
(16) Value of unit-specific CH4 emission factor,
including the units of measure, for each catalytic cracking unit,
traditional fluid coking unit, catalytic reforming unit, and coke
calcining unit (calculation method in Sec. 98.253(c)(4)).
(17) Annual activity data (e.g., input or product rate), including
the units of measure, in units of measure consistent with the emission
factor, for each catalytic cracking unit, traditional fluid coking
unit, catalytic reforming unit, and coke calcining unit (calculation
method in Sec. 98.253(c)(4)).
(18) Value of unit-specific N2O emission factor,
including the units of measure, for each catalytic cracking unit,
traditional fluid coking unit, catalytic reforming unit, and coke
calcining unit (calculation method in Sec. 98.253(c)(5)).
(19) Annual activity data (e.g., input or product rate), including
the units of measure, in units of measure consistent with the emission
factor, for each catalytic cracking unit, traditional fluid coking
unit, catalytic reforming unit, and coke calcining unit (calculation
method in Sec. 98.253(c)(5)).
(20) Carbon content of coke based on measurement or engineering
estimate (default = 0.94) (kg C per kg coke) (Equation Y-11 of Sec.
98.253).
(21) Volumetric flow rate of sour gas (including sour water
stripper gas) feed sent off site for sulfur recovery in the year (scf/
year) (Equation Y-12 of Sec. 98.253).
(22) Mole fraction of carbon in the sour gas feed sent off site for
sulfur recovery (kg-mole C/kg-mole gas) (Equation Y-12).
(23) Molar volume conversion factor for sour gas sent off site (scf
per kg-mole) (Equation Y-12).
(24) Volumetric flow rate of sour gas (including sour water
stripper gas) fed to the onsite sulfur recovery plant (scf/year)
(Equation Y-12).
(25) Mole fraction of carbon in the sour gas fed to the onsite
sulfur recovery plant (kg-mole C/kg-mole gas) (Equation Y-12).
(26) Molar volume conversion factor for onsite sulfur recovery
plant (scf per kg-mole) (Equation Y-12).
(27) Annual mass of green coke fed to the coke calcining unit from
facility records (metric tons/year) (Equation Y-13 of Sec. 98.253).
(28) Annual mass of marketable petroleum coke produced by the coke
calcining unit from facility records (metric tons/year) (Equation Y-
13).
(29) Annual mass of petroleum coke dust removed from the process
through the dust collection system of the coke calcining unit from
facility records. For coke calcining units that recycle the collected
dust, the mass of coke dust removed from the process is the mass of
coke dust collected less the mass of coke dust recycled to the process
(metric tons/year) (Equation Y-13).
(30) Average mass fraction carbon content of green coke from
facility measurement data (metric tons C per metric ton green coke)
(Equation Y-13).
(31) Average mass fraction carbon content of marketable petroleum
coke produced by the coke calcining unit from facility measurement data
(metric tons C per metric ton petroleum coke (Equation Y-13).
(32) Quantity of asphalt blown for each asphalt blowing unit
(million barrels per year (MMbbl/year)) (Equation Y-14 of Sec.
98.253).
(33) Emission factor for CO2 from uncontrolled asphalt
blowing from facility-specific test data for each asphalt blowing unit
(metric tons CO2/MMbbl asphalt blown) (Equation Y-14).
(34) Emission factor for CH4 from uncontrolled asphalt
blowing from facility-specific test data for each asphalt blowing unit
(metric tons CH4/MMbbl asphalt blown) (Equation Y-15 of
Sec. 98.253).
(35) Quantity of asphalt blown (million barrels/year (MMbbl/year))
(Equation Y-16a of Sec. 98.253).
(36) Carbon emission factor from asphalt blowing from facility-
specific test data (metric tons C/MMbbl asphalt blown) (Equation Y-
16a).
(37) Quantity of asphalt blown for each asphalt blowing unit
(million barrels per year (MMbbl/year)) (Equation Y-16b of Sec.
98.253).
[[Page 63797]]
(38) Emission factor for CO2 from uncontrolled asphalt
blowing from facility-specific test data for each asphalt blowing unit
(metric tons CO2/MMbbl asphalt blown) (Equation Y-16b).
(39) Carbon emission factor from asphalt blowing from facility-
specific test data for each asphalt blowing unit (metric tons C/MMbbl
asphalt blown) (Equation Y-16b).
(40) Emission factor for CH4 from uncontrolled asphalt
blowing from facility-specific test data for each asphalt blowing unit
(metric tons CH4/MMbbl asphalt blown) (Equation Y-17 of
Sec. 98.253).
(41) Cumulative number of vessel openings for all delayed coking
unit vessels of the same dimensions during the year (Equation Y-18 of
Sec. 98.253).
(42) Height of coking unit vessel for each set of coke drums or
vessels of the same size (feet) (Equation Y-18).
(43) Gauge pressure of the coking vessel when opened to the
atmosphere prior to coke cutting or, if the alternative method provided
in Sec. 98.253(i)(2) is used, gauge pressure of the coking vessel when
depressurization gases are first routed to the atmosphere for each set
of coke drums or vessels of the same size (pounds per square inch gauge
(psig)) (Equation Y-18).
(44) Volumetric void fraction of coking vessel prior to steaming
for each set of coke drums or vessels of the same size (cf gas/cf of
vessel) (Equation Y-18).
(45) Diameter of coking unit vessel for each set of coke drums or
vessels of the same size (feet) (Equation Y-18).
(46) Molar volume conversion factor for each set of coke drums or
vessels of the same size (scf per kg-mole) (Equation Y-18).
(47) Average volumetric flow rate of process gas during the event
from measurement data, process knowledge, or engineering estimates for
each set of coke drums or vessels of the same size (scf per hour)
(Equation Y-19 of Sec. 98.253).
(48) Mole fraction of methane in process vent during the event from
measurement data, process knowledge, or engineering estimates for each
set of coke drums or vessels of the same size (kg-mole CH4/
kg-mole gas) (Equation Y-19).
(49) Venting time for the event for each set of coke drums or
vessels of the same size (hours) (Equation Y-19).
(50) Molar volume conversion factor for each set of coke drums or
vessels of the same size (scf per kg-mole) (Equation Y-19).
(51) Quantity of crude oil plus the quantity of intermediate
products received from off site that are processed at the facility
(MMbbl/year) (Equation Y-20 of Sec. 98.253).
(52) Molar volume conversion factor (scf per kg-mole) (Equation Y-
20).
(53) Methane emission factor for uncontrolled blown systems (scf
CH4/MMbbl) (Equation Y-20).
(54) Quantity of crude oil plus the quantity of intermediate
products received from off site that are processed at the facility
(MMbbl/year) (Equation Y-22 of Sec. 98.253).
(55) Quantity of unstabilized crude oil received at the facility
(MMbbl/year) (Equation Y-23 of Sec. 98.253).
(56) Pressure differential from the previous storage pressure to
atmospheric pressure (psi) (Equation Y-23).
(57) Average mole fraction of CH4 in vent gas from the
unstabilized crude oil storage tanks from facility measurements (kg-
mole CH4/kg-mole gas) (Equation Y-23).
(58) Molar volume conversion factor (scf per kg-mole) (Equation Y-
23).
(59) Specify whether the calculated or default loading factor L
specified in Sec. 98.253(n) is entered, for each liquid loaded to each
(methods specified in Sec. 98.253(n)).
(60) Saturation factor specified in Sec. 98.253(n), for each
liquid loaded to each vessel (methods specified in Sec. 98.253(n)).
(61) True vapor pressure of liquid loaded, for each liquid loaded
to each vessel (psia) (methods specified in Sec. 98.253(n)).
(62) Molecular weight of vapors (lb per lb-mole), for each liquid
loaded to each vessel (methods specified in Sec. 98.253(n)).
(63) Temperature of bulk liquid loaded, for each liquid loaded to
each vessel ([deg]R, degrees Rankine) (methods specified in Sec.
98.253(n)).
(64) Total loading loss (without efficiency correction), for each
liquid loaded to each vessel (pounds per 1000 gallons loaded) (methods
specified in Sec. 98.253(n)).
(65) Overall emission control system reduction efficiency,
including the vapor collection system efficiency and the vapor recovery
or destruction efficiency (enter zero if no emission controls), for
each liquid loaded to each vessel (percent) (methods specified Sec.
98.253(n)).
(66) Vapor phase concentration of methane in liquid loaded, for
each liquid loaded to each vessel (percent by volume) (methods
specified in Sec. 98.253(n)).
(67) Quantity of material loaded, for each liquid loaded to each
vessel (thousand gallon per year) (methods specified in Sec.
98.253(n)).
Subpart Z--Phosphoric Acid Production
Sec. 98.266 [Amended]
0
39. Section 98.266 is amended by removing and reserving paragraphs
(f)(5) and (6).
0
40. Section 98.267 is amended by revising the introductory text and
adding paragraph (d) to read as follows:
Sec. 98.267 Records that must be retained.
In addition to the records required by Sec. 98.3(g), you must
retain the records specified in paragraphs (a) through (d) of this
section for each wet-process phosphoric acid production facility.
* * * * *
(d) Verification software records. You must keep a record of the
file generated by the verification software specified in Sec. 98.5(b)
for the applicable data specified in paragraphs (d)(1) through (4) of
this section. Retention of this file satisfies the recordkeeping
requirement for the data in paragraphs (d)(1) through (4) of this
section.
(1) Inorganic carbon content of a grab sample batch of phosphate
rock by origin obtained during month by wet-process phosphoric acid
process line, from the carbon analysis results (percent by weight,
expressed as a decimal fraction) (Equation Z-1a of Sec. 98.263).
(2) Mass of phosphate rock by origin consumed in month by wet-
process phosphoric acid process line (tons) (Equation Z-1a).
(3) Carbon dioxide content of a grab sample batch of phosphate rock
by origin obtained during month by wet-process phosphoric acid process
line (percent by weight, expressed as a decimal fraction) (Equation Z-
1b of Sec. 98.263).
(4) Mass of phosphate rock by origin consumed in month by wet-
process phosphoric acid process line (tons) (Equation Z-1b).
Subpart AA--Pulp and Paper Manufacturing
0
41. Section 98.276 is amended by:
0
a. Revising the introductory paragraph;
0
b. Removing and reserving paragraph (b);
0
c. Revising paragraph (c);
0
d. Removing and reserving paragraphs (d), (f), (g), (h) and (i); and
0
e. Adding paragraph (l).
The revisions and addition read as follows:
Sec. 98.276 Data reporting requirements.
In addition to the information required by Sec. 98.3(c) and the
applicable information required by Sec. 98.36, each
[[Page 63798]]
annual report must contain the information in paragraphs (a) through
(l) of this section as applicable:
* * * * *
(c) Basis for determining the annual mass of the spent liquor
solids combusted (whether based on T650 om-05 Solids Content of Black
Liquor, TAPPI (incorporated by reference, see Sec. 98.7) or an online
measurement system).
* * * * *
(l) For each pulp mill lime kiln, report the information specified
in paragraphs (l)(1) and (2) of this section.
(1) The quantity of calcium oxide (CaO) produced (metric tons).
(2) The percent of annual heat input, individually for each fossil
fuel type.
0
42. Section 98.277 is amended by revising the introductory text and
adding paragraph (g) to read as follows:
Sec. 98.277 Records that must be retained.
In addition to the information required by Sec. 98.3(g), you must
retain the records in paragraphs (a) through (g) of this section.
* * * * *
(g) Verification software records. You must keep a record of the
file generated by the verification software specified in Sec. 98.5(b)
for the applicable data specified in paragraphs (g)(1) through (27) of
this section. Retention of this file satisfies the recordkeeping
requirement for the data in paragraphs (g)(1) through (27) of this
section.
(1) Mass of the solid fuel combusted (tons/year) (Equation C-1 of
Sec. 98.33).
(2) Volume of the liquid fuel combusted (gallons/year) (Equation C-
1).
(3) Volume of the gaseous fuel combusted (scf/year) (Equation C-1).
(4) Annual natural gas usage (therms/year) (Equation C-1a of Sec.
98.33).
(5) Annual natural gas usage (mmBtu/year) (Equation C-1b of Sec.
98.33).
(6) Mass of the solid fuel combusted (tons/year) (Equation C-2a of
Sec. 98.33).
(7) Volume of the liquid fuel combusted (gallons/year) (Equation C-
2a).
(8) Volume of the gaseous fuel combusted (scf/year) (Equation C-
2a).
(9) Annual mass of the solid fuel combusted (short tons/year)
(Equation C-3 of Sec. 98.33).
(10) Annual average carbon content of the solid fuel (percent by
weight, expressed as a decimal fraction) (Equation C-3).
(11) Annual volume of the liquid fuel combusted (gallons/year)
(Equation C-4 of Sec. 98.33).
(12) Annual average carbon content of the liquid fuel (kg C per
gallon of fuel) (Equation C-4).
(13) Annual volume of the gaseous fuel combusted (scf/year)
(Equation C-5 of Sec. 98.33).
(14) Annual average carbon content of the gaseous fuel (kg C per kg
of fuel) (Equation C-5).
(15) Annual average molecular weight of the gaseous fuel (kg/kg-
mole) (Equation C-5).
(16) Molar volume conversion factor at standard conditions, as
defined in Sec. 98.6 (scf per kg-mole) (Equation C-5).
(17) Identify if you will use the default high heat value from
Table C-1 of subpart C of this part, or actual HHV data (Equation C-8
of Sec. 98.33).
(18) High heat value of the fuel (mmBTU/tons) (Equation C-8).
(19) High heat value of the fuel (mmBTU/gallons) (Equation C-8).
(20) High heat value of the fuel (mmBTU/scf) (Equation C-8).
(21) Mass of spent liquor solids combusted from each chemical
recovery furnace located at a kraft or soda facility, in short tons in
year, determined according to Sec. 98.274(b) (tons/year) (Equation AA-
1 of Sec. 98.273).
(22) Annual high heat value of the spent liquor solids from each
chemical recovery furnace located at a kraft or soda facility
determined according to Sec. 98.274(b) (mmBtu per kilogram) (Equation
AA-1).
(23) Annual high heat value of the spent liquor solids from each
chemical recovery combustion unit located at a sulfite or stand-alone
semichemical facility, determined according to Sec. 98.274(b) (mmBtu
per kilogram) (Equation AA-1).
(24) Mass of the spent liquor solids combusted in short tons per
year determined according to Sec. 98.274(b) (tons/year) (Equation AA-2
of Sec. 98.273).
(25) Annual carbon content of the spent liquor solids, determined
according to Sec. 98.274(b) (percent by weight, expressed as a decimal
fraction (e.g., 95% = 0.95)) (Equation AA-2).
(26) Make-up quantity of CaCO3 used for the reporting
year (metric tons/year) (Equation AA-3 of Sec. 98.273).
(27) Make-up quantity of Na2CO3 used for the
reporting year metric tons/year) (Equation AA-3).
Subpart BB--Silicon Carbide Production
Sec. 98.286 [Amended]
0
43. Section 98.286 is amended by removing and reserving paragraphs
(b)(1), (4), and (6).
0
44. Section 98.287 is amended by revising the introductory text and
adding paragraph (c) to read as follows:
Sec. 98.287 Records that must be retained.
In addition to the records required by Sec. 98.3(g), you must
retain the records specified in paragraphs (a) through (c) of this
section for each silicon carbide production facility.
* * * * *
(c) Verification software records. You must keep a record of the
file generated by the verification software specified in Sec. 98.5(b)
for the applicable data specified in paragraphs (c)(1) and (2) of this
section. Retention of this file satisfies the recordkeeping requirement
for the data in paragraphs (c)(1) and (2) of this section.
(1) Carbon content factor for petroleum coke consumed in month from
the supplier or as measured by the applicable method (percent by weight
expressed as a decimal fraction) (Equation BB-1 of Sec. 98.283).
(2) Petroleum coke consumption in month (tons) (Equation BB-2 of
Sec. 98.283).
Subpart CC--Soda Ash Manufacturing
0
45. Section 98.296 is amended by removing and reserving paragraphs
(b)(5) through (7) and adding paragraphs (b)(10)(v) and (vi) to read as
follows:
Sec. 98.296 Data reporting requirements.
* * * * *
(b) * * *
(10) * * *
(v) Average process vent flow from mine water stripper/evaporator
during performance test (pounds/hour).
(vi) Annual process vent flow rate from mine water stripper/
evaporator (thousand pounds/hour).
* * * * *
0
46. Section 98.297 is amended by revising the introductory text and
adding paragraph (c) to read as follows:
Sec. 98.297 Records that must be retained.
In addition to the records required by Sec. 98.3(g), you must
retain the records specified in paragraphs (a) through (c) of this
section for each soda ash manufacturing line.
* * * * *
(c) Verification software records. You must keep a record of the
file generated by the verification software specified in Sec. 98.5(b)
for the applicable data specified in paragraphs (c)(1) through (4) of
this section. Retention of this file satisfies the recordkeeping
requirement for the data in paragraphs (c)(1) through (4) of this
section
(1) Inorganic carbon content in trona input, from the carbon
analysis results for month (percent by weight, expressed as a decimal
fraction) (Equation CC-1 of Sec. 98.293).
[[Page 63799]]
(2) Mass of trona input in month (tons) (Equation CC-1).
(3) Inorganic carbon content in soda ash output, from the carbon
analysis results for month (percent by weight, expressed as a decimal
fraction) (Equation CC-2 of Sec. 98.293).
(4) Mass of soda ash output in month (tons) (Equation CC-2).
Subpart EE--Titanium Dioxide Production
Sec. 98.316 [Amended]
0
47. Section 98.316 is amended by removing and reserving paragraphs
(b)(6) and (9).
0
48. Section 98.317 is amended by revising the introductory text and
adding paragraph (c) to read as follows:
Sec. 98.317 Records that must be retained.
In addition to the records required by Sec. 98.3(g), you must
retain the records specified in paragraphs (a) through (c) of this
section for each titanium dioxide production facility.
* * * * *
(c) Verification software records. You must keep a record of the
file generated by the verification software specified in Sec. 98.5(b)
for the applicable data specified in paragraphs (c)(1) and (2) of this
section. Retention of this file satisfies the recordkeeping requirement
for the data in paragraphs (c)(1) and (2) of this section.
(1) Carbon content factor for petroleum coke consumed in month from
the supplier or as measured by the applicable method incorporated by
reference in Sec. 98.7 according to Sec. 98.314(c) (percent by
weight, expressed as a decimal fraction) (Equation EE-2 of Sec.
98.313).
(2) Calcined petroleum coke consumption for process line in month
(tons) (Equation EE-2).
Subpart GG--Zinc Production
Sec. 98.336 [Amended]
0
49. Section 98.336 is amended by removing and reserving paragraphs
(b)(6), (7), and (10).
0
50. Section 98.337 is amended by revising the introductory text and
adding paragraph (c) to read as follows:
Sec. 98.337 Records that must be retained.
In addition to the records required by Sec. 98.3(g), you must
retain the records specified in paragraphs (a) through (c) of this
section for each zinc production facility.
* * * * *
(c) Verification software records. You must keep a record of the
file generated by the verification software specified in Sec. 98.5(b)
for the applicable data specified in paragraphs (c)(1) through (9) of
this section. Retention of this file satisfies the recordkeeping
requirement for the data in paragraphs (c)(1) through (9) of this
section.
(1) Annual mass of zinc bearing material charged to kiln or furnace
(tons) (Equation GG-1 of Sec. 98.333).
(2) Carbon content of the zinc bearing material, from the annual
carbon analysis for kiln or furnace (percent by weight, expressed as a
decimal fraction) (Equation GG-1).
(3) Annual mass of flux materials (e.g., limestone, dolomite)
charged to each kiln or furnace (tons) (Equation GG-1).
(4) Carbon content of the flux materials charged to each kiln or
furnace, from the annual carbon analysis (percent by weight, expressed
as a decimal fraction) (Equation GG-1).
(5) Annual mass of carbon electrode consumed in each furnace (tons)
(Equation GG-1).
(6) Carbon content of the carbon electrode consumed in each
furnace, from the annual carbon analysis (percent by weight, expressed
as a decimal fraction) (Equation GG-1).
(7) Annual mass of carbonaceous materials (e.g., coal, coke)
charged to each kiln or furnace (tons) (Equation GG-1).
(8) Carbon content of the carbonaceous materials charged to each
kiln or furnace, from the annual carbon analysis (percent by weight,
expressed as a decimal fraction) (Equation GG-1).
(9) Identify whether each unit is a Waelz kiln or an electrothermic
furnace.
Subpart TT--Industrial Waste Landfills
0
51. Section 98.466 is amended by:
0
a. Removing and reserving paragraph (c)(3)(i);
0
b. Revising paragraph (c)(3)(ii); and
0
c. Removing and reserving paragraph (c)(3)(iii).
The revisions read as follows:
Sec. 98.466 Data reporting requirements.
* * * * *
(c) * * *
(3) * * *
(ii) The year of the data used in Equation TT-2 of Sec. 98.463 for
the waste disposal quantity and production quantity, for each year used
in Equation TT-2 to calculate the average waste disposal factor (WDF).
* * * * *
0
52. Section 98.467 is amended to read as follows:
Sec. 98.467 Records that must be retained.
In addition to the information required by Sec. 98.3(g), you must
retain:
(a) The calibration records for all monitoring equipment, including
the method or manufacturer's specification used for calibration, and
all measurement data used for the purposes of Sec. 98.460(c)(2)(xii)
or (xiii) or used to determine waste stream-specific DOCX
values for use in Equation TT-1 of Sec. 98.463.
(b) Verification software records. You must keep a record of the
file generated by the verification software specified in Sec. 98.5(b)
for the applicable data specified in paragraphs (b)(1) and (2) of this
section. Retention of this file satisfies the recordkeeping requirement
for the data in paragraphs (b)(1) and (2) of this section.
(1) Quantity of each product produced or feedstock entering the
process or facility per waste stream per year, from measurement data
and/or other company records. You must use the same basis for all years
in the calculation (i.e., based on production or based on quantity of
feedstock) (metric tons) (Equation TT-2 of Sec. 98.463).
(2) [Reserved]
[FR Doc. 2014-23780 Filed 10-23-14; 8:45 am]
BILLING CODE 6560-50-P