National Emission Standards for Hazardous Air Pollutants for Chemical Manufacturing Area Sources, 4522-4540 [2012-1610]
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Federal Register / Vol. 77, No. 19 / Monday, January 30, 2012 / Proposed Rules
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analysis will continue to apply for
required projects under 40 CFR 93.116
and 93.123(b) of the Transportation
Conformity Rule.
Weighing all the factors for an
insignificance finding, particularly the
minor contribution of mobile source
NOX and PM2.5, EPA has determined
that the NOX and PM2.5 contribution
from motor vehicles emissions to the
Annual PM2.5 pollution for the
Kentucky portion of the Area are
insignificant. EPA’s insignificance
finding should be considered and
specifically noted in the transportation
conformity documentation that is
prepared for this area.
The insignificance determination that
Kentucky submitted for the HuntingtonAshland Area was developed with
projected mobile source emissions
derived using the MOBILE6 motor
vehicle emissions model. EPA is
proposing to approve the inventory and
the insignificance determination
because this model was the most current
model available at the time Kentucky
was performing its analysis. However,
EPA has now issued an updated motor
vehicle emissions model known as
Motor Vehicle Emission Simulator or
MOVES. In its announcement of this
model, EPA established a two-year grace
period for continued use of MOBILE6
(extending to March 2, 2012), after
which states (other than California)
must use MOVES in conformity
determinations for transportation plans
and transportation improvement
programs.
V. Proposed Action
EPA is proposing to approve
Kentucky’s annual PM2.5 attainment
plan for the Kentucky portion of the
Huntington-Ashland Area. EPA has
determined that the SIP meets
applicable requirements of the CAA, as
described in the PM2.5 Implementation
Rule. Specifically, EPA is proposing to
approve Kentucky’s attainment
demonstration, including the RACM/
RACT analysis; RFP analysis, base-year
and attainment-year emissions
inventories; and, for transportation
conformity purposes, an insignificance
determination for PM2.5 and NOX for the
mobile source contribution to ambient
PM2.5 levels for the Commonwealth’s
portion of the Huntington-Ashland
Area. The requirement for a RFP plan is
satisfied because Kentucky
period, the maintenance plan will need to include
information to support a finding that on-road
emissions of NOX and direct PM2.5 continue to be
insignificant during the maintenance period. The
insignificance finding for the attainment
demonstration does not automatically continue to
apply to the maintenance plan.
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demonstrated attainment of the 1997
PM2.5 NAAQS in the Area by April
2010. Also, because EPA has
determined that the Area has attained
by the attainment date, the contingency
measures submitted by Kentucky are no
longer necessary for the HuntingtonAshland Area to meet RFP requirements
or to attain the annual PM2.5 NAAQS by
the attainment date.
VI. Statutory and Executive Order
Reviews
methods, under Executive Order 12898
(59 FR 7629, February 16, 1994).
In addition, this proposed rule does
not have tribal implications as specified
by Executive Order 13175 (65 FR 67249,
November 9, 2000), because the SIP is
not approved to apply in Indian country
located in the Commonwealth, and EPA
notes that it will not impose substantial
direct costs on tribal governments or
preempt tribal law.
List of Subjects
Under the CAA, the Administrator is
required to approve a SIP submission
that complies with the provisions of the
Act and applicable federal regulations.
42 U.S.C. 7410(k); 40 CFR 52.02(a).
Thus, in reviewing SIP submissions,
EPA’s role is to approve state choices,
provided that they meet the criteria of
the CAA. Accordingly, this proposed
action merely approves state law as
meeting federal requirements and does
not impose additional requirements
beyond those imposed by state law. For
that reason, this proposed action:
• Is not a ‘‘significant regulatory
action’’ subject to review by the Office
of Management and Budget under
Executive Order 12866 (58 FR 51735,
October 4, 1993);
• Does not impose an information
collection burden under the provisions
of the Paperwork Reduction Act (44
U.S.C. 3501 et seq.);
• Is certified as not having a
significant economic impact on a
substantial number of small entities
under the Regulatory Flexibility Act (5
U.S.C. 601 et seq.);
• Does not contain any unfunded
mandate or significantly or uniquely
affect small governments, as described
in the Unfunded Mandates Reform Act
of 1995 (Pub. L. 104–4);
• Does not have Federalism
implications as specified in Executive
Order 13132 (64 FR 43255, August 10,
1999);
• Is not an economically significant
regulatory action based on health or
safety risks subject to Executive Order
13045 (62 FR 19885, April 23, 1997);
• Is not a significant regulatory action
subject to Executive Order 13211 (66 FR
28355, May 22, 2001);
• Is not subject to requirements of
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (15 U.S.C. 272 note) because
application of those requirements would
be inconsistent with the CAA; and
• Does not provide EPA with the
discretionary authority to address, as
appropriate, disproportionate human
health or environmental effects, using
practicable and legally permissible
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40 CFR Part 52
Environmental protection, Air
pollution control, Intergovernmental
relations, Reporting and recordkeeping
requirements, Particulate matter.
40 CFR Part 81
Environmental protection, Air
pollution control.
Authority: 42 U.S.C. 7401 et seq.
Dated: January 20, 2012.
A. Stanley Meiburg,
Acting Regional Administrator, Region 4.
[FR Doc. 2012–1938 Filed 1–27–12; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 63
[EPA–HQ–OAR–2008–0334; FRL–9621–7]
RIN 2060–AQ89
National Emission Standards for
Hazardous Air Pollutants for Chemical
Manufacturing Area Sources
Environmental Protection
Agency (EPA).
ACTION: Proposed rule; notice of
reconsideration of final rule.
AGENCY:
On October 29, 2009, the EPA
promulgated national emission
standards for the control of hazardous
air pollutants for nine area source
categories in the chemical
manufacturing sector: Agricultural
Chemicals and Pesticides
Manufacturing, Cyclic Crude and
Intermediate Production, Industrial
Inorganic Chemical Manufacturing,
Industrial Organic Chemical
Manufacturing, Inorganic Pigments
Manufacturing, Miscellaneous Organic
Chemical Manufacturing, Plastic
Materials and Resins Manufacturing,
Pharmaceutical Production and
Synthetic Rubber Manufacturing.
Following that action, the Administrator
received a petition for reconsideration.
In response to the petition, the EPA is
reconsidering and requesting comment
SUMMARY:
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Federal Register / Vol. 77, No. 19 / Monday, January 30, 2012 / Proposed Rules
on several provisions of the final rule.
The EPA is also proposing certain
revisions to its approach for addressing
malfunctions and taking comment on
those revisions. The EPA is further
soliciting comment on the standards
applicable during startup and shutdown
periods, as set forth in the final rule.
Additionally, the EPA is proposing
amendments and technical corrections
to the final rule to clarify applicability
and compliance issues raised by
stakeholders subject to the final rule.
DATES: Comments. Comments must be
received on or before March 30, 2012.
Public Hearing. If anyone contacts
EPA requesting to speak at a public
hearing by February 9, 2012, a public
hearing will be held on February 14,
2012. For further information on the
public hearing and requests to speak,
contact Ms. Janet Eck at (919) 541–7946
to verify that a hearing will be held. If
a public hearing is held, it will be held
at 10 a.m. at the EPA’s Environmental
Research Center Auditorium, Research
Triangle Park, North Carolina, or an
alternate site nearby.
ADDRESSES: Submit your comments,
identified by Docket ID No. EPA–HQ–
OAR–2008–0334, by one of the
following methods:
• www.regulations.gov: Follow the
on-line instructions for submitting
comments.
• Email: a-and-r-Docket@epa.gov,
Attention Docket ID No. EPA–HQ–
OAR–2008–0334.
• Fax: (202) 566–9744, Attention
Docket ID No. EPA–HQ–OAR–2008–
0334.
• Mail: U.S. Postal Service, send
comments to: Air and Radiation Docket
and Information Center, Environmental
Protection Agency, Mailcode: 2822T,
1200 Pennsylvania Ave., NW.,
Washington, DC 20460, Attention
Docket ID No. EPA–HQ–OAR–2008–
0334.
• Hand Delivery: In person or by
courier, deliver comments to: EPA
Docket Center (2822T), Room 3334,
1301 Constitution Ave., NW.,
Washington, DC 20004. Such deliveries
are only accepted during the Docket’s
normal hours of operation, and special
arrangements should be made for
deliveries of boxed information.
Instructions: Direct your comments to
Docket ID No. EPA–HQ–OAR–2008–
0334. The EPA’s policy is that all
comments received will be included in
the public docket without change and
may be made available online at
www.regulations.gov, including any
personal information provided, unless
the comment includes information
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claimed to be confidential business
information (CBI) or other information
whose disclosure is restricted by statute.
Do not submit information that you
consider to be CBI or otherwise
protected through www.regulations.gov
or email. The www.regulations.gov Web
site is an ‘‘anonymous access’’ system,
which means the EPA will not know
your identity or contact information
unless you provide it in the body of
your comment. If you send an email
comment directly to the EPA without
going through www.regulations.gov,
your email address will be
automatically captured and included as
part of the comment that is placed in the
public docket and made available on the
Internet. If you submit an electronic
comment, the EPA recommends that
you include your name and other
contact information in the body of your
comment and with any disk or CD–ROM
you submit. If the EPA cannot read your
comment due to technical difficulties
and cannot contact you for clarification,
the EPA may not be able to consider
your comment. Electronic files should
avoid the use of special characters, any
form of encryption and be free of any
defects or viruses. For additional
information about the EPA’s public
docket, visit the EPA Docket Center
homepage at https://www.epa.gov/
epahome/dockets.htm.
Docket: All documents in the docket
are listed in the www.regulations.gov
index. Although listed in the index,
some information is not publicly
available, e.g., CBI or other information
whose disclosure is restricted by statute.
Certain other material, such as
copyrighted material, will be publicly
available only in hard copy. Publicly
available docket materials are available
either electronically in
www.regulations.gov or in hard copy at
the EPA Docket Center, EPA West
Building, Room 3334, 1301 Constitution
Ave., NW., Washington, DC. The Public
Reading Room is open from 8:30 a.m. to
4:30 p.m., Monday through Friday,
excluding legal holidays. The telephone
number for the Public Reading Room is
(202) 566–1744, and the telephone
number for the Docket Center is (202)
566–1742.
Mr.
Nick Parsons, Refining and Chemicals
Group (E143–01), Sector Policies and
Programs Division, Office of Air Quality
Planning and Standards, Environmental
Protection Agency, Research Triangle
Park, North Carolina 27711; telephone
number: (919) 541–5372; fax number:
(919) 541–0246; email address:
parsons.nick@epa.gov.
FOR FURTHER INFORMATION CONTACT:
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SUPPLEMENTARY INFORMATION:
Organization of this Document. The
following outline is provided to aid in
locating information in this preamble.
I. General Information
A. Does this notice of reconsideration
apply to me?
B. What should I consider as I prepare my
comments to the EPA?
C. How do I obtain a copy of this document
and other related information?
II. Background Information
III. Actions We Are Taking
IV. Discussion of Issues for Reconsideration
A. Title V Permitting Requirements
B. Requirements When Other Rules
Overlap With the Final Rule
C. Requirement To Conduct Direct and
Proximal Leak Inspections
D. Requirement for Covers or Lids on
Process Vessels
E. Requirement To Conduct Leak
Inspections When Equipment Is in HAP
Service
F. Applicability of the Family of Materials
Concept
V. Requirements During Periods of Startup,
Shutdown and Malfunctions (SSM)
VI. Requirements for Metal HAP Process
Vents
A. Definition of Metal HAP Process Vent
B. Metal HAP Process Vent Standards
VII. Technical Corrections and Clarifications
VIII. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory
Planning and Review and Executive
Order 13563: Improving Regulation and
Regulatory Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
G. Executive Order 13045: Protection of
Children From Environmental Health
Risks and Safety Risks
H. Executive Order 13211: Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use
I. National Technology Transfer and
Advancement Act
J. Executive Order 12898: Federal Actions
to Address Environmental Justice in
Minority Populations and Low-Income
Populations
A red-line version of the regulatory
language that incorporates the changes
in this action is available in the docket.
I. General Information
A. Does this notice of reconsideration
apply to me?
The regulated categories and entities
potentially affected by this action
include:
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Industry category
NAICS
Code 1
Chemical Manufacturing ...
325
Examples of regulated entities
Chemical manufacturing area sources that use as feedstock, generate as byproduct or produce as product, any of the hazardous air pollutants (HAP) subject to this subpart except for: (1) Processes classified in NAICS Code 325222, 325314 or 325413; (2) processes subject to standards for other listed
area source categories2 in NAICS Code 325; (3) certain fabricating operations; (4) manufacture of
photographic film, paper and plate where material is coated or contains chemicals (but the manufacture of the photographic chemicals is regulated); and (5) manufacture of radioactive elements or isotopes, radium chloride, radium luminous compounds, strontium and uranium.
1 North
American Industry Classification System.
source categories in NAICS Code 325 for which other area source standards apply are: Acrylic Fibers/Modacrylic Fibers Production,
Chemical Preparation, Carbon Black, Chemical Manufacturing: Chromium Compounds, Polyvinyl Chloride and Copolymers Production, Paint and
Allied Coatings and Mercury Cell Chlor-Alkali Manufacturing.
2 The
This table is not intended to be
exhaustive, but rather provides a guide
for readers regarding entities likely to be
regulated by this reconsideration action.
To determine whether your facility may
be affected by this reconsideration
action, you should examine the
applicability criteria in 40 CFR 63.11494
of subpart VVVVVV (National Emission
Standards for Hazardous Air Pollutants
for Chemical Manufacturing Area
Sources). If you have any questions
regarding the applicability of the final
rule to a particular entity, consult either
the air permit authority for the entity or
your EPA regional representative, as
listed in 40 CFR 63.13.
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B. What should I consider as I prepare
my comments to the EPA?
Submitting CBI. Do not submit
information that you consider to be CBI
electronically through https://
www.regulations.gov or email. Send or
deliver information identified as CBI to
only the following address: Mr. Nick
Parsons, c/o OAQPS Document Control
Officer (Room C404–02), U.S.
Environmental Protection Agency,
Research Triangle Park, North Carolina
27711, Attn: Docket ID No. EPA–HQ–
OAR–2008–0334.
Clearly mark the part or all of the
information that you claim to be CBI.
For CBI information in a disk or CD–
ROM that you mail to the EPA, mark the
outside of the disk or CD–ROM as CBI
and then identify electronically within
the disk or CD–ROM the specific
information that is claimed as CBI. In
addition to one complete version of the
comment that includes information
claimed as CBI, a copy of the comment
that does not contain the information
claimed as CBI must be submitted for
inclusion in the public docket. If you
submit a disk or CD–ROM that does not
contain CBI, mark the outside of the
disk or CD–ROM clearly that it does not
contain CBI. Information marked as CBI
will not be disclosed except in
accordance with procedures set forth in
40 CFR part 2.
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If you have any questions about CBI
or the procedures for claiming CBI,
please consult the person identified in
the FOR FURTHER INFORMATION CONTACT
section.
C. How do I obtain a copy of this
document and other related
information?
Docket. The docket number for this
action and the final rule (40 CFR part
63, subpart VVVVVV) is Docket ID No.
EPA–HQ–OAR–2008–0334.
World Wide Web (WWW). In addition
to being available in the docket, an
electronic copy of this action is
available on the WWW through the
Technology Transfer Network (TTN)
Web site. Following signature, a copy of
this notice will be posted on the TTN’s
policy and guidance page for newly
proposed or promulgated rules at
https://www.epa.gov/ttn/oarpg. The TTN
provides information and technology
exchange in various areas of air
pollution control.
II. Background Information
Section 112(d) of the Clean Air Act
(CAA) requires the EPA to establish
national emission standards for
hazardous air pollutants (NESHAP) for
both major and area sources of HAP that
are listed for regulation under CAA
section 112(c). A major source is any
stationary source that emits or has the
potential to emit 10 tons per year (tpy)
or more of any single HAP or 25 tpy or
more of any combination of HAP. An
area source is a stationary source that is
not a major source.
On October 29, 2009 (74 FR 56008),
the EPA issued the NESHAP for the
nine chemical manufacturing area
source (CMAS) categories that were
listed pursuant to CAA sections
112(c)(3) and 112(k)(3)(B). The nine area
source categories are Agricultural
Chemicals and Pesticides
Manufacturing, Cyclic Crude and
Intermediate Production, Industrial
Inorganic Chemical Manufacturing,
Industrial Organic Chemical
Manufacturing, Inorganic Pigments
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Manufacturing, Miscellaneous Organic
Chemical Manufacturing, Plastic
Materials and Resins Manufacturing,
Pharmaceutical Production and
Synthetic Rubber Manufacturing.
CAA section 112(k)(3)(B) directs the
EPA to identify at least 30 HAP that, as
a result of emissions from area sources,
pose the greatest threat to public health
in the largest number of urban areas.
The EPA implemented this provision in
1999 in the Integrated Urban Air Toxics
Strategy, (64 FR 38715, July 19, 1999)
(Strategy). Specifically, in the Strategy,
the EPA identified 30 HAP that pose the
greatest potential health threat in urban
areas, and these HAP are referred to as
the ‘‘30 urban HAP.’’ Section 112(c)(3)
of the CAA requires the EPA to list
sufficient categories or subcategories of
area sources to ensure that area sources
representing 90 percent of the emissions
of the 30 urban HAP are subject to
regulation. The EPA completed this
requirement in 2011 (76 FR 15308,
March 21, 2011). The chemical
manufacturing area source categories
were listed to satisfy this requirement
for 15 of the 30 urban HAP.1 Pursuant
to CAA section 112(d)(5), the NESHAP
reflect generally available control
technologies or management practices
(GACT). The NESHAP apply to each
chemical manufacturing process unit
(CMPU) that uses, generates or produces
any of the 15 urban HAP for which the
area source categories were listed
(collectively ‘‘chemical manufacturing
urban HAP’’ or ‘‘Table 1 HAP’’).
On February 12, 2010, following
promulgation of the final rule, the EPA
received a petition for reconsideration
from the American Chemistry Council
(ACC) and the Society of Chemical
Manufacturers & Affiliates (SOCMA)
(‘‘Petitioners’’). A copy of this petition
is provided in the docket (see Docket ID
No. EPA–HQ–OAR–2008–0334).
Petitioners, pursuant to CAA section
307(d)(7)(B), requested that the EPA
1 The 15 urban HAP for which the chemical
manufacturing area source categories were listed are
identified in table 1 of the final rule.
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reconsider six provisions in the rules:
(1) The requirement that major sources
that installed air pollution controls after
1990, and, as a result, became area
sources, obtain a title V permit; (2) the
requirement that sources subject to the
final rule and any overlapping provision
in another rule comply with each
provision independently, or with the
most stringent requirements of each
rule; (3) the requirement that leak
inspections include direct and proximal
(thorough) inspection of all areas of
potential leak within the CMPU; (4) the
requirement that process vessels in HAP
service be equipped with a cover or lid
that must be in place at all times when
the vessel contains HAP, except for
material addition and sampling; (5) the
requirement to conduct leak inspections
while the equipment is in HAP service;
and (6) the requirement that a CMPU
include all equipment and processes
used to produce a ‘‘family of materials.’’
The arguments in support of these
requests are provided in the petition
and described briefly below. Petitioners
also requested that the EPA stay the
effectiveness of these provisions of the
rule to save many facilities from
needlessly having to file the initial
notifications required by the final rule.
On June 15, 2010, the EPA sent a
letter to Petitioners informing them that
the EPA was granting the request for
reconsideration on at least one issue
raised in the petition, and that the
agency would identify the specific issue
or issues for which it was granting
reconsideration in the reconsideration
notice that would be published in the
Federal Register. The letter also
indicated that the EPA considered the
request for a stay to be moot because the
due date for initial notifications had
already passed.
III. Actions We Are Taking
In this notice, we are granting
reconsideration of, and requesting
comment on, the six issues raised by
Petitioners in their petition for
reconsideration. Section IV of this
preamble summarizes these issues and
discusses our proposed responses to
each issue.
We are also proposing additional
provisions related to malfunctions and
requesting comment on the provisions
in the final rule that address periods of
startup and shutdown. We are also
proposing amendments to, and taking
comment on, the standards applicable to
metal HAP process vents. Finally, we
are proposing technical corrections to
certain applicability and compliance
provisions in the final rule.
We are seeking public comment only
on the issues specifically identified in
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this notice. We will not respond to any
comments addressing other aspects of
the final rule or any other related
rulemakings.
IV. Discussion of Issues for
Reconsideration
This section of the preamble contains
the EPA’s basis for our proposed
responses to the issues identified in the
petition for reconsideration. We solicit
comment on all proposed responses and
revisions discussed in the following
sections.
A. Title V Permitting Requirements
The EPA proposed to exempt all
chemical manufacturing area sources
from the requirement to obtain a title V
permit. In the final rule, in response to
comments and after a full review of the
record, the EPA stated that it was not
finalizing the exemption for major
sources that became synthetic area
sources by installing air pollution
controls after 1990. Among other things,
the agency explained that we made the
change, in part, because we failed to
consider the large number of such
sources in proposing the exemption,
and because these sources had
uncontrolled emissions that made them
much more like major sources. See 74
FR 56013, October 29, 2009. Petitioners
maintain that the proposed exemption
of CMAS facilities from title V
permitting requirements was fully and
correctly justified in the preamble to the
proposed CMAS rule. The Petitioners
also claim:
• The EPA’s assertion in the final rule
that facilities that installed control
equipment to become synthetic area
sources are ‘‘generally larger and more
sophisticated’’ than other chemical
manufacturing area sources contradicts
our earlier finding in the proposed rule
that many of the facilities that would be
affected by the CMAS rule are small
entities without the resources to comply
with permitting requirements. The
Petitioners also state that approximately
87 percent of SOCMA members and 45
percent of ACC members are small
businesses, which they cite as support
for the proposed finding.
• The final rule fails to recognize that,
in order for a facility to be treated as a
synthetic area source due to the
installation of controls, the facility has
a legal duty to use the equipment
because the control requirement must be
federally enforceable. Further, the
Petitioners state that, ‘‘In order to have
been approved by the EPA, a state
operating permit program that imposes
a federally enforceable requirement to
use control equipment must provide the
public with notice and an opportunity
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to comment on draft permits * * * and
must also provide for emissions
reporting and public availability of
reported information.’’
• The final rule is contrary to the
decision in Alabama Power Co. v. EPA,
which held that a source’s potential to
emit is determined by its design
capacity and the anticipated functioning
of the air pollution control equipment.
Thus, the petitioners claim that whether
a facility is a natural area source or a
synthetic area source (due to either
operational limits or the use of control
devices) should not matter for
regulatory purposes.
• The EPA argued in the area source
rules for asphalt processing/asphalt
roofing manufacturing, and paint and
allied products manufacturing, that
state-delegated programs are sufficient
to assure compliance, and that it is not
more difficult for citizens to enforce the
NESHAP absent a title V permit.
According to the Petitioners, these
statements are equally, if not more, true
for chemical manufacturing synthetic
area sources.
• Title V requirements will impose
substantial transactional and
compliance costs on subject facilities,
and limit their flexibility to respond to
market opportunities.
In conclusion, Petitioners suggest that
we should exempt all chemical
manufacturing area sources from the
requirement to obtain a title V permit
consistent with the proposed rule. We
reviewed our rationale, as stated in the
preamble to the final rule (74 FR 56013–
56014) and summarized below, for the
final title V permitting requirement for
facilities that became synthetic area
sources by virtue of installing air
pollution control devices after 1990. We
continue to believe that requiring title V
for synthetic area sources that installed
controls to become area sources is
appropriate; therefore, we are not
proposing to exempt such sources from
the requirement to obtain a title V
permit. We are, however, making
changes to the applicability of the
provision at issue. Instead of requiring
a title V permit for all synthetic area
sources that installed air pollution
controls in order to become an area
source, regardless of whether the
controls were installed on an affected
CMPU, we are now proposing to only
require a title V permit for a synthetic
area source if air pollution controls were
installed on at least one CMPU subject
to the final rule in order to become an
area source. Such a limitation would be
consistent with the standards in the
final rule that are applicable only to the
CMPU that emit one of the chemical
manufacturing urban HAP. We are also
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proposing to add provisions that inform
sources when they must submit a title
V permit application consistent with the
title V regulations at 40 CFR part 70 and
40 CFR part 71.
Pursuant to section 502(a) of the CAA,
the Administrator may ‘‘exempt one or
more [area] source categories (in whole
or in part) from the requirements of
[title V] if the Administrator finds that
compliance with such requirements is
impracticable, infeasible, or
unnecessarily burdensome * * * .’’ In
December 2005, in a national
rulemaking, the EPA interpreted the
term ‘‘unnecessarily burdensome’’ in
CAA section 502, and developed a fourfactor balancing test for determining
whether title V is unnecessarily
burdensome for a particular area source
category, such that an exemption from
title V is appropriate. See 70 FR 75320,
December 19, 2005 (Exemption Rule).
The EPA evaluated the chemical
manufacturing area source categories
pursuant to the four-factor balancing
test in the proposed rule, and
determined that title V permitting was
unnecessarily burdensome. 73 FR
58371–58373. However, as stated above,
the EPA did not finalize the exemption
for synthetic area sources that became
area sources by installing air pollution
controls after November 15, 1990, in
part, because the agency failed to
consider the large number of such
sources in proposing the exemption. 74
FR 56013. We explained the reasons for
our oversight, and then concluded that
title V was not unnecessarily
burdensome and provided a reasoned
basis for that conclusion, as discussed
below. 74 FR 56013–56014.
In the preamble to the final rule, we
noted that the chemical manufacturing
area source categories are different from
other area source categories we have
exempted because the categories
include a large number of synthetic area
sources (major sources that installed air
pollution controls to become area
sources) and the sources in the other
categories generally have very low
emissions of HAP before control. We
then stated that at least 10 percent of the
estimated 75 facilities that are synthetic
area sources for HAP by virtue of
installing controls have uncontrolled
HAP emissions over 100 tpy. We also
indicated that our information showed
that many of the sources are located in
cities, and often in close proximity to
residential and commercial centers
where large numbers of people live and
work. We further stated that these
synthetic area sources have significantly
higher emissions potential when
uncontrolled than the other sources in
the chemical manufacturing area source
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categories, and that they are much more
like the major sources of HAP subject to
the Hazardous Organic Chemical
Manufacturing NESHAP (HON) and the
Miscellaneous Organic Chemical
Manufacturing NESHAP (MON). For
these reasons, and other reasons set
forth in the preamble to the final rule,
we determined that ‘‘requiring
additional public involvement and
compliance assurance requirements
through title V is important to ensure
that these sources are maintaining their
emissions at the area source level, and,
while there is some burden on the
affected facilities, we think that the
burden is not significant because these
facilities are generally larger and more
sophisticated than the natural area
sources and sources that took
operational limits to become area
sources.’’ 74 FR 56014.
Contrary to the Petitioners’ first
assertion, we do not believe that there
is a conflict between our finding that
many CMAS facilities are small entities
that lack the technical and financial
resources to comply with title V, and
our finding that CMAS facilities that are
synthetic area sources due to the use of
control devices are generally larger and
more sophisticated than other facilities
covered by the final rule. The fact that
nearly all SOCMA members are small
businesses does not, by itself, counter
these findings. As we stated in the
preamble to the final rule, an estimated
450 CMAS facilities have processes that
would be subject to the rule. Of those,
we estimated that 75 are synthetic area
sources by virtue of add-on controls,
and only 47 of these facilities were
estimated to need a new title V permit
because the remainder of the sources are
already subject to title V for other
reasons. Of the 47 sources that would
require a new title V permit under the
requirement in the final rule, we
estimated that at least two-thirds of
these facilities are large entities. Since
we do not know whether the add-on
controls at these 75 facilities are
installed on a CMPU subject to the final
rule, we cannot estimate the total
number of facilities that would be
required to obtain a new title V permit
under this proposed revision to the title
V permit requirement. However, we
believe that it would be less than the 47
facilities that would have required a
new title V permit under the final rule
requirement. Based on information from
SOCMA, approximately 270 member
companies are small businesses.
However, it is not clear how many of
these companies have facilities that are
subject to the CMAS rule, how many of
the subject facilities are synthetic area
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sources for HAP emissions due to the
use of control devices or how many of
the synthetic area sources for HAP
emissions are subject to title V
permitting requirements for other
reasons. The information provided by
Petitioner ACC is similarly vague on
this issue.
The Petitioners also argue that the
title V requirement is not appropriate
because: (1) State operating permits that
impose a federally enforceable
requirement must provide the public
with notice and the opportunity to
comment on the draft permit; (2)
synthetic area source limits must be
federally enforceable pursuant to the
definition of ‘‘potential to emit’’ at 40
CFR 63.2, and that it should not matter
whether an area source is synthetic or
natural; (3) the EPA has determined in
other area source rules that statedelegated programs and Federal
enforceability of the standards is
sufficient, and that determination is
equally applicable to the area sources
subject to title V in this rule; and (4) the
requirement to obtain a title V permit
will impose substantial compliance
costs and reduce flexibility at the
subject facilities. We are not proposing
changes to the title V permitting
requirement based on these arguments
because we do not believe that they
support a change in our position. First,
while it is true that the EPA regulations
require Federal enforceability of
limitations on potential to emit HAP,
Petitioners did not provide any
information as to the level of public
participation required to obtain such
limits and whether the level of
participation was as comprehensive as
that required pursuant to title V. Even
if Petitioners could demonstrate that the
level of public participation was
comparable to that required under title
V, our determination would not be
altered on that issue alone because title
V has other important requirements that
may not apply to synthetic area sources
that are not subject to title V (e.g., the
requirement to annually certify
compliance with all applicable
requirements). Second, the EPA
disagrees that natural and synthetic area
sources must be treated the same. As
stated in the preamble to the final rule,
‘‘[synthetic area source] facilities are
generally larger and more sophisticated
than the natural area sources and
sources that took operational limits to
become area sources’’ (74 FR 56014).
Third, we explained in the preamble to
the final rule that the chemical
manufacturing area sources are not
similar to other area source categories
that we have exempted because of the
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large number of synthetic area sources
that installed add-on controls and the
high volume of pre-control device HAP
emissions from the chemical
manufacturing area sources that added
controls as compared with other area
sources. As these synthetic area sources
have essentially the same pre-control
device HAP emissions potential as a
major source chemical manufacturing
facility, we believe that the title V
permit requirement will help ensure
that these control devices remain in
place and that these sources maintain
their area source status. Since it is
possible that the non-operation, failure
or underperformance of a single control
device could result in a source within
this category exceeding the major source
emission threshold (10 tpy or more of
any single HAP or 25 tpy or more of any
combination of HAP), we believe that
the additional scrutiny that permitting
authorities place on sources with title V
permits is warranted. Finally,
Petitioners have provided no
information that demonstrates that the
cost of compliance for affected facilities
will, in fact, significantly burden the
sources subject to the title V
requirement, or that such requirement
will limit operational flexibility. We
request comments and information that
address these issues, including
information and requirements that are
required by state operating permit
programs, so that we can more
thoroughly evaluate applicability of title
V for the identified sources.
As stated above, we are proposing
changes to the applicability of the title
V permit requirement to synthetic area
sources that installed controls. The
proposed changes more clearly identify
the sources subject to title V as those
that route (or have routed) emissions
from at least one process unit subject to
the final rule to a control device(s) that
is required to maintain synthetic area
source status at the facility, which will
likely reduce the number of sources
required to obtain a title V permit, if
promulgated. Specifically, because the
standards apply only to CMPU that meet
the specific applicability criteria in the
rule, we request comment on whether
the title V permitting requirement
should be applicable only if one or more
of the CMPU that are subject to the final
standards are controlled by the air
pollution control equipment necessary
for the facility to maintain area source
status. We are also proposing to include
language that informs sources subject to
title V requirements when they must
submit a title V permit application. The
EPA is including these new provisions
because, on March 14, 2011, the agency
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issued a final rule staying the
requirement to obtain a title V permit
until the final reconsideration rule is
published in the Federal Register. 76 FR
13514. Because the stay will be lifted
once the final rule is published in the
Federal Register, we determined it was
necessary to include an application
deadline for those existing sources
currently subject to the final rule to
avoid confusion as to when title V
permit applications would be due. The
proposed application deadline for
existing sources provides the full 12
months otherwise available to sources
newly subject to title V pursuant to the
EPA regulations at 40 CFR part 70 and
40 CFR part 71. See 40 CFR 70.5(a)(1)
and 40 CFR 71.5(a)(1). We also propose
to include a provision indicating the
time available for new sources and
existing sources that become subject to
the rule after the effective date to submit
a title V permit application.2 We solicit
comment on these proposed changes to
the final rule.
Additionally, we are soliciting
comment on the promulgated final rule
requirement that required a facility to
obtain a title V permit if emissions from
any process unit are (or have been)
routed to the control device(s) that is
required to maintain synthetic area
source status at the facility.
We are requesting comment with
supporting rationale on the requirement,
as specified in this proposed rule and
the promulgated final rule requirement
outlined above. We are also interested
in information that would allow us to
better estimate the burden under the
requirement in this proposed rule and
the alternative. For example, we are
interested in results of any surveys that
document: (1) The percentage and/or
number of CMAS facilities that are
synthetic area sources for HAP
emissions because they use federallyenforceable control devices; (2) the
percentage and/or number of such
facilities that are using the control
devices to control emissions from at
least one CMAS CMPU; (3) the financial
burden of obtaining a title V permit
compared to sales; and (4) the
percentage and/or number of such
facilities that are not already subject to
title V requirements for other reasons.
We are not taking comment on our
decision in the final rule to exempt from
2 Existing sources may become subject to the
NESHAP for CMAS after the effective date of the
standards because the final rule bases applicability
on the use of chemical manufacturing urban HAP
(Table 1 HAP) in a CMPU. 40 CFR 63.11494. If a
source begins using a Table 1 HAP after the
effective date, the facility will be subject to the
CMAS standards, and, if the source is a synthetic
area source that installed controls, the source will
be subject to title V.
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4527
title V chemical manufacturing areas
sources that are natural area sources or
that took operational limits to become
area sources.
B. Requirements When Other Rules
Overlap With the Final Rule
Petitioners note that their comments
on the proposed rule urged the EPA to
include provisions in the final rule that
would minimize the burden associated
with overlapping provisions between
the CMAS rule and other rules.
Specifically, they recommended that the
CMAS rule include provisions to allow
a facility subject to the CMAS rule and
any other applicable area or major
source rule to opt to comply with either,
and noted that such an approach has
been taken in many other rules. In
response to those comments, we added
provisions to address overlapping
requirements in the final rule. See 40
CFR 63.11500. However, Petitioners
consider the overlapping rule
requirements in the final rule, which
specify that a facility may elect to
comply with the most stringent
provisions of the applicable rules as an
alternative to complying fully with each
rule independently, to be
‘‘unprecedented, burdensome, and
highly problematic.’’ According to the
Petitioners, concerns with the
alternative are that: (1) There can be
uncertainty regarding which provision
is more stringent; (2) facilities will be at
risk that the EPA or a delegated
authority will subsequently disagree
with the source’s determination; and (3)
the effort necessary to construct a matrix
of applicable requirements and
determine which are the most stringent
will exceed available staff and financial
resources of many area sources. In
addition, Petitioners state that
complying in every respect with two
overlapping rules is bound to involve
substantial duplication, and, in some
cases, may not be possible due to
conflicts between the two rules. For
these reasons, Petitioners recommend
that we either propose to eliminate the
final language or request comment on it.
We disagree with the Petitioners’
assertion that the requirements in the
final rule are unprecedented and
procedurally invalid. In the absence of
the language in the final rule, a facility
would be required to comply with all
applicable requirements in both the
CMAS rule and all other applicable
rules, regardless of whether some
equipment is subject to more than one
rule. The final CMAS rule merely made
explicit the implicit requirement to
comply with all applicable standards. It
was in response to Petitioners’
comments that the agency provided an
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overlapping requirements alternative
that allows a facility to identify and
comply with only one set of
requirements (i.e., the most stringent
requirements in the overlapping rules).
The alternative was intended as a means
of reducing the compliance burden
without diminishing the level of
environmental protection provided by
each rule.
We did not include language that
defines the more stringent requirements,
as found in other rules, due to the great
variety in characteristics of CMAS
processes and the wide variety of
compliance options in both the CMAS
rule and overlapping rules. This variety
makes it difficult to develop language
that would not inadvertently allow a
CMAS facility to comply with
requirements less stringent than those
contained in 40 CFR part 63, subpart
VVVVVV, or less stringent than the
required control level in an overlapping
rule. Furthermore, as noted in the
economic and control cost impacts
analyses (see Docket ID No. EPA–HQ–
OAR–2008–0334–0079), we expect that
most CMAS facilities will be subject to
only the management practices in
subpart VVVVVV. For those sources, we
anticipate that it generally will not be
difficult or burdensome to determine
which requirements in subpart
VVVVVV and an overlapping rule are
the most stringent. For those sources
that are unable to determine the more
stringent requirement between subpart
VVVVVV and an overlapping
requirement, we believe it would be
more appropriate to address those
situations on a case-by-case basis.
We are granting reconsideration of the
overlapping provisions requirement in
40 CFR 63.11500 of the final rule to
allow comment on both the language in
the final rule and any alternative
suggestions. Specifically, we are
interested in language that would
reduce the compliance burden for the
CMAS rule and any overlapping rules
combined, yet assure that all
requirements in the CMAS rule are met.
We are also interested in specific
examples of requirements in
overlapping rules that conflict with
requirements in the CMAS final rule.
C. Requirement To Conduct Direct and
Proximal Leak Inspections
In the final rule, the EPA revised the
provision for inspections to require that
facilities conduct a ‘‘direct and proximal
(thorough) inspection of all areas of
potential leak within the CMPU.’’
Petitioners object to the requirement in
the final rule to conduct ‘‘direct and
proximal (thorough)’’ inspections
because they believe it requires
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inspections without regard to safety or
difficulty of access. Petitioners also note
that areas that are difficult to inspect or
unsafe to inspect or monitor are
exempted from regular inspection
requirements in other rules, and they
point out that, in their comments on the
proposed CMAS rule, they requested
clarification that sensory inspections
may be done from a distance when
equipment is either inaccessible or
unsafe for close visual inspection.
Therefore, Petitioners maintain that the
agency should either propose to
eliminate the direct and proximal
inspection requirement or request
comment on it.
We have determined that the
inspections required in the final rule
require control that is more stringent
than GACT because we are not aware of
any facility conducting direct and
proximal inspections of all process
vessels and equipment. For this reason,
and to address Petitioners’ concerns, we
are proposing to delete the requirement
for direct and proximal inspections.
However, we want to assure that
sensory inspections be performed at
distances such that the results are
meaningful.
As a result, we are proposing that the
amended rule would specify that a
facility must conduct quarterly sensory
inspections of all equipment and
process vessels, provided these methods
are capable of detecting leaks within the
CMPU (i.e., the inspector is within
sufficient proximity to the equipment
that leaking equipment can be detected
by sight, sound or smell). We are not,
however, proposing to exempt
equipment that is difficult or unsafe to
monitor. Rules that provide such
exemptions do so because they require
instrument monitoring that relies on
being able to locate the instrument
probe very close to the equipment being
inspected (e.g., see 40 CFR part 63,
subparts TT and UU). Sensory
monitoring does not require intimate
contact with each piece of equipment to
be effective at identifying leaks. In
addition, due to the wide variety of
design and operating conditions
throughout the source category, we also
are not proposing criteria regarding an
acceptable distance for inspection or the
types of conditions under which the
inspection may be conducted from a
distance. Our intent is that each facility
should conduct inspections as close as
practical to the equipment to be able to
detect leaks while also following
procedures contained in site-specific
safety plans. The proposed requirements
would be consistent with sensory
inspection requirements in 40 CFR part
63, subpart R. We request comment on
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both the direct and proximal language
in the final rule and these proposed
revisions.
D. Requirement for Covers or Lids on
Process Vessels
We proposed to require process
vessels in HAP service be closed
‘‘except when operator access is
necessary.’’ 73 FR 58377 (proposed 40
CFR 63.11495(a)). The final rule
requires process vessels in HAP service
to be equipped with a cover or lid that
must be in place at all times when the
vessel contains HAP, ‘‘except for
material addition and sampling.’’ 40
CFR 63.11495(a)(1). Petitioners contend
that compliance with this management
practice requirement is impossible due
to safety issues and because it does not
consider the need to take material out of
a vessel or to conduct maintenance.
Petitioners are particularly concerned
that the requirement does not appear to
allow openings for any type of
maintenance, even after the process is
shut down, and only trace levels of HAP
are present. In subsequent
correspondence, Petitioners suggest that
their concerns would be resolved if we
modify the rule so that the cover or lid
requirement applies only when a
process vessel is ‘‘in use’’ (which is a
concept that they state can be easily
applied), and clarify that ‘‘in use’’ does
not include routine cleaning operations.
See Docket ID No. EPA–HQ–OAR–
2008–0334. Petitioners explain that the
exclusion for cleaning is needed
because the definition of a ‘‘chemical
manufacturing process’’ includes
routine cleaning operations, but vessels
must be opened for cleaning. Therefore,
the Petitioners state that we should
either propose changes that would
require the use of covers or lids only
when subject process vessels are in use,
or seek comments on the requirement as
written in the final rule.
We are granting reconsideration of the
requirement to use a cover or lid on
process vessels because the Petitioners
comments indicate that the requirement
can be interpreted as requiring control
more stringent than we intended. The
proposed rule specified that ‘‘all process
equipment in which organic HAP is
used to process material must be
covered when in use, and closure
mechanisms on other openings and
access points in process equipment
must be in the closed position during
operation, except when operator access
is necessary.’’ 73 FR 58377 (proposed 40
CFR 63.11495(a)). The intent of the
requirement for covers in the proposed
rule was to ensure that processes do not
operate with open-top vessels. The
purpose of the cover is to minimize
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emissions from surface evaporation, but
not necessarily to have a tight seal
between the cover and the vessel. For
the final rule, we tried to clarify what
‘‘in use’’ and ‘‘operator access’’ meant
by specifying that the cover (or lid)
‘‘must be in place at all times when the
vessel contains HAP, except for material
addition and sampling.’’ However, as
the Petitioners have pointed out, the
revised language can be interpreted as
prohibiting removal of the cover, even
when only traces of HAP remain in the
vessel after it has been drained, which
would prohibit opening to perform
maintenance or manual cleaning.
Requiring use of the cover in this way
is not GACT, and it was not our intent.
To address the Petitioners’ issues, we
are proposing to revise 40 CFR
63.11495(a)(1) in the final rule to read
as follows: ‘‘Each process vessel must be
equipped with a cover or lid that must
be closed whenever the vessel is in
organic HAP service or metal HAP
service, except for manual operations
that require access, such as material
addition and removal, inspection,
sampling, and cleaning.’’ We note that
allowing opening of a process vessel for
material removal clarifies that process
vessels, such as filter presses, may be
opened in order to remove the filter
cake.
The proposed change also would
exempt manual cleaning operations
from the requirement to maintain closed
covers and lids while a process vessel
is in organic HAP or metal HAP service.
As the Petitioners noted, the definition
of ‘‘chemical manufacturing process’’ is
drawn from the definition of a
‘‘miscellaneous organic chemical
manufacturing process’’ in 40 CFR
63.2550 of the MON. That definition
includes ‘‘routine cleaning operations,’’
which are described in the preamble to
the final MON as ‘‘cleaning conducted
within enclosed equipment between
batches or between campaigns.’’ The
MON preamble goes on to state that
these operations ‘‘often consist of
conducting solvent rinses through the
equipment,’’ and emissions are
characterized as part of the emissions
from a batch process vent. See 68 FR
63860, November 10, 2003. Contrary to
Petitioner’s assertion, this type of
cleaning was included as part of the
process specifically because we
considered the vessels to be ‘‘in use’’
while it is conducted. We also consider
vessels to be in use when manual
cleaning is performed. To clarify this
point, we are proposing to revise the
definition of ‘‘chemical manufacturing
process’’ to specify that all cleaning
activities are part of the process.
However, because GACT does not
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include the use of closed covers and lids
when performing manual cleaning, we
are proposing two additional changes.
First, we are proposing the change noted
above to exempt manual cleaning
operations from the requirement to
maintain covers and lids in the closed
position when the vessel is in organic
HAP service or metal HAP service.
Second, we are proposing to revise the
definition of ‘‘in organic HAP service’’
to specify that a process vessel is no
longer in organic HAP service after the
vessel has been emptied to the extent
practicable (i.e., a vessel with liquid left
on process vessel walls or as bottom
clingage, but not in pools, due to floor
irregularity, is considered completely
empty), and any cleaning has been
completed. We expect emissions to be
minimal during manual cleaning
operations and when a process vessel is
no longer in organic HAP service. We
are not proposing any changes to 40
CFR 63.11494(a)(1) regarding
maintenance activities because those
activities would be conducted after the
vessel has been drained (and possibly
cleaned) and the vessel would no longer
be in organic HAP service.
We request comments on both the
provisions, as specified in the final rule
and the proposed changes. Specifically,
we request comment on whether the
proposed changes effectively address
the issues raised by Petitioners, and
clarify the requirements without
introducing unintended consequences.
We also request comment on whether a
change like that proposed for the
definition of ‘‘in organic HAP service’’
is needed for the definition of ‘‘in metal
HAP service.’’ In particular, we request
comment on whether a change is
needed to address when vessels that
contain metal HAP in the form of
particulate are in use, and, if so, we
request information on the types of
vessels for which the change is needed
and recommendations on how the
language in the definition could be
structured. We are also requesting
comment on possible changes to the
requirements for cleaning that would
include requirements for manual
cleaning as well as for automated rinses
through closed equipment.
E. Requirement To Conduct Leak
Inspections When Equipment Is in HAP
Service
Petitioners state that ‘‘the final rule
can be read to imply that the equipment
must be in HAP service when the
inspection is conducted.’’ Petitioners
note that this is in contrast to the
proposed rule, which would have
required quarterly inspections without
specifying any other conditions.
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4529
Petitioners stated that they did not
comment on the proposed language
because they considered it to be
reasonable; however, Petitioners
contend that the apparent requirement
in the final rule is problematic because
batch processors who operate
equipment in HAP service for short
periods of time and have limited
operating personnel may find it difficult
to accomplish the required inspections
during these narrow windows of time.
Petitioners ask for clarification about
whether this interpretation is correct,
and, if it is, Petitioners state that we
should either propose reverting to the
proposed language, or propose language
allowing quarterly leak detection and
repair inspections when the equipment
is in volatile organic compound (VOC)
service, not just HAP service.
Based on our review of this issue, we
are proposing some editorial changes to
40 CFR 63.11495(a)(3) of the final rule
to make the rule easier to read and
understand. These changes are
described in Section VII of this
preamble. However, we decided not to
propose changes as suggested by the
Petitioners because we have several
concerns regarding how inspections can
be conducted effectively when the
process is not operating in HAP service.
We request comment on both the
specific concerns described below, as
well as all other aspects of the
requirements in the final rule related to
the timing of inspections. First, because
the configuration of process vessels and
equipment likely changes from one
CMPU to the next, we request comment
on how sources would track which
vessels and equipment to inspect in
VOC service if we adopted Petitioners’
approach and whether this effort would
negate any advantages of having
flexibility to inspect at times other than
when the subject CMPU is operating in
organic HAP service. Second, process
vessels are generally opened and
cleaned when reconfiguring to create a
different CMPU, and equipment
connections are also often opened.
Therefore, we also request comment
discussing how inspections in VOC
service for a different configuration
would provide information that is
relevant to determining whether there
are leaks from the subject CMPU.
Finally, if someone elects to conduct
Method 21 monitoring rather than
sensory inspections, the instrument
reading obtained would be related to the
concentration of organic compound in
the fluid and the response factor of the
instrument for that organic compound.
Thus, we request comment on the need
to specify criteria for the type of fluid
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that may be used when conducting
inspections of vessels and equipment in
VOC service (e.g., that the VOC
concentration must be no less than the
total organic compound concentration
in the subject CMPU when in organic
HAP service). We will consider
adopting the Petitioners’ approach after
reconsideration if we can adequately
address these issues.
F. Applicability of the Family of
Materials Concept
After proposal, the rule was revised in
response to comments from Petitioners
and others that argued applicability
should be established on a CMPU basis
instead of facility-wide basis. Petitioners
specifically suggested that the EPA
adopt the CMPU construct. We defined
the CMPU in the final rule to include
‘‘all process vessels, equipment, and
activities necessary to operate a
chemical manufacturing process that
produces a material or family of
materials * * *. A CMPU consists of
one or more unit operations and any
associated recovery device.’’ 40 CFR
63.11494(b). In adopting the CMPU
construct, we determined that, to
adequately characterize the CMPU, the
applicability of the rule should extend
to the ‘‘family of materials’’ because the
CMPU concept is derived from the
MON, and production of a family of
materials is part of a single process unit
in the MON. Furthermore, as in the
MON, the CMAS rule specifies mass
emission thresholds above which more
stringent control of batch process vents
is required. Petitioners state that it can
be difficult under the CMAS rule to
determine what constitutes a family of
materials. Petitioners believe that the
term ‘‘family of materials’’ effectively
expands the scope of a CMPU to include
equipment that is not part of a process
that uses or produces Table 1 HAP.
Petitioners contend that there is no
policy justification for applying the
CMAS rule this broadly. Therefore,
Petitioners request that the EPA
interpret the ‘‘family of materials’’ term
in such a way as to avoid regulating
equipment that is not used to process a
Table 1 HAP. Alternatively, Petitioners
suggest that the EPA propose
eliminating the phrase ‘‘or a family of
materials’’ from the rule.
The definition of ‘‘family of
materials’’ in the MON, and referenced
in 40 CFR 63.11502 of the CMAS final
rule, is as follows:
Family of materials means a grouping of
materials with the same basic composition or
the same basic end use or functionality
produced using the same basic feedstocks
with essentially identical HAP emission
profiles (primary constituent and relative
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magnitude on a pound per pound basis) and
manufacturing equipment configuration.
Examples of families of materials include
multiple grades of the same product or
different variations of a product (e.g., blue,
black and red resins).
As in the MON, the intent of the
family of materials concept in 40 CFR
part 63, subpart VVVVVV is to ensure
that sources will not be able to
improperly avoid installation of add-on
controls for batch process vent
emissions by creating separate CMPU
for production of essentially the same
products (i.e., products produced from
the same basic raw materials, with
essentially identical HAP emissions,
and using the same configuration of
manufacturing equipment). For
example, a series of polymer products
that differ only in molecular weight or
the type of non-HAP additive are
considered a family of materials when
the same primary raw materials are
used, the same types of HAP are emitted
and the same configuration of
production equipment is used.
However, because the definition of
family of materials in the final rule uses
the term ‘‘essentially’’ identical HAP
emission profiles, a family of materials
potentially could include some products
whose production does not involve
Table 1 HAP. Therefore, to clarify the
requirements, we are proposing to revise
the definition of family of materials to
state that only those products whose
production involves emission of the
same Table 1 HAP are to be considered
part of a family of materials.
We also want to clarify the family of
materials concept as it relates to
production of isolated intermediates. A
chemical manufacturing process is
defined, in part, as ‘‘all equipment
which collectively functions to produce
a product or isolated intermediate.’’ An
isolated intermediate is defined, in part,
as ‘‘a product of a process that is stored
before subsequent processing.’’ (As
discussed in section VII of this
preamble, we are proposing to add a
definition of ‘‘isolated intermediate’’
that is consistent with the definition in
the MON.) Even if an isolated
intermediate and final product are
produced using the same manufacturing
equipment configuration and have the
same Table 1 HAP emissions, they
generally cannot be part of a family of
materials because the definition
specifies production of all products in
the family must involve the same basic
feedstocks. This condition would not be
met if an isolated intermediate is used
as a feedstock in later production of a
final product. Furthermore, the
definition of family of materials
specified that all products in the family
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must have the same basic composition,
end use, or functionality. This condition
also would not be met in a situation
where the isolated intermediate is
transformed in the process to produce
the final product.
We are requesting comment on all
aspects of the family of materials
concept, including the proposed change.
We are particularly interested in
descriptions of situations where
someone thinks it would apply, but
should not, and we request suggestions
for additional changes that would make
it easier to understand, apply and
enforce. We are not, however, accepting
comments on the use of the CMPU as
the basis for determining applicability
of the CMAS final rule.
V. Requirements During Periods of
Startup, Shutdown and Malfunction
(SSM)
During the comment period of the
proposed rule, the United States Court
of Appeals for the District of Columbia
Circuit vacated two provisions in the
EPA’s CAA section 112 regulations
governing the emissions of HAP during
periods of startup, shutdown and
malfunction (SSM). Sierra Club v. EPA,
551 F.3d 1019 (D.C. Cir. 2008), cert.
denied, 130 S. Ct. 1735 (U.S. 2010).
Specifically, the Court vacated the SSM
exemption contained in 40 CFR
63.6(f)(1) and 40 CFR 63.6(h)(1), that are
part of a regulation, commonly referred
to as the ‘‘General Provisions Rule,’’ that
the EPA promulgated under section 112
of the CAA. When incorporated into
CAA section 112(d) regulations for
specific source categories, the
exemption in these two provisions
exempts sources from the requirement
to comply with the otherwise applicable
CAA section 112(d) emission standard
during periods of SSM.
The proposed CMAS rule contained
references to the vacated provisions.
Because the provisions were vacated,
we removed the references in the final
rule, and, in their place, we included
alternative standards for startup and
shutdown periods for continuous
process vents. Table 3 to 40 CFR part 63,
subpart VVVVVV. For batch process
vents, we determined that startup and
shutdown periods were already
accounted for in the existing standard,
and we determined that the remaining
equipment did not have periods of
startup and shutdown. 74 FR 56013. We
declined to establish a different
standard for malfunctions, as suggested
by commenters. 74 FR 56033.
Further, as explained in the preamble
to the final rule (74 FR 56033), periods
of startup, normal operations and
shutdown are all predictable and
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routine aspects of a source’s operations.
However, by contrast, malfunction is
defined as a ‘‘sudden, infrequent, and
not reasonably preventable failure of air
pollution control and monitoring
equipment, process equipment or a
process to operate in a normal or usual
manner * * *’’ (40 CFR 63.2). Nothing
in CAA section 112(d) or in case law
requires that the EPA anticipate and
account for the innumerable types of
potential malfunction events in setting
emission standards. See 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.’’). Further, it is reasonable to
interpret CAA section 112(d) as not
requiring the EPA to account for
malfunctions in setting emissions
standards.
We believe it would be impracticable
to take malfunctions into account in
setting CAA section 112(d) standards for
chemical manufacturing area sources.
As noted above, by definition,
malfunctions are sudden and
unexpected events, and it would be
difficult to set a standard that takes into
account the myriad different types of
malfunctions that can occur across all
sources in the categories. Moreover,
malfunctions can vary in frequency,
degree and duration, further
complicating standard setting. 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.’’).
In 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 preventative 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,
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infrequent, not reasonably preventable’’
and was not instead ‘‘caused in part by
poor maintenance or careless
operation.’’ 40 CFR 63.2 (definition of
malfunction).
Finally, the EPA recognizes that even
equipment that is properly designed and
maintained can sometimes fail, and that
such failure can sometimes cause an
exceedance of the relevant emission
standard or other violation. (See, e.g.,
State Implementation Plans: Policy
Regarding Excessive Emissions During
Malfunctions, Startup, and Shutdown
(Sept. 20, 1999); Policy on Excess
Emissions During Startup, Shutdown,
Maintenance, and Malfunctions (Feb.
15, 1983)). The EPA is, therefore,
proposing to add to the final rule an
affirmative defense to civil penalties for
exceedances of emission limits or other
violations of applicable standards that
are caused by malfunctions. See 40 CFR
63.11502 (defining ‘‘affirmative
defense’’ to mean, in the context of an
enforcement proceeding, a response or
defense put forward by a defendant,
regarding which the defendant has the
burden of proof, and the merits of which
are independently and objectively
evaluated in a judicial or administrative
proceeding). We also are proposing
regulatory provisions to specify the
elements that are necessary to establish
this affirmative defense; the source must
prove by a preponderance of the
evidence that it has met all of the
elements set forth in 40 CFR
63.11501(e). See 40 CFR 22.24. The
criteria ensure that the affirmative
defense is available only where the
event that causes an exceedance of the
emission limit meets the narrow
definition of malfunction in 40 CFR 63.2
(sudden, infrequent, not reasonable
preventable and not caused by poor
maintenance and or careless operation).
For example, to successfully assert the
affirmative defense, the source must
prove by a preponderance of the
evidence that excess emissions ‘‘[w]ere
caused by a sudden, infrequent, and
unavoidable failure of air pollution
control and monitoring equipment,
process equipment, or a process to
operate in a normal or usual manner
* * *.’’ The criteria also are designed to
ensure that steps are taken to correct the
malfunction, to minimize emissions in
accordance with CAA section
63.11501(e), and to prevent future
malfunctions. For example, the source
must prove by a preponderance of the
evidence that ‘‘[r]epairs were made as
expeditiously as possible when the
applicable emission limitations were
being exceeded * * *’’ and that ‘‘[a]ll
possible steps were taken to minimize
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4531
the impact of the excess emissions on
ambient air quality, the environment
and human health * * *.’’ In any
judicial or administrative proceeding,
the Administrator may challenge the
assertion of the affirmative defense, and,
if the respondent has not met its burden
of proving all of the requirements in the
affirmative defense, appropriate
penalties may be assessed in accordance
with section 113 of the CAA (see also 40
CFR 22.77).
The EPA included an affirmative
defense in the final rule in an attempt
to balance a tension, inherent in many
types of air regulation, to ensure
adequate compliance while
simultaneously recognizing that despite
the most diligent of efforts, emission
limits may be exceeded under
circumstances beyond the control of the
source. The EPA must establish
emission standards that ‘‘limit the
quantity, rate, or concentration of
emissions of air pollutants on a
continuous basis.’’ 42 U.S.C. 7602(k)
(defining ‘‘emission limitation and
emission standard’’). See, e.g., Sierra
Club v. EPA, 551 F.3d 1019, 1021 (DC
Cir. 2008). Thus, the EPA is required to
ensure that section 112 emissions
limitations are continuous. The
affirmative defense for malfunction
events meets this requirement by
ensuring that even where there is a
malfunction, the emission limitation is
still enforceable through injunctive
relief. While ‘‘continuous’’ limitations,
on the one hand, are required, there is
also case law indicating that, in many
situations, it is appropriate for the EPA
to account for the practical realities of
technology. For example, in Essex
Chemical v. Ruckelshaus, 486 F.2d 427,
433 (DC Cir. 1973), the District of
Columbia Circuit Court acknowledged
that, in setting standards under CAA
section 111 ‘‘variant provisions’’ such as
provisions allowing for upsets during
startup, shutdown and equipment
malfunction ‘‘appear necessary to
preserve the reasonableness of the
standards as a whole and that the record
does not support the ‘never to be
exceeded’ standard currently in force.’’
See also, Portland Cement Association
v. Ruckelshaus, 486 F.2d 375 (DC Cir.
1973). Though intervening case law
such as Sierra Club v. EPA and the CAA
1977 amendments undermine the
relevance of these cases today, they
support the EPA’s view that a system
that incorporates some level of
flexibility is reasonable. The affirmative
defense simply provides for a defense to
civil penalties for excess emissions that
are proven to be beyond the control of
the source. By incorporating an
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affirmative defense, the EPA has
formalized its approach to upset events.
In a Clean Water Act setting, the Ninth
Circuit required this type of formalized
approach when regulating ‘‘upsets
beyond the control of the permit
holder.’’ Marathon Oil Co. v. EPA, 564
F.2d 1253, 1272–73 (9th Cir. 1977). But
see, Weyerhaeuser Co. v. Costle, 590
F.2d 1011, 1057–58 (DC Cir. 1978)
(holding that an informal approach is
adequate). The affirmative defense
provisions give the EPA the flexibility to
both ensure that its emission limitations
are ‘‘continuous’’ as required by 42
U.S.C. 7602(k), and account for
unplanned upsets and thus support the
reasonableness of the standard as a
whole.
The EPA has attempted to ensure that
we have not incorporated into proposed
regulatory language any provisions that
are inappropriate, unnecessary, or
redundant in the absence of the SSM
exemption. We are specifically seeking
comment on whether there are any such
provisions that we have inadvertently
incorporated or overlooked. We are also
seeking comment on the inclusion of the
affirmative defense provisions. Finally,
we solicit comment on provisions in the
final rule applicable to startup and
shutdown periods for continuous and
batch process vents.
In addition to the affirmative defense
provisions described above, we are also
proposing several changes throughout
the rule and in Table 9 (the table that
specifies applicability of General
Provisions to subpart VVVVVV of 40
CFR part 63) to specify applicable
requirements during periods of startup
and shutdown and periods of
malfunction. For example, we are
proposing to add new paragraphs in 40
CFR 63.11501(c)(1)(vii) and (viii) that
would require records of the occurrence
and duration of malfunctions, as well as
records of actions taken to minimize
emissions during these periods and to
fix malfunctioning equipment. We are
also proposing to add a paragraph in 40
CFR 63.11501(d)(8) that would require
reporting of information related to each
malfunction. Table 9 in the final rule
states that 63.6(e)(1)(i) does not apply to
subpart VVVVVV. We are also
proposing to add a new paragraph in 40
CFR 63.11495(d) that specifies the
general duty to minimize emissions
applies at all times. In addition to the
proposed changes in the text of the rule,
entries for 40 CFR 63.6(e)(1)(i),
63.10(b)(2) and 63.10(d)(5) also would
be changed to reference the new
paragraphs in 40 CFR 63.11495(d),
63.11501(c) and 63.11501(d). Finally,
we are proposing to revise Table 9 to
state that the performance testing
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requirements in 40 CFR 63.7(e)(1) do
not apply. The comments to Table 9 for
that provision identify the location of
the applicable performance testing
requirements for CMAS sources.
VI. Requirements for Metal HAP
Process Vents
A. Definition of Metal HAP Process Vent
A metal HAP process vent is defined
in the final rule as ‘‘the point of
discharge to the atmosphere (or inlet to
a control device, if any) of a metal HAPcontaining gas stream from any CMPU
at an affected source.’’ We are
requesting comment on the applicability
of this definition to all types of
equipment from which metal HAP are
emitted. We are particularly interested
in comments on how well it applies to
chemical manufacturing processes in
comparison to the definitions for batch
and continuous process vents, which
have been used in HON, MON and
several other MACT standards for
chemical manufacturing.
B. Metal HAP Process Vent Standards
Since promulgation, we determined
that the final rule does not clearly
explain how the rule applies when the
Table 1 metal HAP are emitted as a
gaseous organo-metallic compound
along with other organic compounds
that are routed to an incinerator for
control. To clarify our intent, the
following discussion summarizes the
requirements in the final rule for all
types of metal HAP compounds,
including organo-metallic compounds.
It also identifies potential limitations in
these requirements and requests
information to enable better
characterization of affected CMPU.
Table 4 to 40 CFR part 63, subpart
VVVVVV specifies that an owner or
operator of an affected CMPU with
metal HAP emissions equal to or greater
than 400 pounds per year (lb/yr) must
reduce the metal HAP emissions by at
least 95 percent. The emission limit
specified in Table 4 to subpart VVVVVV
does not differentiate between
compounds that are emitted as
particulate and compounds that are
emitted as vapor or as liquid droplets,
or between organic and inorganic
compounds. All Table 1 metal HAP
compounds in all phases are subject.
Thus, in the case of a CMPU that uses
an organo-metallic Table 1 metal HAP
compound, both the 400 lb/yr threshold
and 95-percent emission limit apply.
Although combustion would change the
type of Table 1 metal HAP compound(s)
emitted, it would not destroy the metal
itself and likely would not reduce the
mass by 95 percent. Thus, if the
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uncontrolled metal HAP emissions are
greater than 400 lb/yr, additional
control of the metal HAP would be
required either upstream or downstream
of the incinerator.
To demonstrate initial compliance,
the owner or operator must conduct
either a performance test or an
engineering assessment (except new
sources using a baghouse as a control
device are required to conduct a
performance test). If the owner or
operator elects to conduct a
performance test for a CMPU from
which the metal HAP are emitted as a
vapor, then the test must be conducted
using Method 29 because the other
specified alternative, Method 5, is not
applicable. To demonstrate ongoing
compliance, the owner or operator must
develop and operate in accordance with
a site-specific monitoring plan. This
requirement applies for any type of
control device used to control metal
HAP emissions.
Although the metal HAP requirements
apply to all Table 1 metal HAP as
described above, the 400 lb/yr threshold
was developed, primarily, based on
information from CMPU where the
metal HAP is emitted as particulate. In
general, these facilities processed ores
and/or manufactured solid materials
such as pigments, catalysts or
manganese dioxide. Some metal HAP at
certain steps in some processes are
liquids or dissolved in solvents, but
these metal HAP compounds typically
have very low vapor pressures and
emissions; the bulk of the metal HAP
emissions are particulates from
operations such as grinding, mixing,
calcining, drying and packaging. In
addition, the control cost impacts were
developed assuming the metal HAP are
emitted in the form of particulate (See
Docket ID No. EPA–HQ–OAR–2008–
0334–0005). Therefore, we are
requesting comment on whether there
are reasons GACT for processes that
emit gaseous Table 1 metal HAP should
be different from GACT, as specified in
the final rule. We are particularly
interested in information on the types of
processes that emit gaseous Table 1
metal HAP, the range in uncontrolled
emissions from such processes, the
types of emission points (i.e., are these
emission points consistent with the
definition of ‘‘metal HAP process
vent’’), the types of control devices used
to control such emissions and whether
those processes also emit particulate
metal HAP.
VII. Technical Corrections and
Clarifications
We are proposing several technical
corrections. These amendments are
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being proposed to correct inaccuracies
and oversights that were promulgated in
the final rule. These proposed changes
are described in Table 1 of this
4533
preamble. We request comment on all of
these proposed changes.
TABLE 1—MISCELLANEOUS TECHNICAL CORRECTIONS TO 40 CFR PART 63, SUBPART VVVVVV
Section of subpart VVVVVV
Description of correction
40 CFR 63.11494(a)(3) ......................................
We are proposing several changes to this paragraph. First, we are proposing to clarify that the
0.1-percent and 1.0-percent concentration thresholds are on a mass basis of the compound
containing the Table 1 HAP. Second, we are proposing to clarify that all Table 1 HAP, except for quinoline and manganese compounds, are considered carcinogenic, probably carcinogenic or possibly carcinogenic. Therefore, the concentration threshold of 1.0 weight percent applies only to quinoline and manganese compounds, and the threshold of 0.1 weight
percent applies to all other Table 1 HAP. Third, because it is not clear under the final rule
whether an emission stream that contains a Table 1 HAP as a gaseous byproduct is a
‘‘process fluid,’’ we are proposing changes to clarify applicability of CMPU that generate a
Table 1 HAP byproduct. If Table 1 HAP are generated as byproduct, the proposed changes
clarify that the CMPU is subject to the rule if the concentration of the Table 1 HAP in any
liquid stream in the CMPU exceeds the same thresholds that apply to feedstocks. Specifically, if quinoline is generated as a byproduct, then the CMPU is subject if the quinoline
concentration in any liquid stream in the CMPU exceeds 1.0 percent by weight. Similarly, if
hydrazine or any other organic Table 1 HAP is generated as a byproduct, then the process
is subject if the collective concentration of these compounds in any liquid stream is greater
than 0.1 percent by weight. In addition, the proposed changes also specify that a CMPU is
subject if the collective concentration of these Table 1 HAP exceeds 50 parts per million by
volume in any process vent stream. This threshold was specified because this concentration
defines a process vent, and such emissions streams are subject to control. Finally, we are
proposing to consolidate paragraphs (a)(1) and (3) to eliminate redundancy.
We are proposing to add a new paragraph that would list lead oxide production at lead acid
battery manufacturing facilities in those operations for which this subpart does not apply.
These sources are covered by 40 CFR part 63, subpart PPPPPP—NESHAP for Lead Acid
Battery Manufacturing Area Sources.
We are proposing to clarify that a CMPU using only Table 1 metal HAP is not subject to any
requirements for wastewater systems or heat exchange systems. Only organic HAP are
subject to wastewater and heat exchange system requirements. We are proposing this
change based on the fact that most metal HAP compounds have a very low vapor pressure
and would not volatilize from wastewater or cooling water. However, given our discussion of
organo-metallic compounds in section VI.B of this preamble, we are also requesting comment on whether this change should be limited to only certain types or classes of metal
HAP compounds for wastewater systems, heat exchange systems or both types of systems.
To clarify and improve the readability of this section, we are proposing to split it into an introductory section with five subsections. One sentence that contains two concepts also would
be split into two separate sentences. The requirements, however, have not changed.
We are proposing to edit this paragraph to add the acronym ‘‘CMS.’’
We are proposing to edit the first sentence in this paragraph to remove the unnecessary word
‘‘report.’’
To demonstrate initial compliance with the emissions limit for HAP metals, 40 CFR
63.11496(f)(3)(ii) in the final rule requires either a performance test or engineering assessment. This paragraph in the final rule also specifies that a performance test must be conducted under representative process operating conditions, but it does not specify conditions
under which an engineering assessment must be conducted. To correct this oversight, and
maintain consistency with the conditions under which performance testing must be conducted, we are proposing to modify 40 CFR 63.11496(f)(3)(ii) to clarify that if a source elects
to conduct an engineering assessment to demonstrate initial compliance with the standards
for metal HAP process vents, then the design evaluation must be conducted at representative operating conditions for the CMPU.
Other rules, such as the HON, specify that discharge of wastewater to a Resource Conservation and Recovery Act (RCRA)-permitted underground injection well is a treatment (i.e., control) option for wastewater streams. We intended to include the same option in 40 CFR part
63, subpart VVVVVV. However, ‘‘wastewater treatment’’ is defined in 40 CFR 63.11502 as
procedures that remove or reduce HAP, which does not clearly include discharge to an underground injection well. To clarify this point, we are proposing to add a definition of ‘‘hazardous waste treatment’’ in 40 CFR 63.11502(b) to mean treatment in a RCRA-permitted incinerator, process heater, boiler or underground injection well. The specific language in the
proposed definition is consistent with 40 CFR 63.138(h) of the HON wastewater provisions.
We are also proposing corresponding changes to Table 6 to subpart VVVVVV. Specifically,
for each wastewater stream, Item 1.a would require either wastewater treatment or hazardous waste treatment. In addition, Item 2.b would be edited to use the new term ‘‘hazardous waste treatment.’’ The proposed changes to Item 1.a also make it clear that the
treatment conducted to meet Item 2.b would satisfy the requirements of Item 1.a.
We are proposing to replace the incorrect word ‘‘dimension’’ with the correct word ‘‘dimensions.’’
We are proposing to insert a reference to the definition of the term ‘‘isolated intermediate’’ in
40 CFR 63.2550 of the MON because this term is used in the definitions of several other
terms in 40 CFR 63.11502.
40 CFR 63.11494(c)(1)(vii) .................................
40 CFR 63.11494(d) ...........................................
40 CFR 63.11495(a)(3) ......................................
40 CFR 63.11496(f)(3)(i)(C) ...............................
40 CFR 63.11496(f)(3)(ii) ...................................
40 CFR 63.11496(f)(3)(ii) ...................................
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6.
40 CFR 63.11501(c)(4)(i) ...................................
40 CFR 63.11502(a) ...........................................
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TABLE 1—MISCELLANEOUS TECHNICAL CORRECTIONS TO 40 CFR PART 63, SUBPART VVVVVV—Continued
Section of subpart VVVVVV
Description of correction
40 CFR 63.11502(b) ...........................................
We are proposing to modify the definition of ‘‘product’’ to remove ‘‘isolated intermediates’’ from
the list of materials that are not considered products. This change would make the definition
of product consistent with the definitions of chemical manufacturing process and isolated intermediate. A chemical manufacturing process is defined as all equipment which collectively
functions to produce a product or isolated intermediate. Isolated intermediate is defined as a
product of a process that is stored before subsequent processing.
We are proposing to add a definition for the term ‘‘uncontrolled emissions’’ because the control
threshold for batch process vents and metal HAP process vents in 40 CFR 63.11496(a) and
(f) use this term. The proposed definition would read as follows: ‘‘Uncontrolled emissions
means process vent emissions at the outlet of the last recovery device, if any, and prior to
any control device. In the absence of both recovery devices and control devices, uncontrolled emissions are the emissions discharged to the atmosphere.’’
40 CFR 63.11502(b) ...........................................
VIII. Statutory and Executive Order
Reviews
emcdonald on DSK29S0YB1PROD with PROPOSALS
A. Executive Order 12866: Regulatory
Planning and Review and Executive
Order 13563: Improving Regulation and
Regulatory Review
Under Executive Order 12866 (58 FR
51735, October 4, 1993), this action is a
‘‘significant regulatory action’’ because
it may raise novel legal or policy issues.
Accordingly, the EPA submitted this
action to the Office of Management and
Budget (OMB) for review under
Executive Order 12866 and Executive
Order 13563 (76 FR 3821, January 21,
2011), and any changes made in
response to OMB recommendations
have been documented in the docket for
this action.
B. Paperwork Reduction Act
The information collection
requirements in this rule have been
submitted for approval to the Office of
Management and Budget (OMB) under
the Paperwork Reduction Act, 44 U.S.C.
3501, et seq. The Information Collection
Request (ICR) document prepared by the
EPA has been assigned EPA ICR number
2323.03. The information collection
requirements are not enforceable until
OMB approves them.
The information requirements are
based on notification, recordkeeping
and reporting requirements in the
NESHAP General Provisions (40 CFR
part 63, subpart A), which are
mandatory for all operators subject to
national emission standards. These
recordkeeping and reporting
requirements are specifically authorized
by section 114 of the CAA (42 U.S.C.
7414). All information submitted to the
EPA pursuant to the recordkeeping and
reporting requirements for which a
claim of confidentiality is made is
safeguarded according to agency
policies set forth in 40 CFR part 2,
subpart B.
For this proposed rule, the EPA is
adding affirmative defense to the
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estimate of burden in the ICR. To
provide the public with an estimate of
the relative magnitude of the burden
associated with an assertion of the
affirmative defense position adopted by
a source, the EPA has provided
administrative adjustments to this ICR
to show what the notification,
recordkeeping and reporting
requirements associated with the
assertion of the affirmative defense
might entail. The EPA’s estimate for the
required notification, reports and
records for any individual incident,
including the root cause analysis, totals
$2,958 and is based on the time and
effort required of a source to review
relevant data, interview plant
employees, and document the events
surrounding a malfunction that has
caused an exceedance of an emissions
limit. The estimate also includes time to
produce and retain the record and
reports for submission to the EPA. The
EPA provides this illustrative estimate
of this burden because these costs are
only incurred if there has been a
violation and a source chooses to take
advantage of the affirmative defense.
Given the variety of circumstances
under which malfunctions could occur,
as well as differences among sources’
operation and maintenance practices,
we cannot reliably predict the severity
and frequency of malfunction-related
excess emissions events for a particular
source. It is important to note that the
EPA has no basis currently for
estimating the number of malfunctions
that would qualify for an affirmative
defense. Current historical records
would be an inappropriate basis, as
source owners or operators previously
operated their facilities in recognition
that they were exempt from the
requirement to comply with emissions
standards during malfunctions. Of the
number of excess emissions events
reported by source operators, only a
small number would be expected to
result from a malfunction (based on the
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definition above), and only a subset of
excess emissions caused by
malfunctions would result in the source
choosing to assert the affirmative
defense. Thus, we believe the number of
instances in which source operators
might be expected to avail themselves of
the affirmative defense will be
extremely small. For this reason, we
estimate no more than 2 or 3 such
occurrences for all sources subject to 40
CFR part 63, subpart VVVVVV over the
3-year period covered by this ICR. We
expect to gather information on such
events in the future and will revise this
estimate as better information becomes
available. The annual monitoring,
reporting and recordkeeping burden for
this collection (averaged over the first 3
years after the effective date of the
standards) for these amendments to
subpart VVVVVV is estimated to be
$3,141 per year. This includes 30 labor
hours per year at a total labor cost of
$3,141 per year. There is no change in
annual burden to the Federal
government for these amendments.
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
these ICR are approved by OMB, the
agency will publish a technical
amendment to 40 CFR part 9 in the
Federal Register to display the OMB
control numbers for the approved
information collection requirements
contained in the final rules.
To comment on the agency’s need for
this information, the accuracy of the
provided burden estimates, and any
suggested methods for minimizing
respondent burden, the EPA has
established a public docket for this rule,
which includes this ICR, under Docket
ID number EPA–HQ–OAR–2008–0334.
Submit any comments related to the ICR
to the EPA and OMB. See the ADDRESSES
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emcdonald on DSK29S0YB1PROD with PROPOSALS
section at the beginning of this notice
for where to submit comments to the
EPA. Send comments to OMB at the
Office of Information and Regulatory
Affairs, Office of Management and
Budget, 725 17th Street NW.,
Washington, DC 20503, Attention: Desk
Office for the EPA. Since OMB is
required to make a decision concerning
the ICR between 30 and 60 days after
March 30, 2012, a comment to OMB is
best assured of having its full effect if
OMB receives it by February 29, 2012.
The final rule will respond to any OMB
or public comments on the information
collection requirements contained in
this proposal.
Act of 1995 (UMRA), 2 U.S.C. 1531–
1538 for state, local or tribal
governments or the private sector. This
proposed rule imposes no enforceable
duty on any state, local or tribal
governments or the private sector.
Therefore, this proposed rule is not
subject to the requirements of sections
202 and 205 of the UMRA.
This action is also not subject to the
requirements of section 203 of UMRA
because it contains no regulatory
requirements that might significantly or
uniquely affect small governments. This
rule proposes amendments to aid with
compliance, but does not change the
level of the standards in the rule.
C. Regulatory Flexibility Act
The Regulatory Flexibility Act
generally requires an agency to prepare
a regulatory flexibility analysis of any
rule subject to notice and comment
rulemaking requirements under the
Administrative Procedures Act or any
other statute unless the agency certifies
that the rule will not have a significant
economic impact on a substantial
number of small entities. Small entities
include small businesses, small
organizations, and small governmental
jurisdictions.
For purposes of assessing the impacts
of this proposed rule on small entities,
small entity is defined as: (1) A small
business as defined by the Small
Business Administration’s regulations at
13 CFR 121.201(less than 500, 750 or
1,000 employees, depending on the
specific NAICS Code under subcategory
325); (2) a small governmental
jurisdiction that is a government of a
city, county, town, school district or
special district with a population of less
than 50,000; and (3) a small
organization that is any not-for-profit
enterprise that is independently owned
and operated and is not dominant in its
field.
After considering the economic
impacts of this proposed rule on small
entities, I certify that this action will not
have a significant economic impact on
a substantial number of small entities.
This proposed rule will not impose any
new requirements on any small entities
because it does not impose any
additional regulatory requirements
beyond those already promulgated in
the final rule. We continue to be
interested in the potential impacts of the
proposed rule on small entities and
welcome comments on issues related to
such impacts.
E. 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, as specified in
Executive Order 13132. This proposed
rule will not impose direct compliance
costs on state or local governments, and
will not preempt state law. Thus,
Executive Order 13132 does not apply
to this action.
In the spirit of Executive Order 13132,
and consistent with EPA policy to
promote communications between the
EPA and state and local governments,
the EPA specifically solicits comment
on this proposed action from state and
local officials.
D. Unfunded Mandates Reform Act
This action contains no Federal
mandates under the provisions of Title
II of the Unfunded Mandates Reform
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F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
This proposed rule does not have
tribal implications, as specified in
Executive Order 13175 (65 FR 67249,
November 9, 2000). It will not have
substantial direct effects on tribal
governments, on the relationship
between the Federal government and
Indian tribes or on the distribution of
power and responsibilities between the
Federal government and Indian tribes,
as specified in Executive Order 13175.
Thus, Executive Order 13175 does not
apply to this proposed rule.
The EPA specifically solicits
additional comment on this proposed
action from tribal officials.
G. Executive Order 13045: Protection of
Children From Environmental Health
Risks and Safety Risks
The EPA interprets Executive Order
13045 (62 FR 19885, April 23, 1997) as
applying to those regulatory actions that
concern health or safety risks, such that
the analysis required under section 5–
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4535
501 of the Executive Order has the
potential to influence the regulation.
This proposed rule is not subject to
Executive Order 13045 because it is
based solely on technology
performance.
H. Executive Order 13211: Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use
This action is not a ‘‘significant
energy action’’ as defined in Executive
Order 13211 (66 FR 28355, May 22,
2001), because it is not likely to have a
significant adverse effect on the supply,
distribution or use of energy. Further,
this action does not change the level of
standards already in place.
I. National Technology Transfer and
Advancement Act
Section 12(d) of the National
Technology Transfer and Advancement
Act (NTTAA) of 1995, Public Law 104–
113, 12(d) (15 U.S.C. 272 note) directs
the EPA to use voluntary consensus
standards (VCS) in its regulatory
activities, unless to do so would be
inconsistent with applicable law or
otherwise impractical. VCS are
technical standards (e.g., materials
specifications, test methods, sampling
procedures and business practices) that
are developed or adopted by VCS
bodies. NTTAA directs the EPA to
provide Congress, through OMB,
explanations when the agency decides
not use available and applicable VCS.
This proposed rulemaking does not
involve technical standards. Therefore,
the EPA did not consider the use of any
VCS.
J. Executive Order 12898: Federal
Actions To Address Environmental
Justice in Minority Populations and
Low-Income Populations
Executive Order 12898 (59 FR 7629,
February 16, 1994) establishes Federal
executive policy on environmental
justice. Its main provision directs
Federal agencies, to the greatest extent
practicable and permitted by law, to
make environmental justice part of their
mission by identifying and addressing,
as appropriate, disproportionately high
and adverse human health or
environmental effects of their programs,
policies and activities on minority
populations and low-income
populations in the United States.
The EPA has determined that this
proposed rule will not have
disproportionately high and adverse
human health or environmental effects
on minority or low-income populations
because it increases the level of
environmental protection for all affected
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populations without having any
disproportionately high and adverse
human health or environmental effects
on any population, including any
minority or low-income population. The
amendments do not relax the control
measures on sources regulated by the
rules, and, therefore, will not cause
emissions increases from these sources.
List of Subjects in 40 CFR Part 63
Environmental protection,
Administrative practice and procedure,
Air pollution control, Hazardous
substances.
Dated: January 13, 2012.
Lisa P. Jackson,
Administrator.
For the reasons cited in the preamble,
title 40, chapter I, part 63 of the Code
of Federal Regulations is proposed to be
amended as follows:
PART 63—[AMENDED]
1. The authority citation for part 63
continues to read as follows:
Authority: 42 U.S.C. 7401, et seq.
Subpart VVVVVV—[AMENDED]
2. Section 63.11494 is amended by:
a. Revising paragraph (a);
b. Adding paragraph (c)(1)(vii);
c. Revising the last sentence in
paragraph (d); and
d. Revising paragraph (e) to read as
follows:
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§ 63.11494 What are the applicability
requirements and compliance dates?
(a) Except as specified in paragraph
(c) of this section, you are subject to this
subpart if you own or operate a
chemical manufacturing process unit
(CMPU) that meets the conditions
specified in paragraphs (a)(1) and (2) of
this section.
(1) The CMPU is located at an area
source of hazardous air pollutant (HAP)
emissions.
(2) HAP listed in Table 1 to this
subpart (Table 1 HAP) are present in the
CMPU, as specified in paragraph
(a)(2)(i), (ii), (iii), (iv) or (v) of this
section.
(i) The CMPU uses as feedstock, any
material that contains quinoline and/or
manganese compounds at a
concentration greater than 1.0 percent
by weight, or other Table 1 HAP at a
collective concentration greater than 0.1
percent by weight. To determine the
Table 1 HAP content of feedstocks, you
may rely on formulation data provided
by the manufacturer or supplier, such as
the Material Safety Data Sheet (MSDS)
for the material. If the concentration in
an MSDS is presented as a range, use
the upper bound of the range.
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(ii) Quinoline is generated as
byproduct and is present in the CMPU
in any liquid stream (process or waste)
at a concentration greater than 1.0
percent by weight.
(iii) Hydrazine and/or Table 1 organic
compounds other than quinoline are
generated as byproduct and are present
in the CMPU in any liquid stream
(process or waste) at a collective
concentration greater than 0.1 percent
by weight.
(iv) Hydrazine and/or any Table 1
organic compounds are generated as
byproduct and are present in the CMPU
in any process vent stream at a
collective concentration greater than 50
parts per million by volume (ppmv).
(v) Hydrazine or any Table 1 organic
compound is produced as a product of
the CMPU.
*
*
*
*
*
(c) * * *
(1) * * *
(vii) Lead oxide production at Lead
Acid Battery Manufacturing Facilities,
subject to subpart PPPPPP of this part.
*
*
*
*
*
(d) * * * A CMPU using only Table
1 metal HAP is required to control only
total CAA section 112(b) metal HAP in
accordance with § 63.11495 and, if
applicable, § 63.11496(f).
*
*
*
*
*
(e) Any source subject to this subpart
that installed a federally-enforceable
control device on an affected CMPU by
the first substantive compliance date of
an otherwise applicable MACT
standard, and, as a result, became an
area source under 40 CFR part 63, is
required to obtain a permit under 40
CFR part 70 or 40 CFR part 71. For
existing sources subject to title V, as a
result of this rule, a complete title V
permit application must be submitted
no later than 12 months after date of
publication of the final rule
amendments in the Federal Register if
the source is subject to this rule on that
date. New sources and existing sources
that become subject to this rule after
date of publication of the final rule
amendments in the Federal Register
must submit a complete title V permit
application no later than 12 months
after becoming subject to this rule.
Otherwise, you are exempt from the
obligation to obtain a permit under 40
CFR part 70 or 40 CFR part 71, provided
you are not otherwise required by law
to obtain a permit under 40 CFR 70.3(a)
or 40 CFR 71.3(a). Notwithstanding the
previous sentence, you must continue to
comply with the provisions of this
subpart.
*
*
*
*
*
3. Section 63.11495 is amended by:
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a. Revising paragraphs (a)(1) and
(a)(3);
b. Adding paragraph (c) heading; and
c. Adding paragraph (d) to read as
follows:
§ 63.11495 What are the management
practices and other requirements?
(a) * * *
(1) Each process vessel must be
equipped with a cover or lid that must
be closed at all times when it is in
organic HAP service or metal HAP
service, except for manual operations
that require access, such as material
addition and removal, inspection,
sampling and cleaning.
*
*
*
*
*
(3) You must conduct inspections of
process vessels and equipment for each
CMPU in organic HAP service or metal
HAP service, as specified in paragraphs
(a)(3)(i) through (v) of this section, to
demonstrate compliance with paragraph
(a)(1) of this section and to determine
that the process vessels and equipment
are sound and free of leaks.
(i) Inspections must be conducted at
least quarterly.
(ii) For these inspections, detection
methods incorporating sight, sound or
smell are acceptable. Indications of a
leak identified using such methods
constitute a leak unless you demonstrate
that the indications of a leak are due to
a condition other than loss of HAP. If
indications of a leak are determined not
to be HAP in one quarterly monitoring
period, you must still perform the
inspection and demonstration in the
next quarterly monitoring period.
(iii) As an alternative to conducting
inspections, as specified in paragraph
(a)(3)(ii) of this section, you may use
Method 21 of 40 CFR part 60, appendix
A–7, with a leak definition of 500 ppmv
to detect leaks. You may also use
Method 21 with a leak definition of 500
ppmv to determine if indications of a
leak identified during an inspection
conducted in accordance with
paragraph (a)(3)(ii) of this section are
due to a condition other than loss of
HAP. The procedures in this paragraph
(a)(3)(iii) may not be used as an
alternative to the inspection required by
paragraph (a)(3)(ii) of this section for
process vessels that contain metal HAP
as particulate.
(iv) Inspections must be conducted
while the subject CMPU is operating.
(v) No inspection is required in a
calendar quarter during which the
subject CMPU does not operate for the
entire calendar quarter and is not in
organic HAP service or metal HAP
service. If the CMPU operates at all
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during a calendar quarter, an inspection
is required.
*
*
*
*
*
(c) Startup, shutdown and
malfunction. * * *
(d) General duty. At all times, you
must operate and maintain any affected
source, including associated air
pollution control equipment and
monitoring equipment, in a manner
consistent with safety and good air
pollution control practices for
minimizing emissions. Determination of
whether such operation and
maintenance procedures are being used
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.
4. Section 63.11496 is amended by
revising paragraphs (f)(3)(i)(C), (f)(3)(ii)
and (g)(1) to read as follows:
§ 63.11496 What are the standards and
compliance requirements for process
vents?
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*
*
*
*
*
(f) * * *
(3) * * *
(i) * * *
(C) Operation and maintenance plan
for the control device (including a
preventative maintenance schedule
consistent with the manufacturer’s
instructions for routine and long-term
maintenance) and continuous
monitoring system (CMS).
*
*
*
*
*
(ii) You must conduct a performance
test or an engineering assessment for
each CMPU subject to a HAP metals
emissions limit in Table 4 to this
subpart and report the results in your
Notification of Compliance Status
(NOCS). Each performance test or
engineering assessment must be
conducted under representative
operating conditions, and sampling for
each performance test must be
conducted at both the inlet and outlet of
the control device. Upon request, you
shall make available to the
Administrator such records as may be
necessary to determine the conditions of
performance tests. If you own or operate
an existing affected source, you are not
required to conduct a performance test
if a prior performance test was
conducted within the 5 years prior to
the effective date using the same
methods specified in paragraph (f)(3)(iii)
of this section, and, either no process
changes have been made since the test,
or, if you can demonstrate that the
results of the performance test, with or
without adjustments, reliably
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demonstrate compliance despite process
changes.
*
*
*
*
*
(g) * * *
(1) Requirements for Performance
Tests. (i) The requirements specified in
§§ 63.2450(g)(1) through (4) apply
instead of, or in addition to, the
requirements specified in 40 CFR part
63, subpart SS.
(ii) Upon request, you shall make
available to the Administrator, such
records as may be necessary to
determine the conditions of
performance tests.
*
*
*
*
*
5. Section 63.11498 is amended by
revising paragraph (a)(2) to read as
follows:
§ 63.11498 What are the standards and
compliance requirements for wastewater
systems?
(a) * * *
(2) You are not required to determine
the partially soluble concentration in
wastewater that is hard piped to a
combustion unit or hazardous waste
treatment unit, as specified in Table 6,
Item 2.b to this subpart, or Table 6, Item
2.c to this subpart.
*
*
*
*
*
6. Section 63.11501 is amended by:
a. Revising the section heading;
b. Revising the second sentence in
paragraph (c) introductory text, and
paragraph (c)(1) introductory text;
c. Adding paragraphs (c)(1)(vii) and
(c)(1)(viii);
d. Revising paragraph (c)(4)(i);
e. Adding paragraph (c)(8);
d. Revising the second sentence in
paragraph (d) introductory text;
e. Adding paragraph (d)(8); and
f. Adding paragraph (e) to read as
follows:
§ 63.11501 What are the notification,
recordkeeping, and reporting requirements,
and how may I assert an affirmative defense
for exceedance of emission limit during
malfunction?
*
*
*
*
*
(c) * * * If you are subject, you must
comply with the recordkeeping and
reporting requirements of
§ 63.10(b)(2)(iii) and (vi) through (xiv),
and the applicable requirements
specified in paragraphs (c)(1) through
(8) of this section.
(1) For each CMPU subject to this
subpart, you must keep the records
specified in paragraphs (c)(1)(i) through
(viii) of this section.
*
*
*
*
*
(vii) Records of the occurrence and
duration of each malfunction of
operation (i.e., process equipment) or
the air pollution control and monitoring
equipment.
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4537
(viii) Records of actions taken during
periods of malfunction to minimize
emissions in accordance with
§ 63.11495(d), including corrective
actions to restore malfunctioning
process and air pollution control and
monitoring equipment to its normal or
usual manner of operation.
*
*
*
*
*
(4) * * *
(i) Keep records of the vessel
dimensions, capacity, and liquid stored,
as specified in § 63.1065(a).
*
*
*
*
*
(8) For continuous process vents
subject to Table 3 to this subpart, keep
records of the occurrence and duration
of each startup and shutdown of
operation of process equipment, or of air
pollution control and monitoring
equipment.
(d) * * * Reports are required only for
semiannual periods during which you
experienced any of the events described
in paragraphs (d)(1) through (8) of this
section.
*
*
*
*
*
(8) Malfunctions. If a malfunction
occurred during the reporting period,
the report must include the number,
duration and a brief description for each
type of malfunction which occurred
during the reporting period, and which
caused or may have caused any
applicable emission limitation to be
exceeded. The report must include an
estimate of the volume of regulated
pollutants emitted and attributed to the
malfunction, with a description of the
method used to estimate the emissions.
The report must also include a
description of actions you took during a
malfunction of an affected source to
minimize emissions in accordance with
§ 63.11495(d), including actions taken to
correct a malfunction.
(e) Affirmative defense for exceedance
of emission limit during malfunction. In
response to an action to enforce the
standards set forth in §§ 63.11495
through 63.11499, you may assert an
affirmative defense to a claim for civil
penalties for exceedances of such
standards that are caused by
malfunction, as defined at 40 CFR 63.2.
Appropriate penalties may be assessed,
however, if you fail to meet your burden
of proving all of the requirements in the
affirmative defense. The affirmative
defense is not available for claims for
injunctive relief.
(1) To establish the affirmative
defense in any action to enforce such a
limit, you must timely meet the
notification requirements in paragraph
(e)(2) of this section, and must prove by
a preponderance of evidence that: (i)
The excess emissions:
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(A) Were caused by a sudden,
infrequent and unavoidable failure of air
pollution control and monitoring
equipment, process equipment, or a
process to operate in a normal or usual
manner; and
(B) Could not have been prevented
through careful planning, proper design,
or better operation and maintenance
practices; and
(C) Did not stem from any activity or
event that could have been foreseen and
avoided, or planned for; and
(D) Were not part of a recurring
pattern indicative of inadequate design,
operation or maintenance; and
(ii) Repairs were made as
expeditiously as possible when the
applicable emission limitations were
being exceeded. Off-shift and overtime
labor were used, to the extent
practicable to make these repairs; and
(iii) The frequency, amount and
duration of the excess emissions
(including any bypass) were minimized
to the maximum extent practicable
during periods of such emissions; and
(iv) If the excess emissions resulted
from a bypass of control equipment or
a process, then the bypass was
unavoidable to prevent loss of life,
personal injury or severe property
damage; and
(v) All possible steps were taken to
minimize the impact of the excess
emissions on ambient air quality, the
environment and human health; and
(vi) All emissions monitoring and
control systems were kept in operation,
if at all possible, consistent with safety
and good air pollution control practices;
and
(vii) All of the actions in response to
the excess emissions were documented
by properly signed, contemporaneous
operating logs; and
(viii) At all times, the affected source
was operated in a manner consistent
with good practices for minimizing
emissions; and
(ix) A written root cause analysis has
been prepared, the purpose of which is
to determine, correct and eliminate the
primary causes of the malfunction and
the excess emissions resulting from the
malfunction event at issue. The analysis
must also specify, using best monitoring
methods and engineering judgment, the
amount of excess emissions that were
the result of the malfunction.
(2) Notification. If you experience an
exceedance of your emission limit(s)
during a malfunction, you must submit
a written report to the Administrator
within 45 business days of the initial
occurrence of the exceedance of the
standard(s) in §§ 63.11495 through
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14:25 Jan 27, 2012
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63.11499 to demonstrate, with all
necessary supporting documentation,
that it has met the requirements set forth
in paragraph (e)(1) of this section. You
may seek an extension of this deadline
for up to 30 additional business days by
submitting a written request to the
Administrator before the expiration of
the 45 business-day period. Until a
request for an extension has been
approved by the Administrator, you are
subject to the requirement to submit
such report within 45 business days.
7. Section 63.11502 is amended by:
a. Adding in alphabetical order the
term ‘‘Isolated intermediate
(§ 63.2550),’’ and removing the term
‘‘Family of materials (§ 63.2550)’’ in
paragraph (a); and
b. Adding in alphabetical order
definitions for ‘‘Affirmative defense,’’
‘‘Family of materials,’’ ‘‘Hazardous
waste treatment,’’ and ‘‘Uncontrolled
emissions,’’ revising paragraph (1) of the
definition of ‘‘Chemical manufacturing
process,’’ and revising the definitions
for ‘‘In organic HAP service’’ and
‘‘Product’’ in paragraph (b) to read as
follows:
§ 63.11502
subpart?
What definitions apply to this
(a) * * *
Isolated intermediate (§ 63.2550)
*
*
*
*
*
(b) * * *
Affirmative defense means, in the
context of an enforcement proceeding, a
response or defense put forward by a
defendant, regarding which the
defendant has the burden of proof, and
the merits of which are independently
and objectively evaluated in a judicial
or administrative proceeding.
*
*
*
*
*
Chemical manufacturing process
* * *
(1) All cleaning operations;
*
*
*
*
*
Family of materials means a grouping
of materials that have the same basic
composition or the same basic end use
or functionality; are produced using the
same basic feedstocks, the same
manufacturing equipment configuration
and in the same sequence of steps; and
whose production results in emissions
of the same Table 1 HAP at
approximately the same rate per pound
of product produced. Examples of
families of materials include multiple
grades of same product or different
variations of a product (e.g., blue, black
and red resins).
*
*
*
*
*
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Sfmt 4702
Hazardous waste treatment, as used
in the wastewater requirements, means
treatment in any of the following units:
(1) A hazardous waste incinerator for
which the owner or operator has been
issued a final permit under 40 CFR part
270 and complies with the requirements
of 40 CFR part 264, subpart O, or has
certified compliance with the interim
status requirements of 40 CFR part 265,
subpart O;
(2) A process heater or boiler for
which you either have been issued a
final permit under 40 CFR part 270 and
comply with the requirements of 40 CFR
part 266, subpart H, or for which you
have certified compliance with the
interim status requirements of 40 CFR
part 266, subpart H; or
(3) An underground injection well for
which the owner or operator has been
issued a final permit under 40 CFR part
270 or 40 CFR part 144 and complies
with the requirements of 40 CFR part
122.
*
*
*
*
*
In organic HAP service means that a
process vessel or piece of equipment
either contains or contacts a feedstock,
byproduct or product that contains an
organic HAP, excluding any organic
HAP used in manual cleaning activities.
A process vessel is no longer in organic
HAP service after the vessel has been
emptied to the extent practicable (i.e., a
vessel with liquid left on process vessel
walls or as bottom clingage, but not in
pools, due to floor irregularity, is
considered completely empty) and any
cleaning has been completed.
*
*
*
*
*
Product means a compound or
chemical which is manufactured as the
intended product of the CMPU.
Products include co-products. Byproducts, impurities, wastes and trace
contaminants are not considered
products.
*
*
*
*
*
Uncontrolled emissions means
process vent emissions at the outlet of
the last recovery device, if any, and
prior to any control device. In the
absence of both recovery devices and
control devices, uncontrolled emissions
are the emissions discharged to the
atmosphere.
*
*
*
*
*
Table 6 to Subpart VVVVVV of Part
63—[Amended]
8. Table 6 to subpart VVVVVV of part
63 is revised to read as follows:
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4539
Federal Register / Vol. 77, No. 19 / Monday, January 30, 2012 / Proposed Rules
TABLE 6 TO SUBPART VVVVVV OF PART 63—EMISSION LIMITS AND COMPLIANCE REQUIREMENTS FOR WASTEWATER
SYSTEMS
[As required in § 63.11498, you must comply with the requirements for wastewater systems as shown in the following table]
For each ...
You must ...
And you must ...
1. Wastewater Stream ........................................
a. Discharge to onsite or offsite wastewater
treatment or hazardous waste treatment.
i. Maintain records identifying each wastewater stream and documenting the type of
treatment that it receives. Multiple wastewater streams with similar characteristics
and from the same type of activity in a
CMPU may be grouped together for recordkeeping purposes.
2. Wastewater stream containing partially soluble HAP at a concentration ≥10,000 ppmw
and separate organic and water phases.
a. Use a decanter, steam stripper, thin film
evaporator, or distillation unit to separate
the water phase from the organic phase(s);
or
i. For the water phase, comply with the requirements in Item 1 of this table, and
ii. For the organic phase(s), recycle to a process, use as fuel, or dispose as hazardous
waste either onsite or offsite, and
iii. Keep records of the wastewater streams
subject to this requirement and the disposition of the organic phase(s).
b. Hard pipe the entire wastewater stream to
onsite hazardous waste treatment, or hard
pipe the entire wastewater stream to a point
of transfer to offsite hazardous waste treatment.
i. Keep records of the wastewater streams
subject to this requirement and the disposition of the wastewater streams.
9. Table 9 to subpart VVVVVV of part
63 is amended by:
a. Revising the entry for 63.6(e)(1)(i)
and (ii), (e)(3) and (f)(1);
b. Removing the entry for 63.7(a)(2),
(b), (d), (e)(1)–(e)(3);
c. Adding a new entry for 63.7(a)(2),
(b), (d), (e)(2)–(e)(3);
d. Adding a new entry for 63.7(e)(1);
e. Removing the entry for 63.8(a)(1),
(a)(4), (b), (c)(1)–(c)(3), (f)(1)–(5);
f. Adding new entries for 63.8(a)(1),
(a)(4), (b), (c)(1)(ii), (c)(2)–(c)(3), (f)(1)–
(5), and 63.8(c)(1)(i) and 63.8(c)(1)(iii);
g. Removing the entry for 63.8(c)(6)–
(c)(8), (d), (e), (f)(6);
h. Adding new entries for 63.8(c)(6)–
(c)(8), (d)(1)–(d)(2), (e), (f)(6) and
63.8(d)(3);
i. Removing the entry for
63.10(b)(2)(i)–(b)(2)(v);
j. Adding new entries for
63.10(b)(2)(i), 63.10(b)(2)(ii),
63.10(b)(2)(iii), and 63.10(b)(2)(iv)–(v);
k. Removing the entry for 63.10(c)(7)–
(c)(8), (c)(10)–(c)(12), (c)(15);
l. Adding new entries for 63.10(c)(7)–
(8), 63.10(c)(10), 63.10(c)(11),
63.10(c)(12) and 63.10(c)(15); and
m. Revising the entry for 63.10(d)(5)
to read as follows:
TABLE 9 TO SUBPART VVVVVV OF PART 63—APPLICABILITY OF GENERAL PROVISIONS TO SUBPART VVVVVV
Citation
*
Applies to Subpart
VVVVVV
Subject
*
*
Explanation
*
*
*
*
*
63.6(e)(1)(i) and (ii),
(e)(3), and (f)(1).
*
*
*
SSM Requirements .... No ...............................
*
*
See § 63.11495(d) for general duty requirement.
*
63.7(a)(2), (b), (d),
(e)(2)–(e)(3).
*
*
*
Performance Testing
Yes/No .......................
Schedule, Notification of Performance
Test, Performance
Testing Facilities,
and Conduct of Performance Tests.
Performance Testing .. No ...............................
*
*
*
Requirements apply if conducting test for metal HAP control; requirements in §§ 63.997(c)(1), (d), (e) and § 63.999(a)(1) apply, as
referenced in § 63.11496(g), if conducting test for organic HAP or
hydrogen halide and halogen HAP control device.
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63.7(e)(1) .....................
63.8(a)(1), (a)(4), (b),
(c)(1)(ii), (c)(2)–(c)(3),
(f)(1)–(5).
63.8(c)(1)(i) ..................
VerDate Mar<15>2010
Monitoring Requirements.
See § 63.11496(f)(3)(ii) if conducting a test for metal HAP emissions. See §§ 63.11496(g) and 63.997(e)(1) if conducting a test
for continuous process vents or for hydrogen halide and halogen
emissions. See §§ 63.11496(g) and 63.2460(c) if conducting a
test for batch process vents.
Yes .............................
General Duty to Minimize Emissions and
CMS Operation.
No ...............................
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E:\FR\FM\30JAP1.SGM
30JAP1
4540
Federal Register / Vol. 77, No. 19 / Monday, January 30, 2012 / Proposed Rules
TABLE 9 TO SUBPART VVVVVV OF PART 63—APPLICABILITY OF GENERAL PROVISIONS TO SUBPART VVVVVV—
Continued
Citation
Subject
Applies to Subpart
VVVVVV
63.8(c)(1)(iii) .................
Requirement to Develop SSM Plan for
CMS.
No ...............................
*
63.8(c)(6)–(c)(8),
(d)(1)–(d)(2), (e),
(f)(6).
63.8(d)(3) .....................
*
*
*
.................................... Yes .............................
*
63.10(b)(2)(i) ................
63.10(b)(2)(ii) ...............
63.10(b)(2)(iii) ..............
63.10(b)(2)(iv) and (v) ..
*
63.10(c)(7)–(8) .............
Written Procedures for
CMS.
Explanation
Yes .............................
*
*
*
Recordkeeping of Oc- No ...............................
currence and Duration of Startups and
Shutdowns.
Recordkeeping of Mal- No ...............................
functions.
Maintenance Records
Yes .............................
Actions Taken to Mini- No ...............................
mize Emissions During SSM.
63.10(c)(12) .................
63.10(c)(15) .................
*
*
*
Additional RecordYes .............................
keeping Requirements for CMS—
Identifying
Exceedances and
Excess Emissions.
Recordkeeping Nature No ...............................
and Cause of Malfunctions.
Recording Corrective
No ...............................
Actions.
.................................... Yes .............................
Use of SSM Plan ....... No ...............................
*
63.10(d)(5) ...................
*
*
*
SSM Reports .............. No ...............................
63.10(c)(10) .................
63.10(c)(11) .................
*
*
*
*
*
*
Requirements apply only if you use a continuous emission monitoring system (CEMS) to demonstrate compliance with the alternative standard in § 63.11496(e).
Requirement applies except for last sentence, which refers to an
SSM plan. SSM plans are not required.
*
*
*
See § 63.11501(c)(8) for recordkeeping of occurrence and duration
of each startup and shutdown for continuous process vents that
are subpart to Table 3 to this subpart.
See § 63.11501(c)(1)(vii) and (viii) for recordkeeping of (1) occurrence and duration and (2) actions taken during malfunction.
*
*
See § 63.11501(c)(1)(vii) and (viii) for malfunctions recordkeeping
requirements.
See § 63.11501(c)(1)(vii) and (viii) for malfunctions recordkeeping
requirements.
*
*
*
See § 63.11501(d)(8) for reporting requirements for malfunctions.
*
*
*
[FR Doc. 2012–1610 Filed 1–27–12; 8:45 am]
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E:\FR\FM\30JAP1.SGM
30JAP1
*
Agencies
[Federal Register Volume 77, Number 19 (Monday, January 30, 2012)]
[Proposed Rules]
[Pages 4522-4540]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2012-1610]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 63
[EPA-HQ-OAR-2008-0334; FRL-9621-7]
RIN 2060-AQ89
National Emission Standards for Hazardous Air Pollutants for
Chemical Manufacturing Area Sources
AGENCY: Environmental Protection Agency (EPA).
ACTION: Proposed rule; notice of reconsideration of final rule.
-----------------------------------------------------------------------
SUMMARY: On October 29, 2009, the EPA promulgated national emission
standards for the control of hazardous air pollutants for nine area
source categories in the chemical manufacturing sector: Agricultural
Chemicals and Pesticides Manufacturing, Cyclic Crude and Intermediate
Production, Industrial Inorganic Chemical Manufacturing, Industrial
Organic Chemical Manufacturing, Inorganic Pigments Manufacturing,
Miscellaneous Organic Chemical Manufacturing, Plastic Materials and
Resins Manufacturing, Pharmaceutical Production and Synthetic Rubber
Manufacturing. Following that action, the Administrator received a
petition for reconsideration. In response to the petition, the EPA is
reconsidering and requesting comment
[[Page 4523]]
on several provisions of the final rule. The EPA is also proposing
certain revisions to its approach for addressing malfunctions and
taking comment on those revisions. The EPA is further soliciting
comment on the standards applicable during startup and shutdown
periods, as set forth in the final rule. Additionally, the EPA is
proposing amendments and technical corrections to the final rule to
clarify applicability and compliance issues raised by stakeholders
subject to the final rule.
DATES: Comments. Comments must be received on or before March 30, 2012.
Public Hearing. If anyone contacts EPA requesting to speak at a
public hearing by February 9, 2012, a public hearing will be held on
February 14, 2012. For further information on the public hearing and
requests to speak, contact Ms. Janet Eck at (919) 541-7946 to verify
that a hearing will be held. If a public hearing is held, it will be
held at 10 a.m. at the EPA's Environmental Research Center Auditorium,
Research Triangle Park, North Carolina, or an alternate site nearby.
ADDRESSES: Submit your comments, identified by Docket ID No. EPA-HQ-
OAR-2008-0334, by one of the following methods:
www.regulations.gov: Follow the on-line instructions for
submitting comments.
Email: a-and-r-Docket@epa.gov, Attention Docket ID No.
EPA-HQ-OAR-2008-0334.
Fax: (202) 566-9744, Attention Docket ID No. EPA-HQ-OAR-
2008-0334.
Mail: U.S. Postal Service, send comments to: Air and
Radiation Docket and Information Center, Environmental Protection
Agency, Mailcode: 2822T, 1200 Pennsylvania Ave., NW., Washington, DC
20460, Attention Docket ID No. EPA-HQ-OAR-2008-0334.
Hand Delivery: In person or by courier, deliver comments
to: EPA Docket Center (2822T), Room 3334, 1301 Constitution Ave., NW.,
Washington, DC 20004. Such deliveries are only accepted during the
Docket's normal hours of operation, and special arrangements should be
made for deliveries of boxed information.
Instructions: Direct your comments to Docket ID No. EPA-HQ-OAR-
2008-0334. The EPA's policy is that all comments received will be
included in the public docket without change and may be made available
online at www.regulations.gov, including any personal information
provided, unless the comment includes information claimed to be
confidential business information (CBI) or other information whose
disclosure is restricted by statute. Do not submit information that you
consider to be CBI or otherwise protected through www.regulations.gov
or email. The www.regulations.gov Web site is an ``anonymous access''
system, which means the EPA will not know your identity or contact
information unless you provide it in the body of your comment. If you
send an email comment directly to the EPA without going through
www.regulations.gov, your email address will be automatically captured
and included as part of the comment that is placed in the public docket
and made available on the Internet. If you submit an electronic
comment, the EPA recommends that you include your name and other
contact information in the body of your comment and with any disk or
CD-ROM you submit. If the EPA cannot read your comment due to technical
difficulties and cannot contact you for clarification, the EPA may not
be able to consider your comment. Electronic files should avoid the use
of special characters, any form of encryption and be free of any
defects or viruses. For additional information about the EPA's public
docket, visit the EPA Docket Center homepage at https://www.epa.gov/epahome/dockets.htm.
Docket: All documents in the docket are listed in the
www.regulations.gov index. Although listed in the index, some
information is not publicly available, e.g., CBI or other information
whose disclosure is restricted by statute. Certain other material, such
as copyrighted material, will be publicly available only in hard copy.
Publicly available docket materials are available either electronically
in www.regulations.gov or in hard copy at the EPA Docket Center, EPA
West Building, Room 3334, 1301 Constitution Ave., NW., Washington, DC.
The Public Reading Room is open from 8:30 a.m. to 4:30 p.m., Monday
through Friday, excluding legal holidays. The telephone number for the
Public Reading Room is (202) 566-1744, and the telephone number for the
Docket Center is (202) 566-1742.
FOR FURTHER INFORMATION CONTACT: Mr. Nick Parsons, Refining and
Chemicals Group (E143-01), Sector Policies and Programs Division,
Office of Air Quality Planning and Standards, Environmental Protection
Agency, Research Triangle Park, North Carolina 27711; telephone number:
(919) 541-5372; fax number: (919) 541-0246; email address:
parsons.nick@epa.gov.
SUPPLEMENTARY INFORMATION:
Organization of this Document. The following outline is provided to
aid in locating information in this preamble.
I. General Information
A. Does this notice of reconsideration apply to me?
B. What should I consider as I prepare my comments to the EPA?
C. How do I obtain a copy of this document and other related
information?
II. Background Information
III. Actions We Are Taking
IV. Discussion of Issues for Reconsideration
A. Title V Permitting Requirements
B. Requirements When Other Rules Overlap With the Final Rule
C. Requirement To Conduct Direct and Proximal Leak Inspections
D. Requirement for Covers or Lids on Process Vessels
E. Requirement To Conduct Leak Inspections When Equipment Is in
HAP Service
F. Applicability of the Family of Materials Concept
V. Requirements During Periods of Startup, Shutdown and Malfunctions
(SSM)
VI. Requirements for Metal HAP Process Vents
A. Definition of Metal HAP Process Vent
B. Metal HAP Process Vent Standards
VII. Technical Corrections and Clarifications
VIII. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory Planning and Review and
Executive Order 13563: Improving Regulation and Regulatory Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation and Coordination With
Indian Tribal Governments
G. Executive Order 13045: Protection of Children From
Environmental Health Risks and Safety Risks
H. Executive Order 13211: Actions Concerning Regulations That
Significantly Affect Energy Supply, Distribution, or Use
I. National Technology Transfer and Advancement Act
J. Executive Order 12898: Federal Actions to Address
Environmental Justice in Minority Populations and Low-Income
Populations
A red-line version of the regulatory language that incorporates the
changes in this action is available in the docket.
I. General Information
A. Does this notice of reconsideration apply to me?
The regulated categories and entities potentially affected by this
action include:
[[Page 4524]]
----------------------------------------------------------------------------------------------------------------
NAICS
Industry category Code \1\ Examples of regulated entities
----------------------------------------------------------------------------------------------------------------
Chemical Manufacturing...................... 325 Chemical manufacturing area sources that use as
feedstock, generate as byproduct or produce as product,
any of the hazardous air pollutants (HAP) subject to
this subpart except for: (1) Processes classified in
NAICS Code 325222, 325314 or 325413; (2) processes
subject to standards for other listed area source
categories\2\ in NAICS Code 325; (3) certain
fabricating operations; (4) manufacture of photographic
film, paper and plate where material is coated or
contains chemicals (but the manufacture of the
photographic chemicals is regulated); and (5)
manufacture of radioactive elements or isotopes, radium
chloride, radium luminous compounds, strontium and
uranium.
----------------------------------------------------------------------------------------------------------------
\1\ North American Industry Classification System.
\2\ The source categories in NAICS Code 325 for which other area source standards apply are: Acrylic Fibers/
Modacrylic Fibers Production, Chemical Preparation, Carbon Black, Chemical Manufacturing: Chromium Compounds,
Polyvinyl Chloride and Copolymers Production, Paint and Allied Coatings and Mercury Cell Chlor-Alkali
Manufacturing.
This table is not intended to be exhaustive, but rather provides a
guide for readers regarding entities likely to be regulated by this
reconsideration action. To determine whether your facility may be
affected by this reconsideration action, you should examine the
applicability criteria in 40 CFR 63.11494 of subpart VVVVVV (National
Emission Standards for Hazardous Air Pollutants for Chemical
Manufacturing Area Sources). If you have any questions regarding the
applicability of the final rule to a particular entity, consult either
the air permit authority for the entity or your EPA regional
representative, as listed in 40 CFR 63.13.
B. What should I consider as I prepare my comments to the EPA?
Submitting CBI. Do not submit information that you consider to be
CBI electronically through https://www.regulations.gov or email. Send or
deliver information identified as CBI to only the following address:
Mr. Nick Parsons, c/o OAQPS Document Control Officer (Room C404-02),
U.S. Environmental Protection Agency, Research Triangle Park, North
Carolina 27711, Attn: Docket ID No. EPA-HQ-OAR-2008-0334.
Clearly mark the part or all of the information that you claim to
be CBI. For CBI information in a disk or CD-ROM that you mail to the
EPA, mark the outside of the disk or CD-ROM as CBI and then identify
electronically within the disk or CD-ROM the specific information that
is claimed as CBI. In addition to one complete version of the comment
that includes information claimed as CBI, a copy of the comment that
does not contain the information claimed as CBI must be submitted for
inclusion in the public docket. If you submit a disk or CD-ROM that
does not contain CBI, mark the outside of the disk or CD-ROM clearly
that it does not contain CBI. Information marked as CBI will not be
disclosed except in accordance with procedures set forth in 40 CFR part
2.
If you have any questions about CBI or the procedures for claiming
CBI, please consult the person identified in the FOR FURTHER
INFORMATION CONTACT section.
C. How do I obtain a copy of this document and other related
information?
Docket. The docket number for this action and the final rule (40
CFR part 63, subpart VVVVVV) is Docket ID No. EPA-HQ-OAR-2008-0334.
World Wide Web (WWW). In addition to being available in the docket,
an electronic copy of this action is available on the WWW through the
Technology Transfer Network (TTN) Web site. Following signature, a copy
of this notice will be posted on the TTN's policy and guidance page for
newly proposed or promulgated rules at https://www.epa.gov/ttn/oarpg.
The TTN provides information and technology exchange in various areas
of air pollution control.
II. Background Information
Section 112(d) of the Clean Air Act (CAA) requires the EPA to
establish national emission standards for hazardous air pollutants
(NESHAP) for both major and area sources of HAP that are listed for
regulation under CAA section 112(c). A major source is any stationary
source that emits or has the potential to emit 10 tons per year (tpy)
or more of any single HAP or 25 tpy or more of any combination of HAP.
An area source is a stationary source that is not a major source.
On October 29, 2009 (74 FR 56008), the EPA issued the NESHAP for
the nine chemical manufacturing area source (CMAS) categories that were
listed pursuant to CAA sections 112(c)(3) and 112(k)(3)(B). The nine
area source categories are Agricultural Chemicals and Pesticides
Manufacturing, Cyclic Crude and Intermediate Production, Industrial
Inorganic Chemical Manufacturing, Industrial Organic Chemical
Manufacturing, Inorganic Pigments Manufacturing, Miscellaneous Organic
Chemical Manufacturing, Plastic Materials and Resins Manufacturing,
Pharmaceutical Production and Synthetic Rubber Manufacturing.
CAA section 112(k)(3)(B) directs the EPA to identify at least 30
HAP that, as a result of emissions from area sources, pose the greatest
threat to public health in the largest number of urban areas. The EPA
implemented this provision in 1999 in the Integrated Urban Air Toxics
Strategy, (64 FR 38715, July 19, 1999) (Strategy). Specifically, in the
Strategy, the EPA identified 30 HAP that pose the greatest potential
health threat in urban areas, and these HAP are referred to as the ``30
urban HAP.'' Section 112(c)(3) of the CAA requires the EPA to list
sufficient categories or subcategories of area sources to ensure that
area sources representing 90 percent of the emissions of the 30 urban
HAP are subject to regulation. The EPA completed this requirement in
2011 (76 FR 15308, March 21, 2011). The chemical manufacturing area
source categories were listed to satisfy this requirement for 15 of the
30 urban HAP.\1\ Pursuant to CAA section 112(d)(5), the NESHAP reflect
generally available control technologies or management practices
(GACT). The NESHAP apply to each chemical manufacturing process unit
(CMPU) that uses, generates or produces any of the 15 urban HAP for
which the area source categories were listed (collectively ``chemical
manufacturing urban HAP'' or ``Table 1 HAP'').
---------------------------------------------------------------------------
\1\ The 15 urban HAP for which the chemical manufacturing area
source categories were listed are identified in table 1 of the final
rule.
---------------------------------------------------------------------------
On February 12, 2010, following promulgation of the final rule, the
EPA received a petition for reconsideration from the American Chemistry
Council (ACC) and the Society of Chemical Manufacturers & Affiliates
(SOCMA) (``Petitioners''). A copy of this petition is provided in the
docket (see Docket ID No. EPA-HQ-OAR-2008-0334). Petitioners, pursuant
to CAA section 307(d)(7)(B), requested that the EPA
[[Page 4525]]
reconsider six provisions in the rules: (1) The requirement that major
sources that installed air pollution controls after 1990, and, as a
result, became area sources, obtain a title V permit; (2) the
requirement that sources subject to the final rule and any overlapping
provision in another rule comply with each provision independently, or
with the most stringent requirements of each rule; (3) the requirement
that leak inspections include direct and proximal (thorough) inspection
of all areas of potential leak within the CMPU; (4) the requirement
that process vessels in HAP service be equipped with a cover or lid
that must be in place at all times when the vessel contains HAP, except
for material addition and sampling; (5) the requirement to conduct leak
inspections while the equipment is in HAP service; and (6) the
requirement that a CMPU include all equipment and processes used to
produce a ``family of materials.'' The arguments in support of these
requests are provided in the petition and described briefly below.
Petitioners also requested that the EPA stay the effectiveness of these
provisions of the rule to save many facilities from needlessly having
to file the initial notifications required by the final rule.
On June 15, 2010, the EPA sent a letter to Petitioners informing
them that the EPA was granting the request for reconsideration on at
least one issue raised in the petition, and that the agency would
identify the specific issue or issues for which it was granting
reconsideration in the reconsideration notice that would be published
in the Federal Register. The letter also indicated that the EPA
considered the request for a stay to be moot because the due date for
initial notifications had already passed.
III. Actions We Are Taking
In this notice, we are granting reconsideration of, and requesting
comment on, the six issues raised by Petitioners in their petition for
reconsideration. Section IV of this preamble summarizes these issues
and discusses our proposed responses to each issue.
We are also proposing additional provisions related to malfunctions
and requesting comment on the provisions in the final rule that address
periods of startup and shutdown. We are also proposing amendments to,
and taking comment on, the standards applicable to metal HAP process
vents. Finally, we are proposing technical corrections to certain
applicability and compliance provisions in the final rule.
We are seeking public comment only on the issues specifically
identified in this notice. We will not respond to any comments
addressing other aspects of the final rule or any other related
rulemakings.
IV. Discussion of Issues for Reconsideration
This section of the preamble contains the EPA's basis for our
proposed responses to the issues identified in the petition for
reconsideration. We solicit comment on all proposed responses and
revisions discussed in the following sections.
A. Title V Permitting Requirements
The EPA proposed to exempt all chemical manufacturing area sources
from the requirement to obtain a title V permit. In the final rule, in
response to comments and after a full review of the record, the EPA
stated that it was not finalizing the exemption for major sources that
became synthetic area sources by installing air pollution controls
after 1990. Among other things, the agency explained that we made the
change, in part, because we failed to consider the large number of such
sources in proposing the exemption, and because these sources had
uncontrolled emissions that made them much more like major sources. See
74 FR 56013, October 29, 2009. Petitioners maintain that the proposed
exemption of CMAS facilities from title V permitting requirements was
fully and correctly justified in the preamble to the proposed CMAS
rule. The Petitioners also claim:
The EPA's assertion in the final rule that facilities that
installed control equipment to become synthetic area sources are
``generally larger and more sophisticated'' than other chemical
manufacturing area sources contradicts our earlier finding in the
proposed rule that many of the facilities that would be affected by the
CMAS rule are small entities without the resources to comply with
permitting requirements. The Petitioners also state that approximately
87 percent of SOCMA members and 45 percent of ACC members are small
businesses, which they cite as support for the proposed finding.
The final rule fails to recognize that, in order for a
facility to be treated as a synthetic area source due to the
installation of controls, the facility has a legal duty to use the
equipment because the control requirement must be federally
enforceable. Further, the Petitioners state that, ``In order to have
been approved by the EPA, a state operating permit program that imposes
a federally enforceable requirement to use control equipment must
provide the public with notice and an opportunity to comment on draft
permits * * * and must also provide for emissions reporting and public
availability of reported information.''
The final rule is contrary to the decision in Alabama
Power Co. v. EPA, which held that a source's potential to emit is
determined by its design capacity and the anticipated functioning of
the air pollution control equipment. Thus, the petitioners claim that
whether a facility is a natural area source or a synthetic area source
(due to either operational limits or the use of control devices) should
not matter for regulatory purposes.
The EPA argued in the area source rules for asphalt
processing/asphalt roofing manufacturing, and paint and allied products
manufacturing, that state-delegated programs are sufficient to assure
compliance, and that it is not more difficult for citizens to enforce
the NESHAP absent a title V permit. According to the Petitioners, these
statements are equally, if not more, true for chemical manufacturing
synthetic area sources.
Title V requirements will impose substantial transactional
and compliance costs on subject facilities, and limit their flexibility
to respond to market opportunities.
In conclusion, Petitioners suggest that we should exempt all
chemical manufacturing area sources from the requirement to obtain a
title V permit consistent with the proposed rule. We reviewed our
rationale, as stated in the preamble to the final rule (74 FR 56013-
56014) and summarized below, for the final title V permitting
requirement for facilities that became synthetic area sources by virtue
of installing air pollution control devices after 1990. We continue to
believe that requiring title V for synthetic area sources that
installed controls to become area sources is appropriate; therefore, we
are not proposing to exempt such sources from the requirement to obtain
a title V permit. We are, however, making changes to the applicability
of the provision at issue. Instead of requiring a title V permit for
all synthetic area sources that installed air pollution controls in
order to become an area source, regardless of whether the controls were
installed on an affected CMPU, we are now proposing to only require a
title V permit for a synthetic area source if air pollution controls
were installed on at least one CMPU subject to the final rule in order
to become an area source. Such a limitation would be consistent with
the standards in the final rule that are applicable only to the CMPU
that emit one of the chemical manufacturing urban HAP. We are also
[[Page 4526]]
proposing to add provisions that inform sources when they must submit a
title V permit application consistent with the title V regulations at
40 CFR part 70 and 40 CFR part 71.
Pursuant to section 502(a) of the CAA, the Administrator may
``exempt one or more [area] source categories (in whole or in part)
from the requirements of [title V] if the Administrator finds that
compliance with such requirements is impracticable, infeasible, or
unnecessarily burdensome * * * .'' In December 2005, in a national
rulemaking, the EPA interpreted the term ``unnecessarily burdensome''
in CAA section 502, and developed a four-factor balancing test for
determining whether title V is unnecessarily burdensome for a
particular area source category, such that an exemption from title V is
appropriate. See 70 FR 75320, December 19, 2005 (Exemption Rule). The
EPA evaluated the chemical manufacturing area source categories
pursuant to the four-factor balancing test in the proposed rule, and
determined that title V permitting was unnecessarily burdensome. 73 FR
58371-58373. However, as stated above, the EPA did not finalize the
exemption for synthetic area sources that became area sources by
installing air pollution controls after November 15, 1990, in part,
because the agency failed to consider the large number of such sources
in proposing the exemption. 74 FR 56013. We explained the reasons for
our oversight, and then concluded that title V was not unnecessarily
burdensome and provided a reasoned basis for that conclusion, as
discussed below. 74 FR 56013-56014.
In the preamble to the final rule, we noted that the chemical
manufacturing area source categories are different from other area
source categories we have exempted because the categories include a
large number of synthetic area sources (major sources that installed
air pollution controls to become area sources) and the sources in the
other categories generally have very low emissions of HAP before
control. We then stated that at least 10 percent of the estimated 75
facilities that are synthetic area sources for HAP by virtue of
installing controls have uncontrolled HAP emissions over 100 tpy. We
also indicated that our information showed that many of the sources are
located in cities, and often in close proximity to residential and
commercial centers where large numbers of people live and work. We
further stated that these synthetic area sources have significantly
higher emissions potential when uncontrolled than the other sources in
the chemical manufacturing area source categories, and that they are
much more like the major sources of HAP subject to the Hazardous
Organic Chemical Manufacturing NESHAP (HON) and the Miscellaneous
Organic Chemical Manufacturing NESHAP (MON). For these reasons, and
other reasons set forth in the preamble to the final rule, we
determined that ``requiring additional public involvement and
compliance assurance requirements through title V is important to
ensure that these sources are maintaining their emissions at the area
source level, and, while there is some burden on the affected
facilities, we think that the burden is not significant because these
facilities are generally larger and more sophisticated than the natural
area sources and sources that took operational limits to become area
sources.'' 74 FR 56014.
Contrary to the Petitioners' first assertion, we do not believe
that there is a conflict between our finding that many CMAS facilities
are small entities that lack the technical and financial resources to
comply with title V, and our finding that CMAS facilities that are
synthetic area sources due to the use of control devices are generally
larger and more sophisticated than other facilities covered by the
final rule. The fact that nearly all SOCMA members are small businesses
does not, by itself, counter these findings. As we stated in the
preamble to the final rule, an estimated 450 CMAS facilities have
processes that would be subject to the rule. Of those, we estimated
that 75 are synthetic area sources by virtue of add-on controls, and
only 47 of these facilities were estimated to need a new title V permit
because the remainder of the sources are already subject to title V for
other reasons. Of the 47 sources that would require a new title V
permit under the requirement in the final rule, we estimated that at
least two-thirds of these facilities are large entities. Since we do
not know whether the add-on controls at these 75 facilities are
installed on a CMPU subject to the final rule, we cannot estimate the
total number of facilities that would be required to obtain a new title
V permit under this proposed revision to the title V permit
requirement. However, we believe that it would be less than the 47
facilities that would have required a new title V permit under the
final rule requirement. Based on information from SOCMA, approximately
270 member companies are small businesses. However, it is not clear how
many of these companies have facilities that are subject to the CMAS
rule, how many of the subject facilities are synthetic area sources for
HAP emissions due to the use of control devices or how many of the
synthetic area sources for HAP emissions are subject to title V
permitting requirements for other reasons. The information provided by
Petitioner ACC is similarly vague on this issue.
The Petitioners also argue that the title V requirement is not
appropriate because: (1) State operating permits that impose a
federally enforceable requirement must provide the public with notice
and the opportunity to comment on the draft permit; (2) synthetic area
source limits must be federally enforceable pursuant to the definition
of ``potential to emit'' at 40 CFR 63.2, and that it should not matter
whether an area source is synthetic or natural; (3) the EPA has
determined in other area source rules that state-delegated programs and
Federal enforceability of the standards is sufficient, and that
determination is equally applicable to the area sources subject to
title V in this rule; and (4) the requirement to obtain a title V
permit will impose substantial compliance costs and reduce flexibility
at the subject facilities. We are not proposing changes to the title V
permitting requirement based on these arguments because we do not
believe that they support a change in our position. First, while it is
true that the EPA regulations require Federal enforceability of
limitations on potential to emit HAP, Petitioners did not provide any
information as to the level of public participation required to obtain
such limits and whether the level of participation was as comprehensive
as that required pursuant to title V. Even if Petitioners could
demonstrate that the level of public participation was comparable to
that required under title V, our determination would not be altered on
that issue alone because title V has other important requirements that
may not apply to synthetic area sources that are not subject to title V
(e.g., the requirement to annually certify compliance with all
applicable requirements). Second, the EPA disagrees that natural and
synthetic area sources must be treated the same. As stated in the
preamble to the final rule, ``[synthetic area source] facilities are
generally larger and more sophisticated than the natural area sources
and sources that took operational limits to become area sources'' (74
FR 56014). Third, we explained in the preamble to the final rule that
the chemical manufacturing area sources are not similar to other area
source categories that we have exempted because of the
[[Page 4527]]
large number of synthetic area sources that installed add-on controls
and the high volume of pre-control device HAP emissions from the
chemical manufacturing area sources that added controls as compared
with other area sources. As these synthetic area sources have
essentially the same pre-control device HAP emissions potential as a
major source chemical manufacturing facility, we believe that the title
V permit requirement will help ensure that these control devices remain
in place and that these sources maintain their area source status.
Since it is possible that the non-operation, failure or
underperformance of a single control device could result in a source
within this category exceeding the major source emission threshold (10
tpy or more of any single HAP or 25 tpy or more of any combination of
HAP), we believe that the additional scrutiny that permitting
authorities place on sources with title V permits is warranted.
Finally, Petitioners have provided no information that demonstrates
that the cost of compliance for affected facilities will, in fact,
significantly burden the sources subject to the title V requirement, or
that such requirement will limit operational flexibility. We request
comments and information that address these issues, including
information and requirements that are required by state operating
permit programs, so that we can more thoroughly evaluate applicability
of title V for the identified sources.
As stated above, we are proposing changes to the applicability of
the title V permit requirement to synthetic area sources that installed
controls. The proposed changes more clearly identify the sources
subject to title V as those that route (or have routed) emissions from
at least one process unit subject to the final rule to a control
device(s) that is required to maintain synthetic area source status at
the facility, which will likely reduce the number of sources required
to obtain a title V permit, if promulgated. Specifically, because the
standards apply only to CMPU that meet the specific applicability
criteria in the rule, we request comment on whether the title V
permitting requirement should be applicable only if one or more of the
CMPU that are subject to the final standards are controlled by the air
pollution control equipment necessary for the facility to maintain area
source status. We are also proposing to include language that informs
sources subject to title V requirements when they must submit a title V
permit application. The EPA is including these new provisions because,
on March 14, 2011, the agency issued a final rule staying the
requirement to obtain a title V permit until the final reconsideration
rule is published in the Federal Register. 76 FR 13514. Because the
stay will be lifted once the final rule is published in the Federal
Register, we determined it was necessary to include an application
deadline for those existing sources currently subject to the final rule
to avoid confusion as to when title V permit applications would be due.
The proposed application deadline for existing sources provides the
full 12 months otherwise available to sources newly subject to title V
pursuant to the EPA regulations at 40 CFR part 70 and 40 CFR part 71.
See 40 CFR 70.5(a)(1) and 40 CFR 71.5(a)(1). We also propose to include
a provision indicating the time available for new sources and existing
sources that become subject to the rule after the effective date to
submit a title V permit application.\2\ We solicit comment on these
proposed changes to the final rule.
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\2\ Existing sources may become subject to the NESHAP for CMAS
after the effective date of the standards because the final rule
bases applicability on the use of chemical manufacturing urban HAP
(Table 1 HAP) in a CMPU. 40 CFR 63.11494. If a source begins using a
Table 1 HAP after the effective date, the facility will be subject
to the CMAS standards, and, if the source is a synthetic area source
that installed controls, the source will be subject to title V.
---------------------------------------------------------------------------
Additionally, we are soliciting comment on the promulgated final
rule requirement that required a facility to obtain a title V permit if
emissions from any process unit are (or have been) routed to the
control device(s) that is required to maintain synthetic area source
status at the facility.
We are requesting comment with supporting rationale on the
requirement, as specified in this proposed rule and the promulgated
final rule requirement outlined above. We are also interested in
information that would allow us to better estimate the burden under the
requirement in this proposed rule and the alternative. For example, we
are interested in results of any surveys that document: (1) The
percentage and/or number of CMAS facilities that are synthetic area
sources for HAP emissions because they use federally-enforceable
control devices; (2) the percentage and/or number of such facilities
that are using the control devices to control emissions from at least
one CMAS CMPU; (3) the financial burden of obtaining a title V permit
compared to sales; and (4) the percentage and/or number of such
facilities that are not already subject to title V requirements for
other reasons. We are not taking comment on our decision in the final
rule to exempt from title V chemical manufacturing areas sources that
are natural area sources or that took operational limits to become area
sources.
B. Requirements When Other Rules Overlap With the Final Rule
Petitioners note that their comments on the proposed rule urged the
EPA to include provisions in the final rule that would minimize the
burden associated with overlapping provisions between the CMAS rule and
other rules. Specifically, they recommended that the CMAS rule include
provisions to allow a facility subject to the CMAS rule and any other
applicable area or major source rule to opt to comply with either, and
noted that such an approach has been taken in many other rules. In
response to those comments, we added provisions to address overlapping
requirements in the final rule. See 40 CFR 63.11500. However,
Petitioners consider the overlapping rule requirements in the final
rule, which specify that a facility may elect to comply with the most
stringent provisions of the applicable rules as an alternative to
complying fully with each rule independently, to be ``unprecedented,
burdensome, and highly problematic.'' According to the Petitioners,
concerns with the alternative are that: (1) There can be uncertainty
regarding which provision is more stringent; (2) facilities will be at
risk that the EPA or a delegated authority will subsequently disagree
with the source's determination; and (3) the effort necessary to
construct a matrix of applicable requirements and determine which are
the most stringent will exceed available staff and financial resources
of many area sources. In addition, Petitioners state that complying in
every respect with two overlapping rules is bound to involve
substantial duplication, and, in some cases, may not be possible due to
conflicts between the two rules. For these reasons, Petitioners
recommend that we either propose to eliminate the final language or
request comment on it.
We disagree with the Petitioners' assertion that the requirements
in the final rule are unprecedented and procedurally invalid. In the
absence of the language in the final rule, a facility would be required
to comply with all applicable requirements in both the CMAS rule and
all other applicable rules, regardless of whether some equipment is
subject to more than one rule. The final CMAS rule merely made explicit
the implicit requirement to comply with all applicable standards. It
was in response to Petitioners' comments that the agency provided an
[[Page 4528]]
overlapping requirements alternative that allows a facility to identify
and comply with only one set of requirements (i.e., the most stringent
requirements in the overlapping rules). The alternative was intended as
a means of reducing the compliance burden without diminishing the level
of environmental protection provided by each rule.
We did not include language that defines the more stringent
requirements, as found in other rules, due to the great variety in
characteristics of CMAS processes and the wide variety of compliance
options in both the CMAS rule and overlapping rules. This variety makes
it difficult to develop language that would not inadvertently allow a
CMAS facility to comply with requirements less stringent than those
contained in 40 CFR part 63, subpart VVVVVV, or less stringent than the
required control level in an overlapping rule. Furthermore, as noted in
the economic and control cost impacts analyses (see Docket ID No. EPA-
HQ-OAR-2008-0334-0079), we expect that most CMAS facilities will be
subject to only the management practices in subpart VVVVVV. For those
sources, we anticipate that it generally will not be difficult or
burdensome to determine which requirements in subpart VVVVVV and an
overlapping rule are the most stringent. For those sources that are
unable to determine the more stringent requirement between subpart
VVVVVV and an overlapping requirement, we believe it would be more
appropriate to address those situations on a case-by-case basis.
We are granting reconsideration of the overlapping provisions
requirement in 40 CFR 63.11500 of the final rule to allow comment on
both the language in the final rule and any alternative suggestions.
Specifically, we are interested in language that would reduce the
compliance burden for the CMAS rule and any overlapping rules combined,
yet assure that all requirements in the CMAS rule are met. We are also
interested in specific examples of requirements in overlapping rules
that conflict with requirements in the CMAS final rule.
C. Requirement To Conduct Direct and Proximal Leak Inspections
In the final rule, the EPA revised the provision for inspections to
require that facilities conduct a ``direct and proximal (thorough)
inspection of all areas of potential leak within the CMPU.''
Petitioners object to the requirement in the final rule to conduct
``direct and proximal (thorough)'' inspections because they believe it
requires inspections without regard to safety or difficulty of access.
Petitioners also note that areas that are difficult to inspect or
unsafe to inspect or monitor are exempted from regular inspection
requirements in other rules, and they point out that, in their comments
on the proposed CMAS rule, they requested clarification that sensory
inspections may be done from a distance when equipment is either
inaccessible or unsafe for close visual inspection. Therefore,
Petitioners maintain that the agency should either propose to eliminate
the direct and proximal inspection requirement or request comment on
it.
We have determined that the inspections required in the final rule
require control that is more stringent than GACT because we are not
aware of any facility conducting direct and proximal inspections of all
process vessels and equipment. For this reason, and to address
Petitioners' concerns, we are proposing to delete the requirement for
direct and proximal inspections. However, we want to assure that
sensory inspections be performed at distances such that the results are
meaningful.
As a result, we are proposing that the amended rule would specify
that a facility must conduct quarterly sensory inspections of all
equipment and process vessels, provided these methods are capable of
detecting leaks within the CMPU (i.e., the inspector is within
sufficient proximity to the equipment that leaking equipment can be
detected by sight, sound or smell). We are not, however, proposing to
exempt equipment that is difficult or unsafe to monitor. Rules that
provide such exemptions do so because they require instrument
monitoring that relies on being able to locate the instrument probe
very close to the equipment being inspected (e.g., see 40 CFR part 63,
subparts TT and UU). Sensory monitoring does not require intimate
contact with each piece of equipment to be effective at identifying
leaks. In addition, due to the wide variety of design and operating
conditions throughout the source category, we also are not proposing
criteria regarding an acceptable distance for inspection or the types
of conditions under which the inspection may be conducted from a
distance. Our intent is that each facility should conduct inspections
as close as practical to the equipment to be able to detect leaks while
also following procedures contained in site-specific safety plans. The
proposed requirements would be consistent with sensory inspection
requirements in 40 CFR part 63, subpart R. We request comment on both
the direct and proximal language in the final rule and these proposed
revisions.
D. Requirement for Covers or Lids on Process Vessels
We proposed to require process vessels in HAP service be closed
``except when operator access is necessary.'' 73 FR 58377 (proposed 40
CFR 63.11495(a)). The final rule requires process vessels in HAP
service to be equipped with a cover or lid that must be in place at all
times when the vessel contains HAP, ``except for material addition and
sampling.'' 40 CFR 63.11495(a)(1). Petitioners contend that compliance
with this management practice requirement is impossible due to safety
issues and because it does not consider the need to take material out
of a vessel or to conduct maintenance. Petitioners are particularly
concerned that the requirement does not appear to allow openings for
any type of maintenance, even after the process is shut down, and only
trace levels of HAP are present. In subsequent correspondence,
Petitioners suggest that their concerns would be resolved if we modify
the rule so that the cover or lid requirement applies only when a
process vessel is ``in use'' (which is a concept that they state can be
easily applied), and clarify that ``in use'' does not include routine
cleaning operations. See Docket ID No. EPA-HQ-OAR-2008-0334.
Petitioners explain that the exclusion for cleaning is needed because
the definition of a ``chemical manufacturing process'' includes routine
cleaning operations, but vessels must be opened for cleaning.
Therefore, the Petitioners state that we should either propose changes
that would require the use of covers or lids only when subject process
vessels are in use, or seek comments on the requirement as written in
the final rule.
We are granting reconsideration of the requirement to use a cover
or lid on process vessels because the Petitioners comments indicate
that the requirement can be interpreted as requiring control more
stringent than we intended. The proposed rule specified that ``all
process equipment in which organic HAP is used to process material must
be covered when in use, and closure mechanisms on other openings and
access points in process equipment must be in the closed position
during operation, except when operator access is necessary.'' 73 FR
58377 (proposed 40 CFR 63.11495(a)). The intent of the requirement for
covers in the proposed rule was to ensure that processes do not operate
with open-top vessels. The purpose of the cover is to minimize
[[Page 4529]]
emissions from surface evaporation, but not necessarily to have a tight
seal between the cover and the vessel. For the final rule, we tried to
clarify what ``in use'' and ``operator access'' meant by specifying
that the cover (or lid) ``must be in place at all times when the vessel
contains HAP, except for material addition and sampling.'' However, as
the Petitioners have pointed out, the revised language can be
interpreted as prohibiting removal of the cover, even when only traces
of HAP remain in the vessel after it has been drained, which would
prohibit opening to perform maintenance or manual cleaning. Requiring
use of the cover in this way is not GACT, and it was not our intent.
To address the Petitioners' issues, we are proposing to revise 40
CFR 63.11495(a)(1) in the final rule to read as follows: ``Each process
vessel must be equipped with a cover or lid that must be closed
whenever the vessel is in organic HAP service or metal HAP service,
except for manual operations that require access, such as material
addition and removal, inspection, sampling, and cleaning.'' We note
that allowing opening of a process vessel for material removal
clarifies that process vessels, such as filter presses, may be opened
in order to remove the filter cake.
The proposed change also would exempt manual cleaning operations
from the requirement to maintain closed covers and lids while a process
vessel is in organic HAP or metal HAP service. As the Petitioners
noted, the definition of ``chemical manufacturing process'' is drawn
from the definition of a ``miscellaneous organic chemical manufacturing
process'' in 40 CFR 63.2550 of the MON. That definition includes
``routine cleaning operations,'' which are described in the preamble to
the final MON as ``cleaning conducted within enclosed equipment between
batches or between campaigns.'' The MON preamble goes on to state that
these operations ``often consist of conducting solvent rinses through
the equipment,'' and emissions are characterized as part of the
emissions from a batch process vent. See 68 FR 63860, November 10,
2003. Contrary to Petitioner's assertion, this type of cleaning was
included as part of the process specifically because we considered the
vessels to be ``in use'' while it is conducted. We also consider
vessels to be in use when manual cleaning is performed. To clarify this
point, we are proposing to revise the definition of ``chemical
manufacturing process'' to specify that all cleaning activities are
part of the process. However, because GACT does not include the use of
closed covers and lids when performing manual cleaning, we are
proposing two additional changes. First, we are proposing the change
noted above to exempt manual cleaning operations from the requirement
to maintain covers and lids in the closed position when the vessel is
in organic HAP service or metal HAP service. Second, we are proposing
to revise the definition of ``in organic HAP service'' to specify that
a process vessel is no longer in organic HAP service after the vessel
has been emptied to the extent practicable (i.e., a vessel with liquid
left on process vessel walls or as bottom clingage, but not in pools,
due to floor irregularity, is considered completely empty), and any
cleaning has been completed. We expect emissions to be minimal during
manual cleaning operations and when a process vessel is no longer in
organic HAP service. We are not proposing any changes to 40 CFR
63.11494(a)(1) regarding maintenance activities because those
activities would be conducted after the vessel has been drained (and
possibly cleaned) and the vessel would no longer be in organic HAP
service.
We request comments on both the provisions, as specified in the
final rule and the proposed changes. Specifically, we request comment
on whether the proposed changes effectively address the issues raised
by Petitioners, and clarify the requirements without introducing
unintended consequences. We also request comment on whether a change
like that proposed for the definition of ``in organic HAP service'' is
needed for the definition of ``in metal HAP service.'' In particular,
we request comment on whether a change is needed to address when
vessels that contain metal HAP in the form of particulate are in use,
and, if so, we request information on the types of vessels for which
the change is needed and recommendations on how the language in the
definition could be structured. We are also requesting comment on
possible changes to the requirements for cleaning that would include
requirements for manual cleaning as well as for automated rinses
through closed equipment.
E. Requirement To Conduct Leak Inspections When Equipment Is in HAP
Service
Petitioners state that ``the final rule can be read to imply that
the equipment must be in HAP service when the inspection is
conducted.'' Petitioners note that this is in contrast to the proposed
rule, which would have required quarterly inspections without
specifying any other conditions. Petitioners stated that they did not
comment on the proposed language because they considered it to be
reasonable; however, Petitioners contend that the apparent requirement
in the final rule is problematic because batch processors who operate
equipment in HAP service for short periods of time and have limited
operating personnel may find it difficult to accomplish the required
inspections during these narrow windows of time. Petitioners ask for
clarification about whether this interpretation is correct, and, if it
is, Petitioners state that we should either propose reverting to the
proposed language, or propose language allowing quarterly leak
detection and repair inspections when the equipment is in volatile
organic compound (VOC) service, not just HAP service.
Based on our review of this issue, we are proposing some editorial
changes to 40 CFR 63.11495(a)(3) of the final rule to make the rule
easier to read and understand. These changes are described in Section
VII of this preamble. However, we decided not to propose changes as
suggested by the Petitioners because we have several concerns regarding
how inspections can be conducted effectively when the process is not
operating in HAP service. We request comment on both the specific
concerns described below, as well as all other aspects of the
requirements in the final rule related to the timing of inspections.
First, because the configuration of process vessels and equipment
likely changes from one CMPU to the next, we request comment on how
sources would track which vessels and equipment to inspect in VOC
service if we adopted Petitioners' approach and whether this effort
would negate any advantages of having flexibility to inspect at times
other than when the subject CMPU is operating in organic HAP service.
Second, process vessels are generally opened and cleaned when
reconfiguring to create a different CMPU, and equipment connections are
also often opened. Therefore, we also request comment discussing how
inspections in VOC service for a different configuration would provide
information that is relevant to determining whether there are leaks
from the subject CMPU. Finally, if someone elects to conduct Method 21
monitoring rather than sensory inspections, the instrument reading
obtained would be related to the concentration of organic compound in
the fluid and the response factor of the instrument for that organic
compound. Thus, we request comment on the need to specify criteria for
the type of fluid
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that may be used when conducting inspections of vessels and equipment
in VOC service (e.g., that the VOC concentration must be no less than
the total organic compound concentration in the subject CMPU when in
organic HAP service). We will consider adopting the Petitioners'
approach after reconsideration if we can adequately address these
issues.
F. Applicability of the Family of Materials Concept
After proposal, the rule was revised in response to comments from
Petitioners and others that argued applicability should be established
on a CMPU basis instead of facility-wide basis. Petitioners
specifically suggested that the EPA adopt the CMPU construct. We
defined the CMPU in the final rule to include ``all process vessels,
equipment, and activities necessary to operate a chemical manufacturing
process that produces a material or family of materials * * *. A CMPU
consists of one or more unit operations and any associated recovery
device.'' 40 CFR 63.11494(b). In adopting the CMPU construct, we
determined that, to adequately characterize the CMPU, the applicability
of the rule should extend to the ``family of materials'' because the
CMPU concept is derived from the MON, and production of a family of
materials is part of a single process unit in the MON. Furthermore, as
in the MON, the CMAS rule specifies mass emission thresholds above
which more stringent control of batch process vents is required.
Petitioners state that it can be difficult under the CMAS rule to
determine what constitutes a family of materials. Petitioners believe
that the term ``family of materials'' effectively expands the scope of
a CMPU to include equipment that is not part of a process that uses or
produces Table 1 HAP. Petitioners contend that there is no policy
justification for applying the CMAS rule this broadly. Therefore,
Petitioners request that the EPA interpret the ``family of materials''
term in such a way as to avoid regulating equipment that is not used to
process a Table 1 HAP. Alternatively, Petitioners suggest that the EPA
propose eliminating the phrase ``or a family of materials'' from the
rule.
The definition of ``family of materials'' in the MON, and
referenced in 40 CFR 63.11502 of the CMAS final rule, is as follows:
Family of materials means a grouping of materials with the same
basic composition or the same basic end use or functionality
produced using the same basic feedstocks with essentially identical
HAP emission profiles (primary constituent and relative magnitude on
a pound per pound basis) and manufacturing equipment configuration.
Examples of families of materials include multiple grades of the
same product or different variations of a product (e.g., blue, black
and red resins).
As in the MON, the intent of the family of materials concept in 40
CFR part 63, subpart VVVVVV is to ensure that sources will not be able
to improperly avoid installation of add-on controls for batch process
vent emissions by creating separate CMPU for production of essentially
the same products (i.e., products produced from the same basic raw
materials, with essentially identical HAP emissions, and using the same
configuration of manufacturing equipment). For example, a series of
polymer products that differ only in molecular weight or the type of
non-HAP additive are considered a family of materials when the same
primary raw materials are used, the same types of HAP are emitted and
the same configuration of production equipment is used. However,
because the definition of family of materials in the final rule uses
the term ``essentially'' identical HAP emission profiles, a family of
materials potentially could include some products whose production does
not involve Table 1 HAP. Therefore, to clarify the requirements, we are
proposing to revise the definition of family of materials to state that
only those products whose production involves emission of the same
Table 1 HAP are to be considered part of a family of materials.
We also want to clarify the family of materials concept as it
relates to production of isolated intermediates. A chemical
manufacturing process is defined, in part, as ``all equipment which
collectively functions to produce a product or isolated intermediate.''
An isolated intermediate is defined, in part, as ``a product of a
process that is stored before subsequent processing.'' (As discussed in
section VII of this preamble, we are proposing to add a definition of
``isolated intermediate'' that is consistent with the definition in the
MON.) Even if an isolated intermediate and final product are produced
using the same manufacturing equipment configuration and have the same
Table 1 HAP emissions, they generally cannot be part of a family of
materials because the definition specifies production of all products
in the family must involve the same basic feedstocks. This condition
would not be met if an isolated intermediate is used as a feedstock in
later production of a final product. Furthermore, the definition of
family of materials specified that all products in the family must have
the same basic composition, end use, or functionality. This condition
also would not be met in a situation where the isolated intermediate is
transformed in the process to produce the final product.
We are requesting comment on all aspects of the family of materials
concept, including the proposed change. We are particularly interested
in descriptions of situations where someone thinks it would apply, but
should not, and we request suggestions for additional changes that
would make it easier to understand, apply and enforce. We are not,
however, accepting comments on the use of the CMPU as the basis for
determining applicability of the CMAS final rule.
V. Requirements During Periods of Startup, Shutdown and Malfunction
(SSM)
During the comment period of the proposed rule, the United States
Court of Appeals for the District of Columbia Circuit vacated two
provisions in the EPA's CAA section 112 regulations governing the
emissions of HAP during periods of startup, shutdown and malfunction
(SSM). Sierra Club v. EPA, 551 F.3d 1019 (D.C. Cir. 2008), cert.
denied, 130 S. Ct. 1735 (U.S. 2010). Specifically, the Court vacated
the SSM exemption contained in 40 CFR 63.6(f)(1) and 40 CFR 63.6(h)(1),
that are part of a regulation, commonly referred to as the ``General
Provisions Rule,'' that the EPA promulgated under section 112 of the
CAA. When incorporated into CAA section 112(d) regulations for specific
source categories, the exemption in these two provisions exempts
sources from the requirement to comply with the otherwise applicable
CAA section 112(d) emission standard during periods of SSM.
The proposed CMAS rule contained references to the vacated
provisions. Because the provisions were vacated, we removed the
references in the final rule, and, in their place, we included
alternative standards for startup and shutdown periods for continuous
process vents. Table 3 to 40 CFR part 63, subpart VVVVVV. For batch
process vents, we determined that startup and shutdown periods were
already accounted for in the existing standard, and we determined that
the remaining equipment did not have periods of startup and shutdown.
74 FR 56013. We declined to establish a different standard for
malfunctions, as suggested by commenters. 74 FR 56033.
Further, as explained in the preamble to the final rule (74 FR
56033), periods of startup, normal operations and shutdown are all
predictable and
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routine aspects of a source's operations. However, by contrast,
malfunction is defined as a ``sudden, infrequent, and not reasonably
preventable failure of air pollution control and monitoring equipment,
process equipment or a process to operate in a normal or usual manner *
* *'' (40 CFR 63.2). Nothing in CAA section 112(d) or in case law
requires that the EPA anticipate and account for the innumerable types
of potential malfunction events in setting emission standards. See
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.'').
Further, it is reasonable to interpret CAA section 112(d) as not
requiring the EPA to account for malfunctions in setting emissions
standards.
We believe it would be impracticable to take malfunctions into
account in setting CAA section 112(d) standards for chemical
manufacturing area sources. As noted above, by definition, malfunctions
are sudden and unexpected events, and it would be difficult to set a
standard that takes into account the myriad different types of
malfunctions that can occur across all sources in the categories.
Moreover, malfunctions can vary in frequency, degree and duration,
further complicating standard setting. See, e.g., Sierra Club v. EPA,
167 F.3d 658, 662 (D.C. Cir. 1999) (the EPA typically has