National Emission Standards for Hazardous Air Pollutants: Solvent Extraction for Vegetable Oil Production Residual Risk and Technology Review, 15608-15636 [2020-04459]
Download as PDF
15608
Federal Register / Vol. 85, No. 53 / Wednesday, March 18, 2020 / Rules and Regulations
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 63
[EPA–HQ–OAR–2019–0208; FRL–10006–06–
OAR]
RIN 2060–AU17
National Emission Standards for
Hazardous Air Pollutants: Solvent
Extraction for Vegetable Oil Production
Residual Risk and Technology Review
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
This action finalizes the
residual risk and technology review
(RTR) conducted for the Solvent
Extraction for Vegetable Oil Production
source category regulated under
national emission standards for
hazardous air pollutants (NESHAP).
Based on the results of the U.S.
Environmental Protection Agency’s
(EPA’s) risk review, the Agency is
finalizing the decision that risks due to
emissions of air toxics from this source
category are acceptable and that the
current NESHAP provides an ample
margin of safety to protect public health.
Under the technology review, the EPA
is finalizing the decision that there are
no developments in practices,
processes, or control technologies that
necessitate revision of the standards.
Therefore, the EPA is finalizing no
revisions to the numerical emission
limits based on the risk and technology
reviews. We are taking final action to
correct and clarify regulatory provisions
related to emissions during periods of
startup, shutdown, and malfunction
(SSM), including removing general
exemptions for periods of SSM, adding
alternative work practice standards for
periods of initial startup for new or
significantly modified sources, and
making other minor clarifications or
corrections. The EPA is also taking final
action to add provisions for electronic
reporting of certain notifications and
reports and performance test results;
and make other minor clarifications and
corrections. These final amendments
will result in improved compliance and
implementation of the rule.
DATES: This final rule is effective on
March 18, 2020.
ADDRESSES: The EPA has established a
docket for this action under Docket ID
No. EPA–HQ–OAR–2019–0208. All
documents in the docket are listed on
the https://www.regulations.gov/
website. Although listed, some
information is not publicly available,
e.g., Confidential Business Information
jbell on DSKJLSW7X2PROD with RULES3
SUMMARY:
VerDate Sep<11>2014
20:53 Mar 17, 2020
Jkt 250001
(CBI) or other information whose
disclosure is restricted by statute.
Certain other material, such as
copyrighted material, is not placed on
the internet and will be publicly
available only in hard copy form.
Publicly available docket materials are
available either electronically through
https://www.regulations.gov/, or in hard
copy at the EPA Docket Center, WJC
West Building, Room Number 3334,
1301 Constitution Ave., NW,
Washington, DC. The Public Reading
Room hours of operation are 8:30 a.m.
to 4:30 p.m. Eastern Standard Time
(EST), Monday through Friday. The
telephone number for the Public
Reading Room is (202) 566–1744, and
the telephone number for the EPA
Docket Center is (202) 566–1742.
FOR FURTHER INFORMATION CONTACT: For
questions about this final action, contact
Mr. Bill Schrock, Natural Resources
Group, Sector Policies and Programs
Division (E143–03), Office of Air
Quality Planning and Standards, U.S.
Environmental Protection Agency,
Research Triangle Park, North Carolina
27711; telephone number: (919) 541–
5032; fax number: (919) 541–0516; and
email address: schrock.bill@epa.gov. For
specific information regarding the risk
modeling methodology, contact Mr.
Matthew Woody, Health and
Environmental Impacts Division (C539–
02), Office of Air Quality Planning and
Standards, U.S. Environmental
Protection Agency, Research Triangle
Park, North Carolina 27711; telephone
number: (919) 541–1535; fax number:
(919) 541–0840; and email address:
woody.matthew@epa.gov. For
information about the applicability of
the NESHAP to a particular entity,
contact Ms. Maria Malave, Office of
Enforcement and Compliance
Assurance, U.S. Environmental
Protection Agency, WJC South Building
(Mail Code 2227A), 1200 Pennsylvania
Avenue NW, Washington, DC 20460;
telephone number: (202) 564–7027; and
email address: malave.maria@epa.gov.
SUPPLEMENTARY INFORMATION:
Preamble acronyms and
abbreviations. We use multiple
acronyms and terms in this preamble.
While this list may not be exhaustive, to
ease the reading of this preamble and for
reference purposes, the EPA defines the
following terms and acronyms here:
CAA Clean Air Act
CBI Confidential Business Information
CDX Central Data Exchange
CEDRI Compliance and Emissions Data
Reporting Interface
CFR Code of Federal Regulations
EPA Environmental Protection Agency
HAP hazardous air pollutant(s)
HI hazard index
PO 00000
Frm 00002
Fmt 4701
Sfmt 4700
HQ hazard quotient
ICR Information Collection Request
km kilometer
MACT maximum achievable control
technology
MIR maximum individual risk
NAICS North American Industry
Classification System
NESHAP national emission standards for
hazardous air pollutants
NTTAA National Technology Transfer and
Advancement Act
OMB Office of Management and Budget
PRA Paperwork Reduction Act
REL reference exposure level
RFA Regulatory Flexibility Act
RTR residual risk and technology review
SSM startup, shutdown, and malfunction
the Court United States Court of Appeals
for the District of Columbia Circuit
TOSHI target organ-specific hazard index
tpy tons per year
UMRA Unfunded Mandates Reform Act
VCS voluntary consensus standards
Background information. On June 27,
2019, the EPA proposed revisions to the
Solvent Extraction for Vegetable Oil
Production NESHAP in conjunction
with our RTR for the Solvent Extraction
for Vegetable Oil Production source
category (84 FR 30812). In this action,
we are finalizing decisions and
revisions for the rule. We summarize
some of the more significant comments
we timely received regarding the
proposed rule and provide our
responses in this preamble. A summary
of all other public comments on the
proposal and the EPA’s responses to
those comments is available in the
Summary of Public Comments and
Responses for the Risk and Technology
Review for Solvent Extraction For
Vegetable Oil Production, in Docket ID
No. EPA–HQ–OAR–2019–0208. A
‘‘track changes’’ version of the
regulatory language that incorporates
the changes in this action is available in
the docket.
Organization of this document. The
information in this preamble is
organized as follows:
I. General Information
A. Does this action apply to me?
B. Where can I get a copy of this document
and other related information?
C. Judicial Review and Administrative
Reconsideration
II. Background
A. What is the statutory authority for this
action?
B. What is the Solvent Extraction for
Vegetable Oil Production source category
and how does the NESHAP regulate HAP
emissions from the source category?
C. What changes did we propose for the
Solvent Extraction for Vegetable Oil
Production source category in our June
27, 2019, RTR proposal?
III. What is included in this final rule?
A. What are the final rule amendments
based on the risk review for the Solvent
E:\FR\FM\18MRR3.SGM
18MRR3
Federal Register / Vol. 85, No. 53 / Wednesday, March 18, 2020 / Rules and Regulations
Extraction for Vegetable Oil Production
source category?
B. What are the final rule amendments
based on the technology review for the
Solvent Extraction for Vegetable Oil
Production source category?
C. What are the final rule amendments
addressing emissions during periods of
SSM?
D. What other changes have been made to
the NESHAP?
E. What are the effective and compliance
dates of the standards?
IV. What is the rationale for our final
decisions and amendments for the
Solvent Extraction for Vegetable Oil
Production source category?
A. Residual Risk Review for the Solvent
Extraction for Vegetable Oil Production
Source Category
B. Technology Review for the Solvent
Extraction for Vegetable Oil Production
Source Category
C. SSM for the Solvent Extraction for
Vegetable Oil Production Source
Category
D. Technical amendments to the MACT
standards for the Solvent Extraction for
Vegetable Oil Production Source
Category
V. Summary of Cost, Environmental, and
Economic Impacts and Additional
Analyses Conducted
A. What are the affected sources?
B. What are the air quality impacts?
C. What are the cost impacts?
D. What are the economic impacts?
E. What are the benefits?
F. What analysis of environmental justice
did we conduct?
G. What analysis of children’s
environmental health did we conduct?
VI. Statutory and Executive Order Reviews
A. Executive Orders 12866: Regulatory
Planning and Review and Executive
Order 13563: Improving Regulation and
Regulatory Review
B. Executive Order 13771: Reducing
Regulations and Controlling Regulatory
Costs
C. Paperwork Reduction Act (PRA)
D. Regulatory Flexibility Act (RFA)
E. Unfunded Mandates Reform Act
(UMRA)
F. Executive Order 13132: Federalism
15609
G. Executive Order 13175: Consultation
and Coordination with Indian Tribal
Governments
H. Executive Order 13045: Protection of
Children From Environmental Health
Risks and Safety Risks
I. Executive Order 13211: Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use
J. National Technology Transfer and
Advancement Act (NTTAA)
K. Executive Order 12898: Federal Actions
to Address Environmental Justice in
Minority Populations and Low-Income
Populations
L. Congressional Review Act (CRA)
I. General Information
A. Does this action apply to me?
Regulated entities. Categories and
entities potentially regulated by this
action are shown in Table 1 of this
preamble.
TABLE 1—NESHAP AND INDUSTRIAL SOURCE CATEGORIES AFFECTED BY THIS FINAL ACTION
Source category
Flour Milling ............................................................................
Wet Corn Milling .....................................................................
Fats and Oils Refining and Blending .....................................
Other Animal Food Manufacturing .........................................
Soybean and Other Oilseed Processing ................................
Fats and Oils Refining and Blending .....................................
a North
Solvent Extraction for Vegetable Oil Production ....................
311211
311221
311225
311119
311224
311225
American Industry Classification System.
Table 1 of this preamble is not
intended to be exhaustive, but rather to
provide a guide for readers regarding
entities likely to be affected by the final
action for the source category listed. To
determine whether your facility is
affected, you should examine the
applicability criteria in the appropriate
NESHAP. If you have any questions
regarding the applicability of any aspect
of this NESHAP, please contact the
appropriate person listed in the
preceding FOR FURTHER INFORMATION
CONTACT section of this preamble.
B. Where can I get a copy of this
document and other related
information?
jbell on DSKJLSW7X2PROD with RULES3
NAICS a code
NESHAP
In addition to being available in the
docket, an electronic copy of this final
action will also be available on the
internet. Following signature by the
EPA Administrator, the EPA will post a
copy of this final action at: https://
www.epa.gov/stationary-sources-airpollution/solvent-extraction-vegetableoil-production-national-emission.
Following publication in the Federal
Register, the EPA will post the Federal
VerDate Sep<11>2014
20:53 Mar 17, 2020
Jkt 250001
Register version and key technical
documents at this same website.
Additional information is available on
the RTR website at https://
www.epa.gov/stationary-sources-airpollution/risk-and-technology-reviewnational-emissions-standardshazardous. This information includes
an overview of the RTR program and
links to project websites for the RTR
source categories.
C. Judicial Review and Administrative
Reconsideration
Under Clean Air Act (CAA) section
307(b)(1), judicial review of this final
action is available only by filing a
petition for review in the United States
Court of Appeals for the District of
Columbia Circuit (the Court) by May 18,
2020. 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 the
requirements.
Section 307(d)(7)(B) of the CAA
further provides that only an objection
to a rule or procedure which was raised
with reasonable specificity during the
PO 00000
Frm 00003
Fmt 4701
Sfmt 4700
period for public comment (including
any public hearing) may be raised
during judicial review. This section also
provides a mechanism for the EPA to
reconsider the rule if the person raising
an objection can demonstrate to the
Administrator 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 should
submit a Petition for Reconsideration to
the Office of the Administrator, U.S.
EPA, Room 3000, WJC South Building,
1200 Pennsylvania Ave. NW,
Washington, DC 20460, with a copy to
both the person(s) listed in the
preceding FOR FURTHER INFORMATION
CONTACT section, and the Associate
General Counsel for the Air and
Radiation Law Office, Office of General
Counsel (Mail Code 2344A), U.S. EPA,
1200 Pennsylvania Ave. NW,
Washington, DC 20460.
E:\FR\FM\18MRR3.SGM
18MRR3
15610
Federal Register / Vol. 85, No. 53 / Wednesday, March 18, 2020 / Rules and Regulations
jbell on DSKJLSW7X2PROD with RULES3
II. Background
A. What is the statutory authority for
this action?
Section 112 of the CAA establishes a
two-stage regulatory process to address
emissions of hazardous air pollutants
(HAP) from stationary sources. In the
first stage, we must identify categories
of sources emitting one or more of the
HAP listed in CAA section 112(b) and
then promulgate technology-based
NESHAP for those sources. ‘‘Major
sources’’ are those that emit, or have the
potential to emit, any single HAP at a
rate of 10 tons per year (tpy) or more,
or 25 tpy or more of any combination of
HAP. For major sources, these standards
are commonly referred to as maximum
achievable control technology (MACT)
standards and must reflect the
maximum degree of emission reductions
of HAP achievable (after considering
cost, energy requirements, and non-air
quality health and environmental
impacts). In developing MACT
standards, CAA section 112(d)(2) directs
the EPA to consider the application of
measures, processes, methods, systems,
or techniques, including, but not limited
to, those that reduce the volume of or
eliminate HAP emissions through
process changes, substitution of
materials, or other modifications;
enclose systems or processes to
eliminate emissions; collect, capture, or
treat HAP when released from a process,
stack, storage, or fugitive emissions
point; are design, equipment, work
practice, or operational standards; or
any combination of the above.
For these MACT standards, the statute
specifies certain minimum stringency
requirements, which are referred to as
MACT floor requirements, and which
may not be based on cost considerations
(see CAA section 112(d)(3)). For new
sources, the MACT floor cannot be less
stringent than the emission control
achieved in practice by the bestcontrolled similar source. The MACT
standards for existing sources can be
less stringent than floors for new
sources, but they cannot be less
stringent than the average emission
limitation achieved by the bestperforming 12 percent of existing
sources in the category or subcategory
(or the best-performing five sources for
categories or subcategories with fewer
than 30 sources). In developing MACT
standards, we must also consider
control options that are more stringent
than the floor under CAA section
112(d)(2). We may establish standards
more stringent than the floor, based on
the consideration of the cost of
achieving the emissions reductions, any
non-air quality health and
VerDate Sep<11>2014
20:53 Mar 17, 2020
Jkt 250001
environmental impacts, and energy
requirements.
In the second stage of the regulatory
process, the CAA requires the EPA to
undertake two different analyses, which
we refer to as the technology review and
the residual risk review. Under the
technology review, we must review the
technology-based standards and revise
them ‘‘as necessary (taking into account
developments in practices, processes,
and control technologies)’’ no less
frequently than every 8 years, pursuant
to CAA section 112(d)(6). Under the
residual risk review, we must evaluate
the risk to public health remaining after
application of the technology-based
standards and revise the standards, if
necessary, to provide an ample margin
of safety to protect public health or to
prevent, taking into consideration costs,
energy, safety, and other relevant
factors, an adverse environmental effect.
The residual risk review is required
within 8 years after promulgation of the
technology-based standards, pursuant to
CAA section 112(f). In conducting the
residual risk review, if the EPA
determines that the current standards
provide an ample margin of safety to
protect public health, it is not necessary
to revise the MACT standards pursuant
to CAA section 112(f).1 For more
information on the statutory authority
for this rule, see 84 FR 30812, June 27,
2019.
B. What is the Solvent Extraction for
Vegetable Oil Production source
category and how does the NESHAP
regulate HAP emissions from the source
category?
The EPA promulgated the Solvent
Extraction for Vegetable Oil Production
NESHAP on April 12, 2001 (66 FR
19006). The standards are codified at 40
CFR part 63, subpart GGGG. As
promulgated in 2001 and further
amended on April 5, 2002 (67 FR
16317), and September 1, 2004 (69 FR
53338), the NESHAP regulates HAP
emissions from solvent extraction for
vegetable oil production processes at a
facility that is a major source of HAP
emissions. The affected source is each
vegetable oil production process. A
vegetable oil production process means
the equipment comprising a continuous
process for producing crude vegetable
oil and meal products, including
specialty soybean products, in which oil
is removed from oilseeds listed in Table
1 The Court has affirmed this approach of
implementing CAA section 112(f)(2)(A): NRDC v.
EPA, 529 F.3d 1077, 1083 (DC Cir. 2008) (‘‘If EPA
determines that the existing technology-based
standards provide an ‘ample margin of safety,’ then
the Agency is free to readopt those standards during
the residual risk rulemaking.’’).
PO 00000
Frm 00004
Fmt 4701
Sfmt 4700
1 of 40 CFR 63.2840 through direct
contact with an organic solvent. Process
equipment typically includes the
following components: oilseed
preparation operations (including
conditioning, drying, dehulling, and
cracking), solvent extractors,
desolventizer-toasters, meal dryers,
meal coolers, meal conveyor systems,
oil distillation units, solvent evaporators
and condensers, solvent recovery
system (also referred to as a mineral oil
absorption system), vessels storing
solvent-laden materials, and crude meal
packaging and storage vessels. A
vegetable oil production process does
not include vegetable oil refining
operations (including operations such as
bleaching, hydrogenation, and
deodorizing) and operations that engage
in additional chemical treatment of
crude soybean meals produced in
specialty desolventizer units (including
operations such as soybean isolate
production). The source category
covered by this MACT standard
currently includes 89 facilities.
The primary HAP emitted from
vegetable oil production processes is nhexane. The EPA does not consider nhexane classifiable as a human
carcinogen. However, short-term
exposure to n-hexane can cause
reactions such as irritation, dizziness,
headaches, and nausea. Long-term
exposure can cause permanent nerve
damage.
The current NESHAP controls facilitywide n-hexane emissions by setting
emission limitations based on the
number of gallons of HAP lost per ton
of oilseeds processed, expressed as
oilseed solvent loss ratios. Facilities
demonstrate compliance by calculating
a compliance ratio comparing the actual
HAP loss to the allowable HAP loss for
the previous 12 operating months.
Allowable HAP loss is based on the
oilseed solvent loss ratios provided in
Table 1 of 40 CFR 63.2840 of the rule
for new and existing sources.
Compliance is demonstrated when the
facility’s calculated compliance ratio is
less than or equal to 1.00 (i.e., the actual
HAP loss is no greater than the
calculated allowable HAP loss).
Determination of compliance with the
requirements of the Solvent Extraction
for Vegetable Oil Production NESHAP
requires the facility to keep records of
the amount of n-hexane purchased,
used, and recovered from the oilseed
extraction process, the amount of
oilseed processed, and the volume
fraction of each HAP exceeding 1
percent in the extraction solvent used.
Facilities may also adjust their solvent
loss to account for cases where solvent
is routed through a closed vent system
E:\FR\FM\18MRR3.SGM
18MRR3
Federal Register / Vol. 85, No. 53 / Wednesday, March 18, 2020 / Rules and Regulations
to a control device that is used to reduce
emissions to meet the standard.
jbell on DSKJLSW7X2PROD with RULES3
C. What changes did we propose for the
Solvent Extraction for Vegetable Oil
Production source category in our June
27, 2019, RTR proposal?
On June 27, 2019, the EPA published
a proposed rule in the Federal Register
for the Solvent Extraction for Vegetable
Oil Production NESHAP, 40 CFR part
63, subpart GGGG, that took into
consideration the RTR analyses. In the
proposed rule, we proposed that the
risks from the source category are
acceptable and the current standards
provide an ample margin of safety to
protect public health. In addition,
pursuant to the technology review for
the Solvent Extraction for Vegetable Oil
Production source category, we
proposed no revisions to the current
standards based on these analyses.
We proposed revisions to the SSM
provisions of the standards to ensure
that they are consistent with the Court
decision in Sierra Club v. EPA, 551 F.
3d 1019 (D.C. Cir. 2008). Specifically,
the Court vacated the SSM exemption
contained in 40 CFR 63.6(f)(1) and 40
CFR 63.6(h)(1), holding that under
section 302(k) of the CAA, emissions
standards or limitations must be
continuous in nature and that the SSM
exemption violates the CAA’s
requirement that some CAA section 112
standards apply continuously. We
therefore proposed that the standards
would apply at all times, including
during startups, shutdowns, and
malfunctions (see 40 CFR 63.2840(a)
and Table 1 to 40 CFR 63.2870 (General
Provisions Applicability Table).
Additionally, we proposed to remove
requirements that allowed sources to
previously designate a source operating
status period as a ‘‘malfunction period’’
and exclude data collected during the
‘‘malfunction period’’ when
determining compliance with the
emission standards.2 Under the
2 The 2001 NESHAP allowed for facilities to
determine compliance based on the distinct
categorized operating status of the facility (normal
operating, nonoperating, initial startup,
malfunction, or exempt) during a compliance
period, as defined in Table 1 of 40 CFR 63.2853.
Existing and new sources operating during a
malfunction period could either meet the
compliance requirements for normal operation
periods in 40 CFR 63.2850 and Table 1 of 40 CFR
63.2850 or the requirements for malfunction
periods subject to 40 CFR 63.2850(e)(2) and Table
1 of 40 CFR 63.2850 (for which no limits or work
practices applied). Sources operating during a
malfunction period were not required to determine
compliance using data recorded for the malfunction
period. We proposed to remove the option for
facilities to categorize the operating period as a
malfunction period and to remove the option to
meet the requirements for malfunction periods
subject to 40 CFR 63.2850(e)(2) and Table 1 of 40
VerDate Sep<11>2014
20:53 Mar 17, 2020
Jkt 250001
15611
proposed rule, sources that continue to
operate must instead meet the emission
standard requirements for either a
normal operating period or the work
practice standards for an initial startup
period (if applicable) in 40 CFR 63.2850
and Table 1 of 40 CFR 63.2850. In
proposing the revised standards, the
EPA considered whether to set separate
standards for startup and shutdown
periods, but only found that separate
standards were necessary for initial
startup periods for new or significantly
modified sources. For periods of initial
startup following new construction or
significant modification, we proposed
work practice standards and a
requirement to establish and follow sitespecific operating ranges for
temperature and vacuum for the
desolventizing and oil distillation units
associated with solvent recovery, as
well as associated recordkeeping and
reporting requirements (e.g., initial
startup report) for these periods.
We proposed to require electronic
reporting of initial notifications, initial
startup reports, annual compliance
certifications, deviation reports, and
performance test reports through the
EPA’s Central Data Exchange (CDX)
using the Compliance and Emissions
Data Reporting Interface (CEDRI). We
also proposed minor clarifications and
corrections to five definitions (i.e.,
‘‘Compliance ratio,’’ ‘‘Nonoperating
period,’’ ‘‘Normal operating period,’’
‘‘Operating month,’’ and ‘‘Hazardous air
pollutant (HAP)’’) and to 40 CFR
63.2840(a)(1) and (b)(1), 40 CFR
63.2853(a)(2), 40 CFR 63.2855(a)(3), and
Table 1 of 40 CFR 63.2850. Refer to
section IV.D of the June 27, 2019,
proposal preamble for further
discussion of these proposed
amendments and the EPA’s rationale for
these changes (84 FR 60825).
reports, annual compliance
certifications, deviation reports, and
performance test reports; and other
minor editorial and technical changes.
This action reflects several changes to
the proposed rule in consideration of
comments received during the public
comment period as described in section
IV of this preamble.
III. What is included in this final rule?
This action finalizes the EPA’s
determinations pursuant to the RTR
provisions of CAA section 112 for the
Solvent Extraction for Vegetable Oil
Production source category. This action
also finalizes other changes to the
NESHAP, including revisions to the
SSM provisions of the MACT rule in
order to ensure that they are consistent
with the Court decision in Sierra Club
v. EPA, 551 F. 3d 1019 (D.C. Cir. 2008),
provisions for electronic reporting of
initial notifications, initial startup
C. What are the final rule amendments
addressing emissions during periods of
SSM?
We are finalizing the proposed
amendments to the Solvent Extraction
for Vegetable Oil Production NESHAP
to remove and revise provisions related
to SSM. As detailed in section IV.D of
the proposal preamble (84 FR 30825),
the final amendments to the Solvent
Extraction for Vegetable Oil Production
NESHAP require that the standards
apply at all times (see 40 CFR 63.2840(a)
and Table 1 to 40 CFR 63.2870 (General
Provisions applicability table),
consistent with the Court decision in
Sierra Club v. EPA, 551 F. 3d 1019 (D.C.
Cir. 2008).
We are finalizing that the emission
standards for normal operation apply at
all times, except for periods of initial
CFR 63.2850, such that the standards apply at all
times. Sources that continue to operate during a
malfunction must continue to meet the general duty
requirements at 40 CFR 63.2840(g). The term
‘‘malfunction period’’ is retained in the rule only
as it applies to facilities prior to September 15,
2020.
PO 00000
Frm 00005
Fmt 4701
Sfmt 4700
A. What are the final rule amendments
based on the risk review for the Solvent
Extraction for Vegetable Oil Production
source category?
This section describes the final risk
determination for the Solvent Extraction
for Vegetable Oil Production NESHAP
being promulgated pursuant to CAA
section 112(f). The EPA proposed no
changes to the Solvent Extraction for
Vegetable Oil Production NESHAP
based on the risk review conducted
pursuant to CAA section 112(f). In this
action, we are finalizing our proposed
determination that risks from this
source category are acceptable, and that
the standards provide an ample margin
of safety to protect public health and
prevent an adverse environmental
effect. Section IV.A.3 of this preamble
provides a summary of key comments
we received regarding the risk review
and our responses to those comments.
B. What are the final rule amendments
based on the technology review for the
Solvent Extraction for Vegetable Oil
Production source category?
The EPA is finalizing the technology
review as proposed. We determined that
there are no developments in practices,
processes, and control technologies that
warrant revisions to the MACT
standards for this source category.
Therefore, we are not finalizing
revisions to the MACT standards under
CAA section 112(d)(6).
E:\FR\FM\18MRR3.SGM
18MRR3
jbell on DSKJLSW7X2PROD with RULES3
15612
Federal Register / Vol. 85, No. 53 / Wednesday, March 18, 2020 / Rules and Regulations
startup for new and significantly
modified sources, as described below in
this section and in section IV.C of this
preamble. For periods of initial startup
for new or significantly modified
sources, we are finalizing work practice
standards, including operation of the
mineral oil absorption system and
solvent condensers at all times during
the initial startup period, and a
requirement to establish and follow sitespecific operating ranges for
temperature and vacuum for the
desolventizing and oil distillation units
associated with solvent recovery, as
well as associated recordkeeping and
reporting requirements (e.g., initial
startup report) for these periods.
Facilities will continue to have the
option to meet the requirements for
normal operating periods in Table 1 of
40 CFR 63.2850. The EPA is also
finalizing the definition of ‘‘initial
startup period’’ and the requirements of
40 CFR 62.2850(c)(2) and (d)(2) to
clarify that the end of the initial startup
period occurs when the plant meets and
maintains steady-state operations.
Steady-state is defined as operating at or
above 90 percent of the extractor
nominal design production rate or at or
above 90 percent of the production rate
in the plant’s permit for 15 consecutive
days. Any initial startup period may not
exceed 6 calendar months after startup
for new or reconstructed sources or 3
calendar months after startup for
modified sources.
As discussed in section IV.D of the
June 27, 2019, proposal preamble, the
EPA interprets CAA section 112 as not
requiring emissions that occur during
periods of malfunction to be factored
into development of CAA section 112
standards, although the EPA has the
discretion to set standards for
malfunctions where feasible. We noted
that our interpretation regarding CAA
section 112 not requiring emissions that
occur during periods of malfunction to
be factored into development of CAA
section 112 standards has been upheld
as reasonable by the Court in U.S. Sugar
Corp. v. EPA, 830 F.3d 579, 606–610
(2016). The EPA further explained that,
‘‘EPA will consider whether
circumstances warrant setting standards
for a particular type of malfunction and,
if so, whether the EPA has sufficient
information to identify the relevant best
performing sources and establish a
standard for such malfunctions’’ (84 FR
30827).
While we requested comment on
work practice standards during periods
of malfunction, and received some
information in support of such
standards, we did not receive sufficient
information on which to base a
VerDate Sep<11>2014
20:53 Mar 17, 2020
Jkt 250001
malfunction standard. As further
explained at proposal, ‘‘[i]n the event
that a source fails to comply with the
applicable CAA section 112(d)
standards as a result of a malfunction
event, the EPA would determine an
appropriate response based on, among
other things, the good faith efforts of the
source to minimize emissions during
malfunction periods, including
preventive and corrective actions, as
well as root cause analyses to ascertain
and rectify excess emissions. The EPA
would also consider whether the
source’s failure to comply with the CAA
section 112(d) standard was, in fact,
sudden, infrequent, not reasonably
preventable and was not instead caused
in part by poor maintenance or careless
operation. 40 CFR 63.2 (definition of
malfunction). If the EPA determines in
a particular case that an enforcement
action against a source for violation of
an emission standard is warranted, the
source can raise any and all defenses in
that enforcement action and the Federal
district court will determine what, if
any, relief is appropriate. The same is
true for citizen enforcement actions.
Similarly, the presiding officer in an
administrative proceeding can consider
any defense raised and determine
whether administrative penalties are
appropriate’’ (84 FR 30828).
For these reasons, we are not setting
separate standards for periods of
malfunction. Under the final rule,
sources that experience an unscheduled
shutdown as a result of a malfunction,
continue to operate during a
malfunction (including the period
reasonably necessary to correct the
malfunction), or start up after a
shutdown resulting from a malfunction
must instead meet the emission
standard requirements for either a
normal operating period or the work
practice standards for an initial startup
period (if a new or significantly
modified source) in 40 CFR 63.2850 and
Table 1 of 40 CFR 63.2850. Although we
did not propose and are not finalizing
work practice standards for periods of
malfunction, we are finalizing revisions
to deviation reporting to account for
one-time malfunction events in which
the potential solvent loss could result in
a deviation for one or more consecutive
monthly compliance ratio
determinations. Specifically, we have
revised the final rule to include a
requirement that facilities flag and
provide an explanation for any
deviation from the compliance ratio for
which a deviation report is being
submitted for more than one
consecutive month (i.e., include a
reference to the original date and
PO 00000
Frm 00006
Fmt 4701
Sfmt 4700
reporting of the deviation). Although a
facility would need to retain records of
any deviation and the corrective
action(s) performed, no additional
corrective action would be required at
the time the 12-month compliance ratio
is officially exceeded in subsequent
months if the facility demonstrates the
exceedance is from a prior malfunction
that has been corrected.
As is explained in more detail below,
we are finalizing revisions related to
requirements that apply during periods
of SSM. We eliminated or revised
certain recordkeeping and reporting
requirements related to the eliminated
SSM exemption. The EPA also made
changes to the rule to remove or modify
inappropriate, unnecessary, or
redundant language in the absence of
the SSM exemption. Refer to sections
III.C.1 through III.C.6 of this preamble
for a detailed discussion of the final
amendments.
1. 40 CFR 63.2840
General Duty
We are finalizing as proposed
revisions to the General Provisions
applicability table (Table 1 to 40 CFR
63.2870) entry for 40 CFR 63.6(e)(1)(i)
by changing the ‘‘Yes’’ in column 4 to
a ‘‘No.’’ The EPA is instead adding
general duty regulatory text at 40 CFR
63.2840(g) to reflect the general duty to
minimize emissions while eliminating
the reference to periods covered by an
SSM exemption. The general duty to
minimize emissions continues to apply
during periods of malfunction and
sources must still address malfunctions
expeditiously in order to maintain any
affected source, including associated air
pollution control equipment and
monitoring equipment, and minimize
emissions. The EPA is also revising the
General Provisions applicability table
(Table 1 to 40 CFR 63.2870) entry for 40
CFR 63.6(e)(1)(ii) by changing the ‘‘Yes’’
in column 4 to a ‘‘No’’ to remove
requirements that are not necessary with
the elimination of the SSM exemption
or are redundant with the general duty
requirement being added at 40 CFR
63.2840(g).
2. SSM Plan
As proposed, the EPA is revising the
General Provisions applicability table
(Table 1 to 40 CFR 63.2870) entries for
40 CFR 63.6(e)(3)(i) through (e)(3)(ii), 40
CFR 63.6(e)(3)(v) through (vii), and 40
CFR 63.6(e)(3)(viii) and (ix) by changing
the ‘‘Yes’’ in column 4 to a ‘‘No.’’ The
EPA is also revising 40 CFR 63.2852,
which cross-references the requirements
of 40 CFR 63.6(e)(3). The final
amendments remove requirements
related to the SSM plan.
E:\FR\FM\18MRR3.SGM
18MRR3
Federal Register / Vol. 85, No. 53 / Wednesday, March 18, 2020 / Rules and Regulations
3. Compliance With Standards
The EPA is revising the General
Provisions applicability table (Table 1 to
40 CFR 63.2870) entry for 40 CFR
63.6(f)(1) by revising the text in column
4 and removing the text in column 5 to
clarify that the SSM exemption
previously applied but will not apply
going forward.
4. 40 CFR 63.2853
Testing
Performance
We are also finalizing a revision to the
performance testing requirements. The
EPA is revising the General Provisions
applicability table (Table 1 to 40 CFR
63.2870) entry for 40 CFR 63.7(e)(1) by
changing the ‘‘Yes’’ in column 4 to a
‘‘No,’’ and adding a revised performance
testing requirement at 40 CFR
63.2853(a)(5)(i)(A). The final
performance testing provisions prohibit
performance testing for purposes of
demonstrating compliance during
startup, shutdown, or malfunction
because these conditions are not
representative of normal operating
periods. The final rule also requires that
operators maintain records to document
that operating conditions during the test
represent normal operations.
jbell on DSKJLSW7X2PROD with RULES3
5. 40 CFR 63.2862
Recordkeeping
The EPA is revising the General
Provisions applicability table (Table 1 to
40 CFR 63.2870) entry for 40 CFR
63.10(b)(2)(i) by changing the ‘‘Yes’’ in
column 4 to a ‘‘No,’’ and is adding
recordkeeping requirements to 40 CFR
63.2862(f). The final revisions require
owners or operators of sources subject to
a work practice standard during initial
startup times to report a description and
dates of the initial startup period, the
reason it qualifies as an initial startup
period, an estimate of the solvent loss in
gallons for the duration of the initial
startup, and the nominal design rate and
operating rate of the extractor or the
permitted and actual production rates
for the duration of the initial startup
period. The final revisions also require
facilities to record information
including the measured temperature
and pressure for desolventizing and oil
distillation units; an indication that the
mineral oil absorption system was
operating at all times; and (3) an
indication that the solvent condensers
were operating at all times.
The EPA is revising the General
Provisions applicability table (Table 1 to
40 CFR 63.2870) entry for 40 CFR
63.10(b)(2)(ii) by changing the ‘‘Yes’’ in
column 4 to a ‘‘No.’’ The final rule
includes recordkeeping requirements for
malfunctions in 40 CFR 63.2862(g),
including any ‘‘failure to meet an
VerDate Sep<11>2014
20:53 Mar 17, 2020
Jkt 250001
applicable standard’’ (including any
deviation from the emissions standards
of 40 CFR 63.2840 or the work practice
standards for periods of initial startup).
Source owners or operators must record
the date and duration of the ‘‘failure.’’
We have revised the final rule
requirements from proposal to clarify
how to designate the date a deviation
occurred and the duration of the
deviation. For deviations from the
compliance ratio, the date of the
deviation is the date the compliance
ratio determination is made, and the
duration of the deviation is the length
of time taken to address the cause of the
deviation (including the duration of any
malfunction) and to return the affected
unit(s) to its normal or usual manner of
operation. For deviations from the work
practice standard during the initial
startup period, the date of the deviation
is the date when the facility fails to
comply with any of the work practice
standards in 40 CFR 63.2840(h), and the
duration of the deviation is the length
of time taken to return to the work
practice standards. We have also
removed the requirement to record and
report the time of the deviation as
described in section IV.C of this
preamble.
The EPA is adding to 40 CFR
63.2862(g) a requirement that source
owners or operators keep records that
include a statement of the cause of each
deviation (including unknown cause, if
applicable), a list of the affected source
or equipment and actions taken to
minimize emissions, an estimate of the
quantity of each regulated pollutant
emitted over the standard when the
standard is not met, and a description
of the method used to estimate the
emissions.
The EPA is revising the General
Provisions applicability table (Table 1 to
40 CFR 63.2870) entry for 40 CFR
63.10(b)(2)(iv) and 40 CFR 63.10(b)(2)(v)
by changing the ‘‘Yes’’ in column 4 to
a ‘‘No’’ to remove requirements related
to the SSM plan. The final rule includes
a requirement to record actions to
minimize emissions and record
corrective actions in 40 CFR 63.2862(g).
6. 40 CFR 63.2861 Reporting
To replace the SSM reporting
requirements, the EPA is eliminating the
periodic SSM reports in 40 CFR
63.2861(c), which were required to be
submitted at the end of each calendar
month of an initial startup period or
malfunction period. The EPA is also
removing the requirement in 40 CFR
63.2861(d) to submit an immediate
report for SSM when a source failed to
meet an applicable standard but did not
follow the SSM plan. The EPA is
PO 00000
Frm 00007
Fmt 4701
Sfmt 4700
15613
instead requiring that existing or new
source owners or operators that fail to
meet the applicable emission standards
(including sources that experience a
malfunction) or the work practice
standards for initial startup periods at
any time must report the information
concerning such events in the deviation
report, including the number, date,
duration, and the cause of such events
(including unknown cause, if
applicable), a list of the affected source
or equipment, an estimate of the
quantity of HAP emitted over the
emission requirements of 40 CFR
63.2840, and a description of the
method used to estimate the emissions.
For sources operating under an initial
startup period, the EPA is also finalizing
a provision that source owners or
operators that fail to meet the work
practice standard must include a
description of the deviation and include
the records for the initial startup period
in 40 CFR 63.2862(f).
Finally, the EPA is finalizing that
source owners or operators that choose
to operate under an initial startup
period according to 40 CFR
63.2850(c)(2) or (d)(2) must also provide
an initial startup report, including a
compliance certification indicating
whether the source was in compliance
with the work practice standard of 40
CFR 63.2840(h). The initial report must
be submitted within 30 days of the end
of the initial startup period.
The legal rationale and detailed
changes for SSM periods that we are
finalizing here are set forth in the
proposed rule (see 84 FR 30825).
Section IV.C of this preamble provides
a summary of key comments we
received on the SSM provisions and our
responses.
D. What other changes have been made
to the NESHAP?
This rule also finalizes, as proposed,
revisions to several other NESHAP
requirements. To increase the ease and
efficiency of data submittal and data
accessibility, we are finalizing a
requirement that owners and operators
of facilities in the Solvent Extraction for
Vegetable Oil Production source
category submit electronic copies of
initial notifications, initial startup
reports, annual compliance
certifications, deviation reports, and
performance test reports through the
EPA’s CDX using the CEDRI. The initial
notifications, initial startup reports,
annual compliance certifications,
deviation reports, and performance test
reports are required to be submitted
according to the deadlines specified in
40 CFR 63.2861. We also are finalizing,
as proposed, provisions that allow
E:\FR\FM\18MRR3.SGM
18MRR3
15614
Federal Register / Vol. 85, No. 53 / Wednesday, March 18, 2020 / Rules and Regulations
facility operators the ability to seek
extensions for submitting electronic
reports for circumstances beyond the
control of the facility, i.e., for a possible
outage in the CDX or CEDRI or for a
force majeure event in the time just
prior to a report’s due date, as well as
the process to assert such a claim.
The EPA is finalizing several minor
technical editorial changes to the rule.
The EPA is finalizing several definitions
in 40 CFR 63.2872 to harmonize with
the removal of the SSM requirements
and to clarify existing provisions. The
definitions of ‘‘Compliance ratio,’’
‘‘Nonoperating period,’’ ‘‘Normal
operating period,’’ and ‘‘Operating
month’’ are revised in the final rule to
clarify that we have removed
malfunction periods as a distinct source
operating status during which no limits
or work practices applied. The
definition of ‘‘Normal operating period’’
is also revised to clarify that this
definition also applies to ‘‘normal
operation.’’
The EPA is revising the definition of
‘‘Hazardous Air Pollutant (HAP)’’ as
proposed to remove the reference to the
date of April 12, 2001. Finally, the EPA
is adding a definition for ‘‘Nonoperating
month’’ as proposed.
The EPA is finalizing minor revisions
to 40 CFR 63.2840(a)(1) and (b)(1), 40
CFR 63.2853(a)(2), and 40 CFR
63.2855(a)(3) to remove text that is
redundant with the definition of
‘‘Operating month’’ in 40 CFR 63.2872.
Finally, the EPA is revising Table 1 of
40 CFR 63.2850 to correct a
typographical error in row ‘‘(a)’’ for
malfunction periods.
The legal rationale and detailed
changes for these revisions are set forth
in the proposed rule (see 84 FR 30830).
E. What are the effective and
compliance dates of the standards?
The revisions to the MACT standards
being promulgated in this action are
effective on March 18, 2020.
Existing affected sources and affected
sources that commenced construction or
reconstruction on or before June 27,
2019, must comply with the
amendments no later than 180 days after
March 18, 2020. Affected sources that
commence construction or
reconstruction after June 27, 2019 must
comply with all requirements of 40 CFR
part 63, subpart GGGG, no later than the
effective date of the final rule or upon
startup, whichever is later. The EPA is
finalizing three changes that would
affect ongoing compliance requirements
for the Solvent Extraction for Vegetable
Oil Production NESHAP. First, for all
sources, we are finalizing a requirement
that initial notifications, initial startup
reports, annual compliance
certifications, deviation reports, and
performance test results be
electronically submitted. Next, the EPA
is finalizing changing the requirements
for SSM by removing the exemption
from the requirements to meet the
standard during SSM periods. For new
or significantly modified sources, we are
finalizing an option for facilities to
follow new work practice standards for
periods of initial startup. From our
assessment of the timeframe needed for
implementing the entirety of the revised
requirements, the EPA proposed a
period of 180 days to be the most
expeditious compliance period
practicable for existing affected sources
or affected sources that commenced
construction or reconstruction on or
before June 27, 2019. No comments on
the compliance period were received
during the public comment period and
the 180-day period is being finalized as
proposed. Thus, the compliance date of
the final amendments for all existing
sources and new sources that
commenced construction or
reconstruction on or before June 27,
2019, will be September 15, 2020. The
compliance date of the final
amendments for new sources that
commence construction or
reconstruction after June 27, 2019, will
be March 18, 2020.
IV. What is the rationale for our final
decisions and amendments for the
Solvent Extraction for Vegetable Oil
Production source category?
For each issue, this section provides
a description of what we proposed and
what we are finalizing for the issue, the
EPA’s rationale for the final decisions
and amendments, and a summary of key
comments and responses. For all
comments not discussed in this
preamble, comment summaries, and the
EPA’s responses can be found in the
comment summary and response
document, Summary of Public
Comments and Responses for the Risk
and Technology Review for Solvent
Extraction For Vegetable Oil Production,
which is available in the docket for this
rulemaking.
A. Residual Risk Review for the Solvent
Extraction for Vegetable Oil Production
Source Category
1. What did we propose pursuant to
CAA section 112(f) for the Solvent
Extraction for Vegetable Oil Production
source category?
Pursuant to CAA section 112(f), the
EPA conducted a residual risk review
and presented the results of this review,
along with our proposed decisions
regarding risk acceptability and ample
margin of safety, in the June 27, 2019,
proposed rule for 40 CFR part 63,
subpart GGGG (84 FR 30812). The
results of the risk assessment for the
proposal are presented briefly in Table
2 of this preamble. More detail may be
found in the residual risk technical
support document, Residual Risk
Assessment for the Solvent Extraction
for Vegetable Oil Production Source
Category in Support of the 2019 Risk
and Technology Review Final Rule,
which is available in the docket for this
rulemaking.
TABLE 2—SOLVENT EXTRACTION FOR VEGETABLE OIL PRODUCTION INHALATION PROPOSED RISK ASSESSMENT RESULTS
Number of
facilities 1
Maximum
individual
cancer risk
(in 1 million) 2
Estimated
population
at increased
risk of cancer
≥1-in-1 million
Estimated
annual cancer
incidence
(cases per
year)
88 ....................................
Maximum screening acute
noncancer HQ
Maximum chronic noncancer TOSHI 3
Based on Actual Emissions Level
<1
0
0.00005
0.7 (n-hexane) ..........................................
HQREL = 0.7 (acrolein)
jbell on DSKJLSW7X2PROD with RULES3
Based on Allowable Emissions Level
<1
0
0.0002
2 (n-hexane) .............................................
N/A
1 Number
of facilities evaluated in the risk analysis.
individual excess lifetime cancer risk due to HAP emissions from the source category.
target organ with the highest target organ-specific hazard index (TOSHI) for the Solvent Extraction for Vegetable Oil Production source category is the nervous system (neurocognitive and neurobehavioral effects).
2 Maximum
3 The
VerDate Sep<11>2014
20:53 Mar 17, 2020
Jkt 250001
PO 00000
Frm 00008
Fmt 4701
Sfmt 4700
E:\FR\FM\18MRR3.SGM
18MRR3
jbell on DSKJLSW7X2PROD with RULES3
Federal Register / Vol. 85, No. 53 / Wednesday, March 18, 2020 / Rules and Regulations
The results of the proposed inhalation
risk assessment using actual emissions
data, as shown in Table 2 of this
preamble, indicate the estimated cancer
maximum individual risk (MIR) is less
than 1-in-1 million. At proposal, the
total estimated cancer incidence from
this source category was estimated to be
0.00005 excess cancer cases per year, or
1 case every 20,000 years and for
allowable emissions was 0.0002 excess
cancer cases per year, or 1 case every
5,000 years driven by emissions of
acetaldehyde and formaldehyde. At
proposal, the maximum modeled
chronic noncancer TOSHI for the source
category based on actual emissions was
estimated to be 0.7 and, for allowable
emissions, was estimated to be 2 due to
emissions of n-hexane. Approximately
13 people were estimated to have
exposures resulting in a TOSHI greater
than 1 if exposed to allowable emissions
from this source category.
As shown in Table 2 of this preamble,
the worst-case acute hazard quotient
(HQ) (based on the reference exposure
level (REL)) at proposal was less than 1
(0.7 based on the REL for acrolein). This
value is the highest HQ that is outside
facility boundaries. The multipathway
risk screening assessment did not
identify emissions of any HAP known to
be persistent and bio-accumulative in
the environment; therefore, no further
evaluation of multipathway risk was
conducted for this source category.
Further, because we did not identify
environmental HAP emissions, no
quantitative environmental risk
screening was conducted for this source
category.
We conducted an assessment of
facility-wide risks. The maximum
lifetime individual cancer risk posed by
the 88 facilities, based on facility-wide
emissions at proposal, was 5-in-1
million with cadmium, nickel, arsenic,
chromium (VI), and formaldehyde
emissions from facility-wide external
combustion boilers driving the risk. The
maximum chronic noncancer TOSHI
posed by facility-wide emissions was
estimated to be 0.7 (for the nervous
system) driven by source category nhexane emissions.
We weighed all health risk factors,
including those shown in Table 2 of this
preamble, in our risk acceptability
determination and proposed that the
risks from the Solvent Extraction for
Vegetable Oil Production source
category are acceptable (section IV.C.1
of proposal preamble, 84 FR 30812, June
27, 2019).
We then considered whether the
existing MACT standards for this source
category provide an ample margin of
safety to protect public health and
VerDate Sep<11>2014
20:53 Mar 17, 2020
Jkt 250001
whether, taking into consideration costs,
energy, safety, and other relevant
factors, standards are required to
prevent an adverse environmental
effect. In considering whether standards
are required to provide an ample margin
of safety to protect public health, we
considered the same risk factors that we
considered for our acceptability
determination and also considered the
costs, technological feasibility, and
other relevant factors related to
emissions control options that might
reduce risk associated with emissions
from the source category. We proposed
that the current standards provide an
ample margin of safety to protect public
health and revision of the standards for
the Solvent Extraction for Vegetable Oil
Production source category are not
required to provide an ample margin of
safety to protect public health. We also
proposed that it is not necessary to set
a more stringent standard to prevent,
taking into consideration costs, energy,
safety, and other relevant factors, an
adverse environmental effect (see
section IV.B of proposal preamble, 84
FR 30812, June 27, 2019.)
2. How did the risk review change for
the Solvent Extraction For Vegetable Oil
Production source category?
We have not changed any aspect of
the risk assessment since the June 27,
2019, RTR proposal for the Solvent
Extraction for Vegetable Oil Production
source category. We received several
comments indicating that the risk
assessment (1) Improperly included
emissions of acetaldehyde that are not
associated with the Solvent Extraction
for Vegetable Oil Production source
category, but are emitted from other
facility processes; (2) overestimated
actual emissions for certain facilities
where the EPA assumed that reported
volatile organic compound (VOC)
emissions were n-hexane; and (3)
overestimated allowable emissions for
the source category based on the
assumptions used to develop the MACT
allowable-to-actual emissions
multiplier.
As discussed in section IV.A.3 of this
preamble, the inputs and assumptions
in the risk assessment at proposal are
likely to overestimate the risks from the
Solvent Extraction for Vegetable Oil
Production source category. However,
the risks as modeled at proposal
indicate that both the actual and
allowable inhalation cancer risks to the
individual most exposed are less than 1in-1 million, well below the
presumptive limit of acceptability of
100-in-1 million. The maximum chronic
noncancer TOSHI due to inhalation
exposures is less than 1 for actual
PO 00000
Frm 00009
Fmt 4701
Sfmt 4700
15615
emissions, and 2 for MACT-allowable
emissions with an estimated 13 people
exposed to a TOSHI greater than 1.
Although for MACT-allowable
emissions, the maximum chronic
noncancer TOSHI due to inhalation
exposures is 2, we note that due to the
inherent health protective nature of our
risk assessment methods and the
uncertainties in this assessment (i.e., the
emissions dataset, dispersion modeling,
and exposure estimates), our risk
estimates are conservative. For example,
risk estimates for allowable emissions
were based on scaled-up actual
emissions. At the first facility with a
TOSHI value greater than 1, allowable
emissions are based on permit data. At
the other facility, allowable emissions
are based on an allowable multiplier
applied to actual emissions.
Additionally, the results of the acute
screening analysis showed that acute
risks were below a level of concern.
Because the risk assessment already
shows risks from the source category are
acceptable and that the existing
standards provide an ample margin of
safety to protect public health, revision
of the risk assessment to address the
comments that our emission estimates
were too high would not change the
EPA’s finding that the risks from the
Solvent Extraction for Vegetable Oil
Production source category are
acceptable.
3. What key comments did we receive
on the risk review, and what are our
responses?
We received comments in support of
and opposed to our proposed risk
assessment and determination that no
revisions to the standards are warranted
under CAA section 112(f)(2) for the
Solvent Extraction for Vegetable Oil
Production source category. Generally,
the comments that were not supportive
of the acceptability and ample margin of
safety determinations suggested changes
to the underlying risk assessment
methodology. The suggested changes to
the EPA’s risk assessment methodology
included that the EPA should lower its
presumptive limit of acceptability for
cancer risks to below 100-in-1 million,
include emissions outside of the source
categories in question in the risk
assessment, and assume that pollutants
with noncancer health effects have no
safe level of exposure. Other
commenters asserted that the
methodology for developing modeling
inputs overestimated the actual or
allowable emissions of certain
pollutants from specific facilities, and
subsequently overstated the risks from
the source category. We evaluated all
comments and determined that no
E:\FR\FM\18MRR3.SGM
18MRR3
jbell on DSKJLSW7X2PROD with RULES3
15616
Federal Register / Vol. 85, No. 53 / Wednesday, March 18, 2020 / Rules and Regulations
changes regarding our risk review were
needed. These comments and our
specific responses can be found below
and in the comment summary and
response document titled Summary of
Public Comments and Responses for the
Risk and Technology Review for Solvent
Extraction for Vegetable Oil Production,
which is available in the docket for this
action.
Comment: One commenter stated that
the acetaldehyde emissions that were
modeled for the ADM-Clinton facility
were not associated with the vegetable
oil process and should not have been
included in the source category
modeling file. The commenter stated
that the EPA should correct the risk
assessment by removing acetaldehyde
for the ADM-Clinton facility.
Response: As noted at proposal, we
included acetaldehyde emissions in the
modeling file for the source category
with the understanding that their
inclusion in the assessment would
result in a conservative estimate of risk.
We acknowledge that a reassessment of
risk that excludes acetaldehyde
emissions from the facility would result
in lower facility emissions, and
potentially lower the source category
risks associated with acetaldehyde.
Therefore, because revising the
assessment by removing acetaldehyde
emissions from the source category
modeling file would not change the
outcome of our risk determination, we
are not undertaking further analysis. We
note that the acetaldehyde emissions
would continue to be considered as part
of the facility-wide risk assessment (see
84 FR 30824) and whole facility risks.
Comment: One commenter stated that
the EPA overestimated actual emissions
for nine facilities where the EPA
assumed that 100 percent of the
reported VOC emissions were emitted as
n-hexane. The commenter stated that
although the EPA did not identify the
nine facilities, the commenter’s review
indicated that actual emissions in the
modeling file for several sources
significantly exceeded the actual 2014
emissions of n-hexane. The commenter
stated that the EPA should identify the
extent to which the reported HI (0.7)
may be affected by this assumption. The
commenter also stated that the EPA
overestimated the allowable-to-actual
ratio used to estimate allowable
emissions for multiple facilities. The
commenter asserted that although the
EPA did not identify the facilities that
were used to estimate an allowable-toactual ratio, they believe, based on a
review of the data, that the EPA
overestimated the allowable-to-actual
ratio by incorrectly assuming that nhexane emissions were equal to total
VerDate Sep<11>2014
20:53 Mar 17, 2020
Jkt 250001
solvent (VOC) loss or by not accounting
for the volume fraction of n-hexane in
solvent.
Response: As noted at proposal (84 FR
30818), the EPA assumed for certain
facilities that all solvent loss reported as
VOC is emitted as n-hexane. We
adopted this approach where data for
facility hexane emissions were
unavailable or lacking, recognizing that
this approach would provide the most
conservative estimate of risk.
Additionally, the MACT allowable
emissions multiplier conservatively
assumed that all loss of n-hexane in the
solvent extraction process is emitted to
the atmosphere (84 FR 30819). The
proposed approach was adopted taking
into consideration that the volume
fraction of n-hexane may vary
significantly within a solvent (the
solvent used in vegetable oil production
facilities is 100-percent VOC and may
range from less than 1 percent to 88percent n-hexane). Where emissions of
n-hexane or the volume fraction of nhexane were not readily available from
permit materials, we conservatively
assumed all solvent loss is n-hexane.
Therefore, the risk assessment does
likely overestimate the actual and
allowable emissions for certain
facilities; as noted at proposal, these
conservative assumptions were adopted
to account for the potential ‘‘worst-case’’
risks given that we lacked complete
information on the n-hexane emissions
for specific facilities. Although we
acknowledge that the source category
risks would be lower with the
adjustments requested by the
commenters, revision of the actual
emissions or MACT-allowable
emissions in the modeling file would
not change the EPA’s conclusions
regarding risk.
Comment: One commenter objected to
the EPA’s methodology for the acute
risk assessment. The commenter stated
that the risk assessment is weakened
because the EPA used ‘‘reasonable
worst-case’’ conditions. The commenter
stated that after recognizing the need to
evaluate the worst-case set of
conditions, it is inherently contradictory
and circular for the EPA to decide to
ignore the impacts by deciding that the
worst-case is not actually ‘‘reasonable.’’
Another commenter stated the
assessment of risks for acute exposure is
conservative. It assumes that estimated
1-hour peak emissions occur at the same
time as the ‘‘reasonable worst-case’’
meteorological conditions and that an
individual will be exposed at this time
and under these conditions at the
location of the maximum predicted
impact.
PO 00000
Frm 00010
Fmt 4701
Sfmt 4700
Response: The EPA disagrees that our
Acute Screening-Level Assessment
should not be based on ‘‘reasonable
worst-case’’ meteorological conditions.
In developing an acute exposure
scenario, we estimate 1-hour exposure
concentrations through air dispersion
modeling during hours of peak
emissions. However, hourly emissions
data are not typically available, and the
exact hours of peak emissions are often
unknown, making it difficult to
determine the meteorological conditions
to model with the peak emissions. We
make assumptions about when peak
hourly emissions occur. In a worst-case
scenario, peak hourly emissions would
occur during the 1 hour of the year with
the worst-case air dispersion conditions
(i.e., low, continuous wind speeds
blowing in a specific direction).
However, the probability of peak hourly
emissions occurring in the same hour as
the worst-case air dispersion conditions
is extremely low. For example, as
documented in Appendix 5 of the
Residual Risk Assessment for the
Solvent Extraction for Vegetable Oil
Production Source Category in Support
of the 2019 Risk and Technology Review
Final Rule, available in the docket for
this rulemaking, conservatively the
probability of these two events
occurring simultaneously is about 1-in200,000 (or a 0.0005 percent chance).
Instead, we use ‘‘reasonable worst-case’’
meteorological conditions. This
approach strikes a balance of being
health protective without
overestimating acute exposures and has
a reasonable probability of occurrence
(conservatively, an 88-in-200,000
chance or 0.044 percent). Using the
‘‘reasonable worst-case’’ meteorological
conditions, the scenario we modeled is
a rare event (peak emissions would have
a 0.044% chance of occuring during the
same hour as the ‘‘reasonable worstcase’’ meteorology based on
conservative assumptions, or a 99.956%
chance of not occuring during that hour)
rather than a scenario that is extremely
unlikely (peak emissions would have a
0.0005% chance of occuring during the
same hour as the worst-case
meteorology, or a 99.9995% chance of
not occuring during that hour).
After review of all the comments
received, we determined that no
changes to the risk assessment were
necessary. The comments and our
specific responses can be found in the
document, Summary of Public
Comments and Responses for the Risk
and Technology Review for the Solvent
Extraction for Vegetable Oil Production
Source Category, available in the docket
for this action.
E:\FR\FM\18MRR3.SGM
18MRR3
Federal Register / Vol. 85, No. 53 / Wednesday, March 18, 2020 / Rules and Regulations
4. What is the rationale for our final
approach and final decisions for the risk
review?
As noted in our proposal, the EPA
sets standards under CAA section
112(f)(2) using ‘‘a two-step standardsetting approach, with an analytical first
step to determine an ‘acceptable risk’
that considers all health information,
including risk estimation uncertainty,
and includes a presumptive limit on
MIR of ‘‘approximately 1-in-10
thousand’’ (see 54 FR 38045, September
14, 1989). We weigh all health risk
factors in our risk acceptability
determination, including the cancer
MIR, cancer incidence, the maximum
cancer TOSHI, the maximum acute
noncancer HQ, the extent of noncancer
risks, the distribution of cancer and
noncancer risks in the exposed
population, and the risk estimation
uncertainties.
Since proposal, neither the risk
assessment nor our determinations
regarding risk acceptability, ample
margin of safety, and adverse
environmental effects have changed. For
the reasons explained in the proposed
rule, we determined that the risks from
the Solvent Extraction for Vegetable Oil
Production source category are
acceptable, and the current standards
provide an ample margin of safety to
protect public health and prevent an
adverse environmental effect. Therefore,
we are not revising the standards for
this source category pursuant to CAA
section 112(f)(2) based on the residual
risk review, and we are readopting the
existing standards under CAA section
112(f)(2).
jbell on DSKJLSW7X2PROD with RULES3
B. Technology Review for the Solvent
Extraction for Vegetable Oil Production
Source Category
1. What did we propose pursuant to
CAA section 112(d)(6) for the Solvent
Extraction for Vegetable Oil Production
source category?
Pursuant to CAA section 112(d)(6), we
proposed to conclude that no revisions
to the current MACT standards for this
source category are necessary for control
of n-hexane emissions from vegetable
oil production facilities (sections IV.C of
proposal preamble, 84 FR 30825). We
did not find any developments in
practices, processes, and control
technologies that could be applied to
solvent extraction for vegetable oil
process vents and that could be used to
reduce emissions from solvent
extraction for vegetable oil production
facilities. We also did not identify any
developments in work practices,
pollution prevention techniques, or
process changes that could achieve
VerDate Sep<11>2014
20:53 Mar 17, 2020
Jkt 250001
emission reductions from solvent
extraction for vegetable oil process
vents. We identified for consideration
the use of a cryogenic condenser after
the main vent as an add-on control
option, based on a review of best
available control technology analyses
where such controls were previously
considered. However, based on the costs
and emission reductions for the
proposed options, we did not find the
use of a cryogenic condenser as cost
effective for reducing emissions from
these emission sources at solvent
extraction for vegetable oil production
units; and we proposed that it is not
necessary to revise the MACT standards
for these emission sources pursuant to
CAA section 112(d)(6). Additional
details of our technology review can be
found in the memorandum, CAA
Section 112(d)(6) Technology Review for
the Solvent Extraction for Vegetable Oil
Production Source Category, which is
available in the docket for this action.
2. How did the technology review
change for the Solvent Extraction for
Vegetable Oil Production source
category?
We have not changed any aspect of
the technology review since the June 27,
2019, RTR proposal for the Solvent
Extraction for Vegetable Oil Production
source category.
3. What key comments did we receive
on the technology review, and what are
our responses?
We received comments in support of
and opposed to the proposed
determination from the technology
review that no revisions were warranted
under CAA section 112(d)(6). We
evaluated the comments and
determined that no changes regarding
our determination were needed. These
comments and our specific responses
can be found in the comment summary
and response document titled Summary
of Public Comments and Responses for
the Risk and Technology Review for
Solvent Extraction for Vegetable Oil
Production, which is available in the
docket for this action.
4. What is the rationale for our final
approach for the technology review?
We evaluated all of the comments on
the EPA’s technology review and
determined that no changes to the
review are needed. For the reasons
explained in the proposed rule, we
determined that no cost-effective
developments in practices, processes, or
control technologies were identified in
our technology review to warrant
revisions to the standards. More
information concerning our technology
PO 00000
Frm 00011
Fmt 4701
Sfmt 4700
15617
review, and how we evaluate cost
effectiveness, can be found in the
memorandum titled CAA Section
112(d)(6) Technology Review for the
Solvent Extraction for Vegetable Oil
Production Source Category, which is
available in the docket for this action,
and in the preamble to the proposed
rule (84 FR 30825). Therefore, pursuant
to CAA section 112(d)(6), we are
finalizing our technology review as
proposed.
C. SSM for the Solvent Extraction for
Vegetable Oil Production Source
Category
1. What amendments did we propose to
address emissions during periods of
SSM?
We proposed removing and revising
provisions related to SSM that are not
consistent with the requirement that
standards apply at all times. We
proposed that the emission standards
for normal operation apply at all times,
except for periods of initial startup, for
new or significantly modified sources as
described below. We proposed alternate
standards for initial startup periods for
new or significantly modified sources.
Specifically, we proposed that new or
significantly modified facilities
operating in an initial startup period
would operate the mineral oil
absorption system and solvent
condensers at all times during the initial
startup period. We also proposed that
facilities establish and follow sitespecific operating ranges for
temperature and vacuum for the
desolventizing and oil distillation units
associated with solvent recovery. New
and significantly modified facilities
would also continue to have the option
to meet the requirements for normal
operating periods in Table 1 of 40 CFR
63.2850, in lieu of the work practice
standards. We also proposed to revise
the definition of ‘‘Initial startup period’’
to clarify the time at which an initial
startup period ends and a normal
operating period begins.
We proposed to remove malfunction
periods as a distinct source operating
status, which previously allowed
sources to exclude data collected during
the ‘‘malfunction period’’ when
determining compliance with the
emission standards. Under the proposed
rule, sources that experience an
unscheduled shutdown as a result of a
malfunction, continue to operate during
a malfunction (including the period
reasonably necessary to correct the
malfunction), or start up after a
shutdown resulting from a malfunction
must instead meet the emission
standard requirements for either a
E:\FR\FM\18MRR3.SGM
18MRR3
15618
Federal Register / Vol. 85, No. 53 / Wednesday, March 18, 2020 / Rules and Regulations
jbell on DSKJLSW7X2PROD with RULES3
normal operating period or the work
practice standards for an initial startup
period (if applicable) in 40 CFR 63.2850
and Table 1 of 40 CFR 63.2850. We also
proposed to remove reference to SSM
exemptions from the general duty
requirements,3 to remove SSM plans, to
remove references to SSM exemptions
in requirements related to compliance
with the standards and performance
testing, and to revise recordkeeping and
reporting requirements that are not
consistent with the requirement that
standards apply at all times. More
information concerning our proposal on
SSM can be found in the proposed rule
(84 FR 30825, June 27, 2019).
2. How did the SSM provisions change
since proposal?
We are finalizing the SSM provisions
as proposed, except for minor
clarifications. We are finalizing the
proposed alternate work practice
standards for initial startup periods for
new or significantly modified sources,
and we are finalizing our proposal to
remove malfunction periods as a source
operating status, which previously
allowed sources to exclude data
collected during the ‘‘malfunction
period’’ when calculating their
compliance ratio according to 40 CFR
63.2840. We are finalizing the removal
and revision of SSM requirements
related to general duty, SSM plans,
compliance with the standards, and
performance testing as proposed (84 FR
30825). We are revising the
recordkeeping requirements at 40 CFR
63.2862 and the reporting requirements
at 40 CFR 63.2861 as proposed, with the
exception of minor revisions to clarify
how to designate the date a deviation
occurred and the duration of the
deviation. For deviations from the
compliance ratio for facilities operating
under a normal operating period, the
date of the deviation is the date the
compliance ratio determination is made,
and the duration of the deviation is the
length of time taken to address the cause
of the deviation (including the duration
of any malfunction) and to return the
affected unit(s) to its normal or usual
manner of operation. For deviations
from the work practice standard for
facilities operating under an initial
startup period, the date of the deviation
is the date when the facility fails to
comply with any of the work practice
standards in 40 CFR 63.2840(h), and the
duration of the deviation is the length
of time taken to return to the work
3 We proposed to add general duty regulatory text
at 40 CFR 63.2840(g) to reflect the general duty to
minimize emissions, while eliminating the
reference to periods covered by an SSM exemption
(see 84 FR 30828).
VerDate Sep<11>2014
20:53 Mar 17, 2020
Jkt 250001
practice standards. We have also
removed the requirement to record and
report the time of day the deviation
occurred, since deviations from the
compliance ratio are determined at the
end of the period.
3. What key comments did we receive
on the SSM revisions and what are our
responses?
We received one comment supporting
our proposed removal of the exemption
in the regulations for emissions during
SSM periods. We received two
comments supporting our proposal to
establish an option to follow a work
practice standard during initial startup
periods for new or significantly
modified sources, and did not receive
any comments opposing the proposed
work practice standards during initial
startup periods. We received additional
comments requesting that startup or
shutdown periods be taken into account
when setting the MACT standard. We
received comments both for and against
the proposed removal of ‘‘malfunction
periods’’ as a distinct source operating
status. We also received comments
requesting clarification on the
recordkeeping and reporting
requirements for the date, time, and
duration of a deviation. We evaluated
all comments and determined that no
changes to the proposed alternate work
practice standards for initial startup
periods for new or significantly
modified sources; no changes to the
proposed removal of requirements that
allowed sources to designate the
operating status as a distinct
‘‘malfunction periods’’ (facilities must
instead meet the requirements of normal
operation or initial startup); and no
changes to the proposed removal or
revision of provisions related to SSM
are required, with the exception of
minor clarifications as discussed in this
section.
Comment: Two commenters stated
that the EPA should take periods of
startup and shutdown into account
when setting the MACT emissions
standards. The commenters stated that if
the EPA is removing the exemption of
startup and shutdown emissions from
the calculation of the compliance ratio,
the EPA should recalculate the MACT
emission limits based on normal
operation plus periods of startup and
shutdown. The commenters stated that
the EPA has indicated the current
NESHAP provides an ample margin of
safety to protect public health, and that
this indicates there is ample room to
increase the MACT limits to more
appropriate levels that include the
startup and shutdown operations.
Another commenter stated that the
PO 00000
Frm 00012
Fmt 4701
Sfmt 4700
proposed elimination of relief for SSM
events is not required for the rule to be
consistent with Sierra Club v. EPA. The
commenter asserted that other court
opinions have emphasized the need for
standards to accommodate higher
emission levels that occur at times other
than normal operations.
Response: We do not agree that the
MACT emission limits should be
recalculated to include periods of
startup and shutdown. We disagree with
the commenter’s suggestion that the
legal precedent established in case law
(i.e., Sierra Club v. EPA, 551 F.3d 1019
(D.C. Cir. 2008)) is not relevant. The
Sierra Club decision held that emissions
limitations under CAA section 112 must
apply continuously and meet minimum
stringency requirements, even during
periods of SSM. Consistent with Sierra
Club v. EPA, for the reasons explained
in the proposal preamble at 83 FR
30285, we are finalizing our proposal to
eliminate the SSM language in 40 CFR
part 63, subpart GGGG. Subpart GGGG
had both rule-specific SSM language
and references to SSM language in the
part 63 General Provisions in Table 1 of
63.2870, specifically reference to 40
CFR 63.6(f)(1). As we explained in the
proposal, our SSM-related rule revisions
are in response to the Sierra Club
Court’s vacatur of the SSM exemption in
40 CFR 63.6(f)(1) and 40 CFR 63.6(h)(1).
When incorporated into CAA section
112(d) regulations for specific source
categories, these two provisions
exempted sources from the requirement
to comply with otherwise applicable
MACT standards during periods of
SSM. The Court’s vacatur rendered
those provisions null and void prior to
this rulemaking. The mandate
implementing the Court’s decision was
issued on October 16, 2009, at which
time the vacated SSM provision 40 CFR
63.6(f)(1) referenced by subpart GGGG
was no longer in effect. Eliminating
reference to this provision, and other
related General Provisions referenced in
subpart GGGG, is a ministerial action by
the EPA to reflect the vacatur by the
Court. We also eliminated the rulespecific SSM provisions in subpart
GGGG. The final standards will apply at
all times, consistent with the Sierra
Club decision.
As an alternative approach consistent
with Sierra Club, the EPA may designate
different standards to apply during
startup and shutdown (as noted in the
proposal, the EPA is not obligated to set
standards for periods of malfunction).
For this category, the compliance
approaches required by state regulatory
authorities led us to decide special
startup/shutdown standards were
unnecessary for existing sources. Based
E:\FR\FM\18MRR3.SGM
18MRR3
jbell on DSKJLSW7X2PROD with RULES3
Federal Register / Vol. 85, No. 53 / Wednesday, March 18, 2020 / Rules and Regulations
on discussions with industry, there are
not significant differences in the
production process or operation of
solvent recovery equipment during
startup or shutdown of an existing
facility that would preclude the facility
from complying with the existing
standards. A review of title V permits
identified that approximately 35 percent
of existing facilities are already required
to account for periods of routine startup
(not initial startup) and shutdown in
determining their compliance ratio. This
requirement was found commonly
across states and regions, indicating that
existing sources operating during
periods of routine startup and shutdown
are able to demonstrate compliance with
the emission standards. Furthermore,
the commenter did not provide any
evidence that emissions during routine
startup and shutdown vary considerably
from normal operation. Consequently,
the final rule’s elimination of periods of
startup and shutdown for existing
sources reflects this capability.
For the reasons explained in the
proposal preamble, we are finalizing
alternate standards for periods of initial
startup for new or significantly modified
sources. Because the initial startup
period reflects a non-steady state of
production, emissions testing during
this period would not likely be
representative or yield meaningful
results for the establishment of separate
emission limits. As discussed at
proposal, control of n-hexane emissions
at vegetable oil production facilities is
accomplished through solvent recovery
and is based on inter-related process
equipment that is often custom built to
the specific configuration and needs of
the plant. During an initial startup
period, facility equipment is tested,
added, or replaced as the facility
gradually increases production, and
emissions during this period may reflect
variability that is not generally reflective
of normal or steady-state operations.
New and modified equipment is often
brought online in a phased approach,
and each phase can necessitate
adjustments in both new and existing
equipment in the process in order to
identify and correct problems, such as
equipment that is not operating as
designed and that requires repair or
replacement. The EPA evaluated the
available data for new or significantly
modified sources to establish potential
standards for periods of initial startup,
including review of operating permits
from various state and local agencies
and EPA Regional offices. We noted that
the standards have not previously
required—and state, local, and Regional
offices have not collected—emissions
VerDate Sep<11>2014
20:53 Mar 17, 2020
Jkt 250001
data for these facilities during their
initial startup periods. Further, where
the EPA identified a recently
constructed facility with permitted
MACT allowable solvent loss for an
initial startup period, we determined
that the allowable solvent loss for the
facility was not based on measured data,
and would not be representative of
initial startup periods for other facilities
in the source category. Although we
requested information on emissions and
the operation of processes during initial
startup periods, we did not receive
sufficient information, including
additional quantitative emissions data,
on which to base a numeric standard for
initial startup periods at new or
significantly modified facilities. The
EPA recognizes that the initial startup
period, which is a one-time event for
new sources and an infrequent event for
significantly modified sources, is not a
typical startup period that may occur as
part of routine or seasonal startups of a
plant. Instead, the initial startup period
includes evaluation and replacement of
new equipment as each phase is brought
online and production is gradually
increased. Therefore, emissions testing
during initial startup would be both
economically and technically infeasible.
Consequently, the EPA is finalizing a
work practice standard rather than an
emissions limit for this period.
Notwithstanding the finding that the
MACT-based limits of the initial
NESHAP provide and ample margin of
safety, the EPA lacks the authority to
relax limits developed in the MACT
process based on finding that the limits
provide an ample margin of safety. Were
the EPA to do so, then the limits would
not meet the strict structure of MACT.
The risk-based limits under CAA
section 112(f)(2) were intended to
augment MACT when the post-MACT
risks did not provide an ample margin
of safety to protect public health. There
is no indication in the statute that the
risk-based standards were intended to
revoke the requirements to have MACT
standards. A risk-based standard is only
required when the MACT-based does
not sufficiently reduce risk (see CAA
section 112(f)(2)(A)).
Additionally, the EPA’s finding is that
the existing MACT-based standard does
not need to be made more stringent to
comply with CAA section 112(f)(2) (i.e.,
to provide an ample margin of safety).
The EPA has not made a finding that the
existing standards somehow exceed an
ample margin of safety. There is no
finding that there is ‘‘room to increase’’
the limits while also complying with the
requirement to provide an ample margin
of safety required by CAA section
112(f)(2).
PO 00000
Frm 00013
Fmt 4701
Sfmt 4700
15619
Comment: One commenter asserted
that it would be arbitrary and capricious
for the EPA to ignore the existence of
malfunctions even at best-performing
sources, or to assume that the bestperforming sources achieve emission
levels that they do not achieve part of
the time. The commenter urged that if
the EPA adopts MACT standards that it
recognizes even the best-performing
existing sources cannot achieve part of
the time, the EPA would be going
beyond the MACT floor. Three
commenters stated that the EPA should
take malfunctions into account when
adopting emissions standards. One
commenter stated that it is not apparent
from the proposed rule why the EPA
believes it needs to remove the current
provisions related to malfunctions. The
commenter asserted that the EPA cannot
change its position and withdraw a
previously promulgated provision
without providing a full explanation of
the reason(s) for the change. The same
commenter recommended that the EPA
could instead establish numerical
emission limitations that have an
averaging time of sufficient duration
that short, infrequent spikes in
emissions due to malfunctions would
not cause the source to exceed the
emission limitation. Alternatively, the
commenter recommended that the EPA
could promulgate design, equipment,
work practice, or operational standards
in lieu of a numerical standard. Two
commenters stated that the EPA should
maintain an option in 40 CFR
63.2850(e)(2) either to meet the
requirements applicable to normal
operating periods or to meet the
requirements for malfunction periods.
These commenters urged that otherwise
there could be unavoidable exceedances
of the standards. The two commenters
recommended that the EPA could adopt
similar work practice standards for
malfunction periods as proposed for
initial startup periods. Another
commenter suggested work practices
such as monitoring of operating
parameters to identify a malfunction
and stopping or cutting back the
process. One commenter supported the
removal of the malfunction exemptions,
stating there is no lawful or rational
justification for creating non-numerical
work practice standards during
malfunctions.
Response: We disagree with the
commenters’ assertions that we must set
revised or separate standards for periods
of malfunction. As discussed in the
preamble to the proposed rule, as the
Court recognized in U.S. Sugar Corp,
accounting for malfunctions in setting
standards would be difficult, if not
E:\FR\FM\18MRR3.SGM
18MRR3
jbell on DSKJLSW7X2PROD with RULES3
15620
Federal Register / Vol. 85, No. 53 / Wednesday, March 18, 2020 / Rules and Regulations
impossible, given the myriad different
types of malfunctions that can occur
across all sources in the category and
given the difficulties associated with
predicting or accounting for the
frequency, degree, and duration of
various malfunctions that might occur.
Id. at 608 (‘‘the EPA would have to
conceive of a standard that could apply
equally to the wide range of possible
[ ] malfunctions, ranging from an
explosion to minor mechanical defects.
Any possible standard is likely to be
hopelessly generic to govern such a
wide array of circumstances.’’). As such,
the performance of units that are
malfunctioning is not ‘‘reasonably’’
foreseeable. See, e.g., Sierra Club v.
EPA, 167 F.3d 658, 662 (D.C. Cir. 1999)
(‘‘The EPA typically has wide latitude
in determining the extent of datagathering necessary to solve a problem.
We generally defer to an agency’s
decision to proceed on the basis of
imperfect scientific information, rather
than to ‘invest the resources to conduct
the perfect study.’’’). See also,
Weyerhaeuser v. Costle, 590 F.2d 1011,
1058 (D.C. Cir. 1978) (‘‘In the nature of
things, no general limit, individual
permit, or even any upset provision can
anticipate all upset situations. After a
certain point, the transgression of
regulatory limits caused by
‘uncontrollable acts of third parties,’
such as strikes, sabotage, operator
intoxication or insanity, and a variety of
other eventualities, must be a matter for
the administrative exercise of case-bycase enforcement discretion, not for
specification in advance by
regulation.’’). In addition, emissions
during a malfunction event can be
significantly higher than emissions at
any other time of source operation. For
example, if an air pollution control
device with 99-percent removal goes offline as a result of a malfunction (as
might happen if, for example, the bags
in a baghouse catch fire) and the
emission unit is a steady state type unit
that would take days to shut down, the
source would go from 99-percent
control to zero control until the control
device was repaired. The source’s
emissions during the malfunction
would be 100 times higher than during
normal operations. As such, the
emissions over a 4-day malfunction
period would exceed the annual
emissions of the source during normal
operations. As this example illustrates,
accounting for malfunctions could lead
to standards that are not reflective of
(and significantly less stringent than)
levels that are achieved by a wellperforming non-malfunctioning source.
It is reasonable to interpret CAA section
VerDate Sep<11>2014
21:23 Mar 17, 2020
Jkt 250001
112 to avoid such a result. The EPA’s
approach to malfunctions is consistent
with CAA section 112 and is a
reasonable interpretation of the statute.
As noted at proposal, the EPA
considers whether circumstances
warrant setting standards for a
particular type of malfunction and, if so,
whether the EPA has sufficient
information to identify the relevant best
performing sources and establish a
standard for such malfunctions. The
EPA has also considered the need for a
work practice for periods of malfunction
for vegetable oil production facilities.
Although we requested information on
emissions and the operation of
processes during malfunction periods in
our consultations with state agencies
and industry, we did not receive
sufficient information for development
of proposed standards. Therefore, as
part of the proposal, the EPA solicited
information on the type of events that
constitute a malfunction event, industry
best practices, and the best level of
emission control during malfunction
events. The EPA also requested
commenters provide information on the
costs associated with any recommended
work practices. In addition, the EPA
solicited specific supporting data on
HAP emissions during malfunction
events, including the cause of
malfunction, the frequency of
malfunction, duration of malfunction,
and the estimate of HAP emitted during
each malfunction. In this case, although
we requested comment and information
to support the development of a
standard during periods of malfunction,
we did not receive sufficient
information, including additional
quantitative emissions data, on which to
base a standard. Absent sufficient
information, it is not reasonable at this
time to establish a work practice
standard for periods of malfunction for
this source category. For these reasons,
we are not setting separate standards for
periods of malfunction. Under the final
rule, sources that experience an
unscheduled shutdown as a result of a
malfunction, continue to operate during
a malfunction (including the period
reasonably necessary to correct the
malfunction), or start up after a
shutdown resulting from a malfunction
must instead meet the emission
standard requirements for either a
normal operating period or the work
practice standards for an initial startup
period (if a new or significantly
modified source) in 40 CFR 63.2850 and
Table 1 of 40 CFR 63.2850. We note that
sources must still meet the general duty
requirements in 40 CFR 63.2840(g) and
should address malfunctions
PO 00000
Frm 00014
Fmt 4701
Sfmt 4700
expeditiously in order to maintain any
affected source, including associated air
pollution control equipment and
monitoring equipment, and minimize
emissions.
Nevertheless, the EPA acknowledges
that including solvent loss from a onetime event (like a malfunction) in the
12-month compliance ratio could cause
a deviation for one or more monthly
compliance ratio determinations, and
would remain in the rolling compliance
determination for up to 1 year (12
months). We also recognize that it is
possible that a malfunction that causes
a 12-month compliance ratio to be
exceeded might have been corrected
well before the first full 12-months have
passed. Although a facility would need
to retain records of any deviation and
the corrective action(s) performed, no
additional corrective action would be
required at the time the 12-month
compliance ratio is officially exceeded
in subsequent months if the facility
demonstrates the exceedance is from a
prior malfunction that has been
corrected. Facilities would be able to
provide such an explanation in their
deviation reports; specifically, we have
revised the deviation reporting
requirements in the final rule to include
a requirement that facilities flag and
provide an explanation for any
deviation from the compliance ratio for
which a deviation report is being
submitted for more than 1 consecutive
month (i.e., include a reference to the
original date and reporting of the
deviation) (see 40 CFR 63.2861(b)).
Further, as discussed below in this
section, we have clarified that the
duration of the deviation from the
compliance ratio is the length of time
taken to address the cause of the
deviation (including the duration of any
malfunction) and to return the affected
unit(s) to its normal or usual manner of
operation. Therefore, facilities must
retain records of the date and duration
of the malfunction, as well as the
corrective action(s) performed, to
demonstrate the basis for the deviation
in subsequent periods.
As further explained at proposal, ‘‘[i]n
the event that a source fails to comply
with the applicable CAA section 112(d)
standards as a result of a malfunction
event, the EPA would determine an
appropriate response based on, among
other things, the good faith efforts of the
source to minimize emissions during
malfunction periods, including
preventive and corrective actions, as
well as root cause analyses to ascertain
and rectify excess emissions. The EPA
would also consider whether the
source’s failure to comply with the CAA
section 112(d) standard was, in fact,
E:\FR\FM\18MRR3.SGM
18MRR3
jbell on DSKJLSW7X2PROD with RULES3
Federal Register / Vol. 85, No. 53 / Wednesday, March 18, 2020 / Rules and Regulations
sudden, infrequent, not reasonably
preventable and was not instead caused
in part by poor maintenance or careless
operation. 40 CFR 63.2 (definition of
malfunction). If the EPA determines in
a particular case that an enforcement
action against a source for violation of
an emission standard is warranted, the
source can raise any and all defenses in
that enforcement action and the federal
district court will determine what, if
any, relief is appropriate. The same is
true for citizen enforcement actions.
Similarly, the presiding officer in an
administrative proceeding can consider
any defense raised and determine
whether administrative penalties are
appropriate’’ (84 FR 30828).
Comment: We received one comment
requesting clarification on the revised
reporting and recordkeeping
requirements for deviations. The
commenter requested that the EPA
clarify how a facility should designate
the date a deviation occurred. The
commenter recommended that because
there is a single compliance ratio
determination for an operating month,
the rule should specify that a deviation
be reported as occurring on the date the
compliance ratio determination is made.
The commenter also requested
clarification on the duration of a
deviation, noting that solvent loss from
a one-time event (like a malfunction)
could cause a deviation for one or more
monthly compliance ratio
determinations. The commenter stated it
is unreasonable to require facilities to
report events that may last only 1 day
as having a duration of 30 days or even
longer, and asked the EPA to clarify if
the deviation reporting requirements
only apply to work practice standards.
Finally, the commenter stated the
reporting template should not require
facilities to report the time of a
deviation; the commenter urged that the
time of day a deviation occurs is not
needed to determine compliance with
the standards.
Response: We agree with the
commenter and have revised the
reporting and recordkeeping
requirements for deviations for
clarification. Specifically, we have
revised the recordkeeping requirements
of 40 CFR 63.2862(g)(1) to clarify that
for deviations from the compliance
ratio, the date of the deviation is the
date the compliance ratio determination
is made. For deviations from the work
practice standard during the initial
startup period, the date of the deviation
is the date when the facility fails to
comply with any of the work practice
standard in 40 CFR 63.2840(h) (e.g., if
the facility fails to operate the mineral
oil absorption system or the solvent
VerDate Sep<11>2014
20:53 Mar 17, 2020
Jkt 250001
condenser at all times during the initial
startup period, or fails to meet the sitespecific operating limits established by
the facility). These dates must be
reported in the deviation notification
report according to the final rule
requirements at 40 CFR 63.2861(b)(5).
We have revised 40 CFR 63.2862(g)(1) to
clarify that for deviations from the
compliance ratio, the duration of the
deviation is the length of time taken to
address the cause of the deviation
(including the duration of any
malfunction) and to return the affected
unit(s) to its normal or usual manner of
operation. For deviations from the work
practice standard during the initial
startup period, the duration of the
deviation is the length of time taken to
return to the work practice standards.
The final rule requirements are
consistent with the prior requirements
of 40 CFR 63.10(b)(2)(ii) to retain a
record of the ‘‘occurrence and duration
of each malfunction’’ and are necessary
to allow the EPA to determine the
severity of any failure to meet a
standard. Finally, we have revised the
final rule requirements to remove the
requirement to record or report the time
of a deviation, as this information is not
necessary to determine compliance with
the standard.
Additional comments on the SSM
provisions and our specific responses to
those comments can be found in the
document titled Summary of Public
Comments and Responses for the Risk
and Technology Review for Solvent
Extraction for Vegetable Oil Production,
which is available in the docket for this
action.
4. What is the rationale for our final
approach and final decisions to address
emissions during periods of SSM?
We evaluated all the comments on the
EPA’s proposed amendments to the
SSM provisions. For the reasons
explained in the proposed rule (84 FR
30812), we determined that these
amendments appropriately remove and
revise provisions related to SSM that are
not consistent with the requirement that
the standards apply at all times.
Therefore, we are finalizing the
amendments to remove and revise
provisions related to SSM, as proposed,
with the exception of the clarifications
discussed in this section.
PO 00000
Frm 00015
Fmt 4701
Sfmt 4700
15621
D. Technical Amendments to the MACT
Standards for the Solvent Extraction for
Vegetable Oil Production Source
Category
1. What other amendments did we
propose for the Solvent Extraction for
Vegetable Oil Production source
category?
We proposed that owners and
operators submit electronic copies of
initial notifications, initial startup
reports, annual compliance
certifications, deviation reports, and
performance test reports through the
EPA’s CDX using the CEDRI. For initial
notifications, initial startup reports,
annual compliance certifications, and
deviation reports, the proposed rule
requires that owners and operators use
the appropriate spreadsheet template to
submit information to CEDRI. We also
proposed two broad circumstances in
which we may provide extension to
these requirements. We proposed at 40
CFR 63.2862(f) that an extension may be
warranted due to outages of the EPA’s
CDX or CEDRI that precludes an owner
or operator from accessing the system
and submitting required reports. We
also proposed at 40 CFR 63.2862(g) that
an extension may be warranted due to
a force majeure event, such as an act of
nature, act of war or terrorism, or
equipment failure or safety hazards
beyond the control of the facility.
We proposed revisions to several
definitions in 40 CFR 63.2872 to
harmonize with the proposed removal
of the SSM requirements and to clarify
existing provisions, include revisions to
definitions of ‘‘Compliance ratio,’’
‘‘Nonoperating period,’’ ‘‘Normal
operating period,’’ and ‘‘Operating
month’’ to clarify where the malfunction
period is excluded, and to the definition
of ‘‘Normal operating period’’ to clarify
that this definition also applies to
‘‘normal operation.’’ We also proposed
to add a definition for ‘‘Nonoperating
month.’’ We proposed to revise the
definition of ‘‘Hazardous air pollutant
(HAP)’’ to remove the reference to the
date of April 12, 2001.
We proposed minor revisions to 40
CFR 63.2840(a)(1) and (b)(1), 40 CFR
63.2853(a)(2), and 40 CFR 63.2855(a)(3)
to remove text that is redundant with
the definition of ‘‘Operating month’’ in
40 CFR 63.2872. We also proposed a
minor correction to Table 1 of 63.2850
to correct a typographical error in row
‘‘(a)’’ for malfunction periods.
E:\FR\FM\18MRR3.SGM
18MRR3
15622
Federal Register / Vol. 85, No. 53 / Wednesday, March 18, 2020 / Rules and Regulations
2. How did the other amendments for
the Solvent Extraction for Vegetable Oil
Production source category change since
proposal?
There are no changes to the proposed
requirements for owners and operators
to submit electronic copies of initial
notifications, initial startup reports,
annual compliance certifications,
deviation reports, and performance test
reports electronically. We also are
finalizing, as proposed, the provisions
that allow facility operators the ability
to seek extensions for submitting
electronic reports for circumstances
beyond the control of the facility. There
are no changes to the proposed
definitions in 40 CFR 63.2872, or the
minor revisions to 40 CFR 63.2840(a)(1)
and (b)(1), 40 CFR 63.2853(a)(2), 40 CFR
63.2855(a)(3), or Table 1 of 40 CFR
63.2850.
jbell on DSKJLSW7X2PROD with RULES3
3. What key comments did we receive
on the other amendments for the
Solvent Extraction for Vegetable Oil
Production source category and what
are our responses?
We received one comment providing
input on the proposed requirement for
owners and operators of vegetable oil
production facilities to submit
electronic copies of initial notifications,
initial startup reports, annual
compliance certifications, deviation
reports, and performance test reports.
The commenter stated that the EPA may
not lawfully or rationally finalize
‘‘exemption provisions’’ based on
CEDRI outages or ‘‘force majeure
events.’’ The commenter stated the
provisions do not set a firm deadline to
request an extension of the reporting
deadline. No commenters provided
significant comments on the proposed
definitions in 40 CFR 63.2872, or the
proposed minor revisions to 40 CFR
63.2840(a)(1) and (b)(1), 40 CFR
63.2853(a)(2), 40 CFR 63.2855(a)(3), or
Table 1 of 40 CFR 63.2850.
Comment: One commenter stated that
the EPA must not finalize the proposed
electronic reporting extension
provisions because the definition of a
force majeure event is too broad, the
provisions do not set a firm deadline to
request an extension of the reporting
deadline, and the decision to allow an
extension is solely within the discretion
of the Administrator. The commenter
urged that the proposed provisions are
unlawful and arbitrary because they
would create a broad and vague
mechanism that a facility owner or
operator could use to evade binding
emission standards, by evading the
binding compliance reporting deadlines
set to assure compliance with those
VerDate Sep<11>2014
20:53 Mar 17, 2020
Jkt 250001
standards. The commenter further stated
that the EPA should not import the
concept of ‘‘force majeure’’ into any part
of the CAA, as to do so is a variation of
the prior malfunction exemptions that
are unlawful under the CAA. The
commenter also noted that the EPA has
provided that there are no known issues
with submission of ERT-formatted
performance test and evaluation reports
in CEDRI (per the Petroleum Refinery
NESHAP), thus, there is no rational
basis for providing the proposing
reporting extensions. At a minimum, the
commenter requested that the EPA set a
new firm deadline to assure that the
extension request allows only a
temporary period when the facility need
not report, such as a 10-day extension,
rather than an open-ended extension
without a deadline.
Response: The commenter states that
the brief case-by-case extension of
report submittal deadlines is a
‘‘reporting exemption.’’ This is not the
case. The proposed provisions the
commenter questions are in paragraphs
40 CFR 63.2861(h) and (i).
There is no exception or exemption to
reporting, much less an exemption from
compliance with the numerical
emission standards, only a method for
requesting an extension of the reporting
deadline. Reporters are required to
justify their request and identify a
reporting date. There is no
predetermined timeframe for the length
of extension that can be granted, as this
is something best determined by the
Administrator (i.e., the EPA
Administrator or delegated authority as
defined in 40 CFR 63.2) when reviewing
the circumstances surrounding the
request. Different circumstances may
require a different length of extension
for electronic reporting. For example, a
tropical storm may delay electronic
reporting for a day, but a Hurricane
Katrina scale event may delay electronic
reporting much longer, especially if the
facility has no power, and as such, the
owner or operator has no ability to
access electronically stored data or to
submit reports electronically. The
Administrator will be the most
knowledgeable of the events leading to
the request for extension and will assess
whether an extension is appropriate,
and if so, a reasonable length for the
extension. The Administrator may even
request that the report be sent in
hardcopy until electronic reporting can
be resumed. While no new fixed
duration deadline is set, the regulation
requires that the report be submitted
electronically as soon as possible after
the CEDRI outage or after the force
majeure event resolves.
PO 00000
Frm 00016
Fmt 4701
Sfmt 4700
The concept of force majeure has been
implemented by the EPA in this context
since May 2007 within the CAA
requirements through the performance
test extensions provided in 40 CFR
63.7(a)(4) and 60.8(a)(1). Like the
performance test extensions, the
approval of a requested extension of an
electronic reporting deadline is at the
discretion of the Administrator.
The EPA disagrees that the ability to
request a reporting extension ‘‘would
create a broad and vague mechanism’’
that owners and operators ‘‘could use to
evade binding emissions standards’’ or
evade ‘‘binding compliance reporting
deadlines’’ for emissions standards.
While reporting is an important
mechanism for the EPA and air agencies
to assess whether owners and operators
are in compliance with emissions
standards, reporting obligations are
separate from (i.e., in addition to)
requirements that an owner or operator
be in compliance with an emissions
standard, especially where the deadline
for meeting the standard has already
passed and the owner or operator has
certified and is monitoring operations to
show that they are in compliance with
the standard. The commenter references
deadlines set forth in the CAA for
demonstrating initial compliance
following the effective date of emission
standards, which differs from deadlines
for submitting reports. There are no
such deadlines stated in the CAA for
report due dates, meaning the EPA has
discretion to establish reporting
schedules, and also discretion to allow
a mechanism for extension of those
schedules on a case-by-case basis. In
fact, under the commenter’s reasoning,
if the statutory deadlines for compliance
with standards were read to strictly
apply to continuing reporting
requirements, no such reporting could
be required after 3 years from the
promulgation of the standards. This
would not be a reasonable result.
Reporting deadlines are often different
from compliance deadlines. Rules under
40 CFR part 60 and 63 typically allow
months following an initial compliance
deadline to conduct testing and submit
reports, but compliance with standards
is required upon the compliance date.
Additionally, the ability to request a
reporting extension does not apply to a
broad category of circumstances; on the
contrary, the scope for submitting an
extension request for an electronic
report is very limited in that claims can
only be made for an event outside of the
owner’s or operator’s control that occurs
in the five business days prior to the
reporting deadline. The claim must then
be approved by the Administrator, and
in approving such a claim, the
E:\FR\FM\18MRR3.SGM
18MRR3
jbell on DSKJLSW7X2PROD with RULES3
Federal Register / Vol. 85, No. 53 / Wednesday, March 18, 2020 / Rules and Regulations
Administrator agrees that something
outside the control of the owner or
operator prevented the owner or
operator from meeting its reporting
obligation. In no circumstance does this
electronic reporting extension allow for
the owner or operator to be out of
compliance with the underlying
emissions standards. If the
Administrator determines that a facility
has not acted in good faith to reasonably
report in a timely manner, the
Administrator can reject the claim and
find that the failure to report timely is
a deviation from the regulation. CEDRI
system outages are infrequent, but the
EPA knows when they occur and
whether a facility’s claim is legitimate.
Force majeure events (e.g., natural
disasters impacting a facility) are also
usually well-known events.
Finally, EPA disagrees that the
existing statistics on the use of CEDRI
and e-reporting precludes the need for
a provision to account for an outage of
the CEDRI system. Prudent management
of electronic data systems builds in
allowances for unexpected, non-routine
delays, such as occurred on July 1, 2016
and October 20–23, 2017, and is
consistent with the already-existing
provisions afforded for unexpected,
non-routine delays in performance
testing [see 40 CFR 60.8(a)(1) and (2)
and 40 CFR 63.7(a)(4)]. For both
electronic reporting and performance
testing, owners or operators are to
conduct and complete their activities
within a short window of time; the EPA
believes it is prudent to allow owners or
operators to make force majeure claims
for situations beyond their reasonable
control. The EPA also disagrees that
incidental issues with questions on
completing the form or the procedures
for accessing CEDRI for which the
CEDRI Helpdesk is available, are
conditions that would be considered
either force majeure or a CEDRI system
outage. The existence of the Helpdesk
for answering questions on procedures
in submitting reports to CEDRI have no
impact on the availability of CEDRI in
such a circumstance. The purpose of
these requests for extensions are to
accommodate owners and operators in
cases where they cannot successfully
submit a report electronically for
reasons that are beyond their control
and occur during a short window of
time prior to the reporting deadline. The
extension is not automatic, and the
Administrator retains the right to accept
or reject the request. The language was
added as part of the standard electronic
reporting language based on numerous
comments received on the proposal for
the Electronic Reporting and
VerDate Sep<11>2014
20:53 Mar 17, 2020
Jkt 250001
Recordkeeping Requirements for the
New Source Performance Standards (80
FR 15100). As such, we have
determined that no changes to the
electronic reporting requirements are
necessary in the final rule.
Additional comments on the
proposed electronic reporting
requirements and other amendments
and our specific responses to those
comments can be found in the
memorandum titled Summary of Public
Comments and Responses for the Risk
and Technology Review for Solvent
Extraction for Vegetable Oil Production,
available in the docket for this action.
4. What is the rationale for our final
approach and final decisions for the
other amendments for the Solvent
Extraction for Vegetable Oil Production
source category?
We evaluated the comment on the
EPA’s proposed amendments to require
electronic reporting initial notifications,
initial startup reports, annual
compliance certifications, deviation
reports, and performance test reports.
For the reasons explained in the
proposed rule, we determined that these
amendments increase the ease and
efficiency of data submittal and improve
data accessibility. More information
concerning the proposed requirement
for owners and operators of vegetable oil
production facilities to submit
electronic copies of certain notifications
and reports is in the preamble to the
proposed rule (84 FR 30830, June 27,
2019) and the document, Summary of
Public Comments and Responses for the
Risk and Technology Review for the
Solvent Extraction for Vegetable Oil
Production, available in the docket for
this action. Therefore, we are finalizing
our approach for submission of initial
notifications, initial startup reports,
annual compliance certifications,
deviation reports, and performance test
reports as proposed.
V. Summary of Cost, Environmental,
and Economic Impacts and Additional
Analyses Conducted
A. What are the affected facilities?
The EPA estimates that there are 89
vegetable oil production facilities that
are currently subject to the Solvent
Extraction for Vegetable Oil Production
NESHAP and would be affected by the
final amendments. The basis of our
estimate of affected facilities is provided
in the memorandum, Residual Risk
Modeling File Documentation for the
Solvent Extraction for Vegetable Oil
Production Source Category, which is
available in the docket for this action.
We additionally anticipate one new
PO 00000
Frm 00017
Fmt 4701
Sfmt 4700
15623
source per year. The EPA received
comment on the proposed rule that
some larger facilities may have
significant modifications about once a
year, therefore, we assume that eight
existing vegetable oil production
facilities may have a significant
modification that could meet the revised
requirements for initial startup periods.
B. What are the air quality impacts?
The EPA estimates that annual HAP
emissions from the vegetable oil
production facilities that are subject to
the NESHAP are approximately 13,500
tpy.4 Because the EPA is not revising the
emission limits, we do not anticipate
any quantifiable air quality impacts as a
result of these amendments. However,
we anticipate that the final
requirements, including the work
practice standards for the optional
initial startup period, are at least as
stringent as the current rule
requirements. The work practice
standards include requirements for
facilities to operate controls, including
the mineral oil absorption system and
solvent condensers, at all times during
the initial startup period. Facilities must
also establish and follow site-specific
operating ranges for temperature and
vacuum for the desolventizing and oil
distillation units associated with solvent
recovery. We anticipate these
requirements will minimize emissions
during these periods.
C. What are the cost impacts?
The 89 vegetable oil production
facilities that would be subject to the
final amendments, and one additional
new source per year, would incur
minimal net costs to meet revised
recordkeeping and reporting
requirements, some estimated to have
costs and some estimated to have cost
savings. Nationwide costs associated
with the final requirements are
estimated to total $93,100 over the 3
years following promulgation of
amendments (or $31,033 per year). The
EPA believes that the vegetable oil
production facilities that are known to
be subject to the NESHAP can meet the
final requirements without incurring
additional capital or operational costs.
Therefore, the only costs associated
with the final amendments include a
one-time burden for reviewing
requirements of the amended rule, and
a one-time burden associated with
recordkeeping and reporting labor costs
for initial startup periods for new,
reconstructed, or significantly modified
4 The annual HAP emission estimates include
emissions from 88 facilities. Annual emissions are
not yet available for one newly constructed facility.
E:\FR\FM\18MRR3.SGM
18MRR3
jbell on DSKJLSW7X2PROD with RULES3
15624
Federal Register / Vol. 85, No. 53 / Wednesday, March 18, 2020 / Rules and Regulations
facilities. The EPA assumed in the
proposed rule that one potential new or
reconstructed vegetable oil production
facility would be subject to the revised
requirements for initial startup periods
each year. However, we received
comment on the proposed rule that
some larger facilities may have
significant modifications about once a
year. Therefore, we have revised the
costs associated with the final rule to
assume that approximately eight
existing vegetable oil production
facilities (or approximately 10 percent
of existing facilities) may have a
significant modification that could
require that they meet the revised
requirements for initial startup periods.
The revised assumption results in an
increase in the total nationwide annual
costs associated with the final
requirements to account for the
additional facilities anticipated to have
a significant modification (actual costs
per facility have not changed). For
further information on the costs and
cost savings associated with the final
requirements, see the memorandum,
Cost for the Solvent Extraction for
Vegetable Oil Production Source
Category Risk and Technology Review—
Final Amendments, and the document,
Supporting Statement for NESHAP for
Solvent Extraction for Vegetable Oil
Production, which are both available in
the docket for this action.
E. What are the benefits?
D. What are the economic impacts?
As discussed in the preamble to the
proposed rule, to examine the potential
for any environmental justice issues that
might be associated with the source
category, we performed a demographic
analysis, which is an assessment of risks
to individual demographic groups of the
populations living within 5 kilometers
(km) and within 50 km of the facilities.
In the analysis, we evaluated the
distribution of HAP-related cancer and
noncancer risks from the Solvent
Extraction for Vegetable Oil Production
source category across different
demographic groups within the
populations living near facilities. When
examining the risk levels of those
exposed to emissions from solvent
extraction for vegetable oil production
facilities, we found that no one is
exposed to a cancer risk at or above 1in-1 million or to a chronic noncancer
TOSHI greater than 1.
The documentation for this decision
is contained in section IV.A of the
preamble to the proposed rule and the
technical report titled Risk and
Technology Review—Analysis of
Demographic Factors for Populations
Living Near Solvent Extraction for
Economic impact analyses focus on
changes in market prices and output
levels. If changes in market prices and
output levels in the primary markets are
significant enough, impacts on other
markets may also be examined. Both the
magnitude of costs needed to comply
with a final rule and the distribution of
these costs among affected facilities can
have a role in determining how the
market will change in response to a final
rule. The total costs associated with the
final rule are estimated to be $93,100 (or
$31,033 per year) for the 3 years
following the final rule. This includes a
one-time burden for reviewing
requirements of the amended rule, and
a one-time burden associated with the
recordkeeping and reporting for initial
startup periods for new, reconstructed,
or significantly modified facilities. This
is an estimated average cost of
approximately $345 per year per
facility. These costs are not expected to
result in a significant market impact,
regardless of whether they are passed on
to the purchaser or absorbed by the
firms.
VerDate Sep<11>2014
20:53 Mar 17, 2020
Jkt 250001
Although the EPA does not anticipate
quantifiable reductions in HAP
emissions as a result of the final
amendments, we believe that the action
will result in improvements to the rule.
Specifically, the final amendments
revise the standards such that they
apply at all times. For facilities that
choose to operate under an initial
startup period, the EPA is finalizing an
alternative work practice standard that
will ensure that facilities are operating
controls and minimizing emissions
while the source operates under nonsteady state production, which we
expect will protect public health and
the environment through better
compliance during these periods.
Additionally, the final amendments
requiring electronic submittal of initial
notifications, initial startup reports,
annual compliance certifications,
deviation reports, and performance test
results will streamline reporting for
affected sources, increase the usefulness
of the data and improve data
accessibility for the public, will further
assist in the protection of public health
and the environment, and will
ultimately result in less burden on the
regulated community. See section
IV.D.2 of the preamble to the proposed
rule for more information.
F. What analysis of environmental
justice did we conduct?
PO 00000
Frm 00018
Fmt 4701
Sfmt 4700
Vegetable Oil Production, which is
available in the docket for this action.
G. What analysis of children’s
environmental health did we conduct?
This action is not subject to Executive
Order 13045 because it is not
economically significant as defined in
Executive Order 12866, and because the
EPA does not believe the environmental
health or safety risks addressed by this
action present a disproportionate risk to
children. This action’s health and risk
assessments are summarized in section
IV.A of this preamble and are further
documented in the risk report, Residual
Risk Assessment for the Solvent
Extraction for Vegetable Oil Production
Source Category in Support of the 2019
Risk and Technology Review Final Rule,
available in the docket for this action.
VI. Statutory and Executive Order
Reviews
Additional information about these
statutes and Executive Orders can be
found at https://www.epa.gov/lawsregulations/laws-and-executive-orders.
A. Executive Orders 12866: Regulatory
Planning and Review and Executive
Order 13563: Improving Regulation and
Regulatory Review
This action is not a significant
regulatory action and was, therefore, not
submitted to the Office of Management
and Budget (OMB) for review.
B. Executive Order 13771: Reducing
Regulations and Controlling Regulatory
Costs
This action is not an Executive Order
13771 regulatory action because this
action is not significant under Executive
Order 12866.
C. Paperwork Reduction Act (PRA)
The information collection activities
in this rule have been submitted for
approval to the OMB under the PRA.
The Information Collection Request
(ICR) document that the EPA prepared
has been assigned EPA ICR number
1947.09. You can find a copy of the ICR
in the docket for this rule, and it is
briefly summarized here. The
information collection requirements are
not enforceable until OMB approves
them.
The EPA is finalizing amendments
that revise provisions pertaining to
emissions during periods of SSM; add
requirements for electronic reporting of
certain notifications and reports and
performance test results; and make other
minor clarifications and corrections.
This information will be collected to
assure compliance with the Solvent
E:\FR\FM\18MRR3.SGM
18MRR3
Federal Register / Vol. 85, No. 53 / Wednesday, March 18, 2020 / Rules and Regulations
Extraction for Vegetable Oil Production
NESHAP.
Respondents/affected entities:
Owners or operators of vegetable oil
production processes.
Respondent’s obligation to respond:
Mandatory (40 CFR part 63, subpart
GGGG).
Estimated number of respondents: 90
(assumes one new respondent over the
next 3 years).
Frequency of response: Initially,
occasionally, and annually.
Total estimated burden: The annual
recordkeeping and reporting burden for
responding facilities to comply with all
of the requirements in the NESHAP,
averaged over the 3 years of this ICR, is
estimated to be 34,100 hours. Of these,
448 hours (per year) is the incremental
burden to comply with the final rule
amendments. Burden is defined at 5
CFR 1320.3(b).
Total estimated cost: The annual
recordkeeping and reporting cost for
responding facilities to comply with all
of the requirements in the NESHAP,
averaged over the 3 years of this ICR, is
estimated to be $3,490,000 (per year),
including $0 annualized capital or
operation and maintenance costs. Of the
total, $31,033 (per year) is the
incremental cost to comply with the
final amendments to the rule, or
approximately $345 per facility.
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
OMB approves this ICR, the Agency will
announce that approval in the Federal
Register and publish a technical
amendment to 40 CFR part 9 to display
the OMB control number for the
approved information collection
activities contained in this final rule.
jbell on DSKJLSW7X2PROD with RULES3
D. Regulatory Flexibility Act (RFA)
I certify that this action will not have
a significant economic impact on a
substantial number of small entities
under the RFA. The small entities
subject to the requirements of this
action are small vegetable oil
production facilities. The Agency has
determined that up to 12 small entities,
representing approximately 13 percent
of the total number of entities subject to
the final rule, may experience an impact
of less than 1 percent of revenues. See
section V.D of this preamble for
additional information on the economic
impacts of this action.
VerDate Sep<11>2014
20:53 Mar 17, 2020
Jkt 250001
E. Unfunded Mandates Reform Act
(UMRA)
This action does not contain an
unfunded mandate of $100 million or
more as described in UMRA, 2 U.S.C.
1531–1538, and does not significantly or
uniquely affect small governments. The
action imposes no enforceable duty on
any state, local, or tribal governments or
the private sector.
F. Executive Order 13132: Federalism
This action does not have federalism
implications. It will not have substantial
direct effects on the states, on the
relationship between the national
government and the states, or on the
distribution of power and
responsibilities among the various
levels of government.
G. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
This action does not have tribal
implications as specified in Executive
Order 13175. None of the solvent
extraction for vegetable oil production
facilities that have been identified as
being affected by this final action are
owned or operated by tribal
governments or located within tribal
lands. Thus, Executive Order 13175
does not apply to this action.
H. Executive Order 13045: Protection of
Children From Environmental Health
Risks and Safety Risks
This action is not subject to Executive
Order 13045 because the EPA does not
believe the environmental health risks
or safety risks addressed by this action
present a disproportionate risk to
children. This action’s health and risk
assessments are contained in sections
IV.A of this preamble and the
document, Residual Risk Assessment for
the Solvent Extraction for Vegetable Oil
Production Source Category in Support
of the 2019 Risk and Technology Review
Final Rule, which is available in the
docket for this rulemaking.
I. Executive Order 13211: Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use
This action is not subject to Executive
Order 13211, because it is not a
significant regulatory action under
Executive Order 12866.
J. National Technology Transfer and
Advancement Act (NTTAA)
This rulemaking involves technical
standards. As discussed in the preamble
of the proposal, the EPA conducted
searches for the Solvent Extraction for
Vegetable Oil Production Sector Risk
PO 00000
Frm 00019
Fmt 4701
Sfmt 4700
15625
and Technology Review through the
Enhanced National Standards Systems
Network Database managed by the
American National Standards Institute
(ANSI). We also contacted voluntary
consensus standards (VCS)
organizations and accessed and
searched their databases. We conducted
searches for EPA Method 311 of 40 CFR
part 63, appendix A. No applicable VCS
were identified for EPA Method 311.
The search identified two VCS that were
potentially applicable for this rule in
lieu of EPA reference methods. After
reviewing the available standards, the
EPA determined that the two candidate
VCS (ASTM D6438 (1999), CARB
Method 310)) identified for measuring
emissions of pollutants or their
surrogates subject to emissions
standards in the rule would not be
practical due to lack of equivalency,
documentation, validation data, and
other important technical and policy
considerations.
A thorough summary of the search
conducted, and results are included in
the memorandum, Voluntary Consensus
Standard Results for National Emission
Standards for Hazardous Air Pollutants
for Solvent Extraction for Vegetable Oil
Production, which is available in the
docket for this action.
K. Executive Order 12898: Federal
Actions To Address Environmental
Justice in Minority Populations and
Low-Income Populations
The EPA believes that this action does
not have disproportionately high and
adverse human health or environmental
effects on minority populations, lowincome populations, and/or indigenous
peoples, as specified in Executive Order
12898 (59 FR 7629, February 16, 1994).
The documentation for this decision
is contained in section IV.A of this
preamble and in the technical report,
Risk and Technology Review—Analysis
of Demographic Factors for Populations
Living Near Vegetable Oil Production
Facilities, available in the docket for this
action.
L. Congressional Review Act (CRA)
This action is subject to the CRA, and
the EPA will submit a rule report to
each House of the Congress and to the
Comptroller General of the United
States. This action is not a ‘‘major rule’’
as defined by 5 U.S.C. 804(2).
List of Subjects in 40 CFR Part 63
Environmental protection, Air
pollution control, Hazardous
substances, Reporting and
recordkeeping requirements.
E:\FR\FM\18MRR3.SGM
18MRR3
15626
Federal Register / Vol. 85, No. 53 / Wednesday, March 18, 2020 / Rules and Regulations
Dated: February 25, 2020.
Andrew R. Wheeler,
Administrator.
For the reasons set forth in the
preamble, the EPA is amending 40 CFR
part 63 as follows:
PART 63—NATIONAL EMISSION
STANDARDS FOR HAZARDOUS AIR
POLLUTANTS FOR SOURCE
CATEGORIES
Subpart GGGG—National Emission
Standards for Hazardous Air
Pollutants: Solvent Extraction for
Vegetable Oil Production
1. The authority citation for part 63
continues to read as follows:
■
■
Authority: 42 U.S.C. 7401, et seq.
2. Section 63.2834 is amended by
revising Table 1 of § 63.2834 to read as
follows:
§ 63.2834 When do I have to comply with
the standards in this subpart?
*
*
*
*
*
TABLE 1 OF § 63.2834—COMPLIANCE DATES FOR EXISTING AND NEW SOURCES
If your affected source is
categorized as . . .
(a) an existing source .......
(b) a new source ...............
(c) a new source ...............
(d) a new source ...............
And if . . .
you startup your affected source before April 12,
2001.
you startup your affected source on or after April 12,
2001, but before March 18, 2020.
you startup your affected source on or after March
18, 2020.
3. Section 63.2840 is amended by:
a. Revising the introductory text and
paragraphs (a)(1) introductory text and
(b) introductory text;
■ b. Removing and reserving paragraph
(b)(1);
■ c Revising paragraphs (b)(3) through
(5); and
■ d. Adding paragraphs (g) and (h).
The revisions and additions read as
follows:
■
■
jbell on DSKJLSW7X2PROD with RULES3
§ 63.2840 What emission requirements
must I meet?
For each facility meeting the
applicability criteria in § 63.2832, you
must comply with either the
requirements specified in paragraphs (a)
through (d), or the requirements in
paragraph (e) of this section. You must
also comply with the requirements in
paragraph (g) of this section. You must
comply with the work practice standard
provided in paragraph (h) of this
section, if you choose to operate your
source under an initial startup period
subject to § 63.2850(c)(2) or (d)(2).
(a)(1) The emission requirements limit
the number of gallons of HAP lost per
ton of listed oilseeds processed. For
each operating month, as defined in
§ 63.2872, you must calculate a
compliance ratio which compares your
actual HAP loss to your allowable HAP
loss for the previous 12 operating
months as shown in Equation 1 of this
section. Equation 1 of this section
follows:
*
*
*
*
*
VerDate Sep<11>2014
20:53 Mar 17, 2020
Jkt 250001
Then your compliance
date is . . .
Except for certain
requirements, as specified in
§§ 63.2840, 63.2850, 63.2851,
63.2852, 63.2853, 63.2861,
63.2862, and 63.2870, then
your compliance date is . . .
April 12, 2004 ...................
April 12, 2004 ...................
September 15, 2020.
September 15, 2020.
your startup date ..............
September 15, 2020.
your startup date ..............
your startup date.
(b) When your source has processed
listed oilseed for 12 operating months,
calculate the compliance ratio by the
end of each calendar month following
an operating month, as defined in
§ 63.2872, using Equation 2 of this
section. When calculating your
compliance ratio, consider the
conditions and exclusions in paragraphs
(b)(1) through (6) of this section:
*
*
*
*
*
(3) If your source shuts down and
processes no listed oilseed for an entire
calendar or accounting month, then you
must categorize the month as a
nonoperating month, as defined in
§ 63.2872. Exclude any nonoperating
months from the compliance ratio
determination.
(4) If your source is subject to an
initial startup period as defined in
§ 63.2872, you may exclude from the
compliance ratio determination any
solvent and oilseed information
recorded for the initial startup period,
provided you meet the work practice
standard in § 63.2850(c)(2) or (d)(2).
(5) Before September 15, 2020, if your
source is subject to a malfunction period
as defined in § 63.2872, exclude from
the compliance ratio determination any
solvent and oilseed information
recorded for the malfunction period.
The provisions of this paragraph (e) do
not apply on and after September 15,
2020.
*
*
*
*
*
(g) On or after September 15, 2020,
you must operate and maintain any
PO 00000
Frm 00020
Fmt 4701
Sfmt 4700
affected source, including associated air
pollution control equipment and
monitoring equipment, at all times in a
manner consistent with safety and good
air pollution control practices for
minimizing emissions. The general duty
to minimize emissions does not require
you to make any further efforts to
reduce emissions if levels required by
the applicable standard have been
achieved. Determination of whether a
source is operating in compliance with
operation and maintenance
requirements will be based on
information available to the
Administrator which may include, but
is not limited to, monitoring results,
review of operation and maintenance
procedures, review of operation and
maintenance records, and inspection of
the source.
(h) On and after September 15, 2020,
you must meet the requirements in
paragraphs (h)(1) through (3) of this
section if you choose to operate your
source under an initial startup period
subject to § 63.2850(c)(2) or (d)(2).
(1) You must operate the mineral oil
absorption system at all times during
the initial startup period unless doing so
is not possible due to safety
considerations;
(2) You must operate the solvent
condensers at all times during the initial
startup period unless doing so is not
possible due to safety considerations;
and
(3) You must follow site-specific
operating limits, established according
to the requirements in paragraphs
E:\FR\FM\18MRR3.SGM
18MRR3
Federal Register / Vol. 85, No. 53 / Wednesday, March 18, 2020 / Rules and Regulations
(h)(3)(i) and (ii) of this section, for
temperature and pressure for the
desolventizing and oil distillation units
associated with solvent recovery at all
times, unless doing so is not possible
due to safety considerations.
(i) Your site-specific operating limits
may be based on equipment design,
manufacturer’s recommendations, or
other site-specific operating values
established for normal operating
periods.
(ii) The operating limits may be in the
form of a minimum, maximum, or
operating range.
■ 4. Section 63.2850 is amended by:
■ a. Revising paragraph (a)(3) and
paragraph (a)(5) introductory text;
■ b. Adding paragraph (a)(5)(iv);
■ c. Revising paragraphs (b), (c)(1) and
(2), (d)(1) and (2), (e) introductory text,
and (e)(2); and
■ d. Revising Table 1 of § 63.2850.
The revisions and addition read as
follows:
§ 63.2850 How do I comply with the
hazardous air pollutant emission
standards?
(a) * * *
(3) Develop a written startup,
shutdown and malfunction (SSM) plan
in accordance with the provisions in
§ 63.2852. On and after September 15,
2020, an SSM plan is not required.
*
*
*
*
*
(5) Submit the reports in paragraphs
(a)(5)(i) through (iv) of this section, as
applicable:
*
*
*
*
*
(iv) Initial startup period reports in
accordance with § 63.2861(e).
*
*
*
*
*
(b) Existing sources under normal
operation. You must meet all of the
requirements listed in paragraph (a) of
this section and Table 1 of this section
for sources under normal operation, and
the schedules for demonstrating
compliance for existing sources under
normal operation in Table 2 of this
section.
(c) * * *
(1) Normal operation. Upon initial
startup of your new source, you must
meet all of the requirements listed in
§ 63.2850(a) and Table 1 of this section
for sources under normal operation, and
the schedules for demonstrating
compliance for new sources under
normal operation in Table 2 of this
section.
(2) Initial startup period. For up to 6
calendar months after the startup date of
your new source, you must meet all of
the requirements listed in paragraph (a)
of this section and Table 1 of this
section for sources operating under an
initial startup period, and the schedules
for demonstrating compliance for new
sources operating under an initial
startup period in Table 2 of this section.
On and after September 15, 2020, you
must also comply with the work
practice standard in § 63.2840(h) for the
duration of the initial startup period. At
the end of the initial startup period (as
defined in § 63.2872), your new source
must then meet all of the requirements
listed in Table 1 of this section for
sources under normal operation.
(d) * * *
(1) Normal operation. Upon initial
startup of your significantly modified
existing or new source, you must meet
all of the requirements listed in
paragraph (a) of this section and Table
1 of this section for sources under
normal operation, and the schedules for
demonstrating compliance for an
existing or new source that has been
significantly modified in Table 2 of this
section.
(2) Initial startup period. For up to 3
calendar months after the startup date of
your significantly modified existing or
new source, you must meet all of the
requirements listed in paragraph (a) of
this section and Table 1 of this section
for sources operating under an initial
startup period, and the schedules for
demonstrating compliance for a
significantly modified existing or new
source operating under an initial startup
period in Table 2 of this section. On and
after September 15, 2020, you must also
comply with the work practice standard
15627
in § 63.2840(h) for the duration of the
initial startup period. At the end of the
initial startup period (as defined in
§ 63.2872), your new or existing source
must meet all of the requirements listed
in Table 1 of this section for sources
under normal operation.
(e) Existing or new sources
experiencing a malfunction. A
malfunction is defined in § 63.2. In
general, it means any sudden,
infrequent, and not reasonably
preventable failure of air pollution
control equipment, process equipment,
or a process to function in a normal or
usual manner. If your existing or new
source experiences an unscheduled
shutdown as a result of a malfunction,
continues to operate during a
malfunction (including the period
reasonably necessary to correct the
malfunction), or starts up after a
shutdown resulting from a malfunction,
then you must meet the requirements
associated with one of two compliance
options. Routine or scheduled process
startups and shutdowns resulting from,
but not limited to, market demands,
maintenance activities, and switching
types of oilseed processed, are not
startups or shutdowns resulting from a
malfunction and, therefore, do not
qualify for this provision. Within 15
days of the beginning date of the
malfunction, you must choose to
comply with one of the options listed in
paragraphs (e)(1) and (2) of this section.
The provisions of this paragraph (e) do
not apply on and after September 15,
2020.
*
*
*
*
*
(2) Malfunction period. Throughout
the malfunction period, you must meet
all of the requirements listed in
paragraph (a) of this section and Table
1 of this section for sources operating
during a malfunction period. At the end
of the malfunction period, your source
must then meet all of the requirements
listed in Table 1 of this section for
sources under normal operation. Table 1
of this section follows:
jbell on DSKJLSW7X2PROD with RULES3
TABLE 1 OF § 63.2850—REQUIREMENTS FOR COMPLIANCE WITH HAP EMISSION STANDARDS
Are you required to . . .
For periods of normal
operation? a
For initial startup periods subject
to § 63.2850(c)(2) or (d)(2)?
Before September 15, 2020, for
malfunction periods subject to
§ 63.2850(e)(2)? a
(a)(1) Operate and maintain your
source in accordance with general duty provisions of § 63.6(e)
before September 15, 2020?
Yes. Additionally, the HAP emission limits will apply.
Yes, you are required to minimize
emissions to the extent practicable throughout the initial
startup period. Such measures
should be described in the SSM
plan.
Yes, you are required to minimize
emissions to the extent practicable
throughout the initial startup period. Such measures should be
described in the SSM plan.
VerDate Sep<11>2014
20:53 Mar 17, 2020
Jkt 250001
PO 00000
Frm 00021
Fmt 4701
Sfmt 4700
E:\FR\FM\18MRR3.SGM
18MRR3
15628
Federal Register / Vol. 85, No. 53 / Wednesday, March 18, 2020 / Rules and Regulations
jbell on DSKJLSW7X2PROD with RULES3
TABLE 1 OF § 63.2850—REQUIREMENTS FOR COMPLIANCE WITH HAP EMISSION STANDARDS—Continued
Before September 15, 2020, for
malfunction periods subject to
§ 63.2850(e)(2)? a
Are you required to . . .
For periods of normal
operation? a
For initial startup periods subject
to § 63.2850(c)(2) or (d)(2)?
(a)(2) Operate and maintain your
source in accordance with general duty provisions of § 63.6(e)
on and after September 15,
2020?
(b) Determine and record the extraction solvent loss in gallons
from your source?
No, you must meet the requirements of § 63.2840(g). Additionally, the HAP emission limits will apply.
No, you must meet the requirements of § 63.2840(g).
Yes, as described in § 63.2853 ..
Yes, as described in § 63.2862(e).
(c) Record the volume fraction of
HAP present at greater than 1
percent by volume and gallons
of extraction solvent in shipment received?
(d) Determine and record the
tons of each oilseed type processed by your source?
(e) Determine the weighted average volume fraction of HAP in
extraction solvent received as
described in § 63.2854 by the
end of the following calendar
month?
Yes ..............................................
Yes, as described in § 63.2862(e)
(before September 15, 2020)
and § 63.2862(f) (on and after
September 15, 2020).
Yes ................................................
Yes, as described in § 63.2855 ..
No .................................................
No.
Yes ..............................................
No, the HAP volume fraction in any
solvent received during a malfunction period is included in the
weighted average HAP determination for the next operating month.
(f) Determine and record the actual solvent loss, weighted average volume fraction HAP, oilseed processed and compliance ratio for each 12 operating month period as described in § 63.2840 by the end
of the following calendar
month?
(g) Submit a Notification of Compliance Status or Annual Compliance Certification as appropriate?
Yes ..............................................
No. Except for solvent received
by a new or reconstructed
source commencing operation
under an initial startup period,
the HAP volume fraction in any
solvent received during an initial startup period is included in
the weighted average HAP determination for the next operating month.
No, these requirements are not
applicable because your source
is not required to determine the
compliance ratio with data recorded for an initial startup period.
No. However, you may be required
to submit an annual compliance
certification for previous operating
months, if the deadline for the annual compliance certification happens to occur during the malfunction period.
(h)(1) Submit a Deviation Notification Report by the end of the
calendar month following the
month in which you determined
that the compliance ratio exceeds 1.00 as described in
§ 63.2861(b) before September
15, 2020?
(h)(2) Submit a Deviation Notification Report as described in
§ 63.2861(b) on and after September 15, 2020?
(i) Submit a Periodic SSM Report
as described in § 63.2861(c)?
(j) Submit an Immediate SSM
Report
as
described
in
§ 63.2861(d)?
(k) Submit an Initial Startup Report
as
described
in
§ 63.2861(e) on and after September 15, 2020?
Yes ..............................................
No. However, you may be required to submit an annual
compliance certification for previous operating months, if the
deadline for the annual compliance certification happens to
occur during the initial startup
period.
No, these requirements are not
applicable because your source
is not required to determine the
compliance ratio with data recorded for an initial startup period.
Yes,
as
described
in
§§ 63.2860(d) and 63.2861(a).
Yes.
No, these requirements are not applicable because your source is
not required to determine the compliance ratio with data recorded for
a malfunction period.
No, these requirements are not applicable because your source is
not required to determine the compliance ratio with data recorded for
a malfunction period.
Yes ..............................................
Yes ................................................
No.
No, a SSM activity is not categorized as normal operation.
No, a SSM activity is not categorized as normal operation.
Yes, before September 15, 2020
Yes.
Yes, only before September 15,
2020 and if your source does
not follow the SSM plan.
Yes ................................................
Yes, only if your source does not follow the SSM plan.
No ...............................................
No.
a Beginning on September 15, 2020, you must meet the requirements of this table for normal operating periods or for initial startup periods
subject to § 63.2850(c)(2) or (d)(2) at all times. The column ‘‘For malfunction periods subject to § 63.2850(e)(2)?’’ is not applicable beginning on
September 15, 2020.
VerDate Sep<11>2014
20:53 Mar 17, 2020
Jkt 250001
PO 00000
Frm 00022
Fmt 4701
Sfmt 4700
E:\FR\FM\18MRR3.SGM
18MRR3
Federal Register / Vol. 85, No. 53 / Wednesday, March 18, 2020 / Rules and Regulations
5. Section 63.2851 is amended by
revising paragraph (a) introductory text
and adding paragraph (a)(8) to read as
follows:
■
§ 63.2851 What is a plan for demonstrating
compliance?
(a) You must develop and implement
a written plan for demonstrating
compliance that provides the detailed
procedures you will follow to monitor
and record data necessary for
demonstrating compliance with this
subpart. Procedures followed for
quantifying solvent loss from the source
and amount of oilseed processed vary
from source to source because of sitespecific factors such as equipment
design characteristics and operating
conditions. Typical procedures include
one or more accurate measurement
methods such as weigh scales,
volumetric displacement, and material
mass balances. Because the industry
does not have a uniform set of
procedures, you must develop and
implement your own site-specific plan
for demonstrating compliance before the
compliance date for your source. You
must also incorporate the plan for
demonstrating compliance by reference
in the source’s title V permit and keep
the plan on-site and readily available as
long as the source is operational. If you
make any changes to the plan for
demonstrating compliance, then you
must keep all previous versions of the
plan and make them readily available
for inspection for at least 5 years after
each revision. The plan for
demonstrating compliance must include
the items in paragraphs (a)(1) through
(8) of this section:
*
*
*
*
*
(8) On and after September 15, 2020,
if you choose to operate your source
under an initial start-up period subject
to § 63.2850(c)(2) or (d)(2), the items in
paragraphs (c)(8)(i) and (ii) of this
section:
(i) Your site-specific operating limits,
and their basis, for temperature and
pressure for the desolventizing and oil
distillation units associated with solvent
recovery.
(ii) A detailed description of all
methods of measurement your source
will use to measure temperature and
pressure, including the measurement
frequency.
*
*
*
*
*
■ 6. Section 63.2852 is revised to read
as follows:
§ 63.2852 What is a startup, shutdown, and
malfunction plan?
Before September 15, 2020, you must
develop a written SSM plan in
accordance with § 63.6(e)(3). You must
complete the SSM plan before the
compliance date for your source. You
must also keep the SSM plan on-site
and readily available as long as the
source is operational. The SSM plan
provides detailed procedures for
operating and maintaining your source
to minimize emissions during a
qualifying SSM event for which the
source chooses the § 63.2850(e)(2)
malfunction period, or the
§ 63.2850(c)(2) or (d)(2) initial startup
period. The SSM plan must specify a
program of corrective action for
malfunctioning process and air
15629
pollution control equipment and reflect
the best practices now in use by the
industry to minimize emissions. Some
or all of the procedures may come from
plans you developed for other purposes
such as a Standard Operating Procedure
manual or an Occupational Safety and
Health Administration Process Safety
Management plan. To qualify as a SSM
plan, other such plans must meet all the
applicable requirements of these
NESHAP. The provisions of this section
do not apply on and after September 15,
2020.
■ 7. Section 63.2853 is amended by:
■ a. Revising paragraph (a)(2)
introductory text;
■ b. Revising the heading for Table 1 of
§ 63.2853 in paragraph (a)(2);
■ c. Adding Table 2 of § 63.2853(a)(2) to
paragraph (a)(2); and
■ d. Revising paragraphs (a)(3), (a)(5)(i),
and (c)(1), (3), and (4).
The revisions and addition read as
follows:
§ 63.2853 How do I determine the actual
solvent loss?
*
*
*
*
*
(a) * * *
(2) Source operating status. You must
categorize the operating status of your
source for each recorded time interval in
accordance with criteria in Table 1 or
Table 2 of this section, as follows:
TABLE 1 OF § 63.2853(a)(2)—CATEGORIZING YOUR SOURCE OPERATING STATUS BEFORE SEPTEMBER
15, 2020
*
*
*
*
*
jbell on DSKJLSW7X2PROD with RULES3
TABLE 2 OF § 63.2853(a)(2)—CATEGORIZING YOUR SOURCE OPERATING STATUS ON AND AFTER SEPTEMBER 15, 2020
If during a recorded time interval . . .
Then your source operating status
is . . .
(vi) Your source processes any amount of listed oilseed and source is not operating under an initial startup
operating period subject to § 63.2850(c)(2) or (d)(2).
(vii) Your source processes no agricultural product and your source is not operating under an initial startup
period subject to § 63.2850(c)(2) or (d)(2).
(viii) You choose to operate your source under an initial startup period subject to § 63.2850(c)(2) or (d)(2) ..
(ix) Your source processes agricultural products not defined as listed oilseed ................................................
A normal operating period.
(3) Measuring the beginning and
ending solvent inventory. You are
required to measure and record the
solvent inventory on the beginning and
ending dates of each normal operating
period that occurs during an operating
month. You must consistently follow
the procedures described in your plan
for demonstrating compliance, as
specified in § 63.2851, to determine the
extraction solvent inventory, and
maintain readily available records of the
VerDate Sep<11>2014
20:53 Mar 17, 2020
Jkt 250001
actual solvent loss inventory, as
described in § 63.2862(c)(1). In general,
you must measure and record the
solvent inventory only when the source
is actively processing any type of
agricultural product. When the source is
not active, some or all of the solvent
working capacity is transferred to
solvent storage tanks which can
artificially inflate the solvent inventory.
*
*
*
*
*
(5) * * *
PO 00000
Frm 00023
Fmt 4701
Sfmt 4700
A nonoperating period.
An initial startup period.
An exempt period.
(i) Solvent destroyed in a control
device. You may use a control device to
reduce solvent emissions to meet the
emission standard. The use of a control
device does not alter the emission limit
for the source. If you use a control
device that reduces solvent emissions
through destruction of the solvent
instead of recovery, then determine the
gallons of solvent that enter the control
device and are destroyed there during
each normal operating period. All
E:\FR\FM\18MRR3.SGM
18MRR3
jbell on DSKJLSW7X2PROD with RULES3
15630
Federal Register / Vol. 85, No. 53 / Wednesday, March 18, 2020 / Rules and Regulations
solvent destroyed in a control device
during a normal operating period can be
subtracted from the total solvent loss.
Examples of destructive emission
control devices include catalytic
incinerators, boilers, or flares. Identify
and describe, in your plan for
demonstrating compliance, each type of
reasonable and sound measurement
method that you use to quantify the
gallons of solvent entering and exiting
the control device and to determine the
destruction efficiency of the control
device. You may use design evaluations
to document the gallons of solvent
destroyed or removed by the control
device instead of performance testing
under § 63.7. The design evaluations
must be based on the procedures and
options described in § 63.985(b)(1)(i)(A)
through (C) or § 63.11, as appropriate.
All data, assumptions, and procedures
used in such evaluations must be
documented and available for
inspection. If you use performance
testing to determine solvent flow rate to
the control device or destruction
efficiency of the device, follow the
procedures as outlined in § 63.997(e)(1)
and (2) and the requirements in
paragraph (a)(5)(i)(A) of this section.
Instead of periodic performance testing
to demonstrate continued good
operation of the control device, you may
develop a monitoring plan, following
the procedures outlined in § 63.988(c)
and using operational parametric
measurement devices such as fan
parameters, percent measurements of
lower explosive limits, and combustion
temperature.
(A) On or after September 15, 2020,
you must conduct all performance tests
under such conditions as the
Administrator specifies to you based on
representative performance of the
affected source for the period being
tested. Representative conditions
exclude periods of startup and
shutdown unless specified by the
Administrator. You may not conduct
performance tests during periods of
malfunction. You must record the
process information that is necessary to
document operating conditions during
the test and include in such record an
explanation to support that such
conditions represent normal operation.
Upon request, you shall make available
to the Administrator such records as
may be necessary to determine the
conditions of performance tests.
(B) [Reserved]
(c) * * *
(1) Nonoperating periods as described
in paragraph (a)(2) of this section.
*
*
*
*
*
VerDate Sep<11>2014
20:53 Mar 17, 2020
Jkt 250001
(3) Before September 15, 2020,
malfunction periods as described in
§ 63.2850(e)(2).
(4) Exempt operation periods as
described in paragraph (a)(2) of this
section.
■ 8. Section 63.2855 is amended by
revising paragraphs (a)(3), (a)(5)(i), and
(c)(3) to read as follows:
§ 63.2855 How do I determine the quantity
of oilseed processed?
*
*
*
*
*
(a) * * *
(3) Measuring the beginning and
ending inventory for each oilseed. You
are required to measure and record the
oilseed inventory on the beginning and
ending dates of each normal operating
period that occurs during an operating
month. You must consistently follow
the procedures described in your plan
for demonstrating compliance, as
specified in § 63.2851, to determine the
oilseed inventory on an as received
basis and maintain readily available
records of the oilseed inventory as
described by § 63.2862(c)(3).
*
*
*
*
*
(5) * * *
(i) Oilseed that molds or otherwise
become unsuitable for processing.
*
*
*
*
*
(c) * * *
(3) Before September 15, 2020,
malfunction periods as described in
§ 63.2850(e)(2).
*
*
*
*
*
■ 9. Section 63.2861 is amended by
■ a. Revising paragraph (b) introductory
text;
■ b. Adding paragraphs (b)(5) through
(8);
■ c. Revising paragraphs (c)
introductory text and (d) introductory
text; and
■ d. Adding paragraphs (e) through (i).
The revisions and additions read as
follows:
§ 63.2861
when?
What reports must I submit and
*
*
*
*
*
(b) Deviation notification report.
Submit a deviation report for each
compliance determination you make in
which the compliance ratio exceeds
1.00 as determined under § 63.2840(c)
or if you deviate from the work practice
standard for an initial startup period
subject to § 63.2850(c)(2) or (d)(2).
Submit the deviation report by the end
of the month following the calendar
month in which you determined the
deviation. The deviation notification
report must include the items in
paragraphs (b)(1) through (7) of this
section if you exceed the compliance
PO 00000
Frm 00024
Fmt 4701
Sfmt 4700
ratio, and must include the items in
paragraphs (b)(1), (2), and (5) through
(8) of this section if you deviate from the
work practice standard:
*
*
*
*
*
(5) Beginning on September 15, 2020,
the number of deviations and for each
deviation the date and duration of each
deviation. Flag and provide an
explanation for any deviation from the
compliance ratio for which a deviation
report is being submitted for more than
one consecutive month (i.e., include a
reference to the original date and
reporting of the deviation). If the
explanation provides that corrective
actions have returned the affected
unit(s) to its normal operation, you are
not required to include the items in
paragraphs (b)(6) and (7) of this section.
(6) Beginning on September 15, 2020,
a statement of the cause of each
deviation (including unknown cause, if
applicable).
(7) Beginning on September 15, 2020,
for each deviation, a list of the affected
sources or equipment, an estimate of the
quantity of HAP emitted over the
emission requirements of § 63.2840, and
a description of the method used to
estimate the emissions.
(8) A description of the deviation
from the work practice standard during
the initial startup period, including the
records of § 63.2862(f) for the deviation.
(c) Periodic startup, shutdown, and
malfunction report. Before September
15, 2020, if you choose to operate your
source under an initial startup period
subject to § 63.2850(c)(2) or (d)(2) or a
malfunction period subject to
§ 63.2850(e)(2), you must submit a
periodic SSM report by the end of the
calendar month following each month
in which the initial startup period or
malfunction period occurred. The
periodic SSM report must include the
items in paragraphs (c)(1) through (3) of
this section. The provisions of this
paragraph (c) do not apply on and after
September 15, 2020.
*
*
*
*
*
(d) Immediate SSM reports. Before
September 15, 2020, if you handle a
SSM during an initial startup period
subject to § 63.2850(c)(2) or (d)(2) or a
malfunction period subject to
§ 63.2850(e)(2) differently from
procedures in the SSM plan and the
relevant emission requirements in
§ 63.2840 are exceeded, then you must
submit an immediate SSM report.
Immediate SSM reports consist of a
telephone call or facsimile transmission
to the responsible agency within 2
working days after starting actions
inconsistent with the SSM plan,
followed by a letter within 7 working
E:\FR\FM\18MRR3.SGM
18MRR3
jbell on DSKJLSW7X2PROD with RULES3
Federal Register / Vol. 85, No. 53 / Wednesday, March 18, 2020 / Rules and Regulations
days after the end of the event. The
letter must include the items in
paragraphs (d)(1) through (3) of this
section. The provisions of this
paragraph (d) do not apply on and after
September 15, 2020.
*
*
*
*
*
(e) Initial startup period reports. If
you choose to operate your source under
an initial startup period subject to
§ 63.2850(c)(2) or (d)(2) on and after
September 15, 2020, you must submit
an initial startup period report within
30 days after the initial startup period
ends. The report must include the items
in paragraphs (e)(1) through (3) of this
section.
(1) The name and address of the
owner or operator.
(2) The physical address of the
vegetable oil production process.
(3) A compliance certification
indicating whether the source was in
compliance with the work practice
standard of § 63.2840(h).
(f) Performance tests. On and after
September 15, 2020, if you conduct
performance tests to determine solvent
flow rate to a control device or
destruction efficiency of a control
device according to the requirements of
§ 63.2853(a)(5)(i), within 60 days after
the date of completing each
performance test, you must submit the
results of the performance test following
the procedures specified in paragraphs
(f)(1) and (2) of this section.
(1) Data collected using test methods
supported by EPA’s Electronic Reporting
Tool (ERT) as listed on EPA’s ERT
website (https://www.epa.gov/
electronic-reporting-air-emissions/
electronic-reporting-tool-ert) at the time
of the test. Submit the results of the
performance test to EPA via the
Compliance and Emissions Data
Reporting Interface (CEDRI), which can
be accessed through EPA’s Central Data
Exchange (CDX) (https://cdx.epa.gov/).
The data must be submitted in a file
format generated through the use of
EPA’s ERT. Alternatively, you may
submit an electronic file consistent with
the extensible markup language (XML)
schema listed on EPA’s ERT website.
(2) Data collected using test methods
that are not supported by EPA’s ERT as
listed on EPA’s ERT website at the time
of the test. The results of the
performance test must be included as an
attachment in the ERT or an alternate
electronic file consistent with the XML
schema listed on EPA’s ERT website.
Submit the ERT generated package or
alternative file to EPA via CEDRI.
(3) Confidential business information
(CBI). If you claim some of the
information submitted under paragraph
VerDate Sep<11>2014
20:53 Mar 17, 2020
Jkt 250001
(f) or (g) of this section is CBI, you must
submit a complete file, including
information claimed to be CBI, to EPA.
The file must be generated through the
use of EPA’s ERT or an alternate
electronic file consistent with the XML
schema listed on EPA’s ERT website.
Submit the file on a compact disc, flash
drive, or other commonly used
electronic storage medium and clearly
mark the medium as CBI. Mail the
electronic medium to U.S. EPA/OAQPS/
CORE CBI Office, Attention: Group
Leader, Measurement Policy Group, MD
C404–02, 4930 Old Page Rd., Durham,
NC 27703. The same file with the CBI
omitted must be submitted to EPA via
EPA’s CDX as described in paragraph
(f)(1) of this section.
(g) Submitting reports electronically.
On and after September 15, 2020, you
must submit the initial notification
required in § 63.2860(b) and the annual
compliance certification, deviation
report, and initial startup report
required in § 63.2861(a), (b), and (e) to
the EPA via CEDRI, which can be
accessed through the EPA’s CDX
(https://cdx.epa.gov). The owner or
operator must upload to CEDRI an
electronic copy of each applicable
notification in portable document
format (PDF). The applicable
notification must be submitted by the
deadline specified in this subpart,
regardless of the method in which the
reports are submitted. You must use the
appropriate electronic report template
on the CEDRI website (https://
www.epa.gov/electronic-reporting-airemissions/compliance-and-emissionsdata-reporting-interface-cedri) for this
subpart. The date report templates
become available will be listed on the
CEDRI website. The report must be
submitted by the deadline specified in
this subpart, regardless of the method in
which the report is submitted. If you
claim some of the information required
to be submitted via CEDRI is CBI,
submit a complete report, including
information claimed to be CBI, to EPA.
The report must be generated using the
appropriate form on the CEDRI website.
Submit the file on a compact disc, flash
drive, or other commonly used
electronic storage medium and clearly
mark the medium as CBI. Mail the
electronic medium to U.S. EPA/OAQPS/
CORE CBI Office, Attention: Group
Leader, Measurement Policy Group, MD
C404–02, 4930 Old Page Rd., Durham,
NC 27703. The same file with the CBI
omitted must be submitted to EPA via
EPA’s CDX as described earlier in this
paragraph.
(h) Claims of EPA system outage. If
you are required to electronically
submit a report through CEDRI in EPA’s
PO 00000
Frm 00025
Fmt 4701
Sfmt 4700
15631
CDX, you may assert a claim of EPA
system outage for failure to timely
comply with the reporting requirement.
To assert a claim of EPA system outage,
you must meet the requirements
outlined in paragraphs (h)(1) through (7)
of this section.
(1) You must have been or will be
precluded from accessing CEDRI and
submitting a required report within the
time prescribed due to an outage of
either EPA’s CEDRI or CDX systems.
(2) The outage must have occurred
within the period of time beginning five
business days prior to the date that the
submission is due.
(3) The outage may be planned or
unplanned.
(4) You must submit notification to
the Administrator in writing as soon as
possible following the date you first
knew, or through due diligence should
have known, that the event may cause
or has caused a delay in reporting.
(5) You must provide to the
Administrator a written description
identifying:
(i) The date(s) and time(s) when CDX
or CEDRI was accessed and the system
was unavailable;
(ii) A rationale for attributing the
delay in reporting beyond the regulatory
deadline to EPA system outage;
(iii) Measures taken or to be taken to
minimize the delay in reporting; and
(iv) The date by which you propose to
report, or if you have already met the
reporting requirement at the time of the
notification, the date you reported.
(6) The decision to accept the claim
of EPA system outage and allow an
extension to the reporting deadline is
solely within the discretion of the
Administrator.
(7) In any circumstance, the report
must be submitted electronically as
soon as possible after the outage is
resolved.
(i) Claims of force majeure. If you are
required to electronically submit a
report through CEDRI in EPA’s CDX,
you may assert a claim of force majeure
for failure to timely comply with the
reporting requirement. To assert a claim
of force majeure, you must meet the
requirements outlined in paragraphs
(i)(1) through (5) of this section.
(1) You may submit a claim if a force
majeure event is about to occur, occurs,
or has occurred or there are lingering
effects from such an event within the
period of time beginning five business
days prior to the date the submission is
due. For the purposes of this section, a
force majeure event is defined as an
event that will be or has been caused by
circumstances beyond the control of the
affected facility, its contractors, or any
entity controlled by the affected facility
E:\FR\FM\18MRR3.SGM
18MRR3
15632
Federal Register / Vol. 85, No. 53 / Wednesday, March 18, 2020 / Rules and Regulations
that prevents you from complying with
the requirement to submit a report
electronically within the time period
prescribed. Examples of such events are
acts of nature (e.g., hurricanes,
earthquakes, or floods), acts of war or
terrorism, or equipment failure or safety
hazard beyond the control of the
affected facility (e.g., large scale power
outage).
(2) You must submit notification to
the Administrator in writing as soon as
possible following the date you first
knew, or through due diligence should
have known, that the event may cause
or has caused a delay in reporting.
(3) You must provide to the
Administrator:
(i) A written description of the force
majeure event;
(ii) A rationale for attributing the
delay in reporting beyond the regulatory
deadline to the force majeure event;
(iii) Measures taken or to be taken to
minimize the delay in reporting; and
(iv) The date by which you propose to
report, or if you have already met the
reporting requirement at the time of the
notification, the date you reported.
(4) The decision to accept the claim
of force majeure and allow an extension
to the reporting deadline is solely
within the discretion of the
Administrator.
(5) In any circumstance, the reporting
must occur as soon as possible after the
force majeure event occurs.
■ 10. Section 63.2862 is amended by:
■ a. Revising paragraph (b) and
paragraph (c) introductory text;
■ b. Revising paragraphs (c)(3)(ii), (d)
introductory text, and (e) introductory
text; and
■ c. Adding paragraphs (f) through (h).
The revisions and additions read as
follows:
§ 63.2862
What records must I keep?
jbell on DSKJLSW7X2PROD with RULES3
*
*
*
*
*
(b) Before September 15, 2020,
prepare a plan for demonstrating
compliance (as described in § 63.2851)
and a SSM plan (as described in
§ 63.2852). In these two plans, describe
the procedures you will follow in
obtaining and recording data, and
determining compliance under normal
operations or a SSM subject to the
§ 63.2850(c)(2) or (d)(2) initial startup
period or the § 63.2850(e)(2)
malfunction period. Complete both
plans before the compliance date for
your source and keep them on-site and
readily available as long as the source is
operational. On and after September 15,
2020, the requirement to prepare a SSM
plan no longer applies, and the plan for
demonstrating compliance must only
describe the procedures you develop
VerDate Sep<11>2014
20:53 Mar 17, 2020
Jkt 250001
according to the requirements of
§ 63.2851.
(c) If your source processes any listed
oilseed, record the items in paragraphs
(c)(1) through (3) of this section:
*
*
*
*
*
(3) * * *
(ii) The operating status of your
source, as described in § 63.2853(a)(2).
On the log for each type of listed oilseed
that is not being processed during a
normal operating period, you must
record which type of listed oilseed is
being processed in addition to the
source operating status.
*
*
*
*
*
(d) After your source has processed
listed oilseed for 12 operating months,
record the items in paragraphs (d)(1)
through (5) of this section by the end of
the calendar month following each
operating month:
*
*
*
*
*
(e) Before September 15, 2020, for
each SSM event subject to an initial
startup period as described in
§ 63.2850(c)(2) or (d)(2), or a
malfunction period as described in
§ 63.2850(e)(2), record the items in
paragraphs (e)(1) through (3) of this
section by the end of the calendar
month following each month in which
the initial startup period or malfunction
period occurred. The provisions of this
paragraph (e) do not apply on and after
September 15, 2020.
*
*
*
*
*
(f) On and after September 15, 2020,
for each initial startup period subject to
§ 63.2850(c)(2) or (d)(2), record the
items in paragraphs (f)(1) through (6) of
this section by the end of the calendar
month following each month in which
the initial startup period occurred.
(1) A description and dates of the
initial startup period, and reason it
qualifies as an initial startup.
(2) An estimate of the solvent loss in
gallons for the duration of the initial
startup or malfunction period with
supporting documentation.
(3) Nominal design rate of the
extractor and operating rate of the
extractor for the duration of the initial
startup period, or permitted production
rate and actual production rate of your
source for the duration of the initial
startup period.
(4) Measured values for temperature
and pressure for the desolventizing and
oil distillation units associated with
solvent recovery.
(5) Information to indicate the mineral
oil absorption system was operating at
all times during the initial startup
period.
PO 00000
Frm 00026
Fmt 4701
Sfmt 4700
(6) Information to indicate the solvent
condensers were operating at all times
during the initial startup period.
(g) On and after September 15, 2020,
keep the records of deviations specified
in paragraphs (f)(1) through (4) of this
section for each compliance
determination you make in which the
compliance ratio exceeds 1.00 as
determined under § 63.2840(c) or if you
deviate from the work practice standard
for an initial startup period subject to
§ 63.2850(c)(2) or (d)(2).
(1) The number of deviations, and the
date and duration of each deviation. For
deviations from the compliance ratio,
the date of the deviation is the date the
compliance ratio determination is made.
The duration of the deviation from the
compliance ratio is the length of time
taken to address the cause of the
deviation, including the duration of any
malfunction, and return the affected
unit(s) to its normal or usual manner of
operation. For deviations from the work
practice standard during the initial
startup period, the date of the deviation
is the date(s) when the facility fails to
comply with any of the work practice
standard in § 63.2840(h). The duration
of the deviation from the work practice
standard is the length of time taken to
return to the work practice standards.
(2) A statement of the cause of each
deviation (including unknown cause, if
applicable).
(3) For each deviation, a list of the
affected sources or equipment, an
estimate of the quantity of each
regulated pollutant emitted over any
emission limit, and a description of the
method used to estimate the emissions.
(4) Actions taken to minimize
emissions in accordance with
§ 63.2840(g), and any corrective actions
taken to return the affected unit to its
normal or usual manner of operation.
(5) If you deviate from the work
practice standard for an initial startup
period, a description of the deviation
from the work practice standard.
(h) Any records required to be
maintained by this part that are
submitted electronically via EPA’s
CEDRI may be maintained in electronic
format. This ability to maintain
electronic copies does not affect the
requirement for facilities to make
records, data, and reports available
upon request to a delegated air agency
or EPA as part of an on-site compliance
evaluation.
■ 11. Section 63.2870 is amended by
revising Table 1 to § 63.2870 to read as
follows:
§ 63.2870 What parts of the General
Provisions apply to me?
*
E:\FR\FM\18MRR3.SGM
*
*
18MRR3
*
*
Federal Register / Vol. 85, No. 53 / Wednesday, March 18, 2020 / Rules and Regulations
15633
TABLE 1 TO § 63.2870—APPLICABILITY OF 40 CFR PART 63, SUBPART A, TO 40 CFR, PART 63, SUBPART GGGG
General provisions citation
Subject of citation
Brief description of
requirement
§ 63.1 ..................................
Applicability ..............
Yes.
§ 63.2 ..................................
Definitions ................
§ 63.3 ..................................
Units and abbreviations.
§ 63.4 ..................................
Prohibited activities
and circumvention.
§ 63.5 ..................................
Construction/reconstruction.
[Reserved].
Application for approval.
Initial applicability determination; applicability after standard established;
permit requirements; extensions;
notifications.
Definitions for part 63
standards.
Units and abbreviations for part 63
standards.
Prohibited activities;
compliance date;
circumvention; severability.
Applicability; applications; approvals.
Yes ...........................
Except for subsections of § 63.5 as listed
below.
Type and quantity of
HAP, operating parameters.
No .............................
All sources emit HAP. Subpart GGGG
does not require control from specific
emission points.
Application for approval.
No .............................
The requirements of the application for approval for new, reconstructed and significantly modified sources are described in
§ 63.2860(b) and (c) of subpart GGGG.
General provision requirements for identification of HAP emission points or estimates of actual emissions are not required. Descriptions of control and methods, and the estimated and actual control efficiency of such do not apply. Requirements for describing control equipment and the estimated and actual control efficiency of such equipment apply
only to control equipment to which the
subpart GGGG requirements for quantifying.
Except for subsections of § 63.6 as listed
below.
Section 63.2834 of subpart GGGG specifies the compliance dates for new and
reconstructed sources.
§ 63.5(c) ..............................
§ 63.5(d)(1)(ii)(H) .................
Yes ...........................
§ 63.6 ..................................
Applicability of General Provisions.
Compliance dates,
new and reconstructed sources.
[Reserved].
[Reserved].
[Reserved].
Operation and Maintenance.
Applicability ..............
Yes ...........................
..................................
No .............................
..................................
§ 63.6(e)(1)(ii) ......................
Operation and Maintenance.
Requirement to correct malfunctions
as soon as practicable.
§ 63.6(e)(3)(i) through
(e)(3)(ii) and
§ 63.6(e)(3)(v) through
(vii).
§ 63.6(e)(3)(iii) .....................
Operation and maintenance requirements.
..................................
Yes, before September 15, 2020.
No, on or after
September 15,
2020.
Yes, before September 15, 2020].
No, on or after
September 15,
2020.
Yes, before September 15, 2020.
Operation and maintenance requirements.
..................................
No .............................
§ 63.6(e)(3)(iv) .....................
Operation and maintenance requirements.
..................................
No .............................
VerDate Sep<11>2014
21:23 Mar 17, 2020
Jkt 250001
PO 00000
Frm 00027
Fmt 4701
Except as specifically provided in this subpart.
Yes.
[Reserved].
§ 63.6(b)(6) ..........................
§ 63.6(c)(3)–(4) ...................
§ 63.6(d) ..............................
§ 63.6(e)(1)(i) ......................
Explanation
Yes.
§ 63.5(d)(1)(ii)(I) ..................
§ 63.5(d)(1)(iii), (d)(2),
(d)(3)(ii).
§ 63.6(b)(1)–(3) ...................
jbell on DSKJLSW7X2PROD with RULES3
Applies to subpart
Sfmt 4700
See § 63.2840(g) for general duty requirement
See § 63.2840(g) for general duty requirement.
Minimize emissions to the extent practicable. On or after September 15, 2020,
see § 63.2840(g) for general duty requirement.
Minimize emissions to the extent practicable. On or after September 15, 2020,
see § 63.2840(g) for general duty requirement.
Report SSM and in accordance with
§ 63.2861(c) and (d).
E:\FR\FM\18MRR3.SGM
18MRR3
15634
Federal Register / Vol. 85, No. 53 / Wednesday, March 18, 2020 / Rules and Regulations
TABLE 1 TO § 63.2870—APPLICABILITY OF 40 CFR PART 63, SUBPART A, TO 40 CFR, PART 63, SUBPART GGGG—
Continued
General provisions citation
Subject of citation
Brief description of
requirement
§ 63.6(e)(3)(viii) ...................
Operation and maintenance requirements.
..................................
§ 63.6(e)(3)(ix) .....................
Title V permit ............
..................................
§ 63.6(f)(1) ...........................
Compliance with
nonopacity emission standards except during SSM.
Comply with emission standards at
all times except
during SSM.
§ 63.6(f)(2)–(3) ....................
Methods for Deter..................................
mining Compliance.
Use of an Alternative
..................................
Standard.
Opacity/Visible emis..................................
sion (VE) standards.
Compliance extenProcedures and crision.
teria for responsible agency to
grant compliance
extension.
Presidential compliPresident may exance exemption.
empt source category from requirement to comply
with subpart.
Performance testing
Representative conrequirements.
ditions for performance test.
§ 63.6(g) ..............................
§ 63.6(h) ..............................
§ 63.6(i) ...............................
§ 63.6(j) ...............................
§ 63.7(e)(1) ..........................
Yes, before September 15, 2020.
No, on or after
September 15,
2020.
Yes, before September 15, 2020.
No, on or after
September 15,
2020.
Yes, before September 15, 2020.
No, on or after
September 15,
2020.
Yes.
No .............................
Yes, before September 15, 2020.
No, on or after
September 15,
2020.
Yes ...........................
§ 63.8 ..................................
Monitoring requirements.
Notification requirements.
Notification requirements.
..................................
No .............................
Applicability and
state delegation.
Initial notification requirements for existing sources.
Notification requirement for certain
new/reconstructed
sources.
Notify responsible
agency 60 days
ahead.
Notify responsible
agency 30 days
ahead.
Notification of performance evaluation; Notification
using COMS data;
notification that exceeded criterion for
relative accuracy.
Yes ...........................
Notification requirements.
§ 63.9(e) ..............................
Notification of performance test.
§ 63.9(f) ...............................
Notification of VE/
opacity observations.
Additional notifications when using a
continuous monitoring system
(CMS).
§ 63.9(g) ..............................
VerDate Sep<11>2014
21:23 Mar 17, 2020
Jkt 250001
PO 00000
Frm 00028
Fmt 4701
Subpart GGGG has no opacity or VE
standards.
Yes..
Schedule, conditions,
notifications and
procedures.
§ 63.9(b)(3)–(5) ...................
Except, before September 15, 2020, report
each revision to your SSM plan in accordance with § 63.2861(c) rather than
§ 63.10(d)(5)
as
required
under
§ 63.6(e)(3)(viii).
Yes..
Performance testing
requirements.
§ 63.9(b)(2) ..........................
Explanation
Yes.
§ 63.7(e)(2)–(4), (f), (g), and
(h).
§ 63.9 ..................................
jbell on DSKJLSW7X2PROD with RULES3
Applies to subpart
No .............................
Yes ...........................
See § 63.2853(a)(5)(i)(A) for performance
testing requirements.
Subpart GGGG requires performance testing only if the source applies additional
control that destroys solvent. Section
63.2850(a)(6) requires sources to follow
the performance testing guidelines of
the General Provisions if a control is
added.
Subpart GGGG does not require monitoring other than as specified therein.
Except for subsections of § 63.9 as listed
below.
Section 63.2860(a) of subpart GGGG
specifies the requirements of the initial
notification for existing sources.
Except the information requirements differ
as described in § 63.2860(b) of subpart
GGGG.
Yes ...........................
Applies only if performance testing is performed.
No .............................
Subpart GGGG has no opacity or VE
standards.
No .............................
Subpart GGGG has no CMS requirements.
Sfmt 4700
E:\FR\FM\18MRR3.SGM
18MRR3
Federal Register / Vol. 85, No. 53 / Wednesday, March 18, 2020 / Rules and Regulations
15635
TABLE 1 TO § 63.2870—APPLICABILITY OF 40 CFR PART 63, SUBPART A, TO 40 CFR, PART 63, SUBPART GGGG—
Continued
General provisions citation
Subject of citation
Brief description of
requirement
Applies to subpart
Explanation
§ 63.9(h) ..............................
Notification of compliance status.
Contents ...................
No .............................
§ 63.10 ................................
Schedule for reporting, record storage.
Record SSM event ...
Yes ...........................
§ 63.10(b)(2)(i) ....................
Recordkeeping/reporting.
Recordkeeping .........
§ 63.10(b)(2)(ii)–(iii) .............
Recordkeeping .........
Malfunction of air
pollution equipment.
No .............................
Section 63.2860(d) of subpart GGGG
specifies requirements for the notification of compliance status.
Except for subsections of § 63.10 as listed
below.
Before September 15, 2020, applicable to
periods when sources must implement
their SSM plan as specified in subpart
GGGG. On or after September 15,
2020, meet the requirements of
§ 63.2862(f).
Before September 15, 2020, applies only if
air pollution control equipment has been
added to the process and is necessary
for the source to meet the emission
limit. On or after September 15, 2020,
meet the requirements of § 63.2862(g).
§ 63.10(b)(2)(iv)–(v) ............
Recordkeeping .........
SSM recordkeeping
§ 63.10(b)(2)(vi) ...................
Recordkeeping .........
CMS recordkeeping
Yes, before September 15, 2020.
No, on or after
September 15,
2020.
No .............................
§ 63.10(b)(2)(viii)–(ix) ..........
Recordkeeping .........
Conditions of performance test.
Yes ...........................
§ 63.10(b)(2)(x)–(xii) ............
Recordkeeping .........
No .............................
§ 63.10(c) ............................
Recordkeeping .........
No .............................
Subpart GGGG does not require CMS.
§ 63.10(d)(2) ........................
Reporting ..................
Yes ...........................
§ 63.10(d)(3) ........................
Reporting ..................
§ 63.10(d)(4) ........................
Reporting ..................
CMS, performance
testing, and opacity and VE observations recordkeeping.
Additional CMS recordkeeping.
Reporting performance test results.
Reporting opacity or
VE observations.
Progress reports ......
Subpart GGGG has no CMS requirements.
Applies only if performance tests are performed. Subpart GGGG does not have
any CMS opacity or VE observation requirements.
Subpart GGGG does not require CMS.
§ 63.10(d)(5) ........................
Reporting ..................
SSM reporting ..........
No .............................
§ 63.10(e) ............................
Reporting ..................
No .............................
§ 63.11 ................................
Control device requirements.
Additional CMS reports.
Requirements for
flares.
Applies only if performance testing is performed.
Subpart GGGG has no opacity or VE
standards.
Applies only if a condition of compliance
extension exists.
Section 63.2861(c) and (d) specify SSM
reporting requirements.
Subpart GGGG does not require CMS.
§ 63.12 ................................
State authority and
delegations.
State/regional addresses.
State authority to enforce standards.
Addresses where reports, notifications,
and requests are
sent.
Test methods incorporated by reference.
Public and confidential information.
Yes.
jbell on DSKJLSW7X2PROD with RULES3
§ 63.13 ................................
§ 63.14 ................................
Incorporation by reference.
§ 63.15 ................................
Availability of information and confidentiality.
12. Section 63.2872 is amended in
paragraph (c) by:
■ a. Revising the definitions for
‘‘Compliance ratio’’, ‘‘Hazardous air
pollutant (HAP)’’, ‘‘Initial startup
period’’, and ‘‘Malfunction period’’;
■
VerDate Sep<11>2014
21:23 Mar 17, 2020
Jkt 250001
Yes, before September 15, 2020.
No, on or after
September 15,
2020.
No .............................
Yes ...........................
Yes ...........................
Yes.
Yes.
Yes.
b. Adding a definition in alphabetical
order for ‘‘Nonoperating month’’; and
■ c. Revising the definitions of ‘‘Normal
operating period’’ and ‘‘Operating
month’’.
■
PO 00000
Frm 00029
Fmt 4701
Applies only if your source uses a flare to
control solvent emissions. Subpart
GGGG does not require flares.
Sfmt 4700
The revisions and addition read as
follows:
§ 63.2872
subpart?
*
E:\FR\FM\18MRR3.SGM
*
What definitions apply to this
*
18MRR3
*
*
15636
Federal Register / Vol. 85, No. 53 / Wednesday, March 18, 2020 / Rules and Regulations
jbell on DSKJLSW7X2PROD with RULES3
Compliance ratio means a ratio of the
actual HAP loss in gallons from the
previous 12 operating months to an
allowable HAP loss in gallons, which is
determined by using oilseed solvent loss
factors in Table 1 of § 63.2840, the
weighted average volume fraction of
HAP in solvent received for the
previous 12 operating months, and the
tons of each type of listed oilseed
processed in the previous 12 operating
months. Months during which no listed
oilseed is processed, or months during
which the § 63.2850(c)(2) or (d)(2) initial
startup period or, before September 15,
2020, the § 63.2850(e)(2) malfunction
period applies, are excluded from this
calculation. Equation 2 of § 63.2840 is
used to calculate this value. If the value
is less than or equal to 1.00, the source
is in compliance. If the value is greater
than 1.00, the source is deviating from
compliance.
*
*
*
*
*
Hazardous air pollutant (HAP) means
any substance or mixture of substances
listed as a hazardous air pollutant under
section 112(b) of the Clean Air Act.
*
*
*
*
*
Initial startup period means a period
of time from the initial startup date of
a new, reconstructed, or significantly
modified source, for which you choose
to operate the source under an initial
startup period subject to § 63.2850(c)(2)
or (d)(2), until the date your source
operates for 15 consecutive days at or
above 90 percent of the nominal design
rate of the extractor or at or above 90
percent of the permitted production rate
VerDate Sep<11>2014
20:53 Mar 17, 2020
Jkt 250001
for your source. The initial startup
period following initial startup of a new
or reconstructed source may not exceed
6 calendar months. The initial startup
period following a significant
modification may not exceed 3 calendar
months. Solvent and oilseed inventory
information recorded during the initial
startup period is excluded from use in
any compliance ratio determinations.
*
*
*
*
*
Malfunction period means a period of
time between the beginning and end of
a process malfunction and the time
reasonably necessary for a source to
correct the malfunction for which you
choose to operate the source under a
malfunction period subject to
§ 63.2850(e)(2). This period may include
the duration of an unscheduled process
shutdown, continued operation during a
malfunction, or the subsequent process
startup after a shutdown resulting from
a malfunction. During a malfunction
period, a source complies with the
standards by minimizing HAP
emissions to the extent practicable.
Therefore, solvent and oilseed inventory
information recorded during a
malfunction period is excluded from
use in any compliance ratio
determinations.
*
*
*
*
*
Nonoperating month means any
entire calendar or accounting month in
which a source processes no agricultural
product.
Nonoperating period means any
period of time in which a source
processes no agricultural product. This
PO 00000
Frm 00030
Fmt 4701
Sfmt 9990
operating status does not apply during
any period in which the source operates
under an initial startup period as
described in § 63.2850(c)(2) or (d)(2), or,
before September 15, 2020, a
malfunction period as described in
§ 63.2850(e)(2).
Normal operating period or normal
operation means any period of time in
which a source processes a listed
oilseed that is not categorized as an
initial startup period as described in
§ 63.2850(c)(2) or (d)(2), or, before
September 15, 2020, a malfunction
period as described in § 63.2850(e)(2).
At the beginning and ending dates of a
normal operating period, solvent and
oilseed inventory information is
recorded and included in the
compliance ratio determination.
*
*
*
*
*
Operating month means any calendar
or accounting month in which a source
processes any quantity of listed oilseed,
excluding any entire calendar or
accounting month in which the source
operated under an initial startup period
as described in § 63.2850(c)(2) or (d)(2),
or, before September 15, 2020, a
malfunction period as described in
§ 63.2850(e)(2). An operating month
may include time intervals
characterized by several types of
operating status. However, an operating
month must have at least one normal
operating period.
*
*
*
*
*
[FR Doc. 2020–04459 Filed 3–17–20; 8:45 am]
BILLING CODE 6560–50–P
E:\FR\FM\18MRR3.SGM
18MRR3
Agencies
[Federal Register Volume 85, Number 53 (Wednesday, March 18, 2020)]
[Rules and Regulations]
[Pages 15608-15636]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2020-04459]
[[Page 15607]]
Vol. 85
Wednesday,
No. 53
March 18, 2020
Part III
Environmental Protection Agency
-----------------------------------------------------------------------
40 CFR Part 63
National Emission Standards for Hazardous Air Pollutants: Solvent
Extraction for Vegetable Oil Production Residual Risk and Technology
Review; Final Rule
Federal Register / Vol. 85 , No. 53 / Wednesday, March 18, 2020 /
Rules and Regulations
[[Page 15608]]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 63
[EPA-HQ-OAR-2019-0208; FRL-10006-06-OAR]
RIN 2060-AU17
National Emission Standards for Hazardous Air Pollutants: Solvent
Extraction for Vegetable Oil Production Residual Risk and Technology
Review
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: This action finalizes the residual risk and technology review
(RTR) conducted for the Solvent Extraction for Vegetable Oil Production
source category regulated under national emission standards for
hazardous air pollutants (NESHAP). Based on the results of the U.S.
Environmental Protection Agency's (EPA's) risk review, the Agency is
finalizing the decision that risks due to emissions of air toxics from
this source category are acceptable and that the current NESHAP
provides an ample margin of safety to protect public health. Under the
technology review, the EPA is finalizing the decision that there are no
developments in practices, processes, or control technologies that
necessitate revision of the standards. Therefore, the EPA is finalizing
no revisions to the numerical emission limits based on the risk and
technology reviews. We are taking final action to correct and clarify
regulatory provisions related to emissions during periods of startup,
shutdown, and malfunction (SSM), including removing general exemptions
for periods of SSM, adding alternative work practice standards for
periods of initial startup for new or significantly modified sources,
and making other minor clarifications or corrections. The EPA is also
taking final action to add provisions for electronic reporting of
certain notifications and reports and performance test results; and
make other minor clarifications and corrections. These final amendments
will result in improved compliance and implementation of the rule.
DATES: This final rule is effective on March 18, 2020.
ADDRESSES: The EPA has established a docket for this action under
Docket ID No. EPA-HQ-OAR-2019-0208. All documents in the docket are
listed on the https://www.regulations.gov/ website. Although listed,
some information is not publicly available, e.g., Confidential Business
Information (CBI) or other information whose disclosure is restricted
by statute. Certain other material, such as copyrighted material, is
not placed on the internet and will be publicly available only in hard
copy form. Publicly available docket materials are available either
electronically through https://www.regulations.gov/, or in hard copy at
the EPA Docket Center, WJC West Building, Room Number 3334, 1301
Constitution Ave., NW, Washington, DC. The Public Reading Room hours of
operation are 8:30 a.m. to 4:30 p.m. Eastern Standard Time (EST),
Monday through Friday. The telephone number for the Public Reading Room
is (202) 566-1744, and the telephone number for the EPA Docket Center
is (202) 566-1742.
FOR FURTHER INFORMATION CONTACT: For questions about this final action,
contact Mr. Bill Schrock, Natural Resources Group, Sector Policies and
Programs Division (E143-03), Office of Air Quality Planning and
Standards, U.S. Environmental Protection Agency, Research Triangle
Park, North Carolina 27711; telephone number: (919) 541-5032; fax
number: (919) 541-0516; and email address: [email protected]. For
specific information regarding the risk modeling methodology, contact
Mr. Matthew Woody, Health and Environmental Impacts Division (C539-02),
Office of Air Quality Planning and Standards, U.S. Environmental
Protection Agency, Research Triangle Park, North Carolina 27711;
telephone number: (919) 541-1535; fax number: (919) 541-0840; and email
address: [email protected]. For information about the applicability
of the NESHAP to a particular entity, contact Ms. Maria Malave, Office
of Enforcement and Compliance Assurance, U.S. Environmental Protection
Agency, WJC South Building (Mail Code 2227A), 1200 Pennsylvania Avenue
NW, Washington, DC 20460; telephone number: (202) 564-7027; and email
address: [email protected].
SUPPLEMENTARY INFORMATION:
Preamble acronyms and abbreviations. We use multiple acronyms and
terms in this preamble. While this list may not be exhaustive, to ease
the reading of this preamble and for reference purposes, the EPA
defines the following terms and acronyms here:
CAA Clean Air Act
CBI Confidential Business Information
CDX Central Data Exchange
CEDRI Compliance and Emissions Data Reporting Interface
CFR Code of Federal Regulations
EPA Environmental Protection Agency
HAP hazardous air pollutant(s)
HI hazard index
HQ hazard quotient
ICR Information Collection Request
km kilometer
MACT maximum achievable control technology
MIR maximum individual risk
NAICS North American Industry Classification System
NESHAP national emission standards for hazardous air pollutants
NTTAA National Technology Transfer and Advancement Act
OMB Office of Management and Budget
PRA Paperwork Reduction Act
REL reference exposure level
RFA Regulatory Flexibility Act
RTR residual risk and technology review
SSM startup, shutdown, and malfunction
the Court United States Court of Appeals for the District of
Columbia Circuit
TOSHI target organ-specific hazard index
tpy tons per year
UMRA Unfunded Mandates Reform Act
VCS voluntary consensus standards
Background information. On June 27, 2019, the EPA proposed
revisions to the Solvent Extraction for Vegetable Oil Production NESHAP
in conjunction with our RTR for the Solvent Extraction for Vegetable
Oil Production source category (84 FR 30812). In this action, we are
finalizing decisions and revisions for the rule. We summarize some of
the more significant comments we timely received regarding the proposed
rule and provide our responses in this preamble. A summary of all other
public comments on the proposal and the EPA's responses to those
comments is available in the Summary of Public Comments and Responses
for the Risk and Technology Review for Solvent Extraction For Vegetable
Oil Production, in Docket ID No. EPA-HQ-OAR-2019-0208. A ``track
changes'' version of the regulatory language that incorporates the
changes in this action is available in the docket.
Organization of this document. The information in this preamble is
organized as follows:
I. General Information
A. Does this action apply to me?
B. Where can I get a copy of this document and other related
information?
C. Judicial Review and Administrative Reconsideration
II. Background
A. What is the statutory authority for this action?
B. What is the Solvent Extraction for Vegetable Oil Production
source category and how does the NESHAP regulate HAP emissions from
the source category?
C. What changes did we propose for the Solvent Extraction for
Vegetable Oil Production source category in our June 27, 2019, RTR
proposal?
III. What is included in this final rule?
A. What are the final rule amendments based on the risk review
for the Solvent
[[Page 15609]]
Extraction for Vegetable Oil Production source category?
B. What are the final rule amendments based on the technology
review for the Solvent Extraction for Vegetable Oil Production
source category?
C. What are the final rule amendments addressing emissions
during periods of SSM?
D. What other changes have been made to the NESHAP?
E. What are the effective and compliance dates of the standards?
IV. What is the rationale for our final decisions and amendments for
the Solvent Extraction for Vegetable Oil Production source category?
A. Residual Risk Review for the Solvent Extraction for Vegetable
Oil Production Source Category
B. Technology Review for the Solvent Extraction for Vegetable
Oil Production Source Category
C. SSM for the Solvent Extraction for Vegetable Oil Production
Source Category
D. Technical amendments to the MACT standards for the Solvent
Extraction for Vegetable Oil Production Source Category
V. Summary of Cost, Environmental, and Economic Impacts and
Additional Analyses Conducted
A. What are the affected sources?
B. What are the air quality impacts?
C. What are the cost impacts?
D. What are the economic impacts?
E. What are the benefits?
F. What analysis of environmental justice did we conduct?
G. What analysis of children's environmental health did we
conduct?
VI. Statutory and Executive Order Reviews
A. Executive Orders 12866: Regulatory Planning and Review and
Executive Order 13563: Improving Regulation and Regulatory Review
B. Executive Order 13771: Reducing Regulations and Controlling
Regulatory Costs
C. Paperwork Reduction Act (PRA)
D. Regulatory Flexibility Act (RFA)
E. Unfunded Mandates Reform Act (UMRA)
F. Executive Order 13132: Federalism
G. Executive Order 13175: Consultation and Coordination with
Indian Tribal Governments
H. Executive Order 13045: Protection of Children From
Environmental Health Risks and Safety Risks
I. Executive Order 13211: Actions Concerning Regulations That
Significantly Affect Energy Supply, Distribution, or Use
J. National Technology Transfer and Advancement Act (NTTAA)
K. Executive Order 12898: Federal Actions to Address
Environmental Justice in Minority Populations and Low-Income
Populations
L. Congressional Review Act (CRA)
I. General Information
A. Does this action apply to me?
Regulated entities. Categories and entities potentially regulated
by this action are shown in Table 1 of this preamble.
Table 1--NESHAP and Industrial Source Categories Affected By This Final
Action
------------------------------------------------------------------------
Source category NESHAP NAICS \a\ code
------------------------------------------------------------------------
Flour Milling................ 311211
Wet Corn Milling............. 311221
Fats and Oils Refining and 311225
Blending.
Other Animal Food Solvent Extraction 311119
Manufacturing. for Vegetable Oil
Production.
Soybean and Other Oilseed 311224
Processing.
Fats and Oils Refining and 311225
Blending.
------------------------------------------------------------------------
\a\ North American Industry Classification System.
Table 1 of this preamble is not intended to be exhaustive, but
rather to provide a guide for readers regarding entities likely to be
affected by the final action for the source category listed. To
determine whether your facility is affected, you should examine the
applicability criteria in the appropriate NESHAP. If you have any
questions regarding the applicability of any aspect of this NESHAP,
please contact the appropriate person listed in the preceding FOR
FURTHER INFORMATION CONTACT section of this preamble.
B. Where can I get a copy of this document and other related
information?
In addition to being available in the docket, an electronic copy of
this final action will also be available on the internet. Following
signature by the EPA Administrator, the EPA will post a copy of this
final action at: https://www.epa.gov/stationary-sources-air-pollution/solvent-extraction-vegetable-oil-production-national-emission.
Following publication in the Federal Register, the EPA will post the
Federal Register version and key technical documents at this same
website.
Additional information is available on the RTR website at https://www.epa.gov/stationary-sources-air-pollution/risk-and-technology-review-national-emissions-standards-hazardous. This information
includes an overview of the RTR program and links to project websites
for the RTR source categories.
C. Judicial Review and Administrative Reconsideration
Under Clean Air Act (CAA) section 307(b)(1), judicial review of
this final action is available only by filing a petition for review in
the United States Court of Appeals for the District of Columbia Circuit
(the Court) by May 18, 2020. 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 the requirements.
Section 307(d)(7)(B) of the CAA further provides that only an
objection to a rule or procedure which was raised with reasonable
specificity during the period for public comment (including any public
hearing) may be raised during judicial review. This section also
provides a mechanism for the EPA to reconsider the rule if the person
raising an objection can demonstrate to the Administrator 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 should submit a
Petition for Reconsideration to the Office of the Administrator, U.S.
EPA, Room 3000, WJC South Building, 1200 Pennsylvania Ave. NW,
Washington, DC 20460, with a copy to both the person(s) listed in the
preceding FOR FURTHER INFORMATION CONTACT section, and the Associate
General Counsel for the Air and Radiation Law Office, Office of General
Counsel (Mail Code 2344A), U.S. EPA, 1200 Pennsylvania Ave. NW,
Washington, DC 20460.
[[Page 15610]]
II. Background
A. What is the statutory authority for this action?
Section 112 of the CAA establishes a two-stage regulatory process
to address emissions of hazardous air pollutants (HAP) from stationary
sources. In the first stage, we must identify categories of sources
emitting one or more of the HAP listed in CAA section 112(b) and then
promulgate technology-based NESHAP for those sources. ``Major sources''
are those that emit, or have the potential to emit, any single HAP at a
rate of 10 tons per year (tpy) or more, or 25 tpy or more of any
combination of HAP. For major sources, these standards are commonly
referred to as maximum achievable control technology (MACT) standards
and must reflect the maximum degree of emission reductions of HAP
achievable (after considering cost, energy requirements, and non-air
quality health and environmental impacts). In developing MACT
standards, CAA section 112(d)(2) directs the EPA to consider the
application of measures, processes, methods, systems, or techniques,
including, but not limited to, those that reduce the volume of or
eliminate HAP emissions through process changes, substitution of
materials, or other modifications; enclose systems or processes to
eliminate emissions; collect, capture, or treat HAP when released from
a process, stack, storage, or fugitive emissions point; are design,
equipment, work practice, or operational standards; or any combination
of the above.
For these MACT standards, the statute specifies certain minimum
stringency requirements, which are referred to as MACT floor
requirements, and which may not be based on cost considerations (see
CAA section 112(d)(3)). For new sources, the MACT floor cannot be less
stringent than the emission control achieved in practice by the best-
controlled similar source. The MACT standards for existing sources can
be less stringent than floors for new sources, but they cannot be less
stringent than the average emission limitation achieved by the best-
performing 12 percent of existing sources in the category or
subcategory (or the best-performing five sources for categories or
subcategories with fewer than 30 sources). In developing MACT
standards, we must also consider control options that are more
stringent than the floor under CAA section 112(d)(2). We may establish
standards more stringent than the floor, based on the consideration of
the cost of achieving the emissions reductions, any non-air quality
health and environmental impacts, and energy requirements.
In the second stage of the regulatory process, the CAA requires the
EPA to undertake two different analyses, which we refer to as the
technology review and the residual risk review. Under the technology
review, we must review the technology-based standards and revise them
``as necessary (taking into account developments in practices,
processes, and control technologies)'' no less frequently than every 8
years, pursuant to CAA section 112(d)(6). Under the residual risk
review, we must evaluate the risk to public health remaining after
application of the technology-based standards and revise the standards,
if necessary, to provide an ample margin of safety to protect public
health or to prevent, taking into consideration costs, energy, safety,
and other relevant factors, an adverse environmental effect. The
residual risk review is required within 8 years after promulgation of
the technology-based standards, pursuant to CAA section 112(f). In
conducting the residual risk review, if the EPA determines that the
current standards provide an ample margin of safety to protect public
health, it is not necessary to revise the MACT standards pursuant to
CAA section 112(f).\1\ For more information on the statutory authority
for this rule, see 84 FR 30812, June 27, 2019.
---------------------------------------------------------------------------
\1\ The Court has affirmed this approach of implementing CAA
section 112(f)(2)(A): NRDC v. EPA, 529 F.3d 1077, 1083 (DC Cir.
2008) (``If EPA determines that the existing technology-based
standards provide an `ample margin of safety,' then the Agency is
free to readopt those standards during the residual risk
rulemaking.'').
---------------------------------------------------------------------------
B. What is the Solvent Extraction for Vegetable Oil Production source
category and how does the NESHAP regulate HAP emissions from the source
category?
The EPA promulgated the Solvent Extraction for Vegetable Oil
Production NESHAP on April 12, 2001 (66 FR 19006). The standards are
codified at 40 CFR part 63, subpart GGGG. As promulgated in 2001 and
further amended on April 5, 2002 (67 FR 16317), and September 1, 2004
(69 FR 53338), the NESHAP regulates HAP emissions from solvent
extraction for vegetable oil production processes at a facility that is
a major source of HAP emissions. The affected source is each vegetable
oil production process. A vegetable oil production process means the
equipment comprising a continuous process for producing crude vegetable
oil and meal products, including specialty soybean products, in which
oil is removed from oilseeds listed in Table 1 of 40 CFR 63.2840
through direct contact with an organic solvent. Process equipment
typically includes the following components: oilseed preparation
operations (including conditioning, drying, dehulling, and cracking),
solvent extractors, desolventizer-toasters, meal dryers, meal coolers,
meal conveyor systems, oil distillation units, solvent evaporators and
condensers, solvent recovery system (also referred to as a mineral oil
absorption system), vessels storing solvent-laden materials, and crude
meal packaging and storage vessels. A vegetable oil production process
does not include vegetable oil refining operations (including
operations such as bleaching, hydrogenation, and deodorizing) and
operations that engage in additional chemical treatment of crude
soybean meals produced in specialty desolventizer units (including
operations such as soybean isolate production). The source category
covered by this MACT standard currently includes 89 facilities.
The primary HAP emitted from vegetable oil production processes is
n-hexane. The EPA does not consider n-hexane classifiable as a human
carcinogen. However, short-term exposure to n-hexane can cause
reactions such as irritation, dizziness, headaches, and nausea. Long-
term exposure can cause permanent nerve damage.
The current NESHAP controls facility-wide n-hexane emissions by
setting emission limitations based on the number of gallons of HAP lost
per ton of oilseeds processed, expressed as oilseed solvent loss
ratios. Facilities demonstrate compliance by calculating a compliance
ratio comparing the actual HAP loss to the allowable HAP loss for the
previous 12 operating months. Allowable HAP loss is based on the
oilseed solvent loss ratios provided in Table 1 of 40 CFR 63.2840 of
the rule for new and existing sources. Compliance is demonstrated when
the facility's calculated compliance ratio is less than or equal to
1.00 (i.e., the actual HAP loss is no greater than the calculated
allowable HAP loss). Determination of compliance with the requirements
of the Solvent Extraction for Vegetable Oil Production NESHAP requires
the facility to keep records of the amount of n-hexane purchased, used,
and recovered from the oilseed extraction process, the amount of
oilseed processed, and the volume fraction of each HAP exceeding 1
percent in the extraction solvent used. Facilities may also adjust
their solvent loss to account for cases where solvent is routed through
a closed vent system
[[Page 15611]]
to a control device that is used to reduce emissions to meet the
standard.
C. What changes did we propose for the Solvent Extraction for Vegetable
Oil Production source category in our June 27, 2019, RTR proposal?
On June 27, 2019, the EPA published a proposed rule in the Federal
Register for the Solvent Extraction for Vegetable Oil Production
NESHAP, 40 CFR part 63, subpart GGGG, that took into consideration the
RTR analyses. In the proposed rule, we proposed that the risks from the
source category are acceptable and the current standards provide an
ample margin of safety to protect public health. In addition, pursuant
to the technology review for the Solvent Extraction for Vegetable Oil
Production source category, we proposed no revisions to the current
standards based on these analyses.
We proposed revisions to the SSM provisions of the standards to
ensure that they are consistent with the Court decision in Sierra Club
v. EPA, 551 F. 3d 1019 (D.C. Cir. 2008). Specifically, the Court
vacated the SSM exemption contained in 40 CFR 63.6(f)(1) and 40 CFR
63.6(h)(1), holding that under section 302(k) of the CAA, emissions
standards or limitations must be continuous in nature and that the SSM
exemption violates the CAA's requirement that some CAA section 112
standards apply continuously. We therefore proposed that the standards
would apply at all times, including during startups, shutdowns, and
malfunctions (see 40 CFR 63.2840(a) and Table 1 to 40 CFR 63.2870
(General Provisions Applicability Table). Additionally, we proposed to
remove requirements that allowed sources to previously designate a
source operating status period as a ``malfunction period'' and exclude
data collected during the ``malfunction period'' when determining
compliance with the emission standards.\2\ Under the proposed rule,
sources that continue to operate must instead meet the emission
standard requirements for either a normal operating period or the work
practice standards for an initial startup period (if applicable) in 40
CFR 63.2850 and Table 1 of 40 CFR 63.2850. In proposing the revised
standards, the EPA considered whether to set separate standards for
startup and shutdown periods, but only found that separate standards
were necessary for initial startup periods for new or significantly
modified sources. For periods of initial startup following new
construction or significant modification, we proposed work practice
standards and a requirement to establish and follow site-specific
operating ranges for temperature and vacuum for the desolventizing and
oil distillation units associated with solvent recovery, as well as
associated recordkeeping and reporting requirements (e.g., initial
startup report) for these periods.
---------------------------------------------------------------------------
\2\ The 2001 NESHAP allowed for facilities to determine
compliance based on the distinct categorized operating status of the
facility (normal operating, nonoperating, initial startup,
malfunction, or exempt) during a compliance period, as defined in
Table 1 of 40 CFR 63.2853. Existing and new sources operating during
a malfunction period could either meet the compliance requirements
for normal operation periods in 40 CFR 63.2850 and Table 1 of 40 CFR
63.2850 or the requirements for malfunction periods subject to 40
CFR 63.2850(e)(2) and Table 1 of 40 CFR 63.2850 (for which no limits
or work practices applied). Sources operating during a malfunction
period were not required to determine compliance using data recorded
for the malfunction period. We proposed to remove the option for
facilities to categorize the operating period as a malfunction
period and to remove the option to meet the requirements for
malfunction periods subject to 40 CFR 63.2850(e)(2) and Table 1 of
40 CFR 63.2850, such that the standards apply at all times. Sources
that continue to operate during a malfunction must continue to meet
the general duty requirements at 40 CFR 63.2840(g). The term
``malfunction period'' is retained in the rule only as it applies to
facilities prior to September 15, 2020.
---------------------------------------------------------------------------
We proposed to require electronic reporting of initial
notifications, initial startup reports, annual compliance
certifications, deviation reports, and performance test reports through
the EPA's Central Data Exchange (CDX) using the Compliance and
Emissions Data Reporting Interface (CEDRI). We also proposed minor
clarifications and corrections to five definitions (i.e., ``Compliance
ratio,'' ``Nonoperating period,'' ``Normal operating period,''
``Operating month,'' and ``Hazardous air pollutant (HAP)'') and to 40
CFR 63.2840(a)(1) and (b)(1), 40 CFR 63.2853(a)(2), 40 CFR
63.2855(a)(3), and Table 1 of 40 CFR 63.2850. Refer to section IV.D of
the June 27, 2019, proposal preamble for further discussion of these
proposed amendments and the EPA's rationale for these changes (84 FR
60825).
III. What is included in this final rule?
This action finalizes the EPA's determinations pursuant to the RTR
provisions of CAA section 112 for the Solvent Extraction for Vegetable
Oil Production source category. This action also finalizes other
changes to the NESHAP, including revisions to the SSM provisions of the
MACT rule in order to ensure that they are consistent with the Court
decision in Sierra Club v. EPA, 551 F. 3d 1019 (D.C. Cir. 2008),
provisions for electronic reporting of initial notifications, initial
startup reports, annual compliance certifications, deviation reports,
and performance test reports; and other minor editorial and technical
changes. This action reflects several changes to the proposed rule in
consideration of comments received during the public comment period as
described in section IV of this preamble.
A. What are the final rule amendments based on the risk review for the
Solvent Extraction for Vegetable Oil Production source category?
This section describes the final risk determination for the Solvent
Extraction for Vegetable Oil Production NESHAP being promulgated
pursuant to CAA section 112(f). The EPA proposed no changes to the
Solvent Extraction for Vegetable Oil Production NESHAP based on the
risk review conducted pursuant to CAA section 112(f). In this action,
we are finalizing our proposed determination that risks from this
source category are acceptable, and that the standards provide an ample
margin of safety to protect public health and prevent an adverse
environmental effect. Section IV.A.3 of this preamble provides a
summary of key comments we received regarding the risk review and our
responses to those comments.
B. What are the final rule amendments based on the technology review
for the Solvent Extraction for Vegetable Oil Production source
category?
The EPA is finalizing the technology review as proposed. We
determined that there are no developments in practices, processes, and
control technologies that warrant revisions to the MACT standards for
this source category. Therefore, we are not finalizing revisions to the
MACT standards under CAA section 112(d)(6).
C. What are the final rule amendments addressing emissions during
periods of SSM?
We are finalizing the proposed amendments to the Solvent Extraction
for Vegetable Oil Production NESHAP to remove and revise provisions
related to SSM. As detailed in section IV.D of the proposal preamble
(84 FR 30825), the final amendments to the Solvent Extraction for
Vegetable Oil Production NESHAP require that the standards apply at all
times (see 40 CFR 63.2840(a) and Table 1 to 40 CFR 63.2870 (General
Provisions applicability table), consistent with the Court decision in
Sierra Club v. EPA, 551 F. 3d 1019 (D.C. Cir. 2008).
We are finalizing that the emission standards for normal operation
apply at all times, except for periods of initial
[[Page 15612]]
startup for new and significantly modified sources, as described below
in this section and in section IV.C of this preamble. For periods of
initial startup for new or significantly modified sources, we are
finalizing work practice standards, including operation of the mineral
oil absorption system and solvent condensers at all times during the
initial startup period, and a requirement to establish and follow site-
specific operating ranges for temperature and vacuum for the
desolventizing and oil distillation units associated with solvent
recovery, as well as associated recordkeeping and reporting
requirements (e.g., initial startup report) for these periods.
Facilities will continue to have the option to meet the requirements
for normal operating periods in Table 1 of 40 CFR 63.2850. The EPA is
also finalizing the definition of ``initial startup period'' and the
requirements of 40 CFR 62.2850(c)(2) and (d)(2) to clarify that the end
of the initial startup period occurs when the plant meets and maintains
steady-state operations. Steady-state is defined as operating at or
above 90 percent of the extractor nominal design production rate or at
or above 90 percent of the production rate in the plant's permit for 15
consecutive days. Any initial startup period may not exceed 6 calendar
months after startup for new or reconstructed sources or 3 calendar
months after startup for modified sources.
As discussed in section IV.D of the June 27, 2019, proposal
preamble, the EPA interprets CAA section 112 as not requiring emissions
that occur during periods of malfunction to be factored into
development of CAA section 112 standards, although the EPA has the
discretion to set standards for malfunctions where feasible. We noted
that our interpretation regarding CAA section 112 not requiring
emissions that occur during periods of malfunction to be factored into
development of CAA section 112 standards has been upheld as reasonable
by the Court in U.S. Sugar Corp. v. EPA, 830 F.3d 579, 606-610 (2016).
The EPA further explained that, ``EPA will consider whether
circumstances warrant setting standards for a particular type of
malfunction and, if so, whether the EPA has sufficient information to
identify the relevant best performing sources and establish a standard
for such malfunctions'' (84 FR 30827).
While we requested comment on work practice standards during
periods of malfunction, and received some information in support of
such standards, we did not receive sufficient information on which to
base a malfunction standard. As further explained at proposal, ``[i]n
the event that a source fails to comply with the applicable CAA section
112(d) standards as a result of a malfunction event, the EPA would
determine an appropriate response based on, among other things, the
good faith efforts of the source to minimize emissions during
malfunction periods, including preventive and corrective actions, as
well as root cause analyses to ascertain and rectify excess emissions.
The EPA would also consider whether the source's failure to comply with
the CAA section 112(d) standard was, in fact, sudden, infrequent, not
reasonably preventable and was not instead caused in part by poor
maintenance or careless operation. 40 CFR 63.2 (definition of
malfunction). If the EPA determines in a particular case that an
enforcement action against a source for violation of an emission
standard is warranted, the source can raise any and all defenses in
that enforcement action and the Federal district court will determine
what, if any, relief is appropriate. The same is true for citizen
enforcement actions. Similarly, the presiding officer in an
administrative proceeding can consider any defense raised and determine
whether administrative penalties are appropriate'' (84 FR 30828).
For these reasons, we are not setting separate standards for
periods of malfunction. Under the final rule, sources that experience
an unscheduled shutdown as a result of a malfunction, continue to
operate during a malfunction (including the period reasonably necessary
to correct the malfunction), or start up after a shutdown resulting
from a malfunction must instead meet the emission standard requirements
for either a normal operating period or the work practice standards for
an initial startup period (if a new or significantly modified source)
in 40 CFR 63.2850 and Table 1 of 40 CFR 63.2850. Although we did not
propose and are not finalizing work practice standards for periods of
malfunction, we are finalizing revisions to deviation reporting to
account for one-time malfunction events in which the potential solvent
loss could result in a deviation for one or more consecutive monthly
compliance ratio determinations. Specifically, we have revised the
final rule to include a requirement that facilities flag and provide an
explanation for any deviation from the compliance ratio for which a
deviation report is being submitted for more than one consecutive month
(i.e., include a reference to the original date and reporting of the
deviation). Although a facility would need to retain records of any
deviation and the corrective action(s) performed, no additional
corrective action would be required at the time the 12-month compliance
ratio is officially exceeded in subsequent months if the facility
demonstrates the exceedance is from a prior malfunction that has been
corrected.
As is explained in more detail below, we are finalizing revisions
related to requirements that apply during periods of SSM. We eliminated
or revised certain recordkeeping and reporting requirements related to
the eliminated SSM exemption. The EPA also made changes to the rule to
remove or modify inappropriate, unnecessary, or redundant language in
the absence of the SSM exemption. Refer to sections III.C.1 through
III.C.6 of this preamble for a detailed discussion of the final
amendments.
1. 40 CFR 63.2840 General Duty
We are finalizing as proposed revisions to the General Provisions
applicability table (Table 1 to 40 CFR 63.2870) entry for 40 CFR
63.6(e)(1)(i) by changing the ``Yes'' in column 4 to a ``No.'' The EPA
is instead adding general duty regulatory text at 40 CFR 63.2840(g) to
reflect the general duty to minimize emissions while eliminating the
reference to periods covered by an SSM exemption. The general duty to
minimize emissions continues to apply during periods of malfunction and
sources must still address malfunctions expeditiously in order to
maintain any affected source, including associated air pollution
control equipment and monitoring equipment, and minimize emissions. The
EPA is also revising the General Provisions applicability table (Table
1 to 40 CFR 63.2870) entry for 40 CFR 63.6(e)(1)(ii) by changing the
``Yes'' in column 4 to a ``No'' to remove requirements that are not
necessary with the elimination of the SSM exemption or are redundant
with the general duty requirement being added at 40 CFR 63.2840(g).
2. SSM Plan
As proposed, the EPA is revising the General Provisions
applicability table (Table 1 to 40 CFR 63.2870) entries for 40 CFR
63.6(e)(3)(i) through (e)(3)(ii), 40 CFR 63.6(e)(3)(v) through (vii),
and 40 CFR 63.6(e)(3)(viii) and (ix) by changing the ``Yes'' in column
4 to a ``No.'' The EPA is also revising 40 CFR 63.2852, which cross-
references the requirements of 40 CFR 63.6(e)(3). The final amendments
remove requirements related to the SSM plan.
[[Page 15613]]
3. Compliance With Standards
The EPA is revising the General Provisions applicability table
(Table 1 to 40 CFR 63.2870) entry for 40 CFR 63.6(f)(1) by revising the
text in column 4 and removing the text in column 5 to clarify that the
SSM exemption previously applied but will not apply going forward.
4. 40 CFR 63.2853 Performance Testing
We are also finalizing a revision to the performance testing
requirements. The EPA is revising the General Provisions applicability
table (Table 1 to 40 CFR 63.2870) entry for 40 CFR 63.7(e)(1) by
changing the ``Yes'' in column 4 to a ``No,'' and adding a revised
performance testing requirement at 40 CFR 63.2853(a)(5)(i)(A). The
final performance testing provisions prohibit performance testing for
purposes of demonstrating compliance during startup, shutdown, or
malfunction because these conditions are not representative of normal
operating periods. The final rule also requires that operators maintain
records to document that operating conditions during the test represent
normal operations.
5. 40 CFR 63.2862 Recordkeeping
The EPA is revising the General Provisions applicability table
(Table 1 to 40 CFR 63.2870) entry for 40 CFR 63.10(b)(2)(i) by changing
the ``Yes'' in column 4 to a ``No,'' and is adding recordkeeping
requirements to 40 CFR 63.2862(f). The final revisions require owners
or operators of sources subject to a work practice standard during
initial startup times to report a description and dates of the initial
startup period, the reason it qualifies as an initial startup period,
an estimate of the solvent loss in gallons for the duration of the
initial startup, and the nominal design rate and operating rate of the
extractor or the permitted and actual production rates for the duration
of the initial startup period. The final revisions also require
facilities to record information including the measured temperature and
pressure for desolventizing and oil distillation units; an indication
that the mineral oil absorption system was operating at all times; and
(3) an indication that the solvent condensers were operating at all
times.
The EPA is revising the General Provisions applicability table
(Table 1 to 40 CFR 63.2870) entry for 40 CFR 63.10(b)(2)(ii) by
changing the ``Yes'' in column 4 to a ``No.'' The final rule includes
recordkeeping requirements for malfunctions in 40 CFR 63.2862(g),
including any ``failure to meet an applicable standard'' (including any
deviation from the emissions standards of 40 CFR 63.2840 or the work
practice standards for periods of initial startup). Source owners or
operators must record the date and duration of the ``failure.'' We have
revised the final rule requirements from proposal to clarify how to
designate the date a deviation occurred and the duration of the
deviation. For deviations from the compliance ratio, the date of the
deviation is the date the compliance ratio determination is made, and
the duration of the deviation is the length of time taken to address
the cause of the deviation (including the duration of any malfunction)
and to return the affected unit(s) to its normal or usual manner of
operation. For deviations from the work practice standard during the
initial startup period, the date of the deviation is the date when the
facility fails to comply with any of the work practice standards in 40
CFR 63.2840(h), and the duration of the deviation is the length of time
taken to return to the work practice standards. We have also removed
the requirement to record and report the time of the deviation as
described in section IV.C of this preamble.
The EPA is adding to 40 CFR 63.2862(g) a requirement that source
owners or operators keep records that include a statement of the cause
of each deviation (including unknown cause, if applicable), a list of
the affected source or equipment and actions taken to minimize
emissions, an estimate of the quantity of each regulated pollutant
emitted over the standard when the standard is not met, and a
description of the method used to estimate the emissions.
The EPA is revising the General Provisions applicability table
(Table 1 to 40 CFR 63.2870) entry for 40 CFR 63.10(b)(2)(iv) and 40 CFR
63.10(b)(2)(v) by changing the ``Yes'' in column 4 to a ``No'' to
remove requirements related to the SSM plan. The final rule includes a
requirement to record actions to minimize emissions and record
corrective actions in 40 CFR 63.2862(g).
6. 40 CFR 63.2861 Reporting
To replace the SSM reporting requirements, the EPA is eliminating
the periodic SSM reports in 40 CFR 63.2861(c), which were required to
be submitted at the end of each calendar month of an initial startup
period or malfunction period. The EPA is also removing the requirement
in 40 CFR 63.2861(d) to submit an immediate report for SSM when a
source failed to meet an applicable standard but did not follow the SSM
plan. The EPA is instead requiring that existing or new source owners
or operators that fail to meet the applicable emission standards
(including sources that experience a malfunction) or the work practice
standards for initial startup periods at any time must report the
information concerning such events in the deviation report, including
the number, date, duration, and the cause of such events (including
unknown cause, if applicable), a list of the affected source or
equipment, an estimate of the quantity of HAP emitted over the emission
requirements of 40 CFR 63.2840, and a description of the method used to
estimate the emissions. For sources operating under an initial startup
period, the EPA is also finalizing a provision that source owners or
operators that fail to meet the work practice standard must include a
description of the deviation and include the records for the initial
startup period in 40 CFR 63.2862(f).
Finally, the EPA is finalizing that source owners or operators that
choose to operate under an initial startup period according to 40 CFR
63.2850(c)(2) or (d)(2) must also provide an initial startup report,
including a compliance certification indicating whether the source was
in compliance with the work practice standard of 40 CFR 63.2840(h). The
initial report must be submitted within 30 days of the end of the
initial startup period.
The legal rationale and detailed changes for SSM periods that we
are finalizing here are set forth in the proposed rule (see 84 FR
30825). Section IV.C of this preamble provides a summary of key
comments we received on the SSM provisions and our responses.
D. What other changes have been made to the NESHAP?
This rule also finalizes, as proposed, revisions to several other
NESHAP requirements. To increase the ease and efficiency of data
submittal and data accessibility, we are finalizing a requirement that
owners and operators of facilities in the Solvent Extraction for
Vegetable Oil Production source category submit electronic copies of
initial notifications, initial startup reports, annual compliance
certifications, deviation reports, and performance test reports through
the EPA's CDX using the CEDRI. The initial notifications, initial
startup reports, annual compliance certifications, deviation reports,
and performance test reports are required to be submitted according to
the deadlines specified in 40 CFR 63.2861. We also are finalizing, as
proposed, provisions that allow
[[Page 15614]]
facility operators the ability to seek extensions for submitting
electronic reports for circumstances beyond the control of the
facility, i.e., for a possible outage in the CDX or CEDRI or for a
force majeure event in the time just prior to a report's due date, as
well as the process to assert such a claim.
The EPA is finalizing several minor technical editorial changes to
the rule. The EPA is finalizing several definitions in 40 CFR 63.2872
to harmonize with the removal of the SSM requirements and to clarify
existing provisions. The definitions of ``Compliance ratio,''
``Nonoperating period,'' ``Normal operating period,'' and ``Operating
month'' are revised in the final rule to clarify that we have removed
malfunction periods as a distinct source operating status during which
no limits or work practices applied. The definition of ``Normal
operating period'' is also revised to clarify that this definition also
applies to ``normal operation.''
The EPA is revising the definition of ``Hazardous Air Pollutant
(HAP)'' as proposed to remove the reference to the date of April 12,
2001. Finally, the EPA is adding a definition for ``Nonoperating
month'' as proposed.
The EPA is finalizing minor revisions to 40 CFR 63.2840(a)(1) and
(b)(1), 40 CFR 63.2853(a)(2), and 40 CFR 63.2855(a)(3) to remove text
that is redundant with the definition of ``Operating month'' in 40 CFR
63.2872. Finally, the EPA is revising Table 1 of 40 CFR 63.2850 to
correct a typographical error in row ``(a)'' for malfunction periods.
The legal rationale and detailed changes for these revisions are
set forth in the proposed rule (see 84 FR 30830).
E. What are the effective and compliance dates of the standards?
The revisions to the MACT standards being promulgated in this
action are effective on March 18, 2020.
Existing affected sources and affected sources that commenced
construction or reconstruction on or before June 27, 2019, must comply
with the amendments no later than 180 days after March 18, 2020.
Affected sources that commence construction or reconstruction after
June 27, 2019 must comply with all requirements of 40 CFR part 63,
subpart GGGG, no later than the effective date of the final rule or
upon startup, whichever is later. The EPA is finalizing three changes
that would affect ongoing compliance requirements for the Solvent
Extraction for Vegetable Oil Production NESHAP. First, for all sources,
we are finalizing a requirement that initial notifications, initial
startup reports, annual compliance certifications, deviation reports,
and performance test results be electronically submitted. Next, the EPA
is finalizing changing the requirements for SSM by removing the
exemption from the requirements to meet the standard during SSM
periods. For new or significantly modified sources, we are finalizing
an option for facilities to follow new work practice standards for
periods of initial startup. From our assessment of the timeframe needed
for implementing the entirety of the revised requirements, the EPA
proposed a period of 180 days to be the most expeditious compliance
period practicable for existing affected sources or affected sources
that commenced construction or reconstruction on or before June 27,
2019. No comments on the compliance period were received during the
public comment period and the 180-day period is being finalized as
proposed. Thus, the compliance date of the final amendments for all
existing sources and new sources that commenced construction or
reconstruction on or before June 27, 2019, will be September 15, 2020.
The compliance date of the final amendments for new sources that
commence construction or reconstruction after June 27, 2019, will be
March 18, 2020.
IV. What is the rationale for our final decisions and amendments for
the Solvent Extraction for Vegetable Oil Production source category?
For each issue, this section provides a description of what we
proposed and what we are finalizing for the issue, the EPA's rationale
for the final decisions and amendments, and a summary of key comments
and responses. For all comments not discussed in this preamble, comment
summaries, and the EPA's responses can be found in the comment summary
and response document, Summary of Public Comments and Responses for the
Risk and Technology Review for Solvent Extraction For Vegetable Oil
Production, which is available in the docket for this rulemaking.
A. Residual Risk Review for the Solvent Extraction for Vegetable Oil
Production Source Category
1. What did we propose pursuant to CAA section 112(f) for the Solvent
Extraction for Vegetable Oil Production source category?
Pursuant to CAA section 112(f), the EPA conducted a residual risk
review and presented the results of this review, along with our
proposed decisions regarding risk acceptability and ample margin of
safety, in the June 27, 2019, proposed rule for 40 CFR part 63, subpart
GGGG (84 FR 30812). The results of the risk assessment for the proposal
are presented briefly in Table 2 of this preamble. More detail may be
found in the residual risk technical support document, Residual Risk
Assessment for the Solvent Extraction for Vegetable Oil Production
Source Category in Support of the 2019 Risk and Technology Review Final
Rule, which is available in the docket for this rulemaking.
Table 2--Solvent Extraction for Vegetable Oil Production Inhalation Proposed Risk Assessment Results
----------------------------------------------------------------------------------------------------------------
Estimated
Maximum population at Estimated
individual increased annual cancer Maximum chronic Maximum
Number of facilities \1\ cancer risk risk of cancer incidence noncancer TOSHI screening acute
(in 1 million) >=1-in-1 (cases per \3\ noncancer HQ
\2\ million year)
----------------------------------------------------------------------------------------------------------------
88.......................... Based on Actual Emissions Level
-----------------------------------------------------------------------------------
<1 0 0.00005 0.7 (n-hexane).. HQREL = 0.7
(acrolein)
-----------------------------------------------------------------------------------
Based on Allowable Emissions Level
-----------------------------------------------------------------------------------
<1 0 0.0002 2 (n-hexane).... N/A
----------------------------------------------------------------------------------------------------------------
\1\ Number of facilities evaluated in the risk analysis.
\2\ Maximum individual excess lifetime cancer risk due to HAP emissions from the source category.
\3\ The target organ with the highest target organ-specific hazard index (TOSHI) for the Solvent Extraction for
Vegetable Oil Production source category is the nervous system (neurocognitive and neurobehavioral effects).
[[Page 15615]]
The results of the proposed inhalation risk assessment using actual
emissions data, as shown in Table 2 of this preamble, indicate the
estimated cancer maximum individual risk (MIR) is less than 1-in-1
million. At proposal, the total estimated cancer incidence from this
source category was estimated to be 0.00005 excess cancer cases per
year, or 1 case every 20,000 years and for allowable emissions was
0.0002 excess cancer cases per year, or 1 case every 5,000 years driven
by emissions of acetaldehyde and formaldehyde. At proposal, the maximum
modeled chronic noncancer TOSHI for the source category based on actual
emissions was estimated to be 0.7 and, for allowable emissions, was
estimated to be 2 due to emissions of n-hexane. Approximately 13 people
were estimated to have exposures resulting in a TOSHI greater than 1 if
exposed to allowable emissions from this source category.
As shown in Table 2 of this preamble, the worst-case acute hazard
quotient (HQ) (based on the reference exposure level (REL)) at proposal
was less than 1 (0.7 based on the REL for acrolein). This value is the
highest HQ that is outside facility boundaries. The multipathway risk
screening assessment did not identify emissions of any HAP known to be
persistent and bio-accumulative in the environment; therefore, no
further evaluation of multipathway risk was conducted for this source
category. Further, because we did not identify environmental HAP
emissions, no quantitative environmental risk screening was conducted
for this source category.
We conducted an assessment of facility-wide risks. The maximum
lifetime individual cancer risk posed by the 88 facilities, based on
facility-wide emissions at proposal, was 5-in-1 million with cadmium,
nickel, arsenic, chromium (VI), and formaldehyde emissions from
facility-wide external combustion boilers driving the risk. The maximum
chronic noncancer TOSHI posed by facility-wide emissions was estimated
to be 0.7 (for the nervous system) driven by source category n-hexane
emissions.
We weighed all health risk factors, including those shown in Table
2 of this preamble, in our risk acceptability determination and
proposed that the risks from the Solvent Extraction for Vegetable Oil
Production source category are acceptable (section IV.C.1 of proposal
preamble, 84 FR 30812, June 27, 2019).
We then considered whether the existing MACT standards for this
source category provide an ample margin of safety to protect public
health and whether, taking into consideration costs, energy, safety,
and other relevant factors, standards are required to prevent an
adverse environmental effect. In considering whether standards are
required to provide an ample margin of safety to protect public health,
we considered the same risk factors that we considered for our
acceptability determination and also considered the costs,
technological feasibility, and other relevant factors related to
emissions control options that might reduce risk associated with
emissions from the source category. We proposed that the current
standards provide an ample margin of safety to protect public health
and revision of the standards for the Solvent Extraction for Vegetable
Oil Production source category are not required to provide an ample
margin of safety to protect public health. We also proposed that it is
not necessary to set a more stringent standard to prevent, taking into
consideration costs, energy, safety, and other relevant factors, an
adverse environmental effect (see section IV.B of proposal preamble, 84
FR 30812, June 27, 2019.)
2. How did the risk review change for the Solvent Extraction For
Vegetable Oil Production source category?
We have not changed any aspect of the risk assessment since the
June 27, 2019, RTR proposal for the Solvent Extraction for Vegetable
Oil Production source category. We received several comments indicating
that the risk assessment (1) Improperly included emissions of
acetaldehyde that are not associated with the Solvent Extraction for
Vegetable Oil Production source category, but are emitted from other
facility processes; (2) overestimated actual emissions for certain
facilities where the EPA assumed that reported volatile organic
compound (VOC) emissions were n-hexane; and (3) overestimated allowable
emissions for the source category based on the assumptions used to
develop the MACT allowable-to-actual emissions multiplier.
As discussed in section IV.A.3 of this preamble, the inputs and
assumptions in the risk assessment at proposal are likely to
overestimate the risks from the Solvent Extraction for Vegetable Oil
Production source category. However, the risks as modeled at proposal
indicate that both the actual and allowable inhalation cancer risks to
the individual most exposed are less than 1-in-1 million, well below
the presumptive limit of acceptability of 100-in-1 million. The maximum
chronic noncancer TOSHI due to inhalation exposures is less than 1 for
actual emissions, and 2 for MACT-allowable emissions with an estimated
13 people exposed to a TOSHI greater than 1. Although for MACT-
allowable emissions, the maximum chronic noncancer TOSHI due to
inhalation exposures is 2, we note that due to the inherent health
protective nature of our risk assessment methods and the uncertainties
in this assessment (i.e., the emissions dataset, dispersion modeling,
and exposure estimates), our risk estimates are conservative. For
example, risk estimates for allowable emissions were based on scaled-up
actual emissions. At the first facility with a TOSHI value greater than
1, allowable emissions are based on permit data. At the other facility,
allowable emissions are based on an allowable multiplier applied to
actual emissions.
Additionally, the results of the acute screening analysis showed
that acute risks were below a level of concern. Because the risk
assessment already shows risks from the source category are acceptable
and that the existing standards provide an ample margin of safety to
protect public health, revision of the risk assessment to address the
comments that our emission estimates were too high would not change the
EPA's finding that the risks from the Solvent Extraction for Vegetable
Oil Production source category are acceptable.
3. What key comments did we receive on the risk review, and what are
our responses?
We received comments in support of and opposed to our proposed risk
assessment and determination that no revisions to the standards are
warranted under CAA section 112(f)(2) for the Solvent Extraction for
Vegetable Oil Production source category. Generally, the comments that
were not supportive of the acceptability and ample margin of safety
determinations suggested changes to the underlying risk assessment
methodology. The suggested changes to the EPA's risk assessment
methodology included that the EPA should lower its presumptive limit of
acceptability for cancer risks to below 100-in-1 million, include
emissions outside of the source categories in question in the risk
assessment, and assume that pollutants with noncancer health effects
have no safe level of exposure. Other commenters asserted that the
methodology for developing modeling inputs overestimated the actual or
allowable emissions of certain pollutants from specific facilities, and
subsequently overstated the risks from the source category. We
evaluated all comments and determined that no
[[Page 15616]]
changes regarding our risk review were needed. These comments and our
specific responses can be found below and in the comment summary and
response document titled Summary of Public Comments and Responses for
the Risk and Technology Review for Solvent Extraction for Vegetable Oil
Production, which is available in the docket for this action.
Comment: One commenter stated that the acetaldehyde emissions that
were modeled for the ADM-Clinton facility were not associated with the
vegetable oil process and should not have been included in the source
category modeling file. The commenter stated that the EPA should
correct the risk assessment by removing acetaldehyde for the ADM-
Clinton facility.
Response: As noted at proposal, we included acetaldehyde emissions
in the modeling file for the source category with the understanding
that their inclusion in the assessment would result in a conservative
estimate of risk. We acknowledge that a reassessment of risk that
excludes acetaldehyde emissions from the facility would result in lower
facility emissions, and potentially lower the source category risks
associated with acetaldehyde. Therefore, because revising the
assessment by removing acetaldehyde emissions from the source category
modeling file would not change the outcome of our risk determination,
we are not undertaking further analysis. We note that the acetaldehyde
emissions would continue to be considered as part of the facility-wide
risk assessment (see 84 FR 30824) and whole facility risks.
Comment: One commenter stated that the EPA overestimated actual
emissions for nine facilities where the EPA assumed that 100 percent of
the reported VOC emissions were emitted as n-hexane. The commenter
stated that although the EPA did not identify the nine facilities, the
commenter's review indicated that actual emissions in the modeling file
for several sources significantly exceeded the actual 2014 emissions of
n-hexane. The commenter stated that the EPA should identify the extent
to which the reported HI (0.7) may be affected by this assumption. The
commenter also stated that the EPA overestimated the allowable-to-
actual ratio used to estimate allowable emissions for multiple
facilities. The commenter asserted that although the EPA did not
identify the facilities that were used to estimate an allowable-to-
actual ratio, they believe, based on a review of the data, that the EPA
overestimated the allowable-to-actual ratio by incorrectly assuming
that n-hexane emissions were equal to total solvent (VOC) loss or by
not accounting for the volume fraction of n-hexane in solvent.
Response: As noted at proposal (84 FR 30818), the EPA assumed for
certain facilities that all solvent loss reported as VOC is emitted as
n-hexane. We adopted this approach where data for facility hexane
emissions were unavailable or lacking, recognizing that this approach
would provide the most conservative estimate of risk. Additionally, the
MACT allowable emissions multiplier conservatively assumed that all
loss of n-hexane in the solvent extraction process is emitted to the
atmosphere (84 FR 30819). The proposed approach was adopted taking into
consideration that the volume fraction of n-hexane may vary
significantly within a solvent (the solvent used in vegetable oil
production facilities is 100-percent VOC and may range from less than 1
percent to 88-percent n-hexane). Where emissions of n-hexane or the
volume fraction of n-hexane were not readily available from permit
materials, we conservatively assumed all solvent loss is n-hexane.
Therefore, the risk assessment does likely overestimate the actual and
allowable emissions for certain facilities; as noted at proposal, these
conservative assumptions were adopted to account for the potential
``worst-case'' risks given that we lacked complete information on the
n-hexane emissions for specific facilities. Although we acknowledge
that the source category risks would be lower with the adjustments
requested by the commenters, revision of the actual emissions or MACT-
allowable emissions in the modeling file would not change the EPA's
conclusions regarding risk.
Comment: One commenter objected to the EPA's methodology for the
acute risk assessment. The commenter stated that the risk assessment is
weakened because the EPA used ``reasonable worst-case'' conditions. The
commenter stated that after recognizing the need to evaluate the worst-
case set of conditions, it is inherently contradictory and circular for
the EPA to decide to ignore the impacts by deciding that the worst-case
is not actually ``reasonable.'' Another commenter stated the assessment
of risks for acute exposure is conservative. It assumes that estimated
1-hour peak emissions occur at the same time as the ``reasonable worst-
case'' meteorological conditions and that an individual will be exposed
at this time and under these conditions at the location of the maximum
predicted impact.
Response: The EPA disagrees that our Acute Screening-Level
Assessment should not be based on ``reasonable worst-case''
meteorological conditions. In developing an acute exposure scenario, we
estimate 1-hour exposure concentrations through air dispersion modeling
during hours of peak emissions. However, hourly emissions data are not
typically available, and the exact hours of peak emissions are often
unknown, making it difficult to determine the meteorological conditions
to model with the peak emissions. We make assumptions about when peak
hourly emissions occur. In a worst-case scenario, peak hourly emissions
would occur during the 1 hour of the year with the worst-case air
dispersion conditions (i.e., low, continuous wind speeds blowing in a
specific direction). However, the probability of peak hourly emissions
occurring in the same hour as the worst-case air dispersion conditions
is extremely low. For example, as documented in Appendix 5 of the
Residual Risk Assessment for the Solvent Extraction for Vegetable Oil
Production Source Category in Support of the 2019 Risk and Technology
Review Final Rule, available in the docket for this rulemaking,
conservatively the probability of these two events occurring
simultaneously is about 1-in-200,000 (or a 0.0005 percent chance).
Instead, we use ``reasonable worst-case'' meteorological conditions.
This approach strikes a balance of being health protective without
overestimating acute exposures and has a reasonable probability of
occurrence (conservatively, an 88-in-200,000 chance or 0.044 percent).
Using the ``reasonable worst-case'' meteorological conditions, the
scenario we modeled is a rare event (peak emissions would have a 0.044%
chance of occuring during the same hour as the ``reasonable worst-
case'' meteorology based on conservative assumptions, or a 99.956%
chance of not occuring during that hour) rather than a scenario that is
extremely unlikely (peak emissions would have a 0.0005% chance of
occuring during the same hour as the worst-case meteorology, or a
99.9995% chance of not occuring during that hour).
After review of all the comments received, we determined that no
changes to the risk assessment were necessary. The comments and our
specific responses can be found in the document, Summary of Public
Comments and Responses for the Risk and Technology Review for the
Solvent Extraction for Vegetable Oil Production Source Category,
available in the docket for this action.
[[Page 15617]]
4. What is the rationale for our final approach and final decisions for
the risk review?
As noted in our proposal, the EPA sets standards under CAA section
112(f)(2) using ``a two-step standard-setting approach, with an
analytical first step to determine an `acceptable risk' that considers
all health information, including risk estimation uncertainty, and
includes a presumptive limit on MIR of ``approximately 1-in-10
thousand'' (see 54 FR 38045, September 14, 1989). We weigh all health
risk factors in our risk acceptability determination, including the
cancer MIR, cancer incidence, the maximum cancer TOSHI, the maximum
acute noncancer HQ, the extent of noncancer risks, the distribution of
cancer and noncancer risks in the exposed population, and the risk
estimation uncertainties.
Since proposal, neither the risk assessment nor our determinations
regarding risk acceptability, ample margin of safety, and adverse
environmental effects have changed. For the reasons explained in the
proposed rule, we determined that the risks from the Solvent Extraction
for Vegetable Oil Production source category are acceptable, and the
current standards provide an ample margin of safety to protect public
health and prevent an adverse environmental effect. Therefore, we are
not revising the standards for this source category pursuant to CAA
section 112(f)(2) based on the residual risk review, and we are
readopting the existing standards under CAA section 112(f)(2).
B. Technology Review for the Solvent Extraction for Vegetable Oil
Production Source Category
1. What did we propose pursuant to CAA section 112(d)(6) for the
Solvent Extraction for Vegetable Oil Production source category?
Pursuant to CAA section 112(d)(6), we proposed to conclude that no
revisions to the current MACT standards for this source category are
necessary for control of n-hexane emissions from vegetable oil
production facilities (sections IV.C of proposal preamble, 84 FR
30825). We did not find any developments in practices, processes, and
control technologies that could be applied to solvent extraction for
vegetable oil process vents and that could be used to reduce emissions
from solvent extraction for vegetable oil production facilities. We
also did not identify any developments in work practices, pollution
prevention techniques, or process changes that could achieve emission
reductions from solvent extraction for vegetable oil process vents. We
identified for consideration the use of a cryogenic condenser after the
main vent as an add-on control option, based on a review of best
available control technology analyses where such controls were
previously considered. However, based on the costs and emission
reductions for the proposed options, we did not find the use of a
cryogenic condenser as cost effective for reducing emissions from these
emission sources at solvent extraction for vegetable oil production
units; and we proposed that it is not necessary to revise the MACT
standards for these emission sources pursuant to CAA section 112(d)(6).
Additional details of our technology review can be found in the
memorandum, CAA Section 112(d)(6) Technology Review for the Solvent
Extraction for Vegetable Oil Production Source Category, which is
available in the docket for this action.
2. How did the technology review change for the Solvent Extraction for
Vegetable Oil Production source category?
We have not changed any aspect of the technology review since the
June 27, 2019, RTR proposal for the Solvent Extraction for Vegetable
Oil Production source category.
3. What key comments did we receive on the technology review, and what
are our responses?
We received comments in support of and opposed to the proposed
determination from the technology review that no revisions were
warranted under CAA section 112(d)(6). We evaluated the comments and
determined that no changes regarding our determination were needed.
These comments and our specific responses can be found in the comment
summary and response document titled Summary of Public Comments and
Responses for the Risk and Technology Review for Solvent Extraction for
Vegetable Oil Production, which is available in the docket for this
action.
4. What is the rationale for our final approach for the technology
review?
We evaluated all of the comments on the EPA's technology review and
determined that no changes to the review are needed. For the reasons
explained in the proposed rule, we determined that no cost-effective
developments in practices, processes, or control technologies were
identified in our technology review to warrant revisions to the
standards. More information concerning our technology review, and how
we evaluate cost effectiveness, can be found in the memorandum titled
CAA Section 112(d)(6) Technology Review for the Solvent Extraction for
Vegetable Oil Production Source Category, which is available in the
docket for this action, and in the preamble to the proposed rule (84 FR
30825). Therefore, pursuant to CAA section 112(d)(6), we are finalizing
our technology review as proposed.
C. SSM for the Solvent Extraction for Vegetable Oil Production Source
Category
1. What amendments did we propose to address emissions during periods
of SSM?
We proposed removing and revising provisions related to SSM that
are not consistent with the requirement that standards apply at all
times. We proposed that the emission standards for normal operation
apply at all times, except for periods of initial startup, for new or
significantly modified sources as described below. We proposed
alternate standards for initial startup periods for new or
significantly modified sources. Specifically, we proposed that new or
significantly modified facilities operating in an initial startup
period would operate the mineral oil absorption system and solvent
condensers at all times during the initial startup period. We also
proposed that facilities establish and follow site-specific operating
ranges for temperature and vacuum for the desolventizing and oil
distillation units associated with solvent recovery. New and
significantly modified facilities would also continue to have the
option to meet the requirements for normal operating periods in Table 1
of 40 CFR 63.2850, in lieu of the work practice standards. We also
proposed to revise the definition of ``Initial startup period'' to
clarify the time at which an initial startup period ends and a normal
operating period begins.
We proposed to remove malfunction periods as a distinct source
operating status, which previously allowed sources to exclude data
collected during the ``malfunction period'' when determining compliance
with the emission standards. Under the proposed rule, sources that
experience an unscheduled shutdown as a result of a malfunction,
continue to operate during a malfunction (including the period
reasonably necessary to correct the malfunction), or start up after a
shutdown resulting from a malfunction must instead meet the emission
standard requirements for either a
[[Page 15618]]
normal operating period or the work practice standards for an initial
startup period (if applicable) in 40 CFR 63.2850 and Table 1 of 40 CFR
63.2850. We also proposed to remove reference to SSM exemptions from
the general duty requirements,\3\ to remove SSM plans, to remove
references to SSM exemptions in requirements related to compliance with
the standards and performance testing, and to revise recordkeeping and
reporting requirements that are not consistent with the requirement
that standards apply at all times. More information concerning our
proposal on SSM can be found in the proposed rule (84 FR 30825, June
27, 2019).
---------------------------------------------------------------------------
\3\ We proposed to add general duty regulatory text at 40 CFR
63.2840(g) to reflect the general duty to minimize emissions, while
eliminating the reference to periods covered by an SSM exemption
(see 84 FR 30828).
---------------------------------------------------------------------------
2. How did the SSM provisions change since proposal?
We are finalizing the SSM provisions as proposed, except for minor
clarifications. We are finalizing the proposed alternate work practice
standards for initial startup periods for new or significantly modified
sources, and we are finalizing our proposal to remove malfunction
periods as a source operating status, which previously allowed sources
to exclude data collected during the ``malfunction period'' when
calculating their compliance ratio according to 40 CFR 63.2840. We are
finalizing the removal and revision of SSM requirements related to
general duty, SSM plans, compliance with the standards, and performance
testing as proposed (84 FR 30825). We are revising the recordkeeping
requirements at 40 CFR 63.2862 and the reporting requirements at 40 CFR
63.2861 as proposed, with the exception of minor revisions to clarify
how to designate the date a deviation occurred and the duration of the
deviation. For deviations from the compliance ratio for facilities
operating under a normal operating period, the date of the deviation is
the date the compliance ratio determination is made, and the duration
of the deviation is the length of time taken to address the cause of
the deviation (including the duration of any malfunction) and to return
the affected unit(s) to its normal or usual manner of operation. For
deviations from the work practice standard for facilities operating
under an initial startup period, the date of the deviation is the date
when the facility fails to comply with any of the work practice
standards in 40 CFR 63.2840(h), and the duration of the deviation is
the length of time taken to return to the work practice standards. We
have also removed the requirement to record and report the time of day
the deviation occurred, since deviations from the compliance ratio are
determined at the end of the period.
3. What key comments did we receive on the SSM revisions and what are
our responses?
We received one comment supporting our proposed removal of the
exemption in the regulations for emissions during SSM periods. We
received two comments supporting our proposal to establish an option to
follow a work practice standard during initial startup periods for new
or significantly modified sources, and did not receive any comments
opposing the proposed work practice standards during initial startup
periods. We received additional comments requesting that startup or
shutdown periods be taken into account when setting the MACT standard.
We received comments both for and against the proposed removal of
``malfunction periods'' as a distinct source operating status. We also
received comments requesting clarification on the recordkeeping and
reporting requirements for the date, time, and duration of a deviation.
We evaluated all comments and determined that no changes to the
proposed alternate work practice standards for initial startup periods
for new or significantly modified sources; no changes to the proposed
removal of requirements that allowed sources to designate the operating
status as a distinct ``malfunction periods'' (facilities must instead
meet the requirements of normal operation or initial startup); and no
changes to the proposed removal or revision of provisions related to
SSM are required, with the exception of minor clarifications as
discussed in this section.
Comment: Two commenters stated that the EPA should take periods of
startup and shutdown into account when setting the MACT emissions
standards. The commenters stated that if the EPA is removing the
exemption of startup and shutdown emissions from the calculation of the
compliance ratio, the EPA should recalculate the MACT emission limits
based on normal operation plus periods of startup and shutdown. The
commenters stated that the EPA has indicated the current NESHAP
provides an ample margin of safety to protect public health, and that
this indicates there is ample room to increase the MACT limits to more
appropriate levels that include the startup and shutdown operations.
Another commenter stated that the proposed elimination of relief for
SSM events is not required for the rule to be consistent with Sierra
Club v. EPA. The commenter asserted that other court opinions have
emphasized the need for standards to accommodate higher emission levels
that occur at times other than normal operations.
Response: We do not agree that the MACT emission limits should be
recalculated to include periods of startup and shutdown. We disagree
with the commenter's suggestion that the legal precedent established in
case law (i.e., Sierra Club v. EPA, 551 F.3d 1019 (D.C. Cir. 2008)) is
not relevant. The Sierra Club decision held that emissions limitations
under CAA section 112 must apply continuously and meet minimum
stringency requirements, even during periods of SSM. Consistent with
Sierra Club v. EPA, for the reasons explained in the proposal preamble
at 83 FR 30285, we are finalizing our proposal to eliminate the SSM
language in 40 CFR part 63, subpart GGGG. Subpart GGGG had both rule-
specific SSM language and references to SSM language in the part 63
General Provisions in Table 1 of 63.2870, specifically reference to 40
CFR 63.6(f)(1). As we explained in the proposal, our SSM-related rule
revisions are in response to the Sierra Club Court's vacatur of the SSM
exemption in 40 CFR 63.6(f)(1) and 40 CFR 63.6(h)(1). When incorporated
into CAA section 112(d) regulations for specific source categories,
these two provisions exempted sources from the requirement to comply
with otherwise applicable MACT standards during periods of SSM. The
Court's vacatur rendered those provisions null and void prior to this
rulemaking. The mandate implementing the Court's decision was issued on
October 16, 2009, at which time the vacated SSM provision 40 CFR
63.6(f)(1) referenced by subpart GGGG was no longer in effect.
Eliminating reference to this provision, and other related General
Provisions referenced in subpart GGGG, is a ministerial action by the
EPA to reflect the vacatur by the Court. We also eliminated the rule-
specific SSM provisions in subpart GGGG. The final standards will apply
at all times, consistent with the Sierra Club decision.
As an alternative approach consistent with Sierra Club, the EPA may
designate different standards to apply during startup and shutdown (as
noted in the proposal, the EPA is not obligated to set standards for
periods of malfunction). For this category, the compliance approaches
required by state regulatory authorities led us to decide special
startup/shutdown standards were unnecessary for existing sources. Based
[[Page 15619]]
on discussions with industry, there are not significant differences in
the production process or operation of solvent recovery equipment
during startup or shutdown of an existing facility that would preclude
the facility from complying with the existing standards. A review of
title V permits identified that approximately 35 percent of existing
facilities are already required to account for periods of routine
startup (not initial startup) and shutdown in determining their
compliance ratio. This requirement was found commonly across states and
regions, indicating that existing sources operating during periods of
routine startup and shutdown are able to demonstrate compliance with
the emission standards. Furthermore, the commenter did not provide any
evidence that emissions during routine startup and shutdown vary
considerably from normal operation. Consequently, the final rule's
elimination of periods of startup and shutdown for existing sources
reflects this capability.
For the reasons explained in the proposal preamble, we are
finalizing alternate standards for periods of initial startup for new
or significantly modified sources. Because the initial startup period
reflects a non-steady state of production, emissions testing during
this period would not likely be representative or yield meaningful
results for the establishment of separate emission limits. As discussed
at proposal, control of n-hexane emissions at vegetable oil production
facilities is accomplished through solvent recovery and is based on
inter-related process equipment that is often custom built to the
specific configuration and needs of the plant. During an initial
startup period, facility equipment is tested, added, or replaced as the
facility gradually increases production, and emissions during this
period may reflect variability that is not generally reflective of
normal or steady-state operations. New and modified equipment is often
brought online in a phased approach, and each phase can necessitate
adjustments in both new and existing equipment in the process in order
to identify and correct problems, such as equipment that is not
operating as designed and that requires repair or replacement. The EPA
evaluated the available data for new or significantly modified sources
to establish potential standards for periods of initial startup,
including review of operating permits from various state and local
agencies and EPA Regional offices. We noted that the standards have not
previously required--and state, local, and Regional offices have not
collected--emissions data for these facilities during their initial
startup periods. Further, where the EPA identified a recently
constructed facility with permitted MACT allowable solvent loss for an
initial startup period, we determined that the allowable solvent loss
for the facility was not based on measured data, and would not be
representative of initial startup periods for other facilities in the
source category. Although we requested information on emissions and the
operation of processes during initial startup periods, we did not
receive sufficient information, including additional quantitative
emissions data, on which to base a numeric standard for initial startup
periods at new or significantly modified facilities. The EPA recognizes
that the initial startup period, which is a one-time event for new
sources and an infrequent event for significantly modified sources, is
not a typical startup period that may occur as part of routine or
seasonal startups of a plant. Instead, the initial startup period
includes evaluation and replacement of new equipment as each phase is
brought online and production is gradually increased. Therefore,
emissions testing during initial startup would be both economically and
technically infeasible. Consequently, the EPA is finalizing a work
practice standard rather than an emissions limit for this period.
Notwithstanding the finding that the MACT-based limits of the
initial NESHAP provide and ample margin of safety, the EPA lacks the
authority to relax limits developed in the MACT process based on
finding that the limits provide an ample margin of safety. Were the EPA
to do so, then the limits would not meet the strict structure of MACT.
The risk-based limits under CAA section 112(f)(2) were intended to
augment MACT when the post-MACT risks did not provide an ample margin
of safety to protect public health. There is no indication in the
statute that the risk-based standards were intended to revoke the
requirements to have MACT standards. A risk-based standard is only
required when the MACT-based does not sufficiently reduce risk (see CAA
section 112(f)(2)(A)).
Additionally, the EPA's finding is that the existing MACT-based
standard does not need to be made more stringent to comply with CAA
section 112(f)(2) (i.e., to provide an ample margin of safety). The EPA
has not made a finding that the existing standards somehow exceed an
ample margin of safety. There is no finding that there is ``room to
increase'' the limits while also complying with the requirement to
provide an ample margin of safety required by CAA section 112(f)(2).
Comment: One commenter asserted that it would be arbitrary and
capricious for the EPA to ignore the existence of malfunctions even at
best-performing sources, or to assume that the best-performing sources
achieve emission levels that they do not achieve part of the time. The
commenter urged that if the EPA adopts MACT standards that it
recognizes even the best-performing existing sources cannot achieve
part of the time, the EPA would be going beyond the MACT floor. Three
commenters stated that the EPA should take malfunctions into account
when adopting emissions standards. One commenter stated that it is not
apparent from the proposed rule why the EPA believes it needs to remove
the current provisions related to malfunctions. The commenter asserted
that the EPA cannot change its position and withdraw a previously
promulgated provision without providing a full explanation of the
reason(s) for the change. The same commenter recommended that the EPA
could instead establish numerical emission limitations that have an
averaging time of sufficient duration that short, infrequent spikes in
emissions due to malfunctions would not cause the source to exceed the
emission limitation. Alternatively, the commenter recommended that the
EPA could promulgate design, equipment, work practice, or operational
standards in lieu of a numerical standard. Two commenters stated that
the EPA should maintain an option in 40 CFR 63.2850(e)(2) either to
meet the requirements applicable to normal operating periods or to meet
the requirements for malfunction periods. These commenters urged that
otherwise there could be unavoidable exceedances of the standards. The
two commenters recommended that the EPA could adopt similar work
practice standards for malfunction periods as proposed for initial
startup periods. Another commenter suggested work practices such as
monitoring of operating parameters to identify a malfunction and
stopping or cutting back the process. One commenter supported the
removal of the malfunction exemptions, stating there is no lawful or
rational justification for creating non-numerical work practice
standards during malfunctions.
Response: We disagree with the commenters' assertions that we must
set revised or separate standards for periods of malfunction. As
discussed in the preamble to the proposed rule, as the Court recognized
in U.S. Sugar Corp, accounting for malfunctions in setting standards
would be difficult, if not
[[Page 15620]]
impossible, given the myriad different types of malfunctions that can
occur across all sources in the category and given the difficulties
associated with predicting or accounting for the frequency, degree, and
duration of various malfunctions that might occur. Id. at 608 (``the
EPA would have to conceive of a standard that could apply equally to
the wide range of possible [ ] malfunctions, ranging from an explosion
to minor mechanical defects. Any possible standard is likely to be
hopelessly generic to govern such a wide array of circumstances.''). As
such, the performance of units that are malfunctioning is not
``reasonably'' foreseeable. See, e.g., Sierra Club v. EPA, 167 F.3d
658, 662 (D.C. Cir. 1999) (``The EPA typically has wide latitude in
determining the extent of data-gathering necessary to solve a problem.
We generally defer to an agency's decision to proceed on the basis of
imperfect scientific information, rather than to `invest the resources
to conduct the perfect study.'''). See also, Weyerhaeuser v. Costle,
590 F.2d 1011, 1058 (D.C. Cir. 1978) (``In the nature of things, no
general limit, individual permit, or even any upset provision can
anticipate all upset situations. After a certain point, the
transgression of regulatory limits caused by `uncontrollable acts of
third parties,' such as strikes, sabotage, operator intoxication or
insanity, and a variety of other eventualities, must be a matter for
the administrative exercise of case-by- case enforcement discretion,
not for specification in advance by regulation.''). In addition,
emissions during a malfunction event can be significantly higher than
emissions at any other time of source operation. For example, if an air
pollution control device with 99-percent removal goes off- line as a
result of a malfunction (as might happen if, for example, the bags in a
baghouse catch fire) and the emission unit is a steady state type unit
that would take days to shut down, the source would go from 99-percent
control to zero control until the control device was repaired. The
source's emissions during the malfunction would be 100 times higher
than during normal operations. As such, the emissions over a 4-day
malfunction period would exceed the annual emissions of the source
during normal operations. As this example illustrates, accounting for
malfunctions could lead to standards that are not reflective of (and
significantly less stringent than) levels that are achieved by a well-
performing non-malfunctioning source. It is reasonable to interpret CAA
section 112 to avoid such a result. The EPA's approach to malfunctions
is consistent with CAA section 112 and is a reasonable interpretation
of the statute.
As noted at proposal, the EPA considers whether circumstances
warrant setting standards for a particular type of malfunction and, if
so, whether the EPA has sufficient information to identify the relevant
best performing sources and establish a standard for such malfunctions.
The EPA has also considered the need for a work practice for periods of
malfunction for vegetable oil production facilities. Although we
requested information on emissions and the operation of processes
during malfunction periods in our consultations with state agencies and
industry, we did not receive sufficient information for development of
proposed standards. Therefore, as part of the proposal, the EPA
solicited information on the type of events that constitute a
malfunction event, industry best practices, and the best level of
emission control during malfunction events. The EPA also requested
commenters provide information on the costs associated with any
recommended work practices. In addition, the EPA solicited specific
supporting data on HAP emissions during malfunction events, including
the cause of malfunction, the frequency of malfunction, duration of
malfunction, and the estimate of HAP emitted during each malfunction.
In this case, although we requested comment and information to support
the development of a standard during periods of malfunction, we did not
receive sufficient information, including additional quantitative
emissions data, on which to base a standard. Absent sufficient
information, it is not reasonable at this time to establish a work
practice standard for periods of malfunction for this source category.
For these reasons, we are not setting separate standards for periods of
malfunction. Under the final rule, sources that experience an
unscheduled shutdown as a result of a malfunction, continue to operate
during a malfunction (including the period reasonably necessary to
correct the malfunction), or start up after a shutdown resulting from a
malfunction must instead meet the emission standard requirements for
either a normal operating period or the work practice standards for an
initial startup period (if a new or significantly modified source) in
40 CFR 63.2850 and Table 1 of 40 CFR 63.2850. We note that sources must
still meet the general duty requirements in 40 CFR 63.2840(g) and
should address malfunctions expeditiously in order to maintain any
affected source, including associated air pollution control equipment
and monitoring equipment, and minimize emissions.
Nevertheless, the EPA acknowledges that including solvent loss from
a one-time event (like a malfunction) in the 12-month compliance ratio
could cause a deviation for one or more monthly compliance ratio
determinations, and would remain in the rolling compliance
determination for up to 1 year (12 months). We also recognize that it
is possible that a malfunction that causes a 12-month compliance ratio
to be exceeded might have been corrected well before the first full 12-
months have passed. Although a facility would need to retain records of
any deviation and the corrective action(s) performed, no additional
corrective action would be required at the time the 12-month compliance
ratio is officially exceeded in subsequent months if the facility
demonstrates the exceedance is from a prior malfunction that has been
corrected. Facilities would be able to provide such an explanation in
their deviation reports; specifically, we have revised the deviation
reporting requirements in the final rule to include a requirement that
facilities flag and provide an explanation for any deviation from the
compliance ratio for which a deviation report is being submitted for
more than 1 consecutive month (i.e., include a reference to the
original date and reporting of the deviation) (see 40 CFR 63.2861(b)).
Further, as discussed below in this section, we have clarified that the
duration of the deviation from the compliance ratio is the length of
time taken to address the cause of the deviation (including the
duration of any malfunction) and to return the affected unit(s) to its
normal or usual manner of operation. Therefore, facilities must retain
records of the date and duration of the malfunction, as well as the
corrective action(s) performed, to demonstrate the basis for the
deviation in subsequent periods.
As further explained at proposal, ``[i]n the event that a source
fails to comply with the applicable CAA section 112(d) standards as a
result of a malfunction event, the EPA would determine an appropriate
response based on, among other things, the good faith efforts of the
source to minimize emissions during malfunction periods, including
preventive and corrective actions, as well as root cause analyses to
ascertain and rectify excess emissions. The EPA would also consider
whether the source's failure to comply with the CAA section 112(d)
standard was, in fact,
[[Page 15621]]
sudden, infrequent, not reasonably preventable and was not instead
caused in part by poor maintenance or careless operation. 40 CFR 63.2
(definition of malfunction). If the EPA determines in a particular case
that an enforcement action against a source for violation of an
emission standard is warranted, the source can raise any and all
defenses in that enforcement action and the federal district court will
determine what, if any, relief is appropriate. The same is true for
citizen enforcement actions. Similarly, the presiding officer in an
administrative proceeding can consider any defense raised and determine
whether administrative penalties are appropriate'' (84 FR 30828).
Comment: We received one comment requesting clarification on the
revised reporting and recordkeeping requirements for deviations. The
commenter requested that the EPA clarify how a facility should
designate the date a deviation occurred. The commenter recommended that
because there is a single compliance ratio determination for an
operating month, the rule should specify that a deviation be reported
as occurring on the date the compliance ratio determination is made.
The commenter also requested clarification on the duration of a
deviation, noting that solvent loss from a one-time event (like a
malfunction) could cause a deviation for one or more monthly compliance
ratio determinations. The commenter stated it is unreasonable to
require facilities to report events that may last only 1 day as having
a duration of 30 days or even longer, and asked the EPA to clarify if
the deviation reporting requirements only apply to work practice
standards. Finally, the commenter stated the reporting template should
not require facilities to report the time of a deviation; the commenter
urged that the time of day a deviation occurs is not needed to
determine compliance with the standards.
Response: We agree with the commenter and have revised the
reporting and recordkeeping requirements for deviations for
clarification. Specifically, we have revised the recordkeeping
requirements of 40 CFR 63.2862(g)(1) to clarify that for deviations
from the compliance ratio, the date of the deviation is the date the
compliance ratio determination is made. For deviations from the work
practice standard during the initial startup period, the date of the
deviation is the date when the facility fails to comply with any of the
work practice standard in 40 CFR 63.2840(h) (e.g., if the facility
fails to operate the mineral oil absorption system or the solvent
condenser at all times during the initial startup period, or fails to
meet the site-specific operating limits established by the facility).
These dates must be reported in the deviation notification report
according to the final rule requirements at 40 CFR 63.2861(b)(5). We
have revised 40 CFR 63.2862(g)(1) to clarify that for deviations from
the compliance ratio, the duration of the deviation is the length of
time taken to address the cause of the deviation (including the
duration of any malfunction) and to return the affected unit(s) to its
normal or usual manner of operation. For deviations from the work
practice standard during the initial startup period, the duration of
the deviation is the length of time taken to return to the work
practice standards. The final rule requirements are consistent with the
prior requirements of 40 CFR 63.10(b)(2)(ii) to retain a record of the
``occurrence and duration of each malfunction'' and are necessary to
allow the EPA to determine the severity of any failure to meet a
standard. Finally, we have revised the final rule requirements to
remove the requirement to record or report the time of a deviation, as
this information is not necessary to determine compliance with the
standard.
Additional comments on the SSM provisions and our specific
responses to those comments can be found in the document titled Summary
of Public Comments and Responses for the Risk and Technology Review for
Solvent Extraction for Vegetable Oil Production, which is available in
the docket for this action.
4. What is the rationale for our final approach and final decisions to
address emissions during periods of SSM?
We evaluated all the comments on the EPA's proposed amendments to
the SSM provisions. For the reasons explained in the proposed rule (84
FR 30812), we determined that these amendments appropriately remove and
revise provisions related to SSM that are not consistent with the
requirement that the standards apply at all times. Therefore, we are
finalizing the amendments to remove and revise provisions related to
SSM, as proposed, with the exception of the clarifications discussed in
this section.
D. Technical Amendments to the MACT Standards for the Solvent
Extraction for Vegetable Oil Production Source Category
1. What other amendments did we propose for the Solvent Extraction for
Vegetable Oil Production source category?
We proposed that owners and operators submit electronic copies of
initial notifications, initial startup reports, annual compliance
certifications, deviation reports, and performance test reports through
the EPA's CDX using the CEDRI. For initial notifications, initial
startup reports, annual compliance certifications, and deviation
reports, the proposed rule requires that owners and operators use the
appropriate spreadsheet template to submit information to CEDRI. We
also proposed two broad circumstances in which we may provide extension
to these requirements. We proposed at 40 CFR 63.2862(f) that an
extension may be warranted due to outages of the EPA's CDX or CEDRI
that precludes an owner or operator from accessing the system and
submitting required reports. We also proposed at 40 CFR 63.2862(g) that
an extension may be warranted due to a force majeure event, such as an
act of nature, act of war or terrorism, or equipment failure or safety
hazards beyond the control of the facility.
We proposed revisions to several definitions in 40 CFR 63.2872 to
harmonize with the proposed removal of the SSM requirements and to
clarify existing provisions, include revisions to definitions of
``Compliance ratio,'' ``Nonoperating period,'' ``Normal operating
period,'' and ``Operating month'' to clarify where the malfunction
period is excluded, and to the definition of ``Normal operating
period'' to clarify that this definition also applies to ``normal
operation.'' We also proposed to add a definition for ``Nonoperating
month.'' We proposed to revise the definition of ``Hazardous air
pollutant (HAP)'' to remove the reference to the date of April 12,
2001.
We proposed minor revisions to 40 CFR 63.2840(a)(1) and (b)(1), 40
CFR 63.2853(a)(2), and 40 CFR 63.2855(a)(3) to remove text that is
redundant with the definition of ``Operating month'' in 40 CFR 63.2872.
We also proposed a minor correction to Table 1 of 63.2850 to correct a
typographical error in row ``(a)'' for malfunction periods.
[[Page 15622]]
2. How did the other amendments for the Solvent Extraction for
Vegetable Oil Production source category change since proposal?
There are no changes to the proposed requirements for owners and
operators to submit electronic copies of initial notifications, initial
startup reports, annual compliance certifications, deviation reports,
and performance test reports electronically. We also are finalizing, as
proposed, the provisions that allow facility operators the ability to
seek extensions for submitting electronic reports for circumstances
beyond the control of the facility. There are no changes to the
proposed definitions in 40 CFR 63.2872, or the minor revisions to 40
CFR 63.2840(a)(1) and (b)(1), 40 CFR 63.2853(a)(2), 40 CFR
63.2855(a)(3), or Table 1 of 40 CFR 63.2850.
3. What key comments did we receive on the other amendments for the
Solvent Extraction for Vegetable Oil Production source category and
what are our responses?
We received one comment providing input on the proposed requirement
for owners and operators of vegetable oil production facilities to
submit electronic copies of initial notifications, initial startup
reports, annual compliance certifications, deviation reports, and
performance test reports. The commenter stated that the EPA may not
lawfully or rationally finalize ``exemption provisions'' based on CEDRI
outages or ``force majeure events.'' The commenter stated the
provisions do not set a firm deadline to request an extension of the
reporting deadline. No commenters provided significant comments on the
proposed definitions in 40 CFR 63.2872, or the proposed minor revisions
to 40 CFR 63.2840(a)(1) and (b)(1), 40 CFR 63.2853(a)(2), 40 CFR
63.2855(a)(3), or Table 1 of 40 CFR 63.2850.
Comment: One commenter stated that the EPA must not finalize the
proposed electronic reporting extension provisions because the
definition of a force majeure event is too broad, the provisions do not
set a firm deadline to request an extension of the reporting deadline,
and the decision to allow an extension is solely within the discretion
of the Administrator. The commenter urged that the proposed provisions
are unlawful and arbitrary because they would create a broad and vague
mechanism that a facility owner or operator could use to evade binding
emission standards, by evading the binding compliance reporting
deadlines set to assure compliance with those standards. The commenter
further stated that the EPA should not import the concept of ``force
majeure'' into any part of the CAA, as to do so is a variation of the
prior malfunction exemptions that are unlawful under the CAA. The
commenter also noted that the EPA has provided that there are no known
issues with submission of ERT-formatted performance test and evaluation
reports in CEDRI (per the Petroleum Refinery NESHAP), thus, there is no
rational basis for providing the proposing reporting extensions. At a
minimum, the commenter requested that the EPA set a new firm deadline
to assure that the extension request allows only a temporary period
when the facility need not report, such as a 10-day extension, rather
than an open-ended extension without a deadline.
Response: The commenter states that the brief case-by-case
extension of report submittal deadlines is a ``reporting exemption.''
This is not the case. The proposed provisions the commenter questions
are in paragraphs 40 CFR 63.2861(h) and (i).
There is no exception or exemption to reporting, much less an
exemption from compliance with the numerical emission standards, only a
method for requesting an extension of the reporting deadline. Reporters
are required to justify their request and identify a reporting date.
There is no predetermined timeframe for the length of extension that
can be granted, as this is something best determined by the
Administrator (i.e., the EPA Administrator or delegated authority as
defined in 40 CFR 63.2) when reviewing the circumstances surrounding
the request. Different circumstances may require a different length of
extension for electronic reporting. For example, a tropical storm may
delay electronic reporting for a day, but a Hurricane Katrina scale
event may delay electronic reporting much longer, especially if the
facility has no power, and as such, the owner or operator has no
ability to access electronically stored data or to submit reports
electronically. The Administrator will be the most knowledgeable of the
events leading to the request for extension and will assess whether an
extension is appropriate, and if so, a reasonable length for the
extension. The Administrator may even request that the report be sent
in hardcopy until electronic reporting can be resumed. While no new
fixed duration deadline is set, the regulation requires that the report
be submitted electronically as soon as possible after the CEDRI outage
or after the force majeure event resolves.
The concept of force majeure has been implemented by the EPA in
this context since May 2007 within the CAA requirements through the
performance test extensions provided in 40 CFR 63.7(a)(4) and
60.8(a)(1). Like the performance test extensions, the approval of a
requested extension of an electronic reporting deadline is at the
discretion of the Administrator.
The EPA disagrees that the ability to request a reporting extension
``would create a broad and vague mechanism'' that owners and operators
``could use to evade binding emissions standards'' or evade ``binding
compliance reporting deadlines'' for emissions standards. While
reporting is an important mechanism for the EPA and air agencies to
assess whether owners and operators are in compliance with emissions
standards, reporting obligations are separate from (i.e., in addition
to) requirements that an owner or operator be in compliance with an
emissions standard, especially where the deadline for meeting the
standard has already passed and the owner or operator has certified and
is monitoring operations to show that they are in compliance with the
standard. The commenter references deadlines set forth in the CAA for
demonstrating initial compliance following the effective date of
emission standards, which differs from deadlines for submitting
reports. There are no such deadlines stated in the CAA for report due
dates, meaning the EPA has discretion to establish reporting schedules,
and also discretion to allow a mechanism for extension of those
schedules on a case-by-case basis. In fact, under the commenter's
reasoning, if the statutory deadlines for compliance with standards
were read to strictly apply to continuing reporting requirements, no
such reporting could be required after 3 years from the promulgation of
the standards. This would not be a reasonable result. Reporting
deadlines are often different from compliance deadlines. Rules under 40
CFR part 60 and 63 typically allow months following an initial
compliance deadline to conduct testing and submit reports, but
compliance with standards is required upon the compliance date.
Additionally, the ability to request a reporting extension does not
apply to a broad category of circumstances; on the contrary, the scope
for submitting an extension request for an electronic report is very
limited in that claims can only be made for an event outside of the
owner's or operator's control that occurs in the five business days
prior to the reporting deadline. The claim must then be approved by the
Administrator, and in approving such a claim, the
[[Page 15623]]
Administrator agrees that something outside the control of the owner or
operator prevented the owner or operator from meeting its reporting
obligation. In no circumstance does this electronic reporting extension
allow for the owner or operator to be out of compliance with the
underlying emissions standards. If the Administrator determines that a
facility has not acted in good faith to reasonably report in a timely
manner, the Administrator can reject the claim and find that the
failure to report timely is a deviation from the regulation. CEDRI
system outages are infrequent, but the EPA knows when they occur and
whether a facility's claim is legitimate. Force majeure events (e.g.,
natural disasters impacting a facility) are also usually well-known
events.
Finally, EPA disagrees that the existing statistics on the use of
CEDRI and e-reporting precludes the need for a provision to account for
an outage of the CEDRI system. Prudent management of electronic data
systems builds in allowances for unexpected, non-routine delays, such
as occurred on July 1, 2016 and October 20-23, 2017, and is consistent
with the already-existing provisions afforded for unexpected, non-
routine delays in performance testing [see 40 CFR 60.8(a)(1) and (2)
and 40 CFR 63.7(a)(4)]. For both electronic reporting and performance
testing, owners or operators are to conduct and complete their
activities within a short window of time; the EPA believes it is
prudent to allow owners or operators to make force majeure claims for
situations beyond their reasonable control. The EPA also disagrees that
incidental issues with questions on completing the form or the
procedures for accessing CEDRI for which the CEDRI Helpdesk is
available, are conditions that would be considered either force majeure
or a CEDRI system outage. The existence of the Helpdesk for answering
questions on procedures in submitting reports to CEDRI have no impact
on the availability of CEDRI in such a circumstance. The purpose of
these requests for extensions are to accommodate owners and operators
in cases where they cannot successfully submit a report electronically
for reasons that are beyond their control and occur during a short
window of time prior to the reporting deadline. The extension is not
automatic, and the Administrator retains the right to accept or reject
the request. The language was added as part of the standard electronic
reporting language based on numerous comments received on the proposal
for the Electronic Reporting and Recordkeeping Requirements for the New
Source Performance Standards (80 FR 15100). As such, we have determined
that no changes to the electronic reporting requirements are necessary
in the final rule.
Additional comments on the proposed electronic reporting
requirements and other amendments and our specific responses to those
comments can be found in the memorandum titled Summary of Public
Comments and Responses for the Risk and Technology Review for Solvent
Extraction for Vegetable Oil Production, available in the docket for
this action.
4. What is the rationale for our final approach and final decisions for
the other amendments for the Solvent Extraction for Vegetable Oil
Production source category?
We evaluated the comment on the EPA's proposed amendments to
require electronic reporting initial notifications, initial startup
reports, annual compliance certifications, deviation reports, and
performance test reports. For the reasons explained in the proposed
rule, we determined that these amendments increase the ease and
efficiency of data submittal and improve data accessibility. More
information concerning the proposed requirement for owners and
operators of vegetable oil production facilities to submit electronic
copies of certain notifications and reports is in the preamble to the
proposed rule (84 FR 30830, June 27, 2019) and the document, Summary of
Public Comments and Responses for the Risk and Technology Review for
the Solvent Extraction for Vegetable Oil Production, available in the
docket for this action. Therefore, we are finalizing our approach for
submission of initial notifications, initial startup reports, annual
compliance certifications, deviation reports, and performance test
reports as proposed.
V. Summary of Cost, Environmental, and Economic Impacts and Additional
Analyses Conducted
A. What are the affected facilities?
The EPA estimates that there are 89 vegetable oil production
facilities that are currently subject to the Solvent Extraction for
Vegetable Oil Production NESHAP and would be affected by the final
amendments. The basis of our estimate of affected facilities is
provided in the memorandum, Residual Risk Modeling File Documentation
for the Solvent Extraction for Vegetable Oil Production Source
Category, which is available in the docket for this action. We
additionally anticipate one new source per year. The EPA received
comment on the proposed rule that some larger facilities may have
significant modifications about once a year, therefore, we assume that
eight existing vegetable oil production facilities may have a
significant modification that could meet the revised requirements for
initial startup periods.
B. What are the air quality impacts?
The EPA estimates that annual HAP emissions from the vegetable oil
production facilities that are subject to the NESHAP are approximately
13,500 tpy.\4\ Because the EPA is not revising the emission limits, we
do not anticipate any quantifiable air quality impacts as a result of
these amendments. However, we anticipate that the final requirements,
including the work practice standards for the optional initial startup
period, are at least as stringent as the current rule requirements. The
work practice standards include requirements for facilities to operate
controls, including the mineral oil absorption system and solvent
condensers, at all times during the initial startup period. Facilities
must also establish and follow site-specific operating ranges for
temperature and vacuum for the desolventizing and oil distillation
units associated with solvent recovery. We anticipate these
requirements will minimize emissions during these periods.
---------------------------------------------------------------------------
\4\ The annual HAP emission estimates include emissions from 88
facilities. Annual emissions are not yet available for one newly
constructed facility.
---------------------------------------------------------------------------
C. What are the cost impacts?
The 89 vegetable oil production facilities that would be subject to
the final amendments, and one additional new source per year, would
incur minimal net costs to meet revised recordkeeping and reporting
requirements, some estimated to have costs and some estimated to have
cost savings. Nationwide costs associated with the final requirements
are estimated to total $93,100 over the 3 years following promulgation
of amendments (or $31,033 per year). The EPA believes that the
vegetable oil production facilities that are known to be subject to the
NESHAP can meet the final requirements without incurring additional
capital or operational costs. Therefore, the only costs associated with
the final amendments include a one-time burden for reviewing
requirements of the amended rule, and a one-time burden associated with
recordkeeping and reporting labor costs for initial startup periods for
new, reconstructed, or significantly modified
[[Page 15624]]
facilities. The EPA assumed in the proposed rule that one potential new
or reconstructed vegetable oil production facility would be subject to
the revised requirements for initial startup periods each year.
However, we received comment on the proposed rule that some larger
facilities may have significant modifications about once a year.
Therefore, we have revised the costs associated with the final rule to
assume that approximately eight existing vegetable oil production
facilities (or approximately 10 percent of existing facilities) may
have a significant modification that could require that they meet the
revised requirements for initial startup periods. The revised
assumption results in an increase in the total nationwide annual costs
associated with the final requirements to account for the additional
facilities anticipated to have a significant modification (actual costs
per facility have not changed). For further information on the costs
and cost savings associated with the final requirements, see the
memorandum, Cost for the Solvent Extraction for Vegetable Oil
Production Source Category Risk and Technology Review--Final
Amendments, and the document, Supporting Statement for NESHAP for
Solvent Extraction for Vegetable Oil Production, which are both
available in the docket for this action.
D. What are the economic impacts?
Economic impact analyses focus on changes in market prices and
output levels. If changes in market prices and output levels in the
primary markets are significant enough, impacts on other markets may
also be examined. Both the magnitude of costs needed to comply with a
final rule and the distribution of these costs among affected
facilities can have a role in determining how the market will change in
response to a final rule. The total costs associated with the final
rule are estimated to be $93,100 (or $31,033 per year) for the 3 years
following the final rule. This includes a one-time burden for reviewing
requirements of the amended rule, and a one-time burden associated with
the recordkeeping and reporting for initial startup periods for new,
reconstructed, or significantly modified facilities. This is an
estimated average cost of approximately $345 per year per facility.
These costs are not expected to result in a significant market impact,
regardless of whether they are passed on to the purchaser or absorbed
by the firms.
E. What are the benefits?
Although the EPA does not anticipate quantifiable reductions in HAP
emissions as a result of the final amendments, we believe that the
action will result in improvements to the rule. Specifically, the final
amendments revise the standards such that they apply at all times. For
facilities that choose to operate under an initial startup period, the
EPA is finalizing an alternative work practice standard that will
ensure that facilities are operating controls and minimizing emissions
while the source operates under non-steady state production, which we
expect will protect public health and the environment through better
compliance during these periods. Additionally, the final amendments
requiring electronic submittal of initial notifications, initial
startup reports, annual compliance certifications, deviation reports,
and performance test results will streamline reporting for affected
sources, increase the usefulness of the data and improve data
accessibility for the public, will further assist in the protection of
public health and the environment, and will ultimately result in less
burden on the regulated community. See section IV.D.2 of the preamble
to the proposed rule for more information.
F. What analysis of environmental justice did we conduct?
As discussed in the preamble to the proposed rule, to examine the
potential for any environmental justice issues that might be associated
with the source category, we performed a demographic analysis, which is
an assessment of risks to individual demographic groups of the
populations living within 5 kilometers (km) and within 50 km of the
facilities. In the analysis, we evaluated the distribution of HAP-
related cancer and noncancer risks from the Solvent Extraction for
Vegetable Oil Production source category across different demographic
groups within the populations living near facilities. When examining
the risk levels of those exposed to emissions from solvent extraction
for vegetable oil production facilities, we found that no one is
exposed to a cancer risk at or above 1-in-1 million or to a chronic
noncancer TOSHI greater than 1.
The documentation for this decision is contained in section IV.A of
the preamble to the proposed rule and the technical report titled Risk
and Technology Review--Analysis of Demographic Factors for Populations
Living Near Solvent Extraction for Vegetable Oil Production, which is
available in the docket for this action.
G. What analysis of children's environmental health did we conduct?
This action is not subject to Executive Order 13045 because it is
not economically significant as defined in Executive Order 12866, and
because the EPA does not believe the environmental health or safety
risks addressed by this action present a disproportionate risk to
children. This action's health and risk assessments are summarized in
section IV.A of this preamble and are further documented in the risk
report, Residual Risk Assessment for the Solvent Extraction for
Vegetable Oil Production Source Category in Support of the 2019 Risk
and Technology Review Final Rule, available in the docket for this
action.
VI. Statutory and Executive Order Reviews
Additional information about these statutes and Executive Orders
can be found at https://www.epa.gov/laws-regulations/laws-and-executive-orders.
A. Executive Orders 12866: Regulatory Planning and Review and Executive
Order 13563: Improving Regulation and Regulatory Review
This action is not a significant regulatory action and was,
therefore, not submitted to the Office of Management and Budget (OMB)
for review.
B. Executive Order 13771: Reducing Regulations and Controlling
Regulatory Costs
This action is not an Executive Order 13771 regulatory action
because this action is not significant under Executive Order 12866.
C. Paperwork Reduction Act (PRA)
The information collection activities in this rule have been
submitted for approval to the OMB under the PRA. The Information
Collection Request (ICR) document that the EPA prepared has been
assigned EPA ICR number 1947.09. You can find a copy of the ICR in the
docket for this rule, and it is briefly summarized here. The
information collection requirements are not enforceable until OMB
approves them.
The EPA is finalizing amendments that revise provisions pertaining
to emissions during periods of SSM; add requirements for electronic
reporting of certain notifications and reports and performance test
results; and make other minor clarifications and corrections. This
information will be collected to assure compliance with the Solvent
[[Page 15625]]
Extraction for Vegetable Oil Production NESHAP.
Respondents/affected entities: Owners or operators of vegetable oil
production processes.
Respondent's obligation to respond: Mandatory (40 CFR part 63,
subpart GGGG).
Estimated number of respondents: 90 (assumes one new respondent
over the next 3 years).
Frequency of response: Initially, occasionally, and annually.
Total estimated burden: The annual recordkeeping and reporting
burden for responding facilities to comply with all of the requirements
in the NESHAP, averaged over the 3 years of this ICR, is estimated to
be 34,100 hours. Of these, 448 hours (per year) is the incremental
burden to comply with the final rule amendments. Burden is defined at 5
CFR 1320.3(b).
Total estimated cost: The annual recordkeeping and reporting cost
for responding facilities to comply with all of the requirements in the
NESHAP, averaged over the 3 years of this ICR, is estimated to be
$3,490,000 (per year), including $0 annualized capital or operation and
maintenance costs. Of the total, $31,033 (per year) is the incremental
cost to comply with the final amendments to the rule, or approximately
$345 per facility.
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 OMB
approves this ICR, the Agency will announce that approval in the
Federal Register and publish a technical amendment to 40 CFR part 9 to
display the OMB control number for the approved information collection
activities contained in this final rule.
D. Regulatory Flexibility Act (RFA)
I certify that this action will not have a significant economic
impact on a substantial number of small entities under the RFA. The
small entities subject to the requirements of this action are small
vegetable oil production facilities. The Agency has determined that up
to 12 small entities, representing approximately 13 percent of the
total number of entities subject to the final rule, may experience an
impact of less than 1 percent of revenues. See section V.D of this
preamble for additional information on the economic impacts of this
action.
E. Unfunded Mandates Reform Act (UMRA)
This action does not contain an unfunded mandate of $100 million or
more as described in UMRA, 2 U.S.C. 1531-1538, and does not
significantly or uniquely affect small governments. The action imposes
no enforceable duty on any state, local, or tribal governments or the
private sector.
F. Executive Order 13132: Federalism
This action does not have federalism implications. It will not have
substantial direct effects on the states, on the relationship between
the national government and the states, or on the distribution of power
and responsibilities among the various levels of government.
G. Executive Order 13175: Consultation and Coordination With Indian
Tribal Governments
This action does not have tribal implications as specified in
Executive Order 13175. None of the solvent extraction for vegetable oil
production facilities that have been identified as being affected by
this final action are owned or operated by tribal governments or
located within tribal lands. Thus, Executive Order 13175 does not apply
to this action.
H. Executive Order 13045: Protection of Children From Environmental
Health Risks and Safety Risks
This action is not subject to Executive Order 13045 because the EPA
does not believe the environmental health risks or safety risks
addressed by this action present a disproportionate risk to children.
This action's health and risk assessments are contained in sections
IV.A of this preamble and the document, Residual Risk Assessment for
the Solvent Extraction for Vegetable Oil Production Source Category in
Support of the 2019 Risk and Technology Review Final Rule, which is
available in the docket for this rulemaking.
I. Executive Order 13211: Actions Concerning Regulations That
Significantly Affect Energy Supply, Distribution, or Use
This action is not subject to Executive Order 13211, because it is
not a significant regulatory action under Executive Order 12866.
J. National Technology Transfer and Advancement Act (NTTAA)
This rulemaking involves technical standards. As discussed in the
preamble of the proposal, the EPA conducted searches for the Solvent
Extraction for Vegetable Oil Production Sector Risk and Technology
Review through the Enhanced National Standards Systems Network Database
managed by the American National Standards Institute (ANSI). We also
contacted voluntary consensus standards (VCS) organizations and
accessed and searched their databases. We conducted searches for EPA
Method 311 of 40 CFR part 63, appendix A. No applicable VCS were
identified for EPA Method 311. The search identified two VCS that were
potentially applicable for this rule in lieu of EPA reference methods.
After reviewing the available standards, the EPA determined that the
two candidate VCS (ASTM D6438 (1999), CARB Method 310)) identified for
measuring emissions of pollutants or their surrogates subject to
emissions standards in the rule would not be practical due to lack of
equivalency, documentation, validation data, and other important
technical and policy considerations.
A thorough summary of the search conducted, and results are
included in the memorandum, Voluntary Consensus Standard Results for
National Emission Standards for Hazardous Air Pollutants for Solvent
Extraction for Vegetable Oil Production, which is available in the
docket for this action.
K. Executive Order 12898: Federal Actions To Address Environmental
Justice in Minority Populations and Low-Income Populations
The EPA believes that this action does not have disproportionately
high and adverse human health or environmental effects on minority
populations, low-income populations, and/or indigenous peoples, as
specified in Executive Order 12898 (59 FR 7629, February 16, 1994).
The documentation for this decision is contained in section IV.A of
this preamble and in the technical report, Risk and Technology Review--
Analysis of Demographic Factors for Populations Living Near Vegetable
Oil Production Facilities, available in the docket for this action.
L. Congressional Review Act (CRA)
This action is subject to the CRA, and the EPA will submit a rule
report to each House of the Congress and to the Comptroller General of
the United States. This action is not a ``major rule'' as defined by 5
U.S.C. 804(2).
List of Subjects in 40 CFR Part 63
Environmental protection, Air pollution control, Hazardous
substances, Reporting and recordkeeping requirements.
[[Page 15626]]
Dated: February 25, 2020.
Andrew R. Wheeler,
Administrator.
For the reasons set forth in the preamble, the EPA is amending 40
CFR part 63 as follows:
PART 63--NATIONAL EMISSION STANDARDS FOR HAZARDOUS AIR POLLUTANTS
FOR SOURCE CATEGORIES
0
1. The authority citation for part 63 continues to read as follows:
Authority: 42 U.S.C. 7401, et seq.
Subpart GGGG--National Emission Standards for Hazardous Air
Pollutants: Solvent Extraction for Vegetable Oil Production
0
2. Section 63.2834 is amended by revising Table 1 of Sec. 63.2834 to
read as follows:
Sec. 63.2834 When do I have to comply with the standards in this
subpart?
* * * * *
Table 1 of Sec. 63.2834--Compliance Dates for Existing and New Sources
----------------------------------------------------------------------------------------------------------------
Except for certain
requirements, as
specified in Sec. Sec.
63.2840, 63.2850,
If your affected source is And if . . . Then your compliance 63.2851, 63.2852,
categorized as . . . date is . . . 63.2853, 63.2861,
63.2862, and 63.2870,
then your compliance
date is . . .
----------------------------------------------------------------------------------------------------------------
(a) an existing source............... April 12, 2004......... September 15, 2020.
(b) a new source..................... you startup your April 12, 2004......... September 15, 2020.
affected source before
April 12, 2001.
(c) a new source..................... you startup your your startup date...... September 15, 2020.
affected source on or
after April 12, 2001,
but before March 18,
2020.
(d) a new source..................... you startup your your startup date...... your startup date.
affected source on or
after March 18, 2020.
----------------------------------------------------------------------------------------------------------------
0
3. Section 63.2840 is amended by:
0
a. Revising the introductory text and paragraphs (a)(1) introductory
text and (b) introductory text;
0
b. Removing and reserving paragraph (b)(1);
0
c Revising paragraphs (b)(3) through (5); and
0
d. Adding paragraphs (g) and (h).
The revisions and additions read as follows:
Sec. 63.2840 What emission requirements must I meet?
For each facility meeting the applicability criteria in Sec.
63.2832, you must comply with either the requirements specified in
paragraphs (a) through (d), or the requirements in paragraph (e) of
this section. You must also comply with the requirements in paragraph
(g) of this section. You must comply with the work practice standard
provided in paragraph (h) of this section, if you choose to operate
your source under an initial startup period subject to Sec.
63.2850(c)(2) or (d)(2).
(a)(1) The emission requirements limit the number of gallons of HAP
lost per ton of listed oilseeds processed. For each operating month, as
defined in Sec. 63.2872, you must calculate a compliance ratio which
compares your actual HAP loss to your allowable HAP loss for the
previous 12 operating months as shown in Equation 1 of this section.
Equation 1 of this section follows:
* * * * *
(b) When your source has processed listed oilseed for 12 operating
months, calculate the compliance ratio by the end of each calendar
month following an operating month, as defined in Sec. 63.2872, using
Equation 2 of this section. When calculating your compliance ratio,
consider the conditions and exclusions in paragraphs (b)(1) through (6)
of this section:
* * * * *
(3) If your source shuts down and processes no listed oilseed for
an entire calendar or accounting month, then you must categorize the
month as a nonoperating month, as defined in Sec. 63.2872. Exclude any
nonoperating months from the compliance ratio determination.
(4) If your source is subject to an initial startup period as
defined in Sec. 63.2872, you may exclude from the compliance ratio
determination any solvent and oilseed information recorded for the
initial startup period, provided you meet the work practice standard in
Sec. 63.2850(c)(2) or (d)(2).
(5) Before September 15, 2020, if your source is subject to a
malfunction period as defined in Sec. 63.2872, exclude from the
compliance ratio determination any solvent and oilseed information
recorded for the malfunction period. The provisions of this paragraph
(e) do not apply on and after September 15, 2020.
* * * * *
(g) On or after September 15, 2020, you must operate and maintain
any affected source, including associated air pollution control
equipment and monitoring equipment, at all times in a manner consistent
with safety and good air pollution control practices for minimizing
emissions. The general duty to minimize emissions does not require you
to make any further efforts to reduce emissions if levels required by
the applicable standard have been achieved. Determination of whether a
source is operating in compliance with operation and maintenance
requirements will be based on information available to the
Administrator which may include, but is not limited to, monitoring
results, review of operation and maintenance procedures, review of
operation and maintenance records, and inspection of the source.
(h) On and after September 15, 2020, you must meet the requirements
in paragraphs (h)(1) through (3) of this section if you choose to
operate your source under an initial startup period subject to Sec.
63.2850(c)(2) or (d)(2).
(1) You must operate the mineral oil absorption system at all times
during the initial startup period unless doing so is not possible due
to safety considerations;
(2) You must operate the solvent condensers at all times during the
initial startup period unless doing so is not possible due to safety
considerations; and
(3) You must follow site-specific operating limits, established
according to the requirements in paragraphs
[[Page 15627]]
(h)(3)(i) and (ii) of this section, for temperature and pressure for
the desolventizing and oil distillation units associated with solvent
recovery at all times, unless doing so is not possible due to safety
considerations.
(i) Your site-specific operating limits may be based on equipment
design, manufacturer's recommendations, or other site-specific
operating values established for normal operating periods.
(ii) The operating limits may be in the form of a minimum, maximum,
or operating range.
0
4. Section 63.2850 is amended by:
0
a. Revising paragraph (a)(3) and paragraph (a)(5) introductory text;
0
b. Adding paragraph (a)(5)(iv);
0
c. Revising paragraphs (b), (c)(1) and (2), (d)(1) and (2), (e)
introductory text, and (e)(2); and
0
d. Revising Table 1 of Sec. 63.2850.
The revisions and addition read as follows:
Sec. 63.2850 How do I comply with the hazardous air pollutant
emission standards?
(a) * * *
(3) Develop a written startup, shutdown and malfunction (SSM) plan
in accordance with the provisions in Sec. 63.2852. On and after
September 15, 2020, an SSM plan is not required.
* * * * *
(5) Submit the reports in paragraphs (a)(5)(i) through (iv) of this
section, as applicable:
* * * * *
(iv) Initial startup period reports in accordance with Sec.
63.2861(e).
* * * * *
(b) Existing sources under normal operation. You must meet all of
the requirements listed in paragraph (a) of this section and Table 1 of
this section for sources under normal operation, and the schedules for
demonstrating compliance for existing sources under normal operation in
Table 2 of this section.
(c) * * *
(1) Normal operation. Upon initial startup of your new source, you
must meet all of the requirements listed in Sec. 63.2850(a) and Table
1 of this section for sources under normal operation, and the schedules
for demonstrating compliance for new sources under normal operation in
Table 2 of this section.
(2) Initial startup period. For up to 6 calendar months after the
startup date of your new source, you must meet all of the requirements
listed in paragraph (a) of this section and Table 1 of this section for
sources operating under an initial startup period, and the schedules
for demonstrating compliance for new sources operating under an initial
startup period in Table 2 of this section. On and after September 15,
2020, you must also comply with the work practice standard in Sec.
63.2840(h) for the duration of the initial startup period. At the end
of the initial startup period (as defined in Sec. 63.2872), your new
source must then meet all of the requirements listed in Table 1 of this
section for sources under normal operation.
(d) * * *
(1) Normal operation. Upon initial startup of your significantly
modified existing or new source, you must meet all of the requirements
listed in paragraph (a) of this section and Table 1 of this section for
sources under normal operation, and the schedules for demonstrating
compliance for an existing or new source that has been significantly
modified in Table 2 of this section.
(2) Initial startup period. For up to 3 calendar months after the
startup date of your significantly modified existing or new source, you
must meet all of the requirements listed in paragraph (a) of this
section and Table 1 of this section for sources operating under an
initial startup period, and the schedules for demonstrating compliance
for a significantly modified existing or new source operating under an
initial startup period in Table 2 of this section. On and after
September 15, 2020, you must also comply with the work practice
standard in Sec. 63.2840(h) for the duration of the initial startup
period. At the end of the initial startup period (as defined in Sec.
63.2872), your new or existing source must meet all of the requirements
listed in Table 1 of this section for sources under normal operation.
(e) Existing or new sources experiencing a malfunction. A
malfunction is defined in Sec. 63.2. In general, it means any sudden,
infrequent, and not reasonably preventable failure of air pollution
control equipment, process equipment, or a process to function in a
normal or usual manner. If your existing or new source experiences an
unscheduled shutdown as a result of a malfunction, continues to operate
during a malfunction (including the period reasonably necessary to
correct the malfunction), or starts up after a shutdown resulting from
a malfunction, then you must meet the requirements associated with one
of two compliance options. Routine or scheduled process startups and
shutdowns resulting from, but not limited to, market demands,
maintenance activities, and switching types of oilseed processed, are
not startups or shutdowns resulting from a malfunction and, therefore,
do not qualify for this provision. Within 15 days of the beginning date
of the malfunction, you must choose to comply with one of the options
listed in paragraphs (e)(1) and (2) of this section. The provisions of
this paragraph (e) do not apply on and after September 15, 2020.
* * * * *
(2) Malfunction period. Throughout the malfunction period, you must
meet all of the requirements listed in paragraph (a) of this section
and Table 1 of this section for sources operating during a malfunction
period. At the end of the malfunction period, your source must then
meet all of the requirements listed in Table 1 of this section for
sources under normal operation. Table 1 of this section follows:
Table 1 of Sec. 63.2850--Requirements for Compliance With HAP Emission
Standards
------------------------------------------------------------------------
Before September
15, 2020, for
For initial malfunction
Are you required For periods of startup periods periods subject
to . . . normal subject to Sec. to Sec.
operation? \a\ 63.2850(c)(2) 63.2850(e)(2)?
or (d)(2)? \a\
------------------------------------------------------------------------
(a)(1) Operate and Yes. Yes, you are Yes, you are
maintain your Additionally, required to required to
source in the HAP minimize minimize
accordance with emission limits emissions to emissions to
general duty will apply. the extent the extent
provisions of practicable practicable
Sec. 63.6(e) throughout the throughout the
before September initial startup initial startup
15, 2020? period. Such period. Such
measures should measures should
be described in be described in
the SSM plan. the SSM plan.
[[Page 15628]]
(a)(2) Operate and No, you must No, you must
maintain your meet the meet the
source in requirements of requirements of
accordance with Sec. Sec.
general duty 63.2840(g). 63.2840(g).
provisions of Additionally,
Sec. 63.6(e) on the HAP
and after emission limits
September 15, will apply.
2020?
(b) Determine and Yes, as Yes, as Yes, as
record the described in described in described in
extraction Sec. 63.2853. Sec. Sec.
solvent loss in 63.2862(e) 63.2862(e).
gallons from your (before
source? September 15,
2020) and Sec.
63.2862(f) (on
and after
September 15,
2020).
(c) Record the Yes............. Yes............. Yes.
volume fraction
of HAP present at
greater than 1
percent by volume
and gallons of
extraction
solvent in
shipment
received?
(d) Determine and Yes, as No.............. No.
record the tons described in
of each oilseed Sec. 63.2855.
type processed by
your source?
(e) Determine the Yes............. No. Except for No, the HAP
weighted average solvent volume fraction
volume fraction received by a in any solvent
of HAP in new or received during
extraction reconstructed a malfunction
solvent received source period is
as described in commencing included in the
Sec. 63.2854 by operation under weighted
the end of the an initial average HAP
following startup period, determination
calendar month? the HAP volume for the next
fraction in any operating
solvent month.
received during
an initial
startup period
is included in
the weighted
average HAP
determination
for the next
operating month.
(f) Determine and Yes............. No, these No, these
record the actual requirements requirements
solvent loss, are not are not
weighted average applicable applicable
volume fraction because your because your
HAP, oilseed source is not source is not
processed and required to required to
compliance ratio determine the determine the
for each 12 compliance compliance
operating month ratio with data ratio with data
period as recorded for an recorded for a
described in Sec. initial startup malfunction
63.2840 by the period. period.
end of the
following
calendar month?
(g) Submit a Yes, as No. However, you No. However, you
Notification of described in may be required may be required
Compliance Status Sec. Sec. to submit an to submit an
or Annual 63.2860(d) and annual annual
Compliance 63.2861(a). compliance compliance
Certification as certification certification
appropriate? for previous for previous
operating operating
months, if the months, if the
deadline for deadline for
the annual the annual
compliance compliance
certification certification
happens to happens to
occur during occur during
the initial the malfunction
startup period. period.
(h)(1) Submit a Yes............. No, these No, these
Deviation requirements requirements
Notification are not are not
Report by the end applicable applicable
of the calendar because your because your
month following source is not source is not
the month in required to required to
which you determine the determine the
determined that compliance compliance
the compliance ratio with data ratio with data
ratio exceeds recorded for an recorded for a
1.00 as described initial startup malfunction
in Sec. period. period.
63.2861(b) before
September 15,
2020?
(h)(2) Submit a Yes............. Yes............. No.
Deviation
Notification
Report as
described in Sec.
63.2861(b) on
and after
September 15,
2020?
(i) Submit a No, a SSM Yes, before Yes.
Periodic SSM activity is not September 15,
Report as categorized as 2020.
described in Sec. normal
63.2861(c)? operation.
(j) Submit an No, a SSM Yes, only before Yes, only if
Immediate SSM activity is not September 15, your source
Report as categorized as 2020 and if does not follow
described in Sec. normal your source the SSM plan.
63.2861(d)? operation. does not follow
the SSM plan.
(k) Submit an No.............. Yes............. No.
Initial Startup
Report as
described in Sec.
63.2861(e) on
and after
September 15,
2020?
------------------------------------------------------------------------
\a\ Beginning on September 15, 2020, you must meet the requirements of
this table for normal operating periods or for initial startup periods
subject to Sec. 63.2850(c)(2) or (d)(2) at all times. The column
``For malfunction periods subject to Sec. 63.2850(e)(2)?'' is not
applicable beginning on September 15, 2020.
[[Page 15629]]
0
5. Section 63.2851 is amended by revising paragraph (a) introductory
text and adding paragraph (a)(8) to read as follows:
Sec. 63.2851 What is a plan for demonstrating compliance?
(a) You must develop and implement a written plan for demonstrating
compliance that provides the detailed procedures you will follow to
monitor and record data necessary for demonstrating compliance with
this subpart. Procedures followed for quantifying solvent loss from the
source and amount of oilseed processed vary from source to source
because of site-specific factors such as equipment design
characteristics and operating conditions. Typical procedures include
one or more accurate measurement methods such as weigh scales,
volumetric displacement, and material mass balances. Because the
industry does not have a uniform set of procedures, you must develop
and implement your own site-specific plan for demonstrating compliance
before the compliance date for your source. You must also incorporate
the plan for demonstrating compliance by reference in the source's
title V permit and keep the plan on-site and readily available as long
as the source is operational. If you make any changes to the plan for
demonstrating compliance, then you must keep all previous versions of
the plan and make them readily available for inspection for at least 5
years after each revision. The plan for demonstrating compliance must
include the items in paragraphs (a)(1) through (8) of this section:
* * * * *
(8) On and after September 15, 2020, if you choose to operate your
source under an initial start-up period subject to Sec. 63.2850(c)(2)
or (d)(2), the items in paragraphs (c)(8)(i) and (ii) of this section:
(i) Your site-specific operating limits, and their basis, for
temperature and pressure for the desolventizing and oil distillation
units associated with solvent recovery.
(ii) A detailed description of all methods of measurement your
source will use to measure temperature and pressure, including the
measurement frequency.
* * * * *
0
6. Section 63.2852 is revised to read as follows:
Sec. 63.2852 What is a startup, shutdown, and malfunction plan?
Before September 15, 2020, you must develop a written SSM plan in
accordance with Sec. 63.6(e)(3). You must complete the SSM plan before
the compliance date for your source. You must also keep the SSM plan
on-site and readily available as long as the source is operational. The
SSM plan provides detailed procedures for operating and maintaining
your source to minimize emissions during a qualifying SSM event for
which the source chooses the Sec. 63.2850(e)(2) malfunction period, or
the Sec. 63.2850(c)(2) or (d)(2) initial startup period. The SSM plan
must specify a program of corrective action for malfunctioning process
and air pollution control equipment and reflect the best practices now
in use by the industry to minimize emissions. Some or all of the
procedures may come from plans you developed for other purposes such as
a Standard Operating Procedure manual or an Occupational Safety and
Health Administration Process Safety Management plan. To qualify as a
SSM plan, other such plans must meet all the applicable requirements of
these NESHAP. The provisions of this section do not apply on and after
September 15, 2020.
0
7. Section 63.2853 is amended by:
0
a. Revising paragraph (a)(2) introductory text;
0
b. Revising the heading for Table 1 of Sec. 63.2853 in paragraph
(a)(2);
0
c. Adding Table 2 of Sec. 63.2853(a)(2) to paragraph (a)(2); and
0
d. Revising paragraphs (a)(3), (a)(5)(i), and (c)(1), (3), and (4).
The revisions and addition read as follows:
Sec. 63.2853 How do I determine the actual solvent loss?
* * * * *
(a) * * *
(2) Source operating status. You must categorize the operating
status of your source for each recorded time interval in accordance
with criteria in Table 1 or Table 2 of this section, as follows:
Table 1 of Sec. 63.2853(a)(2)--Categorizing Your Source Operating
Status Before September 15, 2020
* * * * *
Table 2 of Sec. 63.2853(a)(2)--Categorizing Your Source Operating
Status On and After September 15, 2020
------------------------------------------------------------------------
Then your source operating
If during a recorded time interval . . . status is . . .
------------------------------------------------------------------------
(vi) Your source processes any amount of A normal operating period.
listed oilseed and source is not operating
under an initial startup operating period
subject to Sec. 63.2850(c)(2) or (d)(2).
(vii) Your source processes no agricultural A nonoperating period.
product and your source is not operating
under an initial startup period subject to
Sec. 63.2850(c)(2) or (d)(2).
(viii) You choose to operate your source An initial startup period.
under an initial startup period subject to
Sec. 63.2850(c)(2) or (d)(2).
(ix) Your source processes agricultural An exempt period.
products not defined as listed oilseed.
------------------------------------------------------------------------
(3) Measuring the beginning and ending solvent inventory. You are
required to measure and record the solvent inventory on the beginning
and ending dates of each normal operating period that occurs during an
operating month. You must consistently follow the procedures described
in your plan for demonstrating compliance, as specified in Sec.
63.2851, to determine the extraction solvent inventory, and maintain
readily available records of the actual solvent loss inventory, as
described in Sec. 63.2862(c)(1). In general, you must measure and
record the solvent inventory only when the source is actively
processing any type of agricultural product. When the source is not
active, some or all of the solvent working capacity is transferred to
solvent storage tanks which can artificially inflate the solvent
inventory.
* * * * *
(5) * * *
(i) Solvent destroyed in a control device. You may use a control
device to reduce solvent emissions to meet the emission standard. The
use of a control device does not alter the emission limit for the
source. If you use a control device that reduces solvent emissions
through destruction of the solvent instead of recovery, then determine
the gallons of solvent that enter the control device and are destroyed
there during each normal operating period. All
[[Page 15630]]
solvent destroyed in a control device during a normal operating period
can be subtracted from the total solvent loss. Examples of destructive
emission control devices include catalytic incinerators, boilers, or
flares. Identify and describe, in your plan for demonstrating
compliance, each type of reasonable and sound measurement method that
you use to quantify the gallons of solvent entering and exiting the
control device and to determine the destruction efficiency of the
control device. You may use design evaluations to document the gallons
of solvent destroyed or removed by the control device instead of
performance testing under Sec. 63.7. The design evaluations must be
based on the procedures and options described in Sec.
63.985(b)(1)(i)(A) through (C) or Sec. 63.11, as appropriate. All
data, assumptions, and procedures used in such evaluations must be
documented and available for inspection. If you use performance testing
to determine solvent flow rate to the control device or destruction
efficiency of the device, follow the procedures as outlined in Sec.
63.997(e)(1) and (2) and the requirements in paragraph (a)(5)(i)(A) of
this section. Instead of periodic performance testing to demonstrate
continued good operation of the control device, you may develop a
monitoring plan, following the procedures outlined in Sec. 63.988(c)
and using operational parametric measurement devices such as fan
parameters, percent measurements of lower explosive limits, and
combustion temperature.
(A) On or after September 15, 2020, you must conduct all
performance tests under such conditions as the Administrator specifies
to you based on representative performance of the affected source for
the period being tested. Representative conditions exclude periods of
startup and shutdown unless specified by the Administrator. You may not
conduct performance tests during periods of malfunction. You must
record the process information that is necessary to document operating
conditions during the test and include in such record an explanation to
support that such conditions represent normal operation. Upon request,
you shall make available to the Administrator such records as may be
necessary to determine the conditions of performance tests.
(B) [Reserved]
(c) * * *
(1) Nonoperating periods as described in paragraph (a)(2) of this
section.
* * * * *
(3) Before September 15, 2020, malfunction periods as described in
Sec. 63.2850(e)(2).
(4) Exempt operation periods as described in paragraph (a)(2) of
this section.
0
8. Section 63.2855 is amended by revising paragraphs (a)(3), (a)(5)(i),
and (c)(3) to read as follows:
Sec. 63.2855 How do I determine the quantity of oilseed processed?
* * * * *
(a) * * *
(3) Measuring the beginning and ending inventory for each oilseed.
You are required to measure and record the oilseed inventory on the
beginning and ending dates of each normal operating period that occurs
during an operating month. You must consistently follow the procedures
described in your plan for demonstrating compliance, as specified in
Sec. 63.2851, to determine the oilseed inventory on an as received
basis and maintain readily available records of the oilseed inventory
as described by Sec. 63.2862(c)(3).
* * * * *
(5) * * *
(i) Oilseed that molds or otherwise become unsuitable for
processing.
* * * * *
(c) * * *
(3) Before September 15, 2020, malfunction periods as described in
Sec. 63.2850(e)(2).
* * * * *
0
9. Section 63.2861 is amended by
0
a. Revising paragraph (b) introductory text;
0
b. Adding paragraphs (b)(5) through (8);
0
c. Revising paragraphs (c) introductory text and (d) introductory text;
and
0
d. Adding paragraphs (e) through (i).
The revisions and additions read as follows:
Sec. 63.2861 What reports must I submit and when?
* * * * *
(b) Deviation notification report. Submit a deviation report for
each compliance determination you make in which the compliance ratio
exceeds 1.00 as determined under Sec. 63.2840(c) or if you deviate
from the work practice standard for an initial startup period subject
to Sec. 63.2850(c)(2) or (d)(2). Submit the deviation report by the
end of the month following the calendar month in which you determined
the deviation. The deviation notification report must include the items
in paragraphs (b)(1) through (7) of this section if you exceed the
compliance ratio, and must include the items in paragraphs (b)(1), (2),
and (5) through (8) of this section if you deviate from the work
practice standard:
* * * * *
(5) Beginning on September 15, 2020, the number of deviations and
for each deviation the date and duration of each deviation. Flag and
provide an explanation for any deviation from the compliance ratio for
which a deviation report is being submitted for more than one
consecutive month (i.e., include a reference to the original date and
reporting of the deviation). If the explanation provides that
corrective actions have returned the affected unit(s) to its normal
operation, you are not required to include the items in paragraphs
(b)(6) and (7) of this section.
(6) Beginning on September 15, 2020, a statement of the cause of
each deviation (including unknown cause, if applicable).
(7) Beginning on September 15, 2020, for each deviation, a list of
the affected sources or equipment, an estimate of the quantity of HAP
emitted over the emission requirements of Sec. 63.2840, and a
description of the method used to estimate the emissions.
(8) A description of the deviation from the work practice standard
during the initial startup period, including the records of Sec.
63.2862(f) for the deviation.
(c) Periodic startup, shutdown, and malfunction report. Before
September 15, 2020, if you choose to operate your source under an
initial startup period subject to Sec. 63.2850(c)(2) or (d)(2) or a
malfunction period subject to Sec. 63.2850(e)(2), you must submit a
periodic SSM report by the end of the calendar month following each
month in which the initial startup period or malfunction period
occurred. The periodic SSM report must include the items in paragraphs
(c)(1) through (3) of this section. The provisions of this paragraph
(c) do not apply on and after September 15, 2020.
* * * * *
(d) Immediate SSM reports. Before September 15, 2020, if you handle
a SSM during an initial startup period subject to Sec. 63.2850(c)(2)
or (d)(2) or a malfunction period subject to Sec. 63.2850(e)(2)
differently from procedures in the SSM plan and the relevant emission
requirements in Sec. 63.2840 are exceeded, then you must submit an
immediate SSM report. Immediate SSM reports consist of a telephone call
or facsimile transmission to the responsible agency within 2 working
days after starting actions inconsistent with the SSM plan, followed by
a letter within 7 working
[[Page 15631]]
days after the end of the event. The letter must include the items in
paragraphs (d)(1) through (3) of this section. The provisions of this
paragraph (d) do not apply on and after September 15, 2020.
* * * * *
(e) Initial startup period reports. If you choose to operate your
source under an initial startup period subject to Sec. 63.2850(c)(2)
or (d)(2) on and after September 15, 2020, you must submit an initial
startup period report within 30 days after the initial startup period
ends. The report must include the items in paragraphs (e)(1) through
(3) of this section.
(1) The name and address of the owner or operator.
(2) The physical address of the vegetable oil production process.
(3) A compliance certification indicating whether the source was in
compliance with the work practice standard of Sec. 63.2840(h).
(f) Performance tests. On and after September 15, 2020, if you
conduct performance tests to determine solvent flow rate to a control
device or destruction efficiency of a control device according to the
requirements of Sec. 63.2853(a)(5)(i), within 60 days after the date
of completing each performance test, you must submit the results of the
performance test following the procedures specified in paragraphs
(f)(1) and (2) of this section.
(1) Data collected using test methods supported by EPA's Electronic
Reporting Tool (ERT) as listed on EPA's ERT website (https://www.epa.gov/electronic-reporting-air-emissions/electronic-reporting-tool-ert) at the time of the test. Submit the results of the
performance test to EPA via the Compliance and Emissions Data Reporting
Interface (CEDRI), which can be accessed through EPA's Central Data
Exchange (CDX) (https://cdx.epa.gov/). The data must be submitted in a
file format generated through the use of EPA's ERT. Alternatively, you
may submit an electronic file consistent with the extensible markup
language (XML) schema listed on EPA's ERT website.
(2) Data collected using test methods that are not supported by
EPA's ERT as listed on EPA's ERT website at the time of the test. The
results of the performance test must be included as an attachment in
the ERT or an alternate electronic file consistent with the XML schema
listed on EPA's ERT website. Submit the ERT generated package or
alternative file to EPA via CEDRI.
(3) Confidential business information (CBI). If you claim some of
the information submitted under paragraph (f) or (g) of this section is
CBI, you must submit a complete file, including information claimed to
be CBI, to EPA. The file must be generated through the use of EPA's ERT
or an alternate electronic file consistent with the XML schema listed
on EPA's ERT website. Submit the file on a compact disc, flash drive,
or other commonly used electronic storage medium and clearly mark the
medium as CBI. Mail the electronic medium to U.S. EPA/OAQPS/CORE CBI
Office, Attention: Group Leader, Measurement Policy Group, MD C404-02,
4930 Old Page Rd., Durham, NC 27703. The same file with the CBI omitted
must be submitted to EPA via EPA's CDX as described in paragraph (f)(1)
of this section.
(g) Submitting reports electronically. On and after September 15,
2020, you must submit the initial notification required in Sec.
63.2860(b) and the annual compliance certification, deviation report,
and initial startup report required in Sec. 63.2861(a), (b), and (e)
to the EPA via CEDRI, which can be accessed through the EPA's CDX
(https://cdx.epa.gov). The owner or operator must upload to CEDRI an
electronic copy of each applicable notification in portable document
format (PDF). The applicable notification must be submitted by the
deadline specified in this subpart, regardless of the method in which
the reports are submitted. You must use the appropriate electronic
report template on the CEDRI website (https://www.epa.gov/electronic-reporting-air-emissions/compliance-and-emissions-data-reporting-interface-cedri) for this subpart. The date report templates become
available will be listed on the CEDRI website. The report must be
submitted by the deadline specified in this subpart, regardless of the
method in which the report is submitted. If you claim some of the
information required to be submitted via CEDRI is CBI, submit a
complete report, including information claimed to be CBI, to EPA. The
report must be generated using the appropriate form on the CEDRI
website. Submit the file on a compact disc, flash drive, or other
commonly used electronic storage medium and clearly mark the medium as
CBI. Mail the electronic medium to U.S. EPA/OAQPS/CORE CBI Office,
Attention: Group Leader, Measurement Policy Group, MD C404-02, 4930 Old
Page Rd., Durham, NC 27703. The same file with the CBI omitted must be
submitted to EPA via EPA's CDX as described earlier in this paragraph.
(h) Claims of EPA system outage. If you are required to
electronically submit a report through CEDRI in EPA's CDX, you may
assert a claim of EPA system outage for failure to timely comply with
the reporting requirement. To assert a claim of EPA system outage, you
must meet the requirements outlined in paragraphs (h)(1) through (7) of
this section.
(1) You must have been or will be precluded from accessing CEDRI
and submitting a required report within the time prescribed due to an
outage of either EPA's CEDRI or CDX systems.
(2) The outage must have occurred within the period of time
beginning five business days prior to the date that the submission is
due.
(3) The outage may be planned or unplanned.
(4) You must submit notification to the Administrator in writing as
soon as possible following the date you first knew, or through due
diligence should have known, that the event may cause or has caused a
delay in reporting.
(5) You must provide to the Administrator a written description
identifying:
(i) The date(s) and time(s) when CDX or CEDRI was accessed and the
system was unavailable;
(ii) A rationale for attributing the delay in reporting beyond the
regulatory deadline to EPA system outage;
(iii) Measures taken or to be taken to minimize the delay in
reporting; and
(iv) The date by which you propose to report, or if you have
already met the reporting requirement at the time of the notification,
the date you reported.
(6) The decision to accept the claim of EPA system outage and allow
an extension to the reporting deadline is solely within the discretion
of the Administrator.
(7) In any circumstance, the report must be submitted
electronically as soon as possible after the outage is resolved.
(i) Claims of force majeure. If you are required to electronically
submit a report through CEDRI in EPA's CDX, you may assert a claim of
force majeure for failure to timely comply with the reporting
requirement. To assert a claim of force majeure, you must meet the
requirements outlined in paragraphs (i)(1) through (5) of this section.
(1) You may submit a claim if a force majeure event is about to
occur, occurs, or has occurred or there are lingering effects from such
an event within the period of time beginning five business days prior
to the date the submission is due. For the purposes of this section, a
force majeure event is defined as an event that will be or has been
caused by circumstances beyond the control of the affected facility,
its contractors, or any entity controlled by the affected facility
[[Page 15632]]
that prevents you from complying with the requirement to submit a
report electronically within the time period prescribed. Examples of
such events are acts of nature (e.g., hurricanes, earthquakes, or
floods), acts of war or terrorism, or equipment failure or safety
hazard beyond the control of the affected facility (e.g., large scale
power outage).
(2) You must submit notification to the Administrator in writing as
soon as possible following the date you first knew, or through due
diligence should have known, that the event may cause or has caused a
delay in reporting.
(3) You must provide to the Administrator:
(i) A written description of the force majeure event;
(ii) A rationale for attributing the delay in reporting beyond the
regulatory deadline to the force majeure event;
(iii) Measures taken or to be taken to minimize the delay in
reporting; and
(iv) The date by which you propose to report, or if you have
already met the reporting requirement at the time of the notification,
the date you reported.
(4) The decision to accept the claim of force majeure and allow an
extension to the reporting deadline is solely within the discretion of
the Administrator.
(5) In any circumstance, the reporting must occur as soon as
possible after the force majeure event occurs.
0
10. Section 63.2862 is amended by:
0
a. Revising paragraph (b) and paragraph (c) introductory text;
0
b. Revising paragraphs (c)(3)(ii), (d) introductory text, and (e)
introductory text; and
0
c. Adding paragraphs (f) through (h).
The revisions and additions read as follows:
Sec. 63.2862 What records must I keep?
* * * * *
(b) Before September 15, 2020, prepare a plan for demonstrating
compliance (as described in Sec. 63.2851) and a SSM plan (as described
in Sec. 63.2852). In these two plans, describe the procedures you will
follow in obtaining and recording data, and determining compliance
under normal operations or a SSM subject to the Sec. 63.2850(c)(2) or
(d)(2) initial startup period or the Sec. 63.2850(e)(2) malfunction
period. Complete both plans before the compliance date for your source
and keep them on-site and readily available as long as the source is
operational. On and after September 15, 2020, the requirement to
prepare a SSM plan no longer applies, and the plan for demonstrating
compliance must only describe the procedures you develop according to
the requirements of Sec. 63.2851.
(c) If your source processes any listed oilseed, record the items
in paragraphs (c)(1) through (3) of this section:
* * * * *
(3) * * *
(ii) The operating status of your source, as described in Sec.
63.2853(a)(2). On the log for each type of listed oilseed that is not
being processed during a normal operating period, you must record which
type of listed oilseed is being processed in addition to the source
operating status.
* * * * *
(d) After your source has processed listed oilseed for 12 operating
months, record the items in paragraphs (d)(1) through (5) of this
section by the end of the calendar month following each operating
month:
* * * * *
(e) Before September 15, 2020, for each SSM event subject to an
initial startup period as described in Sec. 63.2850(c)(2) or (d)(2),
or a malfunction period as described in Sec. 63.2850(e)(2), record the
items in paragraphs (e)(1) through (3) of this section by the end of
the calendar month following each month in which the initial startup
period or malfunction period occurred. The provisions of this paragraph
(e) do not apply on and after September 15, 2020.
* * * * *
(f) On and after September 15, 2020, for each initial startup
period subject to Sec. 63.2850(c)(2) or (d)(2), record the items in
paragraphs (f)(1) through (6) of this section by the end of the
calendar month following each month in which the initial startup period
occurred.
(1) A description and dates of the initial startup period, and
reason it qualifies as an initial startup.
(2) An estimate of the solvent loss in gallons for the duration of
the initial startup or malfunction period with supporting
documentation.
(3) Nominal design rate of the extractor and operating rate of the
extractor for the duration of the initial startup period, or permitted
production rate and actual production rate of your source for the
duration of the initial startup period.
(4) Measured values for temperature and pressure for the
desolventizing and oil distillation units associated with solvent
recovery.
(5) Information to indicate the mineral oil absorption system was
operating at all times during the initial startup period.
(6) Information to indicate the solvent condensers were operating
at all times during the initial startup period.
(g) On and after September 15, 2020, keep the records of deviations
specified in paragraphs (f)(1) through (4) of this section for each
compliance determination you make in which the compliance ratio exceeds
1.00 as determined under Sec. 63.2840(c) or if you deviate from the
work practice standard for an initial startup period subject to Sec.
63.2850(c)(2) or (d)(2).
(1) The number of deviations, and the date and duration of each
deviation. For deviations from the compliance ratio, the date of the
deviation is the date the compliance ratio determination is made. The
duration of the deviation from the compliance ratio is the length of
time taken to address the cause of the deviation, including the
duration of any malfunction, and return the affected unit(s) to its
normal or usual manner of operation. For deviations from the work
practice standard during the initial startup period, the date of the
deviation is the date(s) when the facility fails to comply with any of
the work practice standard in Sec. 63.2840(h). The duration of the
deviation from the work practice standard is the length of time taken
to return to the work practice standards.
(2) A statement of the cause of each deviation (including unknown
cause, if applicable).
(3) For each deviation, a list of the affected sources or
equipment, an estimate of the quantity of each regulated pollutant
emitted over any emission limit, and a description of the method used
to estimate the emissions.
(4) Actions taken to minimize emissions in accordance with Sec.
63.2840(g), and any corrective actions taken to return the affected
unit to its normal or usual manner of operation.
(5) If you deviate from the work practice standard for an initial
startup period, a description of the deviation from the work practice
standard.
(h) Any records required to be maintained by this part that are
submitted electronically via EPA's CEDRI may be maintained in
electronic format. This ability to maintain electronic copies does not
affect the requirement for facilities to make records, data, and
reports available upon request to a delegated air agency or EPA as part
of an on-site compliance evaluation.
0
11. Section 63.2870 is amended by revising Table 1 to Sec. 63.2870 to
read as follows:
Sec. 63.2870 What parts of the General Provisions apply to me?
* * * * *
[[Page 15633]]
Table 1 to Sec. 63.2870--Applicability of 40 CFR Part 63, Subpart A, to 40 CFR, Part 63, Subpart GGGG
----------------------------------------------------------------------------------------------------------------
Subject of Brief description Applies to
General provisions citation citation of requirement subpart Explanation
----------------------------------------------------------------------------------------------------------------
Sec. 63.1.................... Applicability.... Initial Yes..............
applicability
determination;
applicability
after standard
established;
permit
requirements;
extensions;
notifications.
Sec. 63.2.................... Definitions...... Definitions for Yes.............. Except as specifically
part 63 provided in this
standards. subpart.
Sec. 63.3.................... Units and Units and Yes..............
abbreviations. abbreviations
for part 63
standards.
Sec. 63.4.................... Prohibited Prohibited Yes..............
activities and activities;
circumvention. compliance date;
circumvention;
severability.
Sec. 63.5.................... Construction/ Applicability; Yes.............. Except for subsections
reconstruction. applications; of Sec. 63.5 as
approvals. listed below.
Sec. 63.5(c)................. [Reserved].......
Sec. 63.5(d)(1)(ii)(H)....... Application for Type and quantity No............... All sources emit HAP.
approval. of HAP, Subpart GGGG does not
operating require control from
parameters. specific emission
points.
Sec. 63.5(d)(1)(ii)(I)....... [Reserved].......
Sec. 63.5(d)(1)(iii), (d)(2), Application for No............... The requirements of
(d)(3)(ii). approval. the application for
approval for new,
reconstructed and
significantly
modified sources are
described in Sec.
63.2860(b) and (c) of
subpart GGGG. General
provision
requirements for
identification of HAP
emission points or
estimates of actual
emissions are not
required.
Descriptions of
control and methods,
and the estimated and
actual control
efficiency of such do
not apply.
Requirements for
describing control
equipment and the
estimated and actual
control efficiency of
such equipment apply
only to control
equipment to which
the subpart GGGG
requirements for
quantifying.
Sec. 63.6.................... Applicability of Applicability.... Yes.............. Except for subsections
General of Sec. 63.6 as
Provisions. listed below.
Sec. 63.6(b)(1)-(3).......... Compliance dates, ................. No............... Section 63.2834 of
new and subpart GGGG
reconstructed specifies the
sources. compliance dates for
new and reconstructed
sources.
Sec. 63.6(b)(6).............. [Reserved].......
Sec. 63.6(c)(3)-(4).......... [Reserved].......
Sec. 63.6(d)................. [Reserved].......
Sec. 63.6(e)(1)(i)........... Operation and ................. Yes, before See Sec. 63.2840(g)
Maintenance. September 15, for general duty
2020. No, on or requirement
after September
15, 2020.
Sec. 63.6(e)(1)(ii).......... Operation and Requirement to Yes, before See Sec. 63.2840(g)
Maintenance. correct September 15, for general duty
malfunctions as 2020]. No, on or requirement.
soon as after September
practicable. 15, 2020.
Sec. 63.6(e)(3)(i) through Operation and ................. Yes, before Minimize emissions to
(e)(3)(ii) and Sec. maintenance September 15, the extent
63.6(e)(3)(v) through (vii). requirements. 2020. practicable. On or
after September 15,
2020, see Sec.
63.2840(g) for
general duty
requirement.
Sec. 63.6(e)(3)(iii)......... Operation and ................. No............... Minimize emissions to
maintenance the extent
requirements. practicable. On or
after September 15,
2020, see Sec.
63.2840(g) for
general duty
requirement.
Sec. 63.6(e)(3)(iv).......... Operation and ................. No............... Report SSM and in
maintenance accordance with Sec.
requirements. 63.2861(c) and (d).
[[Page 15634]]
Sec. 63.6(e)(3)(viii)........ Operation and ................. Yes, before Except, before
maintenance September 15, September 15, 2020,
requirements. 2020. No, on or report each revision
after September to your SSM plan in
15, 2020. accordance with Sec.
63.2861(c) rather
than Sec.
63.10(d)(5) as
required under Sec.
63.6(e)(3)(viii).
Sec. 63.6(e)(3)(ix).......... Title V permit... ................. Yes, before
September 15,
2020. No, on or
after September
15, 2020.
Sec. 63.6(f)(1).............. Compliance with Comply with Yes, before
nonopacity emission September 15,
emission standards at all 2020. No, on or
standards except times except after September
during SSM. during SSM. 15, 2020.
Sec. 63.6(f)(2)-(3).......... Methods for ................. Yes..............
Determining
Compliance.
Sec. 63.6(g)................. Use of an ................. Yes..............
Alternative
Standard.
Sec. 63.6(h)................. Opacity/Visible ................. No............... Subpart GGGG has no
emission (VE) opacity or VE
standards. standards.
Sec. 63.6(i)................. Compliance Procedures and Yes..............
extension. criteria for
responsible
agency to grant
compliance
extension.
Sec. 63.6(j)................. Presidential President may Yes..............
compliance exempt source
exemption. category from
requirement to
comply with
subpart.
Sec. 63.7(e)(1).............. Performance Representative Yes, before See Sec.
testing conditions for September 15, 63.2853(a)(5)(i)(A)
requirements. performance test. 2020. No, on or for performance
after September testing requirements.
15, 2020.
Sec. 63.7(e)(2)-(4), (f), Performance Schedule, Yes.............. Subpart GGGG requires
(g), and (h). testing conditions, performance testing
requirements. notifications only if the source
and procedures. applies additional
control that destroys
solvent. Section
63.2850(a)(6)
requires sources to
follow the
performance testing
guidelines of the
General Provisions if
a control is added.
Sec. 63.8.................... Monitoring ................. No............... Subpart GGGG does not
requirements. require monitoring
other than as
specified therein.
Sec. 63.9.................... Notification Applicability and Yes.............. Except for subsections
requirements. state delegation. of Sec. 63.9 as
listed below.
Sec. 63.9(b)(2).............. Notification Initial No............... Section 63.2860(a) of
requirements. notification subpart GGGG
requirements for specifies the
existing sources. requirements of the
initial notification
for existing sources.
Sec. 63.9(b)(3)-(5).......... Notification Notification Yes.............. Except the information
requirements. requirement for requirements differ
certain new/ as described in Sec.
reconstructed 63.2860(b) of
sources. subpart GGGG.
Sec. 63.9(e)................. Notification of Notify Yes.............. Applies only if
performance test. responsible performance testing
agency 60 days is performed.
ahead.
Sec. 63.9(f)................. Notification of Notify No............... Subpart GGGG has no
VE/opacity responsible opacity or VE
observations. agency 30 days standards.
ahead.
Sec. 63.9(g)................. Additional Notification of No............... Subpart GGGG has no
notifications performance CMS requirements.
when using a evaluation;
continuous Notification
monitoring using COMS data;
system (CMS). notification
that exceeded
criterion for
relative
accuracy.
[[Page 15635]]
Sec. 63.9(h)................. Notification of Contents......... No............... Section 63.2860(d) of
compliance subpart GGGG
status. specifies
requirements for the
notification of
compliance status.
Sec. 63.10................... Recordkeeping/ Schedule for Yes.............. Except for subsections
reporting. reporting, of Sec. 63.10 as
record storage. listed below.
Sec. 63.10(b)(2)(i).......... Recordkeeping.... Record SSM event. Yes, before Before September 15,
September 15, 2020, applicable to
2020. No, on or periods when sources
after September must implement their
15, 2020. SSM plan as specified
in subpart GGGG. On
or after September
15, 2020, meet the
requirements of Sec.
63.2862(f).
Sec. 63.10(b)(2)(ii)-(iii)... Recordkeeping.... Malfunction of No............... Before September 15,
air pollution 2020, applies only if
equipment. air pollution control
equipment has been
added to the process
and is necessary for
the source to meet
the emission limit.
On or after September
15, 2020, meet the
requirements of Sec.
63.2862(g).
Sec. 63.10(b)(2)(iv)-(v)..... Recordkeeping.... SSM recordkeeping Yes, before
September 15,
2020. No, on or
after September
15, 2020.
Sec. 63.10(b)(2)(vi)......... Recordkeeping.... CMS recordkeeping No............... Subpart GGGG has no
CMS requirements.
Sec. 63.10(b)(2)(viii)-(ix).. Recordkeeping.... Conditions of Yes.............. Applies only if
performance test. performance tests are
performed. Subpart
GGGG does not have
any CMS opacity or VE
observation
requirements.
Sec. 63.10(b)(2)(x)-(xii).... Recordkeeping.... CMS, performance No............... Subpart GGGG does not
testing, and require CMS.
opacity and VE
observations
recordkeeping.
Sec. 63.10(c)................ Recordkeeping.... Additional CMS No............... Subpart GGGG does not
recordkeeping. require CMS.
Sec. 63.10(d)(2)............. Reporting........ Reporting Yes.............. Applies only if
performance test performance testing
results. is performed.
Sec. 63.10(d)(3)............. Reporting........ Reporting opacity No............... Subpart GGGG has no
or VE opacity or VE
observations. standards.
Sec. 63.10(d)(4)............. Reporting........ Progress reports. Yes.............. Applies only if a
condition of
compliance extension
exists.
Sec. 63.10(d)(5)............. Reporting........ SSM reporting.... No............... Section 63.2861(c) and
(d) specify SSM
reporting
requirements.
Sec. 63.10(e)................ Reporting........ Additional CMS No............... Subpart GGGG does not
reports. require CMS.
Sec. 63.11................... Control device Requirements for Yes.............. Applies only if your
requirements. flares. source uses a flare
to control solvent
emissions. Subpart
GGGG does not require
flares.
Sec. 63.12................... State authority State authority Yes..............
and delegations. to enforce
standards.
Sec. 63.13................... State/regional Addresses where Yes..............
addresses. reports,
notifications,
and requests are
sent.
Sec. 63.14................... Incorporation by Test methods Yes..............
reference. incorporated by
reference.
Sec. 63.15................... Availability of Public and Yes..............
information and confidential
confidentiality. information.
----------------------------------------------------------------------------------------------------------------
0
12. Section 63.2872 is amended in paragraph (c) by:
0
a. Revising the definitions for ``Compliance ratio'', ``Hazardous air
pollutant (HAP)'', ``Initial startup period'', and ``Malfunction
period'';
0
b. Adding a definition in alphabetical order for ``Nonoperating
month''; and
0
c. Revising the definitions of ``Normal operating period'' and
``Operating month''.
The revisions and addition read as follows:
Sec. 63.2872 What definitions apply to this subpart?
* * * * *
[[Page 15636]]
Compliance ratio means a ratio of the actual HAP loss in gallons
from the previous 12 operating months to an allowable HAP loss in
gallons, which is determined by using oilseed solvent loss factors in
Table 1 of Sec. 63.2840, the weighted average volume fraction of HAP
in solvent received for the previous 12 operating months, and the tons
of each type of listed oilseed processed in the previous 12 operating
months. Months during which no listed oilseed is processed, or months
during which the Sec. 63.2850(c)(2) or (d)(2) initial startup period
or, before September 15, 2020, the Sec. 63.2850(e)(2) malfunction
period applies, are excluded from this calculation. Equation 2 of Sec.
63.2840 is used to calculate this value. If the value is less than or
equal to 1.00, the source is in compliance. If the value is greater
than 1.00, the source is deviating from compliance.
* * * * *
Hazardous air pollutant (HAP) means any substance or mixture of
substances listed as a hazardous air pollutant under section 112(b) of
the Clean Air Act.
* * * * *
Initial startup period means a period of time from the initial
startup date of a new, reconstructed, or significantly modified source,
for which you choose to operate the source under an initial startup
period subject to Sec. 63.2850(c)(2) or (d)(2), until the date your
source operates for 15 consecutive days at or above 90 percent of the
nominal design rate of the extractor or at or above 90 percent of the
permitted production rate for your source. The initial startup period
following initial startup of a new or reconstructed source may not
exceed 6 calendar months. The initial startup period following a
significant modification may not exceed 3 calendar months. Solvent and
oilseed inventory information recorded during the initial startup
period is excluded from use in any compliance ratio determinations.
* * * * *
Malfunction period means a period of time between the beginning and
end of a process malfunction and the time reasonably necessary for a
source to correct the malfunction for which you choose to operate the
source under a malfunction period subject to Sec. 63.2850(e)(2). This
period may include the duration of an unscheduled process shutdown,
continued operation during a malfunction, or the subsequent process
startup after a shutdown resulting from a malfunction. During a
malfunction period, a source complies with the standards by minimizing
HAP emissions to the extent practicable. Therefore, solvent and oilseed
inventory information recorded during a malfunction period is excluded
from use in any compliance ratio determinations.
* * * * *
Nonoperating month means any entire calendar or accounting month in
which a source processes no agricultural product.
Nonoperating period means any period of time in which a source
processes no agricultural product. This operating status does not apply
during any period in which the source operates under an initial startup
period as described in Sec. 63.2850(c)(2) or (d)(2), or, before
September 15, 2020, a malfunction period as described in Sec.
63.2850(e)(2).
Normal operating period or normal operation means any period of
time in which a source processes a listed oilseed that is not
categorized as an initial startup period as described in Sec.
63.2850(c)(2) or (d)(2), or, before September 15, 2020, a malfunction
period as described in Sec. 63.2850(e)(2). At the beginning and ending
dates of a normal operating period, solvent and oilseed inventory
information is recorded and included in the compliance ratio
determination.
* * * * *
Operating month means any calendar or accounting month in which a
source processes any quantity of listed oilseed, excluding any entire
calendar or accounting month in which the source operated under an
initial startup period as described in Sec. 63.2850(c)(2) or (d)(2),
or, before September 15, 2020, a malfunction period as described in
Sec. 63.2850(e)(2). An operating month may include time intervals
characterized by several types of operating status. However, an
operating month must have at least one normal operating period.
* * * * *
[FR Doc. 2020-04459 Filed 3-17-20; 8:45 am]
BILLING CODE 6560-50-P