National Emission Standards for Hazardous Air Pollutants: Publicly Owned Treatment Works Residual Risk and Technology Review, 49513-49533 [2017-23067]
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Federal Register / Vol. 82, No. 206 / Thursday, October 26, 2017 / Rules and Regulations
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 63
[EPA–HQ–OAR–2016–0490; FRL–9969–95–
OAR]
RIN 2060–AS85
National Emission Standards for
Hazardous Air Pollutants: Publicly
Owned Treatment Works Residual Risk
and Technology Review
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
This action finalizes the
residual risk and technology review
(RTR) conducted for the Publicly
Owned Treatment Works (POTW)
source category regulated under
national emission standards for
hazardous air pollutants (NESHAP). In
addition, we are taking final action
addressing revised names and
definitions of the subcategories,
revisions to the applicability criteria,
revised regulatory provisions pertaining
to emissions during periods of startup,
shutdown, and malfunction (SSM),
initial notification requirements for
existing Group 1 and Group 2 POTW,
revisions to the requirements for new
Group 1 POTW, requirements for
electronic reporting, and other
miscellaneous edits and technical
corrections. While we do not anticipate
any emission reductions as a result of
these revisions, the changes should
provide clarity for sources determining
applicability and ensuring compliance.
DATES: This final rule is effective on
October 26, 2017.
ADDRESSES: The Environmental
Protection Agency (EPA) has established
a docket for this action under Docket ID
No. EPA–HQ–OAR–2016–0490. All
documents in the docket are listed on
the https://www.regulations.gov Web
site. Although listed in the index, some
information is not publicly available,
e.g., confidential business information
(CBI) or other information whose
disclosure is restricted by statute.
Certain other material, such as
copyrighted material, is not placed on
the Internet and will be publicly
available only in hard copy form.
Publicly available docket materials are
available either electronically through
https://www.regulations.gov, or in hard
copy at the EPA Docket Center, EPA
WJC West Building, Room Number
3334, 1301 Constitution Ave. NW.,
Washington, DC. The Public Reading
Room hours of operation are 8:30 a.m.
to 4:30 p.m. Eastern Standard Time
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SUMMARY:
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(EST), Monday through Friday,
excluding legal holidays. The telephone
number for the Public Reading Room is
(202) 566–1744, and the telephone
number for the EPA Docket Center is
(202) 566–1742.
FOR FURTHER INFORMATION CONTACT: For
questions about this final action, contact
Katie Hanks, Sector Policies and
Programs Division (E143–03), Office of
Air Quality Planning and Standards,
U.S. Environmental Protection Agency,
Research Triangle Park, North Carolina,
27711; telephone number: (919) 541–
2159; fax number: (919) 541–0516; and
email address: hanks.katie@epa.gov. For
specific information regarding the risk
modeling methodology, contact Terri
Hollingsworth, Health and
Environmental Impacts Division (C539–
02), Office of Air Quality Planning and
Standards, U.S. Environmental
Protection Agency, Research Triangle
Park, North Carolina 27711; telephone
number: (919) 541–5623; fax number:
(919) 541–0840; and email address:
hollingsworth.terri@epa.gov. For
information about the applicability of
the NESHAP to a particular entity,
contact Sara Ayres, Office of
Enforcement and Compliance
Assurance, U.S. Environmental
Protection Agency, 77 West Jackson
Boulevard (E–19J), Chicago, Illinois
60604; telephone number: (312) 353–
6266; and email address: ayres.sara@
epa.gov.
SUPPLEMENTARY INFORMATION:
Preamble acronyms and
abbreviations. We use multiple
acronyms and terms in this preamble.
While this list may not be exhaustive, to
ease the reading of this preamble and for
reference purposes, the EPA defines the
following terms and acronyms here:
CAA Clean Air Act
CBI confidential business information
CDX Central Data Exchange
CEDRI Compliance and Emissions Data
Reporting Interface
ERT Electronic Reporting Tool
HAP hazardous air pollutants(s)
HQ hazard quotient
H2S hydrogen sulfide
ICR Information Collection Request
MACT maximum achievable control
technology
MGD million gallons per day
MIR maximum individual risk
NESHAP national emission standards for
hazardous air pollutants
NPDES National Pollutant Discharge
Elimination System
NTTAA National Technology Transfer
and Advancement Act
PB–HAP Hazardous air pollutants known
to be persistent and bio-accumulative in the
environment
POTW Publicly Owned Treatment Works
RFA Regulatory Flexibility Act
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RIN Regulatory Information Number
RTR Risk and Technology Review
SSM startup, shutdown and malfunction
TOSHI Target Organ Specific Hazard
Index
UMRA Unfunded Mandates Reform Act
Background information. On
December 27, 2016, the EPA proposed
revisions to the POTW NESHAP based
on our RTR. In this action, we are
finalizing decisions and revisions for
the rule. We summarize some of the
more significant comments we timely
received regarding the proposed rule
and provide our responses in this
preamble. A summary of all other public
comments on the proposal and the
EPA’s responses to those comments is
available in Response to Public
Comments on the EPA’s Residual Risk
and Technology Review for the Publicly
Owned Treatment Works Source
Category in Docket ID No. EPA–HQ–
OAR–2016–0490. A ‘‘track changes’’
version of the regulatory language that
incorporates the changes in this action
is available in the docket.
Organization of this document. The
information in this preamble is
organized as follows:
I. General Information
A. Does this action apply to me?
B. Where can I get a copy of this document
and other related information?
C. Judicial Review and Administrative
Reconsideration
II. Background
A. What is the statutory authority for this
action?
B. What is the POTW source category and
how does the NESHAP regulate HAP
emissions from the source category?
C. What changes did we propose for the
POTW source category in our December
27, 2016, RTR proposal?
III. What is included in this final rule?
A. What are the final rule amendments
based on the risk review for the POTW
source category?
B. What are the final rule amendments
based on the technology review for the
POTW source category?
C. What are the final rule amendments
addressing emissions during periods of
startup, shutdown, and malfunction?
D. What other changes have been made to
the NESHAP?
E. What are the effective and compliance
dates of the standards?
F. What are the requirements for
submission of performance test data to
the EPA?
IV. What is the rationale for our final
decisions and amendments for the
POTW source category?
A. Residual Risk Review for the POTW
Source Category
B. Technology Review for the POTW
Source Category
C. Applicability Criteria
D. Emissions From Collection Systems
E. Pretreatment Requirements
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F. HAP Fraction Emitted for Existing
Group 1 and Group 2 Sources
G. New and Existing Group 1 POTW
V. Summary of Cost, Environmental, and
Economic Impacts and Additional
Analyses Conducted
A. What are the affected facilities?
B. What are the air quality impacts?
C. What are the cost impacts?
D. What are the economic impacts?
E. What are the benefits?
F. What analysis of environmental justice
did we conduct?
G. What analysis of children’s
environmental health did we conduct?
VI. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory
Planning and Review and Executive
Order 13563: Improving Regulation and
Regulatory Review
B. Executive Order 13771: Reducing
Regulations and Controlling Regulatory
Costs
C. Paperwork Reduction Act (PRA)
D. Regulatory Flexibility Act (RFA)
E. Unfunded Mandates Reform Act
(UMRA)
F. Executive Order 13132: Federalism
G. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
H. Executive Order 13045: Protection of
Children From Environmental Health
Risks and Safety Risks
I. Executive Order 13211: Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use
J. National Technology Transfer and
Advancement Act (NTTAA)
K. Executive Order 12898: Federal Actions
To Address Environmental Justice in
Minority Populations and Low-Income
Populations
L. Congressional Review Act (CRA)
I. General Information
A. Does this action apply to me?
Regulated entities. Categories and
entities potentially regulated by this
action are shown in Table 1 of this
preamble.
intermunicipal or interstate agency, or
any department, agency, or
instrumentality of the federal
government (see 40 CFR 63.1595 of
subpart VVV). To determine whether
your facility is affected, you should
examine the applicability criteria in the
POTW NESHAP. Specifically, if a
POTW is a Group 2 POTW 1 that is a
major source of hazardous air pollutant
(HAP) emissions or a Group 1 POTW
regardless of the HAP emissions, and
the POTW meets the criteria for
development and implementation of a
pretreatment program according to 40
CFR 403.8, then the POTW is affected
by these standards. If you have any
questions regarding the applicability of
any aspect of this NESHAP, please
contact the appropriate person listed in
the preceding FOR FURTHER INFORMATION
CONTACT section of this preamble.
B. Where can I get a copy of this
document and other related
information?
In addition to being available in the
docket, an electronic copy of this final
action will also be available on the
Internet. Following signature by the
EPA Administrator, the EPA will post a
copy of this final action at https://
www.epa.gov/stationary-sources-airpollution/publicly-owned-treatmentworks-potw-national-emissionstandards. Following publication in the
Federal Register, the EPA will post the
Federal Register version and key
technical documents at this same Web
site.
Additional information is available on
the RTR Web site at https://
www.epa.gov/ttn/atw/rrisk/rtrpg.html.
This information includes an overview
of the RTR program, links to project
Web sites for the RTR source categories,
and detailed emissions and other data
we used as inputs to the risk
assessments.
TABLE 1—NESHAP AND INDUSTRIAL
SOURCE CATEGORIES AFFECTED BY C. Judicial Review and Administrative
Reconsideration
THIS FINAL ACTION
NESHAP and source
category
NESHAP
NAICS 1
code
Sewage Treatment Facilities.
Subpart VVV .....
221320
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1 North
American Industry Classification System.
Table 1 of this preamble is not
intended to be exhaustive, but rather to
provide a guide for readers regarding
entities likely to be affected by the final
action for the source category listed. The
standards are directly applicable to the
affected sources. Federal, state, local,
and tribal governments are affected as
discussed below. By definition, a POTW
is owned by a municipality, state,
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Under Clean Air Act (CAA) section
307(b)(1), judicial review of this final
action is available only by filing a
petition for review in the United States
Court of Appeals for the District of
Columbia Circuit by December 26, 2017.
Under CAA section 307(b)(2), the
requirements established by this final
rule may not be challenged separately in
any civil or criminal proceedings
1 As discussed below in section III.D of this
preamble, the terms ‘‘Group 1 POTW’’ and ‘‘Group
2 POTW’’ are replacing the previous terms
‘‘industrial POTW’’ and ‘‘nonindustrial POTW. The
‘‘Group 1’’ and ‘‘Group 2’’ subcategories are
described in the regulatory text at 40 CFR 63.1581.
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brought by the EPA to enforce the
requirements.
Section 307(d)(7)(B) of the CAA
further provides that only an objection
to a rule or procedure which was raised
with reasonable specificity during the
period for public comment (including
any public hearing) may be raised
during judicial review. This section also
provides a mechanism for the EPA to
reconsider the rule if the person raising
an objection can demonstrate to the
Administrator that it was impracticable
to raise such objection within the period
for public comment or if the grounds for
such objection arose after the period for
public comment (but within the time
specified for judicial review) and if such
objection is of central relevance to the
outcome of the rule. Any person seeking
to make such a demonstration should
submit a Petition for Reconsideration to
the Office of the Administrator, U.S.
EPA, Room 3000, EPA WJC South
Building, 1200 Pennsylvania Ave. NW.,
Washington, DC 20460, with a copy to
both the person(s) listed in the
preceding FOR FURTHER INFORMATION
CONTACT section, and the Associate
General Counsel for the Air and
Radiation Law Office, Office of General
Counsel (Mail Code 2344A), U.S. EPA,
1200 Pennsylvania Ave. NW.,
Washington, DC 20460.
II. Background
A. What is the statutory authority for
this action?
Section 112 of the CAA establishes a
two-stage regulatory process to address
emissions of HAP from stationary
sources. In the first stage, we must
identify categories of sources emitting
one or more of the HAP listed in CAA
section 112(b) and then promulgate
technology-based NESHAP for those
sources. ‘‘Major sources’’ are those that
emit, or have the potential to emit, any
single HAP at a rate of 10 tons per year
(tpy) or more, or 25 tpy or more of any
combination of HAP. For major sources,
these standards are commonly referred
to as maximum achievable control
technology (MACT) standards and must
reflect the maximum degree of emission
reductions of HAP achievable (after
considering cost, energy requirements,
and non-air quality health and
environmental impacts). In developing
MACT standards, CAA section 112(d)(2)
directs the EPA to consider the
application of measures, processes,
methods, systems, or techniques,
including but not limited to those that
reduce the volume of or eliminate HAP
emissions through process changes,
substitution of materials, or other
modifications; enclose systems or
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processes to eliminate emissions;
collect, capture, or treat HAP when
released from a process, stack, storage,
or fugitive emissions point; are design,
equipment, work practice, or
operational standards; or any
combination of the above.
For these MACT standards, the statute
specifies certain minimum stringency
requirements, which are referred to as
MACT floor requirements, and which
may not be based on cost
considerations. See CAA section
112(d)(3). For new sources, the MACT
floor cannot be less stringent than the
emission control achieved in practice by
the best-controlled similar source. The
MACT standards for existing sources
can be less stringent than floors for new
sources, but they cannot be less
stringent than the average emission
limitation achieved by the bestperforming 12 percent of existing
sources in the category or subcategory
(or the best-performing five sources for
categories or subcategories with fewer
than 30 sources). In developing MACT
standards, we must also consider
control options that are more stringent
than the floor under CAA section
112(d)(2). We may establish standards
more stringent than the floor, based on
the consideration of the cost of
achieving the emissions reductions, any
non-air quality health and
environmental impacts, and energy
requirements.
In the second stage of the regulatory
process, the CAA requires the EPA to
undertake two different analyses, which
we refer to as the technology review and
the residual risk review. Under the
technology review, we must review the
technology-based standards and revise
them ‘‘as necessary (taking into account
developments in practices, processes,
and control technologies)’’ no less
frequently than every 8 years, pursuant
to CAA section 112(d)(6). Under the
residual risk review, we must evaluate
the risk to public health remaining after
application of the technology-based
standards and revise the standards, if
necessary, to provide an ample margin
of safety to protect public health or to
prevent, taking into consideration costs,
energy, safety, and other relevant
factors, an adverse environmental effect.
The residual risk review is required
within 8 years after promulgation of the
technology-based standards, pursuant to
CAA section 112(f). In conducting the
residual risk review, if the EPA
determines that the current standards
provide an ample margin of safety to
protect public health, it is not necessary
to revise the MACT standards pursuant
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to CAA section 112(f).2 For more
information on the statutory authority
for this rule, see the proposed rule
published on December 27, 2016 (81 FR
95352).
B. What is the POTW source category
and how does the NESHAP regulate
HAP emissions from the source
category?
1. Definition of the POTW Source
Category and the Affected Source
The EPA promulgated the NESHAP
for the POTW source category
(henceforth referred to as the ‘‘POTW
NESHAP’’) on October 26, 1999 (64 FR
57572). The standards are codified at 40
CFR part 63, subpart VVV. The POTW
NESHAP was amended on October 21,
2002 (67 FR 64742). As amended in
2002, the POTW source category
consists of new and existing POTW
treatment plants that are located at a
POTW that is a major source of HAP
emissions and that meets the criteria for
development and implementation of a
pretreatment program as defined by 40
CFR 403.8 under the Clean Water Act
(CWA). Additional information about
the National Pretreatment Program can
be found in the December 27, 2016, RTR
proposal (81 FR 95374). The source
category covered by this MACT
standard currently includes thirteen
facilities.
As used in this regulation, the term
POTW refers to both any POTW that is
owned by a state, municipality, or
intermunicipal or interstate agency and,
therefore, eligible to receive grant
assistance under the Subchapter II of the
CWA, and any federally owned
treatment works as that term is
described in section 3023 of the Solid
Waste Disposal Act. For more
information see the December 27, 2016,
RTR proposal (81 FR 95352). The source
category includes any intercepting
sewers, outfall sewers, sewage
collection systems, pumping, power,
and other equipment. The wastewater
treated by these facilities is generated by
industrial, commercial, and domestic
sources.
2. Applicability of the 2002 POTW
NESHAP
The 2002 POTW NESHAP is
subcategorized based on whether the
POTW is providing treatment for
wastewaters received from an industrial
2 The U.S. Court of Appeals for the District of
Columbia Circuit has affirmed this approach of
implementing CAA section 112(f)(2)(A): NRDC v.
EPA, 529 F.3d 1077, 1083 (D.C. Cir. 2008) (‘‘If EPA
determines that the existing technology-based
standards provide an ‘ample margin of safety,’ then
the Agency is free to readopt those standards during
the residual risk rulemaking.’’).
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49515
user as the means by which that
industrial user complies with another
NESHAP. The 2002 POTW NESHAP
defined an ‘‘industrial POTW’’ as ‘‘a
POTW that accepts a waste stream
regulated by another NESHAP and
provides treatment and controls as an
agent for the industrial discharger. The
industrial discharger complies with its
NESHAP by using the treatment and
controls located at the POTW. For
example, an industry discharges its
benzene-containing waste stream to the
POTW for treatment to comply with 40
CFR part 61, subpart FF—National
Emission Standards for Benzene Waste
Operations. This definition does not
include POTW treating waste streams
not specifically regulated under another
NESHAP.’’ An ‘‘industrial POTW’’ is
subject to the 2002 POTW NESHAP
regardless of the HAP emissions (i.e.,
the POTW does not have to be a major
source). In contrast, a ‘‘non-industrial
POTW’’ was defined in the 2002 POTW
NESHAP as ‘‘a POTW that does not
meet the definition of an industrial
POTW as defined above.’’ A ‘‘nonindustrial POTW’’ must be a major
source to be subject to the 2002 POTW
NESHAP. For more information, see the
December 27, 2016, RTR proposal (81
FR 95357).
3. HAP Emitted and HAP Emission
Points
The amount and type of HAP emitted
from a POTW is dependent on the
composition of the wastewater streams
discharged to a POTW by industrial
users. The primary HAP emitted from
the POTW that were identified as
subject to the POTW NESHAP include
acetaldehyde, acetonitrile, chloroform,
ethylene glycol, formaldehyde,
methanol, methylene chloride,
tetratchloroethylene, toluene, and
xylenes. The HAP present in the
wastewater entering a POTW can
biodegrade, adhere to sewage sludge,
volatilize to the air, or pass through
(remain in the wastewater discharge) to
receiving waters. Emissions can occur at
any point at the POTW, including
collection systems and wastewater
treatment units located at the POTW
treatment plant.
4. Regulation of HAP Emissions in the
2002 POTW NESHAP
The POTW NESHAP specifies
requirements for the industial and nonindustrial POTW subcategories. Under
the 2002 POTW NESHAP, an existing
‘‘industrial POTW’’ must meet the
requirements of the industrial user’s
NESHAP. A new or reconstructed
‘‘industrial POTW’’ must meet the
requirements of the industrial user’s
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NESHAP or the requirements for new or
reconstructed non-industrial POTW,
whichever is more stringent.
There are no control requirements in
the 2002 POTW NESHAP for existing
‘‘non-industrial POTW.’’ However, new
or reconstructed ‘‘non-industrial
POTW’’ must equip each treatment unit
up to, but not including, the secondary
influent pumping station, with a cover.
In addition, all covered units, except the
primary clarifier, must route the air in
the headspace above the surface of the
wastewater to a control device that
meets the requirements for closed-vent
systems and control devices found in
the NESHAP from Off-Site Waste and
Recovery Operations (40 CFR part 63,
subpart DD). As an alternative, a new or
reconstructed ‘‘non-industrial POTW’’
can demonstrate that all units up to, but
not including, the secondary influent
pumping station emit a HAP fraction of
0.014 or less. The HAP fraction emitted
is the fraction of HAP in the wastewater
entering the POTW that is emitted to the
atmosphere. For additional information,
see the December 27, 2016, RTR
proposal (81 FR 95357).
C. What changes did we propose for the
POTW source category in our December
27, 2016, RTR proposal?
On December 27, 2016, the EPA
published a proposed rule in the
Federal Register for the POTW
NESHAP, 40 CFR part 63, subpart VVV,
that took into consideration the RTR
analyses. In the proposed rule, we
proposed that the risks are acceptable
and the current standards provide an
ample margin of safety to protect public
health. Additionally, we did not
identify any developments in practices,
processes, and control technologies for
the POTW source category as part of the
technology review. During this
rulemaking, we evaluated other
revisions to the 2002 POTW NESHAP
outside of the RTR. We proposed to
revise the names and definitions of the
industrial and non-industrial
subcategories to be called Group 1 and
Group 2 POTW. We also proposed to
include requirements to limit emissions
from collection systems and the POTW
treatment plant; requirements for
existing, new, or reconstructed Group 1
POTW to comply with both the
requirements in the POTW NESHAP
and those in the applicable NESHAP for
which the POTW acts as a control agent;
and HAP emission limits for existing
Group 2 POTW. In addition, we
proposed to clarify the applicability
criteria; require initial notification for
existing Group 1 and Group 2 POTW;
revise regulatory provisions pertaining
to emissions during periods of SSM; add
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requirements for electronic reporting;
and make other miscellaneous edits and
technical corrections.
III. What is included in this final rule?
This action finalizes the EPA’s
determinations pursuant to the RTR
provisions of CAA section 112 for the
POTW source category. This action also
finalizes other changes to the NESHAP,
including revised names and definitions
of the subcategories, clarified
applicability criteria, revised regulatory
provisions pertaining to emissions
during periods or SSM, initial
notification requirements for existing
Group 1 and Group 2 POTW,
requirements for new or reconstructed
Group 1 POTW to comply with both the
requirements in the POTW NESHAP
and those in the applicable NESHAP for
which the POTW acts as a control agent,
requirements for electronic reporting,
and other miscellaneous edits and
technical corrections. As explained in
section IV of this preamble, we are not
taking final action at this time on
several provisions that were proposed,
including standards for pretreatment,
the inclusion of collection systems in
the major source determination, and the
HAP fraction emission limit for existing
Group 1 and Group 2 POTW.
A. What are the final rule amendments
based on the risk review for the POTW
source category?
We determined that risks resulting
from emissions from the POTW source
category are acceptable. Specifically, the
maximum individual cancer risk (MIR)
is 2-in-1 million based on allowable
emissions and 1-in-1 million based on
actual emissions, well below the
presumptive limit of acceptability (100in-1 million), and other health
information indicates there is no
appreciable risk of adverse chronic or
acute non-cancer health effects due to
HAP emissions from the source
category. Additionally, emissions of 2methylnaphthalene, the only HAP
emitted from the POTW source category
that is known to be persistent and bioaccumulative in the environment (PB–
HAP), did not exceed the worst-case
Tier I screening emission rate or any
ecological benchmarks. Therefore,
revisions to the standards are not
necessary to reduce risk to an acceptable
level or to prevent an adverse
environmental effect. Further,
considering risk and non-risk factors,
we determined that the 2002 POTW
NESHAP requirements provide an
ample margin of safety to protect public
health. Therefore, we are not finalizing
revisions to the standards under CAA
section 112(f)(2).
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B. What are the final rule amendments
based on the technology review for the
POTW source category?
We determined that there are no
developments in practices, processes,
and control technologies that warrant
revisions to the MACT standards for this
source category. Therefore, we are not
finalizing revisions to the MACT
standards under CAA section 112(d)(6).
C. What are the final rule amendments
addressing emissions during periods of
startup, shutdown, and malfunction?
Consistent with Sierra Club v. EPA,
552 F.3d 1019 (D.C. Cir. 2008), the EPA
has established standards in this rule
that apply at all times. We have revised
Table 1 to Subpart VVV of Part 63 (the
General Provisions applicability table)
in several respects to eliminate the
incorporation of those General
Provisions that stated or were tied to the
SSM exemption. These revisions to
Table 1 are explained in detail in the
proposed rule preamble at 81 FR 95780–
95782. Further, in conjunction with the
elimination of the incorporation of these
General Provisions requirements, we
have (1) added a general duty to
minimize emissions in 40 CFR
63.1582(e) and 63.1586(e), see 81 FR at
95380 (col. 2–3); (2) incorporated
performance testing requirements for
control devices in 40 CFR 63.694, see 81
FR at 95781 (col. 1); (3) added language
to Table 1 related to monitoring that is
identical to 40 CFR 63.8(d)(3) (which is
no longer incorporated) but with certain
revisions to reflect the ending of the
SSM plan requirement, see 81 FR at
95381 (col. 2); (4) made the
recordkeeping requirements in 40 CFR
63.696(h) and 63.1589(d) applicable to
periods that were previously covered by
SSM-related provisions, see 81 FR
95381 (col. 2–3); and (5) amended the
reporting requirements in 40 CFR
63.1590 which, in conjunction with the
existing reporting requirements in 40
CFR 63.693 and 63.1590(a), will
adequately provide for reporting that
was previously governed by SSMrelated provisions, see 81 FR at 95382.
D. What other changes have been made
to the NESHAP?
1. Applicability Criteria
The EPA is not revising the
applicability of 40 CFR part 63, subpart
VVV as proposed on December 27, 2016.
Instead, the EPA is finalizing minor
clarifying changes to the applicability
criteria that are in the 2002 POTW
NESHAP. The renaming of the
subcategories (from ‘‘industrial’’ to
‘‘Group 1’’ and from ‘‘non-industrial’’ to
‘‘Group 2) and the definitions of Group
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1 and Group 2 POTW are being finalized
as proposed, and as discussed below.
However, for clarification, the EPA has
removed the statements regarding
ownership and operation of POTW in
regards to which POTW are required to
develop and implement a pretreatment
program as defined by 40 CFR 403.8.
This change clarifies that any Group 1
POTW (regardless of HAP emissions) or
Group 2 POTW that is a major source of
HAP is subject to the POTW NESHAP
if the POTW also meets the criteria for
development and implementation of a
pretreatment program, regardless of
whether the POTW, state, or other entity
implements the pretreatment program.
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2. Names and Definitions of the
Subcategories
As proposed, the EPA is revising the
names and definitions for the
subcategories identified in the POTW
NESHAP. The EPA is renaming an
‘‘industrial POTW treatment plant’’ as a
‘‘Group 1’’ POTW treatment plant and a
‘‘non-industrial POTW treatment plant’’
as a ‘‘Group 2’’ POTW treatment plant.
The EPA expects that this clarification
will address any confusion that could
have been caused by the previous
subcategory names ‘‘industrial POTW
treatment plant’’ and ‘‘non-industrial
treatment plant’’ because POTW in both
subcategories treat wastewater from
industrial users. The key difference
between Group 1 and Group 2 is that a
Group 1 POTW acts as an agent for an
industrial user by accepting and
controling the industrial user’s waste
stream regulated under another
NESHAP. By contrast, a Group 2 POTW
may treat the waste stream from an
industrial user, but does not act as the
industrial user’s agent to comply with
another NESHAP.
3. Initial Notification Requirements for
Existing Group 1 and Group 2 POTW
In the final rule (40 CFR 63.1586(a)),
existing Group 1 and Group 2 POTW
treatment plants must comply with the
initial notification requirements in 40
CFR 63.1591(a) of subpart VVV. This
notification requirement was not
required for these existing sources in the
2002 POTW NESHAP, but was proposed
in the December 27, 2016, proposal, and
is consistent with notification
requirements that were applicable to
new or reconstructed Group 2 sources
under the 2002 POTW NESHAP.
4. Requirements for New Group 1
POTW
The EPA is finalizing, as proposed,
the requirement that new Group 1
POTW comply with both the
requirements of the other NESHAP for
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which they act as an agent of control for
an industrial user and the requirements
for new Group 2 POTW in this final
rule. The requirements for new Group 2
POTW are unchanged from the 2002
POTW NESHAP and provide the option
of complying with either (a) cover all
primary treatment units and route
emissions through a closed vent system
to a control device or (b) meet a HAP
fraction emission limit of 0.014 for
emissions from all primary treatment
units.
5. Requirements for Electronic
Reporting
The EPA is finalizing electronic
reporting requirements for new POTW
consistent with the proposed rule.
Specifically, new POTW must
electroncally submit all annual reports
and certain performance test reports.
The EPA believes that the electronic
submittal of these reports will increase
the usefulness of data contained in
those reports, is in keeping with current
trends in data availability, will further
assist in the protection of public health
and the environment, and will
ultimately result in less burden on the
regulated community.
6. Other Miscellaneous Edits and
Technical Corrections
The EPA is finalizing the following
technical corrections as proposed:
• Revising all references to ‘‘new or
reconstructed POTW’’ to refer to ‘‘new
POTW’’ because the definition of ‘‘new’’
includes reconstructed POTW.
• Combining text from 40 CFR
63.1581 and 63.1582 because the
language was redundant and confusing.
This includes revising 40 CFR 63.1581
to include all combined text and
revising 40 CFR 63.1583(c) to include
the text from the current 40 CR
63.1582(c).
• Revising 40 CFR 63.1586(b)(1) to
require covers ‘‘designed and operated
to prevent exposure of the wastewater to
the atmosphere’’ instead of ‘‘designed
and operated to minimize exposure of
the wastewater to the atmosphere.’’ This
clarification has also been made to the
definition of ‘‘cover’’ in 40 CFR 63.1595.
• Revising 40 CFR 63.1587 to include
compliance requirements that are
currently found in 40 CFR 64.1584 and
63.1587, and deleting 40 CFR 63.1584.
• Clarifying the method for
calculating the HAP fraction emitted
and moving the detailed instructions for
calculating the HAP fraction emitted
from 40 CFR 63.1588(c)(4) to 40 CFR
63.1588(c)(3). The requirements
remaining in 40 CFR 63.1588(c)(4)
address monitoring for continuous
compliance.
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49517
• Revising 40 CFR 63.1588(a)(3) to
clarify that a cover defect must be
repaired within 45 ‘‘calendar’’ days;
currently the paragraph says ‘‘45 days.’’
• Adding definitions of existing
source/POTW and new source/POTW to
40 CFR 63.1595 to clarify the date that
determines whether a POTW is existing
or new.
• Renaming the title of 40 CFR
63.1588 to ‘‘How do Group 1 and Group
2 POTW treatment plants demonstrate
compliance?’’ from ‘‘What inspections
must I conduct?’’ The new title better
reflects the contents of this section.
• Removing the details on how to
calculate the HAP fraction emitted from
the definition of HAP fraction emitted.
The procedure for how to calculate the
HAP fraction emitted is provided within
the text of the rule. Having a
summarized version of this procedure in
the definition could cause confusion.
• Revising two references to dates to
insert the actual dates. The phrase ‘‘six
months after October 26, 1999’’ was
replaced with ‘‘April 26, 2000’’; and the
phrase ‘‘60 days after October 26, 1999’’
was replaced with ‘‘December 27,
1999.’’ These changes do not result in a
change in the date, but only clarify the
specific dates being referenced.
• Clarifying that the reports required
in 40 CFR 63.1589(b)(1) include the
records associated with the HAP loading
and not just the records associated with
the HAP emissions determination.
• Removing the definition of
‘‘Reconstruction’’ in 40 CFR 63.1595 as
‘‘Reconstruction’’ is already defined in
the General Provisions of 40 CFR 63.2.
E. What are the effective and
compliance dates of the standards?
The revisions to the MACT standards
being promulgated in this action are
effective on October 26, 2017.
The compliance date for existing
Group 1 POTW is found in the
applicable NESHAP for which the
industrial user is subject to wastewater
requirements. The compliance date for
existing Group 2 POTW constructed or
reconstructed on or before December 1,
1998, remains April 26, 2000. While we
do not expect any additional existing
Group 1 or Group 2 POTW beyond the
13 identified, we have chosen to include
an additional compliance date of
October 26, 2018 for existing Group 1
and Group 2 sources to submit their
initial notification. We understand from
public comments that POTW are
evaluating their potential emissions and
additional POTW may find they are
subject to the rule. These POTW are
only required to submit a notification
that they are subject to the rule, and the
additional time given for compliance of
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this notification submittal will provide
time for completion of the necessary
emission calculations. The 13 existing
sources that are subject to the rule and
were previously identified have already
met this notification requirement and do
not need to resubmit a notification. New
sources constructed or reconstructed
after December 27, 2016, must comply
with all of the standards immediately
upon the effective date of the standard,
October 26, 2017, or upon startup,
whichever is later. While we did not
identify any new sources that are
subject to the rule since the original rule
was published in 1999, we are including
a transition period until October 26,
2020 for any new sources constructed or
reconstructed between December 1,
1998, and December 27, 2016, to comply
with the revisions in this rule.
F. What are the requirements for
submission of annual reports and
performance test data to the EPA?
As we proposed, the EPA is finalizing
the requirement for owners and
operators of POTW to submit electronic
copies of certain required performance
test reports and annual reports through
the EPA’s Central Data Exchange (CDX)
using the Compliance and Emissions
Data Reporting Interface (CEDRI). The
electronic submittal of the reports
addressed in this rulemaking will
increase the usefulness of the data
contained in those reports, is in keeping
with current trends in data availability
and transparency, will further assist in
the protection of public health and the
environment, will improve compliance
by facilitating the ability of regulated
facilities to demonstrate compliance
with requirements and by facilitating
the ability of delegated state, local,
tribal, and territorial air agencies and
the EPA to assess and determine
compliance, and will ultimately reduce
burden on regulated facilities, delegated
air agencies, and the EPA. Electronic
reporting also eliminates paper-based,
manual processes, thereby saving time
and resources, simplifying data entry,
eliminating redundancies, minimizing
data reporting errors, and providing data
quickly and accurately to the affected
facilities, air agencies, the EPA, and the
public.
The EPA Web site that stores the
submitted electronic data, WebFIRE, is
easily accessible and provides a userfriendly interface. By making records,
data, and reports addressed in this
rulemaking readily available, the EPA,
the regulated community, and the
public will benefit when the EPA
conducts its CAA-required technology
reviews. As a result of having reports
readily accessible, our ability to carry
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out comprehensive reviews will
increase and be achieved within a
shorter period of time.
We anticipate fewer or less substantial
Information Collection Requests (ICRs)
in conjunction with prospective CAArequired technology reviews may be
needed, which results in a decrease in
time spent by industry to respond to
data collection requests. We also expect
the ICRs to contain less extensive stack
testing provisions, as we will already
have stack test data electronically.
Reduced testing requirements would be
a cost savings to industry. The EPA
should also be able to conduct these
required reviews more quickly. While
the regulated community may benefit
from a reduced burden of ICRs, the
general public benefits from the
agency’s ability to provide these
required reviews more quickly, resulting
in increased public health and
environmental protection.
Air agencies, as well as the EPA, can
benefit from more streamlined and
automated review of the electronically
submitted data. Standardizing report
formats allows air agencies to review
reports and data more quickly. Having
reports and associated data in electronic
format facilitates review through the use
of software ‘‘search’’ options, as well as
the downloading and analyzing of data
in spreadsheet format. Additionally, air
agencies and the EPA can access reports
wherever and whenever they want or
need, as long as they have access to the
Internet. The ability to access and
review reports electronically assists air
agencies in determining compliance
with applicable regulations more
quickly and accurately, potentially
allowing a faster response to violations,
which could minimize harmful air
emissions. This benefits both air
agencies and the general public.
For a more thorough discussion of
electronic reporting required by this
rule, see the discussion in the preamble
of the proposal. In summary, in addition
to supporting regulation development,
control strategy development, and other
air pollution control activities, having
an electronic database populated with
performance test data will save
industry, air agencies, and the EPA
significant time, money, and effort
while improving the quality of emission
inventories and air quality regulations
and enhancing the public’s access to
this important information.
IV. What is the rationale for our final
decisions and amendments for the
POTW source category?
For each decision or amendment, this
section provides a description of what
we proposed and what we are finalizing,
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the EPA’s rationale for the final
decisions and amendments, and a
summary of key comments and
responses. Comments not discussed in
this preamble, comment summaries, and
the EPA’s responses can be found in the
comment summary and response
document available in the docket
(Docket ID No. EPA–HQ–OAR–2016–
0490).
A. Residual Risk Review for the POTW
Source Category
Pursuant to CAA section 112(f), we
conducted a residual risk review and
presented the results of the review,
along with our proposed decisions
regarding risk acceptability and ample
margin of safety, in the December 27,
2016, RTR proposal (81 FR 95372). The
residual risk review for the POTW
source category included assessment of
cancer risk, chronic non-cancer risk,
and acute non-cancer risk due to
inhalation exposure, as well as
multipathway exposure risk and
environmental risk. The results of the
risk assessment are presented briefly in
this preamble and in more detail in the
residual risk document, Residual Risk
Assessment for Publicly Owned
Treatment Works Source Category in
Support of the October 2017 Risk and
Technology Review Final Rule,3 which
is available in the docket for this
rulemaking.
The results indicated that maximum
inhalation cancer risk to the individual
most exposed is 2-in-1 million based on
allowable emissions and 1-in-1 million
based on actual emissions, which is
well below the presumptive limit of
acceptability (i.e., 100-in-1 million). In
addition, the maximum chronic
noncancer target organ specific hazard
index (TOSHI) due to inhalation
exposures is less than 1. The evaluation
of acute noncancer risk, which was
conservative, showed a hazard quotient
at or below 1 for all but one POTW.
Based on the results of the screening
analyses for human multipathway
exposure to, and environmental impacts
from, PB–HAP, we also concluded that
the cancer risk to the individual most
exposed through ingestion is below the
level of concern and no ecological
benchmarks are exceeded. The facilitywide cancer and noncancer risks were
estimated based on the actual emissions
from all sources at the identified POTW
(both MACT and non-MACT sources).
The results indicated the cancer risk to
3 This report is an update to the residual risk
report provided at proposal, Residual Risk
Assessment for Publicly Owned Treatment Works
Source Category in Support of the December 2016
Risk and Technology Review Proposed Rule,
available in the docket.
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the individual most exposed is no
greater than 10-in-1 million and the
noncancer TOSHI is less than 1.
Considering the above information, as
well as other relevant non-health factors
under the Benzene NESHAP analysis
codified in CAA 112(f)(2)(B), we
proposed that the risk is acceptable and
the requirements in the 2002 POTW
NESHAP provide an ample margin of
safety to protect public health and
prevent an adverse environmental
effect.
The risk assessment conducted for the
POTW proposal estimated cancer,
chronic noncancer, and acute noncancer
risk for six of the 13 facilities in the
source category and is summarized and
referenced above. We confirmed the
existence of seven additional POTW
subject to the rule that were identified
through public comments. For these
seven POTW, we conducted a facilitywide risk assessment of potential cancer
and chronic noncancer health effects.
The results of this assessment indicate
that all seven POTW have a facilitywide noncancer TOSHI less than 1, four
of the POTW have a facility-wide cancer
risk estimated less than 1-in-1 million,
and three of the POTW have a facilitywide cancer risk estimated at or above
10-in-1 million. The highest facilitywide MIR was 60-in-1 million driven by
formaldehyde from internal combustion
engines which are covered under the
NESHAP for the Stationary
Reciprocating Internal Combustion
Engines source category. For this POTW
with the highest facility-wide MIR, the
facility-wide emissions of formaldehyde
are 22 tpy while the source category
emissions of formaldehyde are 0.0026
tpy, which indicates that almost 100
percent of the estimated cancer risk is
from emissions sources that are not part
of the POTW source category. This ratio
of source category emissions relative to
facility-wide emissions of formaldehyde
is the same for the other two POTW
with facility-wide cancer risk estimated
at or above 10-in-1 million. Therefore, it
is reasonable to conclude that all 13
POTW have estimated cancer risk close
to or below 1-in-1 million from source
category emissions and we retain our
proposed determination that risk is
acceptable. Further, as discussed in the
December 27, 2016, RTR proposal (81
FR 95373), we retain our determination
that, considering the costs, economic
impacts and technological feasibility of
additional standards to reduce risk
further, the 2002 POTW NESHAP
provides an ample margin of safety to
protect public health and prevents an
adverse environmental effect. Details of
this risk assessment are described in the
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Residual Risk Assessment for the
Publicly Owned Treatment Works
Source Category in Support of the
October 2017 Risk and Technology
Review Final Rule found in the docket
for this rulemaking.
Most of the commenters on the
proposed risk review supported our risk
acceptability and ample margin of safety
determinations for the POTW NESHAP.
Some commenters requested that we
make changes to our residual risk
review approach. However, we
evaluated the comments and
determined that no changes to our risk
assessment methods or conclusions are
warranted. A summary of these
comments and responses are in the
comment summary and response
document, available in the docket for
this action (Docket ID No. EPA–HQ–
OAR–2016–0490).
Since proposal, our risk assessment
has been broadened to include
additional POTW; however, the
conclusions of our risk assessment and
our determinations regarding risk
acceptability, ample margin of safety,
and adverse environmental effects have
not changed. For the reasons explained
in the proposed rule and discussed
above, we determined that the risks
from the POTW source category are
acceptable, and that the current
standards provide an ample margin of
safety to protect public health and
prevent an adverse environmental
effect.
B. Technology Review for the POTW
Source Category
As described in the December 27,
2016, RTR proposal (81 FR 95373), and
as provided by CAA section 112(d)(6),
our technology review focused on
identifying developments in the
practices, processes, and control
technologies for the POTW source
category. We concluded that there are
two different control options that may
be used at a POTW to reduce HAP
emissions: pretreatment programs and
add-on controls (i.e., covers or covers
vented to a control device). While we
proposed specific revisions to the
standards, none of those revisions were
the result of any identified
developments in practices, processes, or
control technologies beyond the
programs and controls already in use at
the time of the promulgation of the
original 40 CFR part 63, subpart VVV
rulemaking.
Comment: We received various
comments related to the information
evaluated for the proposal. Two
commenters stated that there is no
technical basis that requires the EPA to
revise the standards since there have
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been no technology advances since 1998
that warrant a change in the original
MACT analysis. Several commenters
provided additional information on
specific control technologies, including
biofilters, caustic scrubbers, and carbon
absorbers. One of these commenters
stated that biofilters are not reliable
control devices in the context of a
POTW because they are designed for
stable operating conditions. In contrast,
another commenter provided
information that biofilters might have
the ability to reduce HAP in addition to
hydrogen sulfide (H2S) and volatile
organic compounds (VOC). Additional
comments on the technology review can
be found in section 3 of the response to
comments document in the docket for
this rule (EPA–HQ–OAR–2016–0490).
Response: The EPA conducted a
literature review and evaluated
available studies and publications on
the use of add-on controls and process
modifications that are used to reduce
emissions from POTW wastewater
collection and treatment operations. As
noted by the commenters, these
technologies include biotrickling filters,
the use of covers and ducting of the
headspace vent stream to caustic
scrubbers and carbon adsorbers, and
biofiltration/biofilters. These types of
technologies have been used historically
at POTW where they provide a
relatively high degree of H2S control for
the purpose of preventing odor. As
documented in the technology review
memorandum and reflected in the
comments received on the proposed
rule, the efficacy of these technologies
to reduce HAP emissions is highly
variable and dependent on site-specific
operating parameters. Our conclusion is
that the experience with biofilters for
controlling organics at POTW is at the
experimental and pilot scale and that
this technology has not been
demonstrated to be commercially
available and effective for controlling
the range of HAP emitted by POTW.
Thus, we do not consider this
technology to be a development in
practices, processes, or control
technologies for purposes of this
technology review. Scrubbers are
generally not used to control emissions
of organic constituents, and while
carbon adsorbers may be effective at
HAP control in certain applications, as
used in POTW, they are generally not
designed for HAP control. Nevertheless,
40 CFR part 63, subpart VVV allows
flexibility for POTW to develop sitespecific control strategies to meet any
applicable requirements, and such
strategies could include the use of
biologic filters and carbon adsorbers
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that can achieve the required control
levels.
As stated in section III.B of this
preamble, we did not identify any
developments in practices, processes, or
control technology with respect to
programs and controls already in use
when the 2002 POTW NESHAP was
promulgated that warrant revisions to
the standards as part of the technology
review of the POTW NESHAP.
C. Applicability Criteria
The 2002 POTW NESHAP established
three criteria (40 CFR 63.1580(a)(1), (2),
and (3)) for determining what POTW are
subject to the rule. Specifically, the
following criteria must all be true: (1)
You own or operate a POTW that
includes a POTW treatment plant; (2)
the POTW is a major source of HAP
emissions, or an industrial POTW
regardless of the HAP emissions; and (3)
the POTW is required to develop and
implement a pretreatment program as
defined by 40 CFR 403.8. The EPA
proposed to revise the applicability
criteria in order to clarify the original
intent of the rule. Specifically, we
proposed to revise the first and second
criteria in 40 CFR 63.1580(a)(1) and (2)
to state that your POTW is subject to the
POTW NESHAP if ‘‘(1) You own or
operate a POTW that is a major source
of HAP emissions; or (2) you own or
operate a Group 1 POTW regardless of
whether or not it is a major source of
HAP.’’ As stated in the proposal, we
proposed this revision because we
found several instances where a POTW
might not realize they are subject to the
standards, or where the applicability
criteria could be misinterpreted to
exclude facilities that are covered by the
rule. See 81 FR 95377.
The third applicability criterion in the
2002 POTW NESHAP states that ‘‘(3)
Your POTW is required to develop and
implement a pretreatment program as
defined by 40 CFR 403.8 (for a POTW
owned or operated by a municipality,
state, or intermunicipal or interstate
agency), or your POTW would meet the
general criteria for development and
implementation of a pretreatment
program (for a POTW owned or
operated by a department, agency, or
instrumentality of the Federal
government).’’ We proposed revising the
third criterion in 40 CFR 63.1580(a)(3)
to state ‘‘You are subject to this subpart
if your POTW has a design capacity to
treat at least 5 million gallons of
wastewater per day (MGD) and treats
wastewater from an industrial user, and
either paragraph (a)(1) or (a)(2) is true.’’
This proposed revision removed the
requirement that a POTW must already
have a pretreatment program in place in
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order to be subject to the rule. The
proposed revisions were intended to
clarify the intent of the rule, which was
to limit applicability to POTW that treat
at least 5 MGD and wastewater from
industrial users.
Comment: We received numerous
comments that raised specific concerns
related to these proposed changes. First,
commenters disagreed that the proposed
changes were necessary and stated that
the proposed changes created confusion
and changed the scope of affected
sources. One commenter stated that the
applicability of 40 CFR part 63, subpart
VVV has been well-defined for over 17
years, and if sources are confused, the
EPA has methods to correct any
confusion without making rule changes.
Several commenters specifically
objected to the proposed change that
removed pretreatment from the third
applicability criterion and made it a
requirement of the rule. These
commenters stated that removing
pretreatment as an applicability
criterion and making it a requirement
changes the source category that the
EPA intended to control. One state
commented that this proposed change
would cause an additional 12 POTW in
their state to become subject to the rule.
The commenter explained that because
the state (not the POTW) implements
the National Pollutant Discharge
Elimination System (NPDES)
pretreatment program, the original rule
does not apply to any POTW in that
state.
Response: As stated in the proposal,
the EPA did not intend to expand the
applicability criteria from the 2002
POTW NESHAP. After consideration of
the comments received, we agree that
implementing the proposed changes to
rule applicability could have caused
confusion among the regulated
community without a demonstrable
environmental benefit. Therefore, at this
time, we are not making any substantive
change to the 2002 POTW NESHAP
third applicability criterion and are not
adopting the proposed applicability
criterion of 5 MGD. However, it is
important to note that the requirements
in the National Pretreatment Program do
establish a 5 MGD threshold for
applicability.
In response to the apparent potential
for misinterpretation of the regulatory
text that is reflected in the state’s
comment, we are making one minor
change to clarify our interpretation and
the intent of 40 CFR 63.1580(a)(3). In
developing the 2002 POTW NESHAP,
we wrote the rule to apply to POTW that
receive a significant amount of HAPcontaining waste from industrial or
commercial facilities. In developing the
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rule language, we sought to define such
POTW by using a regulatory criterion
that was already established and well
understood in the industry. We selected
the criterion that the POTW be subject
to a pretreatment program under the
NPDES program because this criterion
would encompass industrial and
commercial wastes with HAP that pass
through the POTW untreated and that
could present a safety or health concern
to POTW workers. In adopting this
criterion, we did not limit applicability
based on the entity that administers the
program. In other words, the criterion
encompasses every POTW that receives
a waste stream that is subject to
pretreatment standards, regardless of
whether the standards are prescribed by
the POTW itself or by a state or federal
regulatory body. Thus, to make sure that
the regulatory text is properly read, we
have revised 40 CFR 63.1581(a)(3) to
make clear that a POTW is subject to
this rule if either (1) the POTW is
required to develop and implement a
pretreatment program as defined by 40
CFR 403.8, or (2) the POTW meets the
general criteria for development and
implementation of a pretreatment
program, even if does not develop and
implement the pretreatment program
itself. Specifically, we have removed the
parenthetical text in 40 CFR
63.1580(a)(3) that limited the first part
of the third criterion to POTW owned or
operated by a municipality, state, or
intermunicipal or interstate agency and
limited the second part of the third
criterion to POTW owned or operated
by a department, agency, or
instrumentality of the federal
government.
D. Emissions From Collection Systems
In the 2016 proposal, we stated that
HAP emissions from collection systems
should be included when determining
whether the POTW is a major source,
and therefore, subject to the rule.
Specifically, we stated that the 2002
applicability criteria in 40 CFR
63.1580(a)(2) provided that emissions
from the entire POTW source category
must be considered when determining
whether the POTW is a major source of
HAP emissions, and not just the
emissions from the POTW treatment
plant (i.e., the portion of the POTW
designed to provide treatment of
municipal sewage or industrial waste).
Comment: Several commenters
opposed including emissions from
collection systems in the determination
of whether a POTW is a major source.
The commenters stated that collection
systems/sewers may include hundreds
or thousands of miles of sewers and
other equipment, are not always under
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the jurisdiction of the POTW, and are
typically owned by another entity.
We also received comments that
stated the inclusion of emissions from
collection systems for major source
determination is inconsistent with the
federal definition of a major source. One
commenter stated that expansion of the
major source definition to include
collection sewers as part of the affected
source is not authorized under section
112 of the CAA. The commenter also
stated that the equipment that collect
and convey wastewater to a POTW
treatment plant do not reasonably
constitute a ‘‘building, structure,
facility, or installation’’ as specified in
the definition of a stationary source in
section 112(a)(3) of the CAA, are clearly
not within a contiguous area under
common control, and should not be
considered a single source. Commenters
noted that the determination of a major
source of HAP emissions should be
limited to emission sources within the
fence line of each treatment plant,
which would be consistent with the fact
that the emission fraction requirement
of the proposed POTW NESHAP is
limited to emissions within the
treatment plant. Further, one
commenter contended that excluding
collection system emissions in POTW
major source determinations is also
supported by Alabama Power Co. v.
Costle and EPA’s response to that
decision.
Commenters also noted that the
emission data reviewed by the EPA in
developing the proposed rule
represented the HAP emissions from the
POTW treatment plant only. One
commenter noted that the risk
assessment did not include emissions
from collection systems. Several
commenters disagreed with the EPA’s
statement in the preamble to the
proposed rule that collection systems
may have significant HAP emissions.
Some commenters suggested that
emissions from collection systems are
insignificant and in some cases
collection systems are operated under a
vacuum to control odors. However,
none of the commenters provided data
to demonstrate the level of HAP
emissions from collection systems.
Response: Considering these
comments, the EPA is not taking final
action at this time on any changes to the
emission sources that must be
considered when determining if a
POTW is a major source of HAP
emissions. Specifically, the EPA is not
taking action on whether emissions
from collection systems should be
included in the total HAP emissions
from a POTW. The determination of
source boundaries is a site-specific and
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often a complex determination.
Facilities work with their permitting
authority to consider factors such as
whether activities and equipment are in
a contiguous area and whether they are
under common control. In
contemplating the comments, the EPA
has decided that we do not have enough
information on individual POTW,
including information on the
jurisdiction of the control of collection
system equipment or information on
whether this equipment should be
considered contiguous with the POTW
treatment plant. Also, data on HAP
emissions from collection systems are
not well understood, and we are not
aware of accepted methods for
measuring or calculating emissions from
collection systems at this time. In
addition, we understand that these
source boundary determinations have
already been made for the
approximately 16,000 POTW through
Title V applicability assessment. For
these reasons, we are not taking final
action at this time to change these
determinations. We may take action in
the future if we obtain additional
information on source boundary issues
(i.e., common control, contiguous area),
HAP emissions, and other information
related to the issues described above.
With respect to new sources, we
expect new sources to consult their
permitting authorities on these matters
as they plan for new construction. The
EPA considers these determinations on
source boundaries to be appropriately
under the jurisdiction of the permitting
authority. Accordingly, to avoid
regulatory disruption, this final rule
takes no action to change the definition
of POTW. The definition of POTW
remains the same as originally
promulgated and continues to include
‘‘. . . any intercepting sewers, outfall
sewers, sewage collection systems,
pumping, power and other equipment.’’
Likewise, we are not taking final action
at this time to revise the originally
promulgated definition of the affected
source. The definition of affected source
continues to mean the ‘‘group of all
equipment that comprise the POTW
treatment plant.’’
E. Pretreatment Requirements
As stated in section IV.C of this
preamble, the EPA proposed removing
pretreatment from the applicability
criteria and making it a control
requirement for new and existing
sources. We proposed adding
pretreatment requirements in the rule
because pretreatment would reduce
HAP emissions from the entire source
category (i.e., collection systems and the
treatment plant) by limiting the quantity
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49521
of HAP in the wastewater before it is
discharged to the collection system. The
intent of this requirement was to reduce
the pollutant loading into the POTW in
order to reduce emissions throughout all
stages of treatment.
Comment: Several commenters
objected to the EPA requiring a
pretreatment program for HAP
emissions. Commenters disagreed with
the EPA’s contention that a pretreatment
program will reduce emissions of HAP
by reducing the presence of toxic gases.
Specifically, commenters noted that a
‘‘pretreatment program under CAA
Section 112 is not the same as a
pretreatment program under the Clean
Water Act (CWA)’’, as 40 CFR 403
authorizes POTW to set pretreatment
requirements for air contaminants for
worker and plant safety, and to prevent
interference and pass through. One
commenter contended that the proposed
rule expands the CAA regulatory
framework into the CWA National
Pretreatment Program without a legal
basis.
Additionally, several commenters
opposed requiring POTW to develop
local limits and expressed concerns
about the way in which local limits
should be determined. Instead,
commenters suggested that the EPA
establish wastewater concentration
limits for HAP to identify pollutants
that may need local limits. One
commenter stated that the EPA should
either ‘‘regulate industrial users directly
for HAP or provide technically-based
wastewater concentrations for HAP that
POTW could use for screening (where
analytical methods exist under 40 CFR
part 136)’’ to determine the need for
establishing local limits.
Commenters also expressed concerns
about the costs related to requiring
pretreatment programs wherein POTW
evaluate and set local limits for volatile
organic HAP. The commenters stated
that developing local limits to identify
pollutants of concern, as well as identify
potential pretreatment controls, would
require significant time and that the
significant costs these requirements
would impose on POTW have not been
quantified or justified. In contrast, one
commenter stated that categorical limits
set by the EPA pursuant to the CWA for
certain industries could merit
consideration, but additional analysis is
required.
Response: In response to these
comments, we are not taking final action
at this time to require pretreatment as a
control requirement for the revised
NESHAP. As explained in section IV.C
of this preamble, we are not changing
the applicability criteria for 40 CFR part
63, subpart VVV. The existence of a
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pretreatment program under the CWA
will continue to be one of the three rule
applicability criteria.
The EPA Office of Water is
responsible for administering the
pretreatment program and updates the
requirements of the pretreatment
program based on the best available
technology and taking into account cost
effectiveness. As the pretreatment
requirements are modified through
future updates, additional HAP
reductions may occur. Because all of the
POTW that are subject to the rule
already have pretreatment programs,
specifically requiring pretreatment
under the NESHAP would not reduce
HAP emissions further, but could cause
confusion and increase compliance
costs. Thus, we are not finalizing any
revisions at this time to impose
additional pretreatment requirements
prior to discharging a wastewater stream
to a receiving POTW. Pretreatment will
continue to be handled under the
authority of the CWA. By retaining the
existing regulatory structure of the
NESHAP, the EPA avoids redundancy
and confusion in having pretreatment
requirements included in both air and
water permits.
F. HAP Fraction Emitted for Existing
Group 1 and Group 2 Sources
In the 2016 proposal, we proposed
that existing Group 1 and Group 2
POTW operate with an annual rolling
average HAP fraction emitted from
primary treatment units of 0.08 or less.
As stated in the proposal, we believed
that the existing POTW we knew about
could meet this standard without the
need for additional control.
Comment: We received numerous
comments that opposed the proposed
HAP fraction emission limit, and we
received additional data to suggest the
proposed 0.08 HAP fraction limit was
not appropriate and did not accurately
account for variability in HAP loading at
individual POTW.
Several commenters objected that
merely doubling the single largest HAP
fractions from the two available sources
was not a scientifically or statistically
valid method for setting the emission
limit and stated that the EPA had
provided no support for using the 2x
factor to account for variability of
emissions. For example, the
commenters collectively pointed out
that the two POTW on which the
proposed standard was based were
operating at half capacity, that the
available data represent merely a
snapshot in time, that other potentially
regulated POTW might emit higher HAP
fractions, and that the specific
combination of HAP measured by the
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two POTW might not be representative
of HAP emitted by other POTW. One
commenter suggested that due to the
uncertainty associated with such a small
data set, the EPA should use a larger
multiplier for setting a standard.
Additionally, commenters stated that
the EPA had underestimated the cost of
achieving compliance with the 0.08
HAP fraction emitted standard.
Specifically, commenters stated that in
order to comply, they would incur
capital and operating costs, in addition
to the recordkeeping and reporting costs
that the EPA accounted for in the
proposal. One commenter stated that
they would potentially need to install
covers and controls in order to meet the
HAP fraction emitted limit, which
would be an expense of $20 to $30
million with negligible emission
reductions. Two commenters argued
that the compliance cost for the
proposed standard was not warranted
given the low public health risk that the
EPA estimated. Commenters further
recommended that the EPA gather more
complete data from the universe of
affected sources, conduct statistical
analysis of those data, and determine a
suitable standard based on an
acceptable level of risk and variability of
the data.
Response: After reviewing public
comments and re-evaluating our
analysis, we are not taking final action
to adopt the 0.08 HAP fraction emitted
limit for existing Group 1 and Group 2
POTW at this time. The proposed HAP
fraction emitted limit did not reflect the
performance or application of a specific
control technology. At proposal, we
envisioned this limit as an enforceable
numerical limit that would ensure
performance consistent with that being
achieved by existing sources. However,
after consideration of the information
provided in public comment, we now
recognize that we do not have the
comprehensive data on existing POTW
that are necessary to conduct a
sufficiently robust analysis. The HAP
fraction emitted by different POTW is
influenced by individual HAP vapor
pressures, pollutant loadings, HAP
concentrations, sample measurement
and analytical techniques, and ambient
conditions, which differ from POTW to
POTW. Testing of influent loadings is
limited by applicable test methods, by
compounds identified by dischargers,
and by the HAP for which air permits
require sampling. Without sufficient
data, we cannot determine an
appropriate HAP fraction emitted limit,
considering the variability in operating
conditions that is likely to occur across
even well-operated POTW. Moreover, at
this time, we are unable to analyze the
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control costs for all affected sources or
the emissions reductions that might be
achieved. For all of these reasons, we
are not taking final action on the
proposed 0.08 HAP fraction at this time,
but we may in the future consider
promulgating a limit if we obtain further
information on the issues discussed
above.
G. New and Existing Group 1 POTW
In addition to proposing a HAP
fraction for existing Group 1 POTW, we
also proposed other changes to the
requirements for Group 1 POTW.
The 2002 POTW NESHAP required
existing Group 1 POTW to comply only
with the requirements of the other
NESHAP for which they are acting as an
agent of control for the industrial user.
We proposed that existing Group 1
POTW must meet both the requirements
of the other NESHAP for which they are
acting as an agent of control for an
industrial user and the proposed
requirements for existing Group 2
POTW in the POTW NESHAP (i.e., the
proposed 0.08 HAP fraction emitted
limit discussed in IV.F, above).
The 2002 POTW NESHAP required
new and reconstructed (which we are
now referring to as ‘‘new’’) Group 1
POTW to comply with the more
stringent of the following: (1) The
requirements of the other NESHAP for
which they are acting as an agent of
control for the industrial user; or (2) the
requirements applicable to new Group 2
POTW, which allowed the POTW to
choose to meet either a requirement to
(a) cover all equipment and route
emissions through a closed vent system
to a control device; or (b) meet a HAP
fraction emission limit of 0.014 for
emissions from all primary treatment
units. We proposed that new Group 1
POTW comply with the other NESHAP
for which they are acting as an agent of
control for an industrial user and the
requirements for new Group 2 POTW in
the 2002 POTW NESHAP. (Note that we
did not propose, and are not finalizing,
any revisions to the requirements for
new Group 2 POTW.)
1. Existing Group 1 POTW
Comment: We received comments
from one of the existing Group 1 POTW
that expressed concern that by imposing
the HAP fraction emitted limit on the
existing Group 1 POTW with no
alternative compliance option, the EPA
had ignored existing POTW with covers
and controls already in place. The
commenter stated that new Group 1
POTW have the option of either
installing covers or complying with the
HAP fraction limit. However, the EPA
did not provide that flexibility to
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existing Group 1 POTW, thereby
imposing an additional HAP fraction
limit without a cover option and more
onerous recordkeeping and reporting
requirements. The commenter stated
that the EPA should provide existing
Group 1 POTW that already use covers
the option of adding controls in lieu of
complying with a HAP fraction limit.
Response: The EPA is not taking final
action on the proposed changes for
existing Group 1 sources at this time. As
explained in section IV.F of this
preamble, we are not setting a HAP
fraction limit for existing Group 1 or
Group 2 POTW at this time; therefore,
no additional requirements are being
added for existing Group 1 POTW in the
POTW NESHAP. Thus, as required by
the 2002 POTW NESHAP, an existing
Group 1 POTW must comply with the
control requirements as specified in the
appropriate NESHAP for the industrial
user(s).
2. New Group 1 POTW
We did not receive any comment on
our proposed revision to the
requirements for new Group 1 POTW.
We proposed, and are finalizing, that
new Group 1 POTW must (1) meet the
requirements of the other NESHAP for
which they act as an agent of control for
an industrial user and (2) either (a)
cover all equipment and route emissions
through a closed vent system to a
control device or (b) meet a HAP
fraction emission limit of 0.014 for
emissions from all primary treatment
units. See 81 FR 95375 for our rationale
for this change. Because we received no
adverse comment on our proposal, we
are finalizing these requirements as
proposed.
V. Summary of Cost, Environmental,
and Economic Impacts and Additional
Analyses Conducted
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A. What are the affected facilities?
The EPA estimates, based on the
responses to the 2015 ICR, the 2011 and
2014 National Emissions Inventory
(NEI), and public comments received,
that there are 13 POTW that are engaged
in treatment of industrial wastewater
and are currently subject to the POTW
NESHAP. Two of these facilities are
considered Group 1 POTW, while the
remaining eleven are considered Group
2 POTW. All 13 currently subject to the
POTW NESHAP have already met the
notification requirements for existing
Group 1 and Group 2 POTW. The EPA
is not currently aware of any planned
new Group 1 or Group 2 POTW that will
be constructed or any existing Group 1
or Group 2 POTW that will be
reconstructed.
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B. What are the air quality impacts?
The EPA estimates that annual
organic HAP emissions from the 13
POTW subject to the rule are
approximately 35 tpy. We expect no
emissions of inorganic HAP from this
category. The EPA does not anticipate
any additional emission reductions from
the final changes to the rule, and there
are no anticipated new or reconstructed
facilities.
C. What are the cost impacts?
The 13 entities subject to this
proposal will incur only minimal costs
related to familiarizing themselves with
this rule—estimated to be a one-time
total cost of $790 for all 13 entities. For
further information on the requirements
of this rule, see section IV of this
preamble. For further information on
the costs associated with the
requirements of this rule, see the
document titled Economic Impact
Analysis for the National Emission
Standards for Hazardous Air Pollutants:
Publicly Owned Treatment Works Risk
and Technology Review, in the docket.
The memorandum titled Technology
Review Memorandum for the Publicly
Owned Treatment Works Source
Category, in the docket for this action,
presents costs estimated associated with
the regulatory options that were not
selected for inclusion in this final rule
(Docket ID No. EPA–HQ–OAR–2016–
0490).
D. What are the economic impacts?
The economic impact analysis is
designed to inform decision makers
about the potential economic
consequences of a regulatory action. For
this rule, the EPA estimated the annual
cost of recordkeeping and reporting as a
percentage of reported sewage fees
received by the affected POTW. For the
revisions promulgated in this final rule,
costs are expected to be less than 0.001
percent of collected sewage fees, based
on publicly available financial reports
from the fiscal year ending in 2015 for
the affected entities.
In addition, the EPA performed a
screening analysis for impacts on small
businesses by comparing estimated
population served by the affected
entities to the population limit set forth
by the U.S. Small Business
Administration. The screening analysis
found that the population served for all
affected entities is greater than the limit
qualifying a public entity as a small
business.
More information and details of the
EPA’s analysis of the economic impacts,
including the conclusions stated above,
are provided in the technical document,
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49523
Final Economic Impact Analysis for the
Publicly Owned Treatment Works
National Emissions Standards for
Hazardous Air Pollutants Risk and
Technology Review, which is available
in the docket for this final rule (Docket
ID No. EPA–HQ–OAR–2016–0490).
E. What are the benefits?
We do not anticipate any significant
reductions in HAP emissions as a result
of these final amendments. However, we
think that the amendments will help to
enhance the clarity of the rule, which
can improve compliance and minimize
emissions.
F. What analysis of environmental
justice did we conduct?
We examined the potential for any
environmental justice concerns that
might be associated with this source
category by performing a demographic
analysis of the population close to the
six POTW that were modeled for source
category risk.4 In this analysis, we
evaluated the distribution of HAPrelated cancer and non-cancer risks
from the POTW source category across
different social, demographic, and
economic groups within the populations
living near facilities identified as having
the highest risks. The methodology and
the results of the demographic analyses
are included in a technical report, Risk
and Technology Review—Analysis of
Socio-Economic Factors for Populations
Living Near POTW Facilities, available
in the docket for this action (Docket ID
No. EPA–HQ–OAR–2016–0490). The
results for various demographic groups
are based on the estimated risks from
actual emissions levels for the
population living within 50 kilometers
(km) of the facilities.
The results of the POTW source
category demographic analysis indicate
that actual emissions from the source
category expose no person to a cancer
risk at or above 1-in-1 million or to a
chronic non-cancer TOSHI greater than
1. Therefore, we conclude that this final
rule will not have disproportionately
high and adverse human health or
environmental effects on minority or
low-income populations because it does
not affect the level of protection
provided to human health or the
environment. However, this final rule
may provide additional benefits to these
demographic groups by improving the
compliance and implementation of the
NESHAP. The demographics of the
population living within 50 km of
POTW can be found in Table 2 of the
document titled Risk and Technology
4 See section IV.A of this preamble for an
explanation of the residual risk assessment.
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Review—Analysis of Socio-Economic
Factors for Populations Living Near
Publicly Owned Treatment Works,
available in the docket for this final rule
(Docket ID No. EPA–HQ–OAR–2016–
0490).
G. What analysis of children’s
environmental health did we conduct?
This action is not subject to Executive
Order 13045 because it is not
economically significant as defined in
Executive Order 12866, and because the
EPA does not believe the environmental
health or safety risks addressed by this
action present a disproportionate risk to
children. The results of the POTW
source category demographic analysis
indicate that actual emissions from the
source category expose no person to a
cancer risk at or above 1-in-1 million or
to a chronic non-cancer TOSHI greater
than 1. Therefore, the analysis shows
that actual emissions from the POTW
source category are not expected to have
an adverse human health effect on
children.
VI. Statutory and Executive Order
Reviews
Additional information about these
statutes and Executive Orders can be
found at https://www2.epa.gov/lawsregulations/laws-and-executive-orders.
A. Executive Order 12866: Regulatory
Planning and Review and Executive
Order 13563: Improving Regulation and
Regulatory Review
This action is not a significant
regulatory action and was therefore not
submitted to the Office of Management
and Budget (OMB) for review.
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B. Executive Order 13771: Reducing
Regulations and Controlling Regulatory
Costs
This action is not an Executive Order
13771 regulatory action because this
action is not significant under Executive
Order 12866.
C. Paperwork Reduction Act (PRA)
The information collection activities
in this rule have been submitted for
approval to the OMB under the PRA.
The ICR document that the EPA
prepared has been assigned EPA ICR
number 1891.08. You can find a copy of
the ICR in the docket for this rule, and
it is briefly summarized here. The
information collection requirements are
not enforceable until OMB approves
them.
The information to be collected
includes the initial notification that the
POTW is subject to the rule. However,
as stated in this preamble, the 13
sources that we already know about
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have already met this initial notification
requirement and are not required to
submit an additional notification. The
information will be used to identify
sources subject to the standards.
Respondents/affected entities: The
respondents to the recordkeeping and
reporting requirements are owners and
operators of POTW. The NAICS code for
the respondents affected by the standard
is 221320 (Sewage Treatment Facilities),
which corresponds to the United States
Standard Industrial Classification code
4952 (Sewerage Systems).
Respondent’s obligation to respond:
Respondents are obligated to respond in
accordance with the notification
requirements under 40 CFR 63.1591(a).
Estimated number of respondents:
Zero.
Frequency of response: One response.
Total estimated burden: 0 hours (per
year). Burden is defined at 5 CFR
1320.3(b).
Total estimated cost: $0 (per year),
includes $0 annualized capital or
operation and maintenance costs.
An agency may not conduct or
sponsor, and a person is not required to
respond to, a collection of information
unless it displays a currently valid OMB
control number. The OMB control
numbers for the EPA’s regulations in 40
CFR are listed in 40 CFR part 9. When
OMB approves this ICR, the Agency will
announce that approval in the Federal
Register and publish a technical
amendment to 40 CFR part 9 to display
the OMB control number for the
approved information collection
activities contained in this final rule.
D. Regulatory Flexibility Act (RFA)
I certify that this action will not have
a significant economic impact on a
substantial number of small entities
under the RFA. This action will not
impose any requirements on small
entities. There are no small entities
affected in this regulated industry. See
the technical document, Final Economic
Impact Analysis for the National
Emission Standards for Hazardous Air
Pollutants: Publicly Owned Treatment
Works Risk and Technology Review,
which is available in the docket for this
final rule (Docket ID No. EPA–HQ–
OAR–2016–0490) for more detail.
E. Unfunded Mandates Reform Act
(UMRA)
This action does not contain an
unfunded mandate of $100 million or
more as described in UMRA, 2 U.S.C.
1531–1538, and does not significantly or
uniquely affect small governments. The
action imposes no enforceable duty on
any state, local, or tribal governments or
the private sector.
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F. Executive Order 13132: Federalism
This action does not have federalism
implications. It will not have substantial
direct effects on the states, on the
relationship between the national
government and the states, or on the
distribution of power and
responsibilities among the various
levels of government.
G. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
This action does not have tribal
implications as specified in Executive
Order 13175. As discussed in section
II.B.1 of this preamble, we have
identified only 13 POTW that are
subject to this final rule and none of
those POTW are owned or operated by
tribal governments. Thus, Executive
Order 13175 does not apply to this
action.
H. Executive Order 13045: Protection of
Children From Environmental Health
Risks and Safety Risks
The action is not subject to Executive
Order 13045 because it is not
economically significant as defined in
Executive Order 12866, and because the
EPA does not believe the environmental
health or safety risks addressed by this
action present a disproportionate risk to
children. This action’s health and risk
assessments are contained in sections
III.A and B and sections IV.A and B of
this preamble and the Residual Risk
Report memorandum contained in the
docket for this rulemaking.
I. Executive Order 13211: Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use
This action is not subject to Executive
Order 13211 because it is not a
significant regulatory action under
Executive Order 12866.
J. National Technology Transfer and
Advancement Act (NTTAA)
This rulemaking does not involve
technical standards.
K. Executive Order 12898: Federal
Actions To Address Environmental
Justice in Minority Populations and
Low-Income Populations
The EPA believes that this action does
not have disproportionately high and
adverse human health or environmental
effects on minority populations, lowincome populations, and/or indigenous
peoples, as specified in Executive Order
12898 (59 FR 7629, February 16, 1994).
The documentation for this decision
is contained in section III.A.6 of this
preamble and in the corresponding
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technical report, Risk and Technology
Review—Analysis of Socio-Economic
Factors for Populations Living Near
Publicly Owned Treatment Works,
available in the docket for this action.
The proximity results indicate, for eight
of the 11 demographic categories, that
the population percentages within 5 km
and 50 km of source category emissions
are greater than the corresponding
national percentage for those same
demographics. However, the results of
the risk analysis presented in section
III.A.6 of this preamble and in the
corresponding technical report indicate
that actual emissions from the source
category expose no person to a cancer
risk at or above 1-in-1 million or to a
chronic non-cancer TOSHI greater than
1.
L. Congressional Review Act (CRA)
This action is subject to the CRA, and
the EPA will submit a rule report to
each House of the Congress and to the
Comptroller General of the United
States. This action is not a ‘‘major rule’’
as defined by 5 U.S.C. 804(2).
List of Subjects in 40 CFR Part 63
Environmental protection,
Administrative practice and procedures,
Air pollution control, Hazardous
substances, Intergovernmental relations,
Reporting and recordkeeping
requirements.
Dated: October 16, 2017.
E. Scott Pruitt,
Administrator.
For the reasons stated in the
preamble, the Environmental Protection
Agency amends part 63 of title 40,
chapter I, of the Code of Federal
Regulations as follows:
PART 63—NATIONAL EMISSION
STANDARDS FOR HAZARDOUS AIR
POLLUTANTS FOR SOURCE
CATEGORIES
1. The authority citation for part 63
continues to read as follows:
■
Authority: 42 U.S.C. 7401, et seq.
2. Part 63 is amended by revising
subpart VVV to read as follows:
■
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Subpart VVV—National Emission Standards
for Hazardous Air Pollutants: Publicly
Owned Treatment Works
Applicability
Sec.
63.1580 Am I subject to this subpart?
63.1581 Does the subpart distinguish
between different types of POTW
treatment plants?
18:08 Oct 25, 2017
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Requirements for Group 1 and Group 2
POTW Treatment Plants
63.1586 What are the emission points and
control requirements for a Group 1 or
Group 2 POTW?
63.1587 When do I have to comply?
63.1588 How do Group 1 and Group 2
POTW treatment plants demonstrate
compliance?
63.1589 What records must I keep?
63.1590 What reports must I submit?
63.1591 What are my notification
requirements?
63.1592 Which General Provisions apply to
my POTW treatment plant?
63.1593 [Reserved]
63.1594 Who enforces this subpart?
63.1595 List of definitions.
Table 1 to Subpart VVV of Part 63—
Applicability of 40 CFR part 63 General
Provisions to Subpart VVV
Table 2 to Subpart VVV of Part 63—
Compliance Dates and Requirements
Subpart VVV—National Emission
Standards for Hazardous Air
Pollutants: Publicly Owned Treatment
Works
Applicability
§ 63.1580
Am I subject to this subpart?
(a) You are subject to this subpart if
the following are all true:
(1) You own or operate a publicly
owned treatment works (POTW) that
includes an affected source (§ 63.1595);
(2) The affected source is located at a
Group 2 POTW which is a major source
of HAP emissions, or at any Group 1
POTW regardless of whether or not it is
a major source of HAP; and
(3) Your POTW is required to develop
and implement a pretreatment program
as defined by 40 CFR 403.8, or your
POTW meets the general criteria for
development and implementation of a
pretreatment program.
(b) If your existing POTW treatment
plant is not located at a major source as
of October 26, 1999, but thereafter
becomes a major source for any reason
other than reconstruction, then, for the
purpose of this subpart, your POTW
treatment plant would be considered an
existing source.
Note to paragraph (b): See § 63.2 of the
National Emission Standards for Hazardous
Air Pollutants (NESHAP) General Provisions
in subpart A of this part for the definitions
of major source and area source.
Requirements for Group 1 POTW Treatment
Plants
63.1582 [Reserved]
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63.1583 What are the emission points and
control requirements for a Group 1
POTW treatment plant?
63.1584 [Reserved]
63.1585 How does a Group 1 POTW
treatment plant demonstrate
compliance?
(c) If you commence construction or
reconstruction of your POTW treatment
plant after December 1, 1998, then the
requirements for a new POTW apply.
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§ 63.1581 Does the subpart distinguish
between different types of POTW treatment
plants?
Yes, POTW treatment plants are
divided into two subcategories: Group 1
POTW treatment plants and Group 2
POTW treatment plants, as described in
paragraphs (a) through (c) of this
section.
(a) Your POTW is a Group 1 POTW
treatment plant if an industrial user
complies with its NESHAP by using the
treatment and controls located at your
POTW treatment plant. Your POTW
treatment plant accepts the regulated
waste stream and provides treatment
and controls as an agent for the
industrial user. Group 1 POTW
treatment plant is defined in § 63.1595.
(b) Your POTW is a Group 2 POTW
treatment plant if your POTW treats
wastewater that is not subject to control
by another NESHAP or the industrial
user does not comply with its NESHAP
by using the treatment and controls
located at your POTW treatment plant.
‘‘Group 2 POTW treatment plant’’ is
defined in § 63.1595.
(c) If, in the future, an industrial user
complies with its NESHAP by using the
treatment and controls located at your
POTW treatment plant, then your Group
2 POTW treatment plant becomes a
Group 1 POTW treatment plant on the
date your POTW begins treating that
regulated industrial wastewater stream.
Requirements for Group 1 POTW
Treatment Plants
§ 63.1582
[Reserved]
§ 63.1583 What are the emission points
and control requirements for a Group 1
POTW treatment plant?
(a) The emission points and control
requirements for an existing Group 1
POTW treatment plant are specified in
the appropriate NESHAP for the
industrial user(s).
(b) The emission points and control
requirements for a new Group 1 POTW
treatment plant are both those specified
by the appropriate NESHAP which
apply to the industrial user(s) who
discharge their waste for treatment to
the POTW, and those emission points
and control requirements set forth in
§ 63.1586(b) or (c), as applicable.
(c) If your existing or new Group 1
POTW treatment plant accepts one or
more specific regulated industrial waste
streams as part of compliance with one
or more other NESHAP, then you are
subject to all the requirements of each
appropriate NESHAP for each waste
stream.
(d) At all times, the POTW must
operate and maintain any affected
source, including associated air
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pollution control equipment and
monitoring equipment, in a manner
consistent with safety and good air
pollution control practices for
minimizing emissions. The general duty
to minimize emissions does not require
the POTW to make any further efforts to
reduce emissions if levels required by
the applicable standard have been
achieved. Determination of whether a
source is operating in compliance with
operation and maintenance
requirements will be based on
information available to the
Administrator, which may include, but
is not limited to, monitoring results,
review of operation and maintenance
procedures, review of operation and
maintenance records, and inspection of
the source.
§ 63.1584
[Reserved]
§ 63.1585 How does a Group 1 POTW
treatment plant demonstrate compliance?
(a) An existing Group 1 POTW
treatment plant demonstrates
compliance by operating treatment and
control devices which meet all
requirements specified in the
appropriate NESHAP. Requirements
may include performance tests, routine
monitoring, recordkeeping, and
reporting.
(b) A new Group 1 POTW treatment
plant demonstrates compliance by
operating treatment and control devices
which meet all requirements specified
in the appropriate NESHAP and by
meeting the requirements specified in
§ 63.1586, as applicable, as well as the
applicable requirements in §§ 63.1588
through 63.1595.
Requirements for Group 1 and Group 2
POTW Treatment Plants
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§ 63.1586 What are the emission points
and control requirements for a Group 1 or
Group 2 POTW?
(a) An existing Group 1 or Group 2
POTW treatment plant must comply
with the initial notification
requirements in § 63.1591(a).
(b) Cover and control standard.
Except as provided in paragraph (c) of
this section, new Group 1 and Group 2
POTW treatment plants must install
covers on the emission points up to, but
not including, the secondary influent
pumping station or the secondary
treatment units. These emission points
are treatment units that include, but are
not limited to, influent waste stream
conveyance channels, bar screens, grit
chambers, grinders, pump stations,
aerated feeder channels, primary
clarifiers, primary effluent channels,
and primary screening stations. In
addition, all covered units, except
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primary clarifiers, must have the air in
the headspace underneath the cover
ducted to a control device in accordance
with the standards for closed-vent
systems and control devices in § 63.693
of subpart DD—National Emission
Standards for Hazardous Air Pollutants
from Off-site Waste and Recovery
Operations of this part, except you may
substitute visual inspections for leak
detection rather than Method 21 of
appendix A–7 of part 60 of this chapter.
Covers must meet the following
requirements:
(1) Covers must be tightly fitted and
designed and operated to prevent
exposure of the wastewater to the
atmosphere. This includes, but is not
limited to, the absence of visible cracks,
holes, or gaps in the roof sections or
between the roof and the supporting
wall; broken, cracked, or otherwise
damaged seals or gaskets on closure
devices; and broken or missing hatches,
access covers, caps, or other closure
devices.
(2) If wastewater is in a treatment
unit, each opening in the cover must be
maintained in a closed, sealed position,
unless plant personnel are present and
conducting wastewater or sludge
sampling, or equipment inspection,
maintenance, or repair.
(c) HAP fraction emitted standard. As
an alternative to the requirements in
paragraph (b) of this section, a new
Group 1 and Group 2 POTW treatment
plant may comply by demonstrating, for
all emission points up to, but not
including, the secondary influent
pumping station or the secondary
treatment units, that the annual rolling
average HAP fraction emitted
(calculated as specified in
§ 63.1588(c)(3)) does not exceed 0.014.
You must demonstrate that for your
POTW treatment plant, the sum of all
HAP emissions from these units divided
by the sum of all HAP mass loadings to
the POTW treatment plant results in an
annual rolling average of the HAP
fraction emitted of no greater than
0.014. You may use any combination of
pretreatment, wastewater treatment
plant modifications, and control devices
to achieve this performance standard.
(d) At all times, the POTW 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. The general duty
to minimize emissions does not require
the POTW to make any further efforts to
reduce emissions if the requirements of
the applicable standard have been met.
Determination of whether a source is
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operating in compliance with operation
and maintenance requirements will be
based on information available to the
Administrator, which may include, but
is not limited to, monitoring results,
review of operation and maintenance
procedures, review of operation and
maintenance records, and inspection of
the source.
§ 63.1587
When do I have to comply?
Sources subject to this subpart are
required to achieve compliance on or
before the dates specified in table 2 of
this subpart.
§ 63.1588 How do Group 1 and Group 2
POTW treatment plants demonstrate
compliance?
(a) If you are complying with
§ 63.1586(b) by using covers, you must
conduct the following inspections:
(1) You must visually check the cover
and its closure devices for defects that
could result in air emissions. Defects
include, but are not limited to, visible
cracks, holes, or gaps in the roof
sections or between the roof and the
supporting wall; broken, cracked, or
otherwise damaged seals or gaskets on
closure devices; and broken or missing
hatches, access covers, caps, or other
closure devices.
(2) You must perform an initial visual
inspection within 60 calendar days of
becoming subject to this NESHAP and
perform follow-up inspections at least
once per year, thereafter.
(3) In the event that you find a defect
on a cover on a treatment unit in use,
you must repair the defect within 45
calendar days. If you cannot repair
within 45 calendar days, you must
notify the EPA or the delegated
authority immediately and report the
reason for the delay and the date you
expect to complete the repair. If you
find a defect on a cover on a treatment
unit that is not in service, you must
repair the defect prior to putting the
treatment unit back in wastewater
service.
(b) If you own or operate a control
device used to meet the requirements
for § 63.1586(b), you must comply with
the inspection and monitoring
requirements of § 63.695(c) of subpart
DD of this part.
(c) To comply with the HAP fraction
emitted standard specified in
§ 63.1586(c), you must develop, to the
satisfaction of the Administrator, an
Inspection and Monitoring Plan. This
Inspection and Monitoring Plan must
include, at a minimum, the following:
(1) A method to determine the
influent HAP mass loading, i.e., the
annual mass quantity for each HAP
entering the wastewater treatment plant.
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(2) A method to determine your
POTW treatment plant’s annual HAP
emissions for all units up to, but not
including, the secondary influent
pumping station or the secondary
treatment units. The method you use to
determine your HAP emissions, such as
modeling or direct source measurement,
must:
(i) Be approved by the Administrator
for use at your POTW;
(ii) Account for all factors affecting
emissions from your POTW treatment
plant including, but not limited to,
emissions from wastewater treatment
units; emissions resulting from
inspection, maintenance, and repair
activities; fluctuations (e.g., daily,
monthly, annual, seasonal) in your
influent wastewater HAP
concentrations; annual industrial
loading; performance of control devices;
or any other factors that could affect
your annual HAP emissions; and
(iii) Include documentation that the
values and sources of all data, operating
conditions, assumptions, etc., used in
your method result in an accurate
estimation of annual emissions from
your POTW treatment plant.
(3) A method to demonstrate that your
POTW treatment plant meets the HAP
fraction emitted standard specified in
§ 63.1586(c), i.e., the sum of all HAP
emissions from paragraph (c)(2) of this
section divided by the sum of all HAP
mass loadings from paragraph (c)(1) of
this section results in a fraction emitted
of 0.014 or less to demonstrate
compliance with § 63.1586(c). The
Inspection and Monitoring Plan must
require, at a minimum, that you perform
the calculations shown in paragraphs
(c)(3)(i) through (viii) of this section
within 90 days of the end of each
month. This calculation shall
demonstrate that your annual rolling
average of the HAP fraction emitted is
0.014 or less when demonstrating
compliance with § 63.1586(c).
(i) Determine the average daily flow in
million gallons per day (MGD) of the
wastewater entering your POTW
treatment plant for the month;
(ii) Determine the flow-weighted
monthly concentration of each HAP
listed in Table 1 to subpart DD of this
part that is reasonably anticipated to be
present in your influent;
(iii) Using the information in
paragraphs (c)(3)(i) and (ii) of this
section, determine a total annual flowweighted loading in pounds per day
(lbs/day) of each HAP entering your
POTW treatment plant;
(iv) Sum up the values for each
individual HAP loading in paragraph
(c)(3)(iii) of this section and determine
a total annual flow-weighted loading
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value (lbs/day) for all HAP entering
your POTW treatment plant for the
current month;
(v) Based on the current month’s
information in paragraph (c)(3)(iii) of
this section along with source testing
and emission modeling, for each HAP,
determine the annual emissions (lbs/
day) from all wastewater units up to, but
not including, secondary treatment
units;
(vi) Sum up the values in paragraph
(c)(3)(v) of this section and calculate the
total annual emissions value for the
month for all HAP from all wastewater
treatment units up to, but not including,
secondary treatment units;
(vii) Calculate the HAP fraction
emitted value for the month, using
Equation 1 of this section as follows:
Where:
femonthly = HAP fraction emitted for the
previous month
èE = Total HAP emissions value from
paragraph (c)(3)(vi) of this section
èL = Total annual loading from paragraph
(c)(3)(iv) of this section
(viii) Average the HAP fraction
emitted value for the month determined
in paragraph (c)(3)(vii) of this section,
with the values determined for the
previous 11 months, to calculate an
annual rolling average of the HAP
fraction emitted.
(4) A method to demonstrate, to the
satisfaction of the Administrator, that
your POTW treatment plant is in
continuous compliance with the
requirements of § 63.1586(c).
Continuous compliance means that your
emissions, when averaged over the
course of a year, do not exceed the level
of emissions that allows your POTW to
comply with § 63.1586(c). For example,
you may identify a parameter(s) that you
can monitor that assures your
emissions, when averaged over the
entire year, will meet the requirements
in § 63.1586(c). Some example
parameters that may be considered for
monitoring include your wastewater
influent HAP concentration and flow,
industrial loading from your permitted
industrial users, and your control device
performance criteria. Where emission
reductions are due to proper operation
of equipment, work practices, or other
operational procedures, your
demonstration must specify the
frequency of inspections and the
number of days to completion of repairs.
(d) Prior to receiving approval on the
Inspection and Monitoring Plan, you
must follow the plan submitted to the
Administrator as specified in
§ 63.1590(f).
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§ 63.1589
49527
What records must I keep?
(a) To comply with the cover and
control standard specified in
§ 63.1586(b), you must prepare and
maintain the records required in
paragraphs (a)(1) through (4) of this
section:
(1) A record for each treatment unit
inspection required by § 63.1588(a). You
must include a treatment unit
identification number (or other unique
identification description as selected by
you) and the date of inspection.
(2) For each defect detected during
inspections required by § 63.1588(a),
you must record the location of the
defect, a description of the defect, the
date of detection, the corrective action
taken to repair the defect, and the date
the repair to correct the defect is
completed.
(3) If repair of the defect is delayed as
described in § 63.1588(a)(3), you must
also record the reason for the delay and
the date you expect to complete the
repair.
(4) If you own or operate a control
device used to meet the requirements
for § 63.1586(b), you must comply with
the recordkeeping requirements of
§ 63.696(a), (b), (g), and (h).
(b) To comply with the HAP fraction
emitted standard specified in
§ 63.1586(c), you must prepare and
maintain the records required in
paragraphs (b)(1) through (3) of this
section:
(1) A record of the methods and data
used to determine your POTW treatment
plant’s annual HAP loading and HAP
emissions as determined in
§ 63.1588(c)(1) and (2) as part of your
Inspection and Monitoring Plan;
(2) A record of the methods and data
used to determine that your POTW
treatment plant meets the HAP fraction
emitted standard of 0.014 or less, as
determined in § 63.1588(c)(3) as part of
your Inspection and Monitoring Plan;
and
(3) A record of the methods and data
that demonstrates that your POTW
treatment plant is in continuous
compliance with the requirements of
§ 63.1588(c)(4) to calculate annual
emissions as specified in your
Inspection and Monitoring Plan.
(c) The POTW must record the
malfunction information specified in
paragraphs (c)(1) through (3) of this
section.
(1) In the event that an affected unit
fails to meet an applicable standard,
record the number of failures. For each
failure, record the date, time, and
duration of the failure.
(2) For each failure to meet an
applicable standard, record and retain a
list of the affected sources or equipment,
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an estimate of the tons per year of each
regulated pollutant emitted over any
emission limit and a description of the
method used to estimate the emissions.
(3) Record actions taken to minimize
emissions in accordance with
§ 63.1583(d) or § 63.1586(d) and any
corrective actions taken to return the
affected unit to its normal or usual
manner of operation.
(d) Any records required to be
maintained by this part that are
submitted electronically via the EPA’s
Compliance and Emissions Data
Reporting Interface (CEDRI) may be
maintained in electronic format. This
ability to maintain electronic copies
does not affect the requirement for
facilities to make records, data, and
reports available upon request to a
delegated air agency or the EPA as part
of an on-site compliance evaluation.
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§ 63.1590
What reports must I submit?
(a) An existing Group 1 POTW must
meet the reporting requirements
specified in the appropriate NESHAP
for the industrial user(s).
(b) A new Group 1 or Group 2 POTW
must submit annual reports containing
the information specified in paragraphs
(b)(1) through (4) of this section, if
applicable. You must submit annual
reports following the procedure
specified in paragraph (b)(5) of this
section. For new units, the initial
annual report is due 15 months after
your POTW becomes subject to the
requirements in this subpart and must
cover the first 12 months of operation
after your POTW becomes subject to the
requirements of this subpart.
Subsequent annual reports are due by
the same date each year as the initial
annual report and must contain
information for the 12-month period
following the 12-month period included
in the previous annual report.
(1) The general information specified
in paragraphs (b)(1)(i) and (ii) of this
section must be included in all reports.
(i) The company name, POTW
treatment plant name, and POTW
treatment plant address, including
county where the POTW is located; and
(ii) Beginning and ending dates of the
reporting period.
(2) If you use covers to comply with
the requirements of § 63.1586(b), you
must submit the following:
(i) The dates of each visual inspection
conducted;
(ii) The defects found during each
visual inspection; and
(iii) For each defect found during a
visual inspection, how the defects were
repaired, whether the repair has been
completed, and either the date each
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repair was completed or the date each
repair is expected to be completed.
(3) If you comply with the HAP
fraction emitted standard in
§ 63.1586(c), you must submit each
value of the annual rolling average HAP
fraction emitted as calculated in
§ 63.1588(c)(3)(vii) for the period
covered by the annual report. Identify
each value by the final month included
in the calculation.
(4) If a source fails to meet an
applicable standard, report such events
in the annual report. Report the number
of failures to meet an applicable
standard. For each instance, report the
start date, start time, and duration of
each failure, as well as a list of the
affected sources or equipment. If you
comply with the cover and control
standard in § 63.1586(b), for each
failure, the report must include the
percent control achieved. If you comply
with the HAP fraction emitted standard
in § 63.1586(c), for each failure, the
report must include the HAP fraction
emitted. You must include an estimate
of the tons per year of each regulated
pollutant emitted over the emission
limit and a description of the method
used to estimate the emissions in the
report.
(5) You must submit the report to the
Administrator at the appropriate
address listed in § 63.13, unless the
Administrator agrees to or species an
alternate reporting method. Beginning
on October 28, 2019 or once the
reporting form has been available in
CEDRI for 1 year, whichever is later, you
must submit subsequent annual reports
to the EPA via CEDRI. (CEDRI can be
accessed through the EPA’s Central Data
Exchange (CDX)(https://cdx.epa.gov/)).
You must use the appropriate electronic
report template on the CEDRI Web site
for this subpart or an alternate
electronic file format consistent with the
extensible markup language (XML)
schema listed on the CEDRI Web site
(https://www.epa.gov/electronicreporting-air-emissions/complianceand-emissions-data-reporting-interfacecedri). The date report templates
become available in CEDRI will be listed
on the CEDRI Web site. The reports
must be submitted by the deadline
specified in this subpart, regardless of
the method in which the reports are
submitted. If you claim that some of the
information required to be submitted via
CEDRI is confidential business
information (CBI), you shall submit a
complete report generated using the
appropriate form in CEDRI or an
alternate electronic file consistent with
the extensible markup language (XML)
schema listed on the EPA’s CEDRI Web
site, including information claimed to
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be CBI, on a compact disc, flash drive,
or other commonly used electronic
storage medium to the EPA. The
electronic medium shall be clearly
marked as CBI and mailed to U.S. EPA/
OAQPS/CORE CBI Office, Attention:
Group Leader, Measurement Policy
Group, MD C404–02, 4930 Old Page Rd.,
Durham, NC 27703. The same file with
the CBI omitted shall be submitted to
the EPA via the EPA’s CDX as described
earlier in this paragraph.
(c) If you own or operate a control
device used to meet the cover and
control standard in § 63.1586(b), you
must submit the notifications and
reports required by § 63.697(b),
including a notification of performance
tests; a performance test report; a
malfunction report; and a summary
report. These notifications and reports
must be submitted to the Administrator,
except for performance test reports.
Within 60 calendar days after the date
of completing each performance test (as
defined in § 63.2) required by subpart
DD of this part, you must submit the
results of the performance test following
the procedure specified in paragraphs
(c)(1) through (3) of this section.
(1) For data collected using test
methods supported by the EPA’s
Electronic Reporting Tool (ERT) as
listed on the EPA’s ERT Web site
(https://www.epa/gov/electronicreporting-air-emissions/electronicreporting-tool-ert) at the time of the test,
you must submit the results of the
performance test to the EPA via CEDRI.
Performance test data must be submitted
in a file format generated through the
use of the EPA’s ERT or an alternate
electronic file format consistent with the
XML schema listed on the EPA’s ERT
Web site.
(2) For data collected using test
methods that are not supported by the
EPA’s ERT as listed on the EPA’s ERT
Web site at the time of the test, you must
submit the results of the performance
test to the Administrator at the
appropriate address listed in § 63.13 of
subpart A of this part, unless the
Administrator agrees to or specifies an
alternate reporting method.
(3) If you claim that some of the
performance test information being
submitted under paragraph (b)(1) of this
section is CBI, you must submit a
complete file generated through the use
of the EPA’s ERT or an alternate
electronic file consistent with the XML
schema listed on the EPA’s ERT Web
site, including information claimed to
be CBI, on a compact disc, flash drive,
or other commonly used electronic
storage medium to the EPA. The
electronic medium must be clearly
marked as CBI and mailed to U.S. EPA/
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Federal Register / Vol. 82, No. 206 / Thursday, October 26, 2017 / Rules and Regulations
OAQPS/CORE CBI Office, Attention:
Group Leader, Measurement Policy
Group, MD C404–02, 4930 Old Page Rd.,
Durham, NC 27703. The same ERT or
alternate file with the CBI omitted must
be submitted to the EPA via the EPA’s
CDX as described in paragraph (c)(1) of
this section.
(d) You must comply with the delay
of repair reporting required in
§ 63.1588(a)(3).
(e) You may apply to the
Administrator for a waiver of
recordkeeping and reporting
requirements by complying with the
requirements of § 63.10(f). Electronic
reporting to the EPA cannot be waived.
(f) To comply with the HAP fraction
emitted standard specified in
§ 63.1586(c), you must submit, for
approval by the Administrator, an
Inspection and Monitoring Plan
explaining your compliance approach
90 calendar days prior to beginning
operation of your new POTW or by
April 24, 2018, whichever is later.
(g) If you are required to electronically
submit a report through the CEDRI in
the EPA’s CDX, and due to a planned or
actual outage of either the EPA’s CEDRI
or CDX systems within the period of
time beginning 5 business days prior to
the date that the submission is due, you
will be or are precluded from accessing
CEDRI or CDX and submitting a
required report within the time
prescribed, you may assert a claim of
EPA system outage for failure to timely
comply with the reporting requirement.
You must submit notification to the
Administrator in writing as soon as
possible following the date you first
knew, or through due diligence should
have known, that the event may cause
or caused a delay in reporting. You must
provide to the Administrator a written
description identifying the date, time
and length of the outage; a rationale for
attributing the delay in reporting
beyond the regulatory deadline to the
EPA system outage; describe the
measures taken or to be taken to
minimize the delay in reporting; and
identify a date by which you propose to
report, or if you have already met the
reporting requirement at the time of the
notification, the date you reported. In
any circumstance, the report must be
submitted electronically as soon as
possible after the outage is resolved. The
decision to accept the claim of EPA
system outage and allow an extension to
the reporting deadline is solely within
the discretion of the Administrator.
(h) If you are required to
electronically submit a report through
CEDRI in the EPA’s CDX and a force
majeure event is about to occur, occurs,
or has occurred or there are lingering
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effects from such an event within the
period of time beginning five business
days prior to the date the submission is
due, the owner or operator may assert a
claim of force majeure for failure to
timely comply with the reporting
requirement. For the purposes of this
section, a force majeure event is defined
as an event that will be or has been
caused by circumstances beyond the
control of the affected facility, its
contractors, or any entity controlled by
the affected facility that prevents you
from complying with the requirement to
submit a report electronically within the
time period prescribed. Examples of
such events are acts of nature (e.g.,
hurricanes, earthquakes, or floods), acts
of war or terrorism, or equipment failure
or safety hazard beyond the control of
the affected facility (e.g., large scale
power outage). If you intend to assert a
claim of force majeure, you must submit
notification to the Administrator in
writing as soon as possible following the
date you first knew, or through due
diligence should have known, that the
event may cause or caused a delay in
reporting. You must provide to the
Administrator a written description of
the force majeure event and a rationale
for attributing the delay in reporting
beyond the regulatory deadline to the
force majeure event; describe the
measures taken or to be taken to
minimize the delay in reporting; and
identify a date by which you propose to
report, or if you have already met the
reporting requirement at the time of the
notification, the date you reported. In
any circumstance, the reporting must
occur as soon as possible after the force
majeure event occurs. The decision to
accept the claim of force majeure and
allow an extension to the reporting
deadline is solely within the discretion
of the Administrator.
§ 63.1591 What are my notification
requirements?
(a) You must submit an initial
notification that your POTW treatment
plant is subject to these standards as
specified in paragraphs (a)(1) and (2) of
this section.
(1) If you have an existing Group 1 or
Group 2 POTW treatment plant, you
must submit an initial notification by
October 26, 2018.
(2) If you have a new Group 1 or
Group 2 POTW treatment plant, you
must submit an initial notification upon
startup.
(b) The initial notification must
include the information included in
paragraphs (b)(1) through (4) of this
section.
(1) Your name and address;
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49529
(2) The address (i.e., physical
location) of your POTW treatment plant;
(3) An identification of these
standards as the basis of the notification
and your POTW treatment plant’s
compliance date; and
(4) A brief description of the nature,
size, design, and method of operation of
your POTW treatment plant, including
its operating design capacity and an
identification of each point of emission
for each HAP, or if a definitive
identification is not yet possible, a
preliminary identification of each point
of emission for each HAP.
(c) You must submit a notification of
compliance status as required in
§ 63.9(h), as specified below:
(1) If you comply with § 63.1586(b)
and use covers on the emission points
and route air in the headspace
underneath the cover to a control
device, you must submit a notification
of compliance status as specified in
§ 63.9(h) that includes a description of
the POTW treatment units and installed
covers, as well as the information
required for control devices including
the performance test results.
(2) If you comply with § 63.1586(c) by
meeting the HAP fraction emitted
standard, submission of the Inspection
and Monitoring Plan as required in
§ 63.1588(c) and § 63.1590(f) meets the
requirement for submitting a
notification of compliance status report
in § 63.9(h).
(d) You must notify the
Administrator, within 30 calendar days
of discovering that you are out of
compliance with an applicable
requirement of this subpart, including
the following:
(1) The requirement to route the air in
the headspace underneath the cover of
all units equipped with covers, except
primary clarifiers, to a control device as
specified in § 63.1586(b).
(2) The HAP fraction emitted standard
as specified in § 63.1586(c).
(3) The requirement to operate and
maintain the affected source as specified
in § 63.1586(d).
(4) The requirement to inspect covers
annually and repair defects as specified
in § 63.1588(a).
(5) The requirement to comply with
the inspection and monitoring
requirements of § 63.695(c) as specified
in § 63.1588(b).
(6) The procedures specified in an
Inspection and Monitoring Plan
prepared as specified in § 63.1588(c).
(7) The requirements specified in an
appropriate NESHAP for which the
Group 1 POTW treatment plan treats
regulated industrial waste as specified
in § 63.1583(a) or (b), as applicable.
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§ 63.1592 Which General Provisions apply
to my POTW treatment plant?
(a) Table 1 to this subpart lists the
General Provisions (40 CFR part 63,
subpart A) which do and do not apply
to POTW treatment plants.
(b) Unless a permit is otherwise
required by law, the owner or operator
of a Group 1 POTW treatment plant
which is not a major source is exempt
from the permitting requirements
established by 40 CFR part 70.
§ 63.1593
[Reserved]
§ 63.1594
Who enforces this subpart?
(a) This subpart can be implemented
and enforced by the U.S. EPA, or a
delegated authority such as the
applicable state, local, or tribal agency.
If the U.S. EPA Administrator has
delegated authority to a state, local, or
tribal agency, then that agency, in
addition to the U.S. EPA, has the
authority to implement and enforce this
subpart. Contact the applicable U.S.
EPA Regional Office to find out if
implementation and enforcement of this
subpart is delegated to a state, local, or
tribal agency.
(b) In delegating implementation and
enforcement authority of this subpart to
a state, local, or tribal agency under
subpart E of this part, the authorities
contained in paragraphs (b)(1) through
(5) of this section are retained by the
Administrator of U.S. EPA and cannot
be delegated to the state, local, or tribal
agency.
(1) Approval of alternatives to the
requirements in §§ 63.1580, 63.1583,
and 63.1586 through 63.1588.
(2) Approval of major alternatives to
test methods under § 63.7(e)(2)(ii) and
(f), as defined in § 63.90, and as required
in this subpart.
(3) Approval of major alternatives to
monitoring under § 63.8(f), as defined in
§ 63.90, and as required in this subpart.
(4) Approval of major alternatives to
recordkeeping and reporting under
§ 63.10(f), as defined in § 63.90, and as
required in this subpart.
(5) Approval of an alternative to any
electronic reporting to the EPA required
by this subpart.
§ 63.1595
List of definitions.
As used in this subpart:
Affected source means the group of all
equipment that comprise the POTW
treatment plant.
Cover means a device that prevents or
reduces air pollutant emissions to the
atmosphere by forming a continuous
barrier over the waste material managed
in a treatment unit. A cover may have
openings (such as access hatches,
sampling ports, gauge wells) that are
necessary for operation, inspection,
maintenance, and repair of the
treatment unit on which the cover is
used. A cover may be a separate piece
of equipment which can be detached
and removed from the treatment unit, or
a cover may be formed by structural
features permanently integrated into the
design of the treatment unit. The cover
and its closure devices must be made of
suitable materials that will prevent
exposure of the waste material to the
atmosphere and will maintain the
integrity of the cover and its closure
devices throughout its intended service
life.
Existing source or existing POTW
means a POTW that commenced
construction on or before December 1,
1998, and has not been reconstructed
after December 1, 1998.
Fraction emitted means the fraction of
the mass of HAP entering the POTW
wastewater treatment plant which is
emitted prior to secondary treatment.
Group 1 POTW means a POTW that
accepts a waste stream regulated by
another NESHAP and provides
treatment and controls as an agent for
the industrial user. The industrial user
complies with its NESHAP by using the
treatment and controls located at the
POTW. For example, an industry
discharges its benzene-containing waste
stream to the POTW for treatment to
comply with 40 CFR part 61, subpart
FF—National Emission Standard for
Benzene Waste Operations. This
definition does not include POTW
treating waste streams not specifically
regulated under another NESHAP.
Group 2 POTW means a POTW that
does not meet the definition of a Group
1 POTW. A Group 2 POTW can treat a
waste stream that is either:
(1) Not specifically regulated by
another NESHAP, or
(2) From an industrial user that
complies with the specific wastewater
requirements in their applicable
NESHAP prior to discharging the waste
stream to the POTW.
Industrial user means a nondomestic
source introducing any pollutant or
combination of pollutants into a POTW.
Industrial users can be commercial or
industrial facilities whose wastes enter
local sewers.
New source or new POTW means any
POTW that commenced construction or
reconstruction after December 1, 1998.
Publicly owned treatment works
(POTW) means a treatment works, as
that term is defined by section 112(e)(5)
of the Clean Air Act, which is owned by
a municipality (as defined by section
502(4) of the Clean Water Act), a state,
an intermunicipal or interstate agency,
or any department, agency, or
instrumentality of the federal
government. This definition includes
any intercepting sewers, outfall sewers,
sewage collection systems, pumping,
power, and other equipment. The
wastewater treated by these facilities is
generated by industrial, commercial,
and domestic sources. As used in this
subpart, the term POTW refers to both
any publicly owned treatment works
which is owned by a state, municipality,
or intermunicipal or interstate agency
and, therefore, eligible to receive grant
assistance under the Subchapter II of the
Clean Water Act, and any federally
owned treatment works as that term is
described in section 3023 of the Solid
Waste Disposal Act.
POTW treatment plant means that
portion of the POTW which is designed
to provide treatment (including
recycling and reclamation) of municipal
sewage and industrial waste.
Secondary treatment means treatment
processes, typically biological, designed
to reduce the concentrations of
dissolved and colloidal organic matter
in wastewater.
Waste and wastewater means a
material, or spent or used water or
waste, generated from residential,
industrial, commercial, mining, or
agricultural operations or from
community activities that contain
dissolved or suspended matter, and that
is discarded, discharged, or is being
accumulated, stored, or physically,
chemically, thermally, or biologically
treated in a publicly owned treatment
works.
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TABLE 1 TO SUBPART VVV OF PART 63—APPLICABILITY OF 40 CFR PART 63 GENERAL PROVISIONS TO SUBPART VVV
General provisions
reference
Applicable to subpart VVV
§ 63.1 ........................
§ 63.1(a)(1) ...............
§ 63.1(a)(2) ...............
§ 63.1(a)(3) ...............
.................................................
Yes ..........................................
Yes ..........................................
Yes ..........................................
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Explanation
Applicability.
Terms defined in the Clean Air Act.
General applicability explanation.
Cannot diminish a stricter NESHAP.
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TABLE 1 TO SUBPART VVV OF PART 63—APPLICABILITY OF 40 CFR PART 63 GENERAL PROVISIONS TO SUBPART VVV—
Continued
Applicable to subpart VVV
Explanation
§ 63.1(a)(4) ...............
§ 63.1(a)(5) ...............
§ 63.1(a)(6)–(8) .........
§ 63.1(a)(9) ...............
§ 63.1(a)(10) .............
§ 63.1(a)(11) .............
§ 63.1(a)(12)–(14) .....
§ 63.1(b)(1) ...............
§ 63.1(b)(2) ...............
§ 63.1(b)(3) ...............
§ 63.1(c)(1) ...............
§ 63.1(c)(2)(i) ............
Yes ..........................................
Yes ..........................................
Yes ..........................................
Yes ..........................................
Yes ..........................................
Yes ..........................................
Yes ..........................................
Yes ..........................................
Yes ..........................................
No ...........................................
Yes ..........................................
No ...........................................
§ 63.1(c)(2)(ii)–(iii) ....
§ 63.1(c)(3) ...............
§ 63.1(c)(4) ...............
§ 63.1(c)(5) ...............
§ 63.1(d) ...................
§ 63.1(e) ...................
§ 63.2 ........................
§ 63.3 ........................
§ 63.4 ........................
§ 63.4(a)(1)–(3) .........
§ 63.4(a)(4) ...............
§ 63.4(a)(5) ...............
§ 63.4(b) ...................
§ 63.4(c) ....................
§ 63.5 ........................
§ 63.5(a)(1) ...............
§ 63.5(a)(2) ...............
§ 63.5(b)(1) ...............
§ 63.5(b)(2) ...............
§ 63.5(b)(3) ...............
§ 63.5(b)(4) ...............
§ 63.5(b)(5) ...............
§ 63.5(b)(6) ...............
§ 63.5(c) ....................
§ 63.5(d)(1) ...............
§ 63.5(d)(2) ...............
No ...........................................
Yes ..........................................
Yes ..........................................
No ...........................................
Yes ..........................................
Yes ..........................................
Yes ..........................................
Yes ..........................................
.................................................
Yes ..........................................
Yes ..........................................
Yes ..........................................
Yes ..........................................
Yes ..........................................
.................................................
Yes ..........................................
Yes ..........................................
Yes ..........................................
Yes ..........................................
Yes ..........................................
Yes ..........................................
Yes ..........................................
Yes ..........................................
Yes ..........................................
Yes ..........................................
Yes ..........................................
§ 63.5(d)(3) ...............
§ 63.5(d)(4) ...............
§ 63.5(e) ...................
§ 63.5(f)(1) ................
§ 63.5(f)(2) ................
§ 63.6 ........................
§ 63.6(a) ...................
§ 63.6(b) ...................
§ 63.6(c) ....................
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General provisions
reference
Yes ..........................................
Yes ..........................................
Yes ..........................................
Yes ..........................................
Yes ..........................................
.................................................
Yes ..........................................
Yes ..........................................
Yes ..........................................
§ 63.6(d) ...................
§ 63.6(e) ...................
§ 63.6(e)(1)(i) ............
§ 63.6(e)(1)(ii) ...........
§ 63.6(e)(3) ...............
§ 63.6(f) ....................
§ 63.6(f)(1) ................
§ 63.6(g) ...................
§ 63.6(h) ...................
§ 63.6(i) .....................
§ 63.6(j) .....................
§ 63.7 ........................
§ 63.7(a) ...................
§ 63.7(b) ...................
§ 63.7(c) ....................
§ 63.7(d) ...................
Yes ..........................................
Yes, except as noted below ...
No ...........................................
No ...........................................
No ...........................................
Yes, except as noted below ...
No ...........................................
Yes ..........................................
No ...........................................
Yes ..........................................
Yes ..........................................
.................................................
Yes ..........................................
Yes ..........................................
Yes ..........................................
Yes ..........................................
§ 63.7(e) ...................
§ 63.7(e)(1) ...............
Yes, except as noted below ...
No ...........................................
Not repetitive. Doesn’t apply to section 112(r).
Section reserved.
Contacts and authorities.
Section reserved.
Time period definition.
Postmark explanation.
Time period changes. Regulation conflict. Force and effect of subpart A.
Initial applicability determination of subpart A.
Section reserved.
Subpart VVV specifies recordkeeping of records of applicability determination.
Requires compliance with both subparts A and subpart VVV.
State options regarding title V permit. Unless required by the State, area sources subject to subpart VVV are exempted from permitting requirements.
State options regarding title V permit.
Section reserved.
Extension of compliance.
Subpart VVV addresses area sources becoming major due to increase in emissions.
Section reserved.
Title V permit before a relevant standard is established.
Definitions.
Units and abbreviations.
Prohibited activities and circumvention.
Prohibits operation in violation of subpart A.
Section reserved.
Compliance dates.
Circumvention.
Severability.
Preconstruction review and notification requirements.
Construction and reconstruction.
New source—effective dates.
New sources subject to relevant standards.
Section reserved.
No new major sources without Administrator approval.
New major source notification.
New major sources must comply.
New equipment added considered part of major source.
Section reserved.
Implementation of section 112(I)(2)—application of approval of new source construction.
Application for approval of construction for new sources listing and describing planned
air pollution control system.
Application for reconstruction.
Administrator may request additional information.
Approval of reconstruction.
Approval based on State review.
Application deadline.
Compliance with standards and maintenance requirements.
Applicability of compliance with standards and maintenance requirements.
Compliance dates for new and reconstructed sources.
Compliance dates for existing sources apply to existing Group 1 POTW treatment
plants.
Section reserved.
Operation and maintenance requirements apply to new sources.
General duty; See § 63.1583(d) and § 63.1586(d) for general duty requirements.
Requirement to correct malfunctions.
SSM plans are not required for POTW.
Compliance with non-opacity emission standards applies to new sources.
The POTW standards apply at all times.
Use of alternative non-opacity emission standards applies to new sources.
POTW treatment plants do not typically have visible emissions.
Extension of compliance with emission standards applies to new sources.
Presidential exemption from compliance with emission standards.
Performance testing requirements.
Performance testing is required for new sources.
New sources must notify the Administrator of intention to conduct performance testing.
New sources must comply with quality assurance program requirements.
New sources must provide performance testing facilities at the request of the Administrator.
Requirements for conducting performance tests apply to new sources.
The performance testing provisions of § 63.694 for control devices are incorporated by
reference into subpart DD of this part.
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TABLE 1 TO SUBPART VVV OF PART 63—APPLICABILITY OF 40 CFR PART 63 GENERAL PROVISIONS TO SUBPART VVV—
Continued
Applicable to subpart VVV
Explanation
§ 63.7(f) ....................
§ 63.7(g) ...................
Yes ..........................................
Yes ..........................................
§ 63.7(h) ...................
§ 63.8 ........................
§ 63.8(a) ...................
§ 63.8(b) ...................
§ 63.8(c) ....................
§ 63.8(c)(1)(i) ............
Yes ..........................................
.................................................
Yes ..........................................
Yes ..........................................
Yes, except as noted below ...
No ...........................................
§ 63.8(c)(1)(iii) ..........
§ 63.8(d) ...................
§ 63.8(d)(3) ...............
No ...........................................
Yes, except as noted below ...
No ...........................................
§ 63.8(e) ...................
§ 63.8(f) ....................
§ 63.8(g) ...................
§ 63.9 ........................
§ 63.9(a) ...................
§ 63.9(b) ...................
Yes ..........................................
Yes ..........................................
Yes ..........................................
.................................................
Yes ..........................................
Yes, except as noted below ...
§ 63.9(c) ....................
§ 63.9(d) ...................
Yes ..........................................
Yes ..........................................
§ 63.9(e) ...................
§ 63.9(f) ....................
§ 63.9(g) ...................
Yes ..........................................
No ...........................................
Yes ..........................................
§ 63.9(h) ...................
Yes, except as noted ..............
§ 63.9(i) .....................
Yes ..........................................
§ 63.9(j) .....................
§ 63.10 ......................
§ 63.10(a) .................
§ 63.10(b)(1)–(2) .......
§ 63.10(b)(2)(i) ..........
§ 63.10(b)(2)(ii) .........
§ 63.10(b)(2)(iii) ........
§ 63.10(b)(2)(iv) ........
§ 63.10(b)(2)(v) .........
§ 63.10(b)(2)(vi) ........
§ 63.10(b)(2)(vii)–(ix)
§ 63.10(b)(3) .............
§ 63.10(c) ..................
§ 63.10(c)(7) .............
Yes ..........................................
.................................................
Yes ..........................................
Yes, except as noted below ...
No ...........................................
No ...........................................
Yes ..........................................
No ...........................................
No ...........................................
Yes ..........................................
Yes ..........................................
No ...........................................
Yes, except as noted below ...
No ...........................................
§ 63.10(c)(8) .............
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No ...........................................
§ 63.10(c)(15) ...........
§ 63.10(d) .................
§ 63.10(d)(5) .............
§ 63.10(e) .................
§ 63.10(f) ..................
No ...........................................
Yes, except as noted below ...
No ...........................................
Yes ..........................................
Yes, except as noted ..............
§ 63.11 ......................
§ 63.11(a) and (b) .....
Yes ..........................................
Yes ..........................................
§ 63.11(c), (d) and
(e).
Yes ..........................................
New sources may use an alternative test method.
Requirements for data analysis, recordkeeping, and reporting associated with performance testing apply to new sources.
New sources may request a waiver of performance tests.
Monitoring requirements.
Applicability of monitoring requirements.
Monitoring shall be conducted by new sources.
New sources shall operate and maintain continuous monitoring systems (CMS).
See § 63.1583(d) for general duty requirement with respect to minimizing emissions and
continuous monitoring requirements.
See the applicable CMS quality control requirements under § 63.8(c) and (d).
New sources must develop and implement a CMS quality control program.
The owner or operator must keep these written procedures on record for the life of the
affected source or until the affected source is no longer subject to the provisions of
this part, and make them available for inspection, upon request, by the Administrator.
If the performance evaluation plan is revised, the owner or operator must keep previous (i.e., superseded) versions of the performance evaluation plan on record to be
made available for inspection, upon request, by the Administrator, for a period of 5
years after each revision of the plan. The program of corrective action should be included in the plan required under § 63.8(d)(2).
New sources may be required to conduct a performance evaluation of CMS.
New sources may use an alternative monitoring method.
Requirements for reduction of monitoring data.
Notification requirements.
Applicability of notification requirements.
Initial notification due February 23, 2000 or 60 days after becoming subject to this subpart.
Request for extension of compliance with subpart VVV.
Notification that source is subject to special compliance requirements as specified in
§ 63.6(b)(3) and (4).
Notification of performance test.
POTW treatment plants do not typically have visible emissions.
Additional notification requirements for sources with continuous emission monitoring
systems.
Notification of compliance status when the source becomes subject to subpart VVV.
See exceptions in § 63.1591(b).
Adjustments to time periods or postmark deadlines or submittal and review of required
communications.
Change of information already provided to the Administrator.
Recordkeeping and reporting requirements.
Applicability of notification and reporting requirements.
General recordkeeping requirements.
Recordkeeping for occurrence and duration of startup and shutdown.
Recordkeeping for failure to meet a standard, see § 63.696.
Maintenance records.
Actions taken to minimize emissions during SSM.
Action taken to minimize emissions during SSM.
Recordkeeping for CMS malfunctions.
Other CMS requirements.
Recording requirement for applicability determination.
Additional recordkeeping requirements for sources with continuous monitoring systems.
See § 63.696(h) for recordkeeping of (1) date, time, and duration; (2) listing of affected
source or equipment, and an estimate of the tons per year of each regulated pollutant
emitted over the standard; and (3) actions to minimize emissions and correct the failure.
See § 63.696(h) for recordkeeping of (1) date, time, and duration; (2) listing of affected
source or equipment, and an estimate of the tons per year of each regulated pollutant
emitted over the standard; and (3) actions to minimize emissions and correct the failure.
Use of SSM plan.
General reporting requirements.
See § 63.697(b) for malfunction reporting requirements.
Additional reporting requirements for sources with continuous monitoring systems.
Waiver of recordkeeping and reporting requirements. Electronic reporting to the EPA
cannot be waived.
Control device and equipment leak work practice requirements.
If a new source uses flares to comply with the requirements of subpart VVV, the requirements of § 63.11 apply.
Alternative work practice for equipment leaks.
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Federal Register / Vol. 82, No. 206 / Thursday, October 26, 2017 / Rules and Regulations
49533
TABLE 1 TO SUBPART VVV OF PART 63—APPLICABILITY OF 40 CFR PART 63 GENERAL PROVISIONS TO SUBPART VVV—
Continued
General provisions
reference
§ 63.12
§ 63.13
§ 63.14
§ 63.15
......................
......................
......................
......................
Applicable to subpart VVV
Yes
Yes
Yes
Yes
Explanation
..........................................
..........................................
..........................................
..........................................
State authority and designation.
Addresses of State air pollution control agencies and EPA Regional Offices.
Incorporation by reference.
Availability of information and confidentiality.
TABLE 2 TO SUBPART VVV OF PART 63—COMPLIANCE DATES AND REQUIREMENTS
If the construction/reconstruction
date is
Then the owner or operator must comply with
Group 1 POTW:
(1) After December 27, 2016 ..........
(2) After December 1, 1998 but on
or before December 27, 2016.
(3) On or before December 1, 1998
And the owner or operator must
achieve compliance
(i) New source requirements in §§ 63.1583(b); 63.1586(b) or (c); and
63.1588 through 63.1591.
(i) New source requirements in § 63.1583(b) but instead of complying
with both requirements (industrial user(s) NESHAP and the POTW
standards in §§ 63.1586(b) or (c)), you must comply with the most
stringent requirement1.
(ii) New source requirements in §§ 63.1586(b) or (c); and 63.1588
through 63.1591.
(i) Existing source requirements in §§ 63.1583(a) .................................
Upon initial startup.
(ii) Existing source requirements in §§ 63.1588 through 63.1591 .........
Group 2 POTW:
(4) After December 27, 2016 ..........
(5) After December 1, 1998 but on
or before December 27, 2016.
(6) On or before December 1, 1998
(i) New source requirements in §§ 63.1586(b) or (c); and 63.1588
through 63.1591.
(i) New source requirements in § 63.1586(b) or (c)1 .............................
(ii) New source requirements in §§ 63.1586(b) or (c); and 63.1588
through 63.1591.
(i) Existing source requirements in §§ 63.1586(a); and 63.1591(a) ......
Upon initial startup through October 26, 2020.
On or before October 26, 2020.
By the compliance date specified
in the other applicable NESHAP.
On or before October 26, 2018.
Upon initial startup.
Upon initial startup through October 26, 2020.
On or before October 26, 2020.
On or before October 26, 2018.
1 Note:
This represents the new source requirements in the original 1999 NESHAP, which are applicable until October 26, 2020. Between October 26, 2017 and October 26, 2020, you must transition to the new requirements in Table 2 (2)(ii) and (5)(ii) for Group 1 and Group 2 POTW,
respectively.
[FR Doc. 2017–23067 Filed 10–25–17; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 261
[EPA–R06–RCRA–2017–0153; SW–FRL–
9969–73–Region 6]
Hazardous Waste Management
System; Identification and Listing of
Hazardous Waste
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
The Environmental Protection
Agency (EPA) is granting a petition
submitted by ExxonMobil Oil
Corporation Beaumont Refinery
(ExxonMobil) to exclude from
hazardous waste control (or delist) a
certain solid waste. This final rule
responds to the petition submitted by
ExxonMobil to have the secondary
impoundment basin (SIB) solids
excluded, or delisted from the definition
of a hazardous waste. The SIB solids are
ethrower on DSK3G9T082PROD with RULES
SUMMARY:
VerDate Sep<11>2014
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listed as F037 (primary oil/water/solids
separation sludge); and F038 (secondary
oil/water/solids separation sludge).
After careful analysis and evaluation
of comments submitted by the public,
the EPA has concluded that the
petitioned wastes are not hazardous
waste when disposed of in Subtitle D
landfills. This exclusion applies to the
surface impoundment solids generated
at ExxonMobil’s Beaumont, Texas
facility. Accordingly, this final rule
excludes the petitioned waste from the
requirements of hazardous waste
regulations under the Resource
Conservation and Recovery Act (RCRA)
when disposed of in Subtitle D landfills
but imposes testing conditions to ensure
that the future-generated wastes remain
qualified for delisting.
DATES: Effective October 26, 2017.
ADDRESSES: The EPA has established a
docket for this action under Docket ID
No. EPA–R06–RCRA–2017–0153. All
documents in the docket are listed on
the https://www.regulations.gov Web
site. Although listed in the index, some
information is not publicly available,
e.g., CBI or other information whose
disclosure is restricted by statute.
PO 00000
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Certain other material, such as
copyrighted material, is not placed on
the Internet and will be publicly
available only in hard copy form.
Publicly available docket materials are
available electronically through https://
www.regulations.gov.
FOR FURTHER INFORMATION CONTACT: For
technical information regarding the
ExxonMobil Beaumont Refinery
petition, contact Michelle Peace at 214–
665–7430 or by email at
peace.michelle@epa.gov.
SUPPLEMENTARY INFORMATION: The
information in this section is organized
as follows:
I. Overview Information
A. What action is EPA finalizing?
B. Why is EPA approving this delisting?
C. What are the limits of this exclusion?
D. How will Beaumont Refinery manage
the waste if it is delisted?
E. When is the final delisting exclusion
effective?
F. How does this final rule affect states?
II. Background
A. What is a ‘‘delisting’’?
B. What regulations allow facilities to
delist a waste?
C. What information must the generator
supply?
E:\FR\FM\26OCR1.SGM
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Agencies
[Federal Register Volume 82, Number 206 (Thursday, October 26, 2017)]
[Rules and Regulations]
[Pages 49513-49533]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2017-23067]
[[Page 49513]]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 63
[EPA-HQ-OAR-2016-0490; FRL-9969-95-OAR]
RIN 2060-AS85
National Emission Standards for Hazardous Air Pollutants:
Publicly Owned Treatment Works Residual Risk and Technology Review
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: This action finalizes the residual risk and technology review
(RTR) conducted for the Publicly Owned Treatment Works (POTW) source
category regulated under national emission standards for hazardous air
pollutants (NESHAP). In addition, we are taking final action addressing
revised names and definitions of the subcategories, revisions to the
applicability criteria, revised regulatory provisions pertaining to
emissions during periods of startup, shutdown, and malfunction (SSM),
initial notification requirements for existing Group 1 and Group 2
POTW, revisions to the requirements for new Group 1 POTW, requirements
for electronic reporting, and other miscellaneous edits and technical
corrections. While we do not anticipate any emission reductions as a
result of these revisions, the changes should provide clarity for
sources determining applicability and ensuring compliance.
DATES: This final rule is effective on October 26, 2017.
ADDRESSES: The Environmental Protection Agency (EPA) has established a
docket for this action under Docket ID No. EPA-HQ-OAR-2016-0490. All
documents in the docket are listed on the https://www.regulations.gov
Web site. Although listed in the index, some information is not
publicly available, e.g., confidential business information (CBI) or
other information whose disclosure is restricted by statute. Certain
other material, such as copyrighted material, is not placed on the
Internet and will be publicly available only in hard copy form.
Publicly available docket materials are available either electronically
through https://www.regulations.gov, or in hard copy at the EPA Docket
Center, EPA WJC West Building, Room Number 3334, 1301 Constitution Ave.
NW., Washington, DC. The Public Reading Room hours of operation are
8:30 a.m. to 4:30 p.m. Eastern Standard Time (EST), Monday through
Friday, excluding legal holidays. The telephone number for the Public
Reading Room is (202) 566-1744, and the telephone number for the EPA
Docket Center is (202) 566-1742.
FOR FURTHER INFORMATION CONTACT: For questions about this final action,
contact Katie Hanks, Sector Policies and Programs Division (E143-03),
Office of Air Quality Planning and Standards, U.S. Environmental
Protection Agency, Research Triangle Park, North Carolina, 27711;
telephone number: (919) 541-2159; fax number: (919) 541-0516; and email
address: [email protected]. For specific information regarding the
risk modeling methodology, contact Terri Hollingsworth, Health and
Environmental Impacts Division (C539-02), Office of Air Quality
Planning and Standards, U.S. Environmental Protection Agency, Research
Triangle Park, North Carolina 27711; telephone number: (919) 541-5623;
fax number: (919) 541-0840; and email address:
[email protected]. For information about the applicability of
the NESHAP to a particular entity, contact Sara Ayres, Office of
Enforcement and Compliance Assurance, U.S. Environmental Protection
Agency, 77 West Jackson Boulevard (E-19J), Chicago, Illinois 60604;
telephone number: (312) 353-6266; and email address:
[email protected].
SUPPLEMENTARY INFORMATION:
Preamble acronyms and abbreviations. We use multiple acronyms and
terms in this preamble. While this list may not be exhaustive, to ease
the reading of this preamble and for reference purposes, the EPA
defines the following terms and acronyms here:
CAA Clean Air Act
CBI confidential business information
CDX Central Data Exchange
CEDRI Compliance and Emissions Data Reporting Interface
ERT Electronic Reporting Tool
HAP hazardous air pollutants(s)
HQ hazard quotient
H2S hydrogen sulfide
ICR Information Collection Request
MACT maximum achievable control technology
MGD million gallons per day
MIR maximum individual risk
NESHAP national emission standards for hazardous air pollutants
NPDES National Pollutant Discharge Elimination System
NTTAA National Technology Transfer and Advancement Act
PB-HAP Hazardous air pollutants known to be persistent and bio-
accumulative in the environment
POTW Publicly Owned Treatment Works
RFA Regulatory Flexibility Act
RIN Regulatory Information Number
RTR Risk and Technology Review
SSM startup, shutdown and malfunction
TOSHI Target Organ Specific Hazard Index
UMRA Unfunded Mandates Reform Act
Background information. On December 27, 2016, the EPA proposed
revisions to the POTW NESHAP based on our RTR. In this action, we are
finalizing decisions and revisions for the rule. We summarize some of
the more significant comments we timely received regarding the proposed
rule and provide our responses in this preamble. A summary of all other
public comments on the proposal and the EPA's responses to those
comments is available in Response to Public Comments on the EPA's
Residual Risk and Technology Review for the Publicly Owned Treatment
Works Source Category in Docket ID No. EPA-HQ-OAR-2016-0490. A ``track
changes'' version of the regulatory language that incorporates the
changes in this action is available in the docket.
Organization of this document. The information in this preamble is
organized as follows:
I. General Information
A. Does this action apply to me?
B. Where can I get a copy of this document and other related
information?
C. Judicial Review and Administrative Reconsideration
II. Background
A. What is the statutory authority for this action?
B. What is the POTW source category and how does the NESHAP
regulate HAP emissions from the source category?
C. What changes did we propose for the POTW source category in
our December 27, 2016, RTR proposal?
III. What is included in this final rule?
A. What are the final rule amendments based on the risk review
for the POTW source category?
B. What are the final rule amendments based on the technology
review for the POTW source category?
C. What are the final rule amendments addressing emissions
during periods of startup, shutdown, and malfunction?
D. What other changes have been made to the NESHAP?
E. What are the effective and compliance dates of the standards?
F. What are the requirements for submission of performance test
data to the EPA?
IV. What is the rationale for our final decisions and amendments for
the POTW source category?
A. Residual Risk Review for the POTW Source Category
B. Technology Review for the POTW Source Category
C. Applicability Criteria
D. Emissions From Collection Systems
E. Pretreatment Requirements
[[Page 49514]]
F. HAP Fraction Emitted for Existing Group 1 and Group 2 Sources
G. New and Existing Group 1 POTW
V. Summary of Cost, Environmental, and Economic Impacts and
Additional Analyses Conducted
A. What are the affected facilities?
B. What are the air quality impacts?
C. What are the cost impacts?
D. What are the economic impacts?
E. What are the benefits?
F. What analysis of environmental justice did we conduct?
G. What analysis of children's environmental health did we
conduct?
VI. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory Planning and Review and
Executive Order 13563: Improving Regulation and Regulatory Review
B. Executive Order 13771: Reducing Regulations and Controlling
Regulatory Costs
C. Paperwork Reduction Act (PRA)
D. Regulatory Flexibility Act (RFA)
E. Unfunded Mandates Reform Act (UMRA)
F. Executive Order 13132: Federalism
G. Executive Order 13175: Consultation and Coordination With
Indian Tribal Governments
H. Executive Order 13045: Protection of Children From
Environmental Health Risks and Safety Risks
I. Executive Order 13211: Actions Concerning Regulations That
Significantly Affect Energy Supply, Distribution, or Use
J. National Technology Transfer and Advancement Act (NTTAA)
K. Executive Order 12898: Federal Actions To Address
Environmental Justice in Minority Populations and Low-Income
Populations
L. Congressional Review Act (CRA)
I. General Information
A. Does this action apply to me?
Regulated entities. Categories and entities potentially regulated
by this action are shown in Table 1 of this preamble.
Table 1--NESHAP and Industrial Source Categories Affected by This Final
Action
------------------------------------------------------------------------
NAICS
NESHAP and source category NESHAP \1\
code
------------------------------------------------------------------------
Sewage Treatment Facilities......... Subpart VVV.............. 221320
------------------------------------------------------------------------
\1\ North American Industry Classification System.
Table 1 of this preamble is not intended to be exhaustive, but
rather to provide a guide for readers regarding entities likely to be
affected by the final action for the source category listed. The
standards are directly applicable to the affected sources. Federal,
state, local, and tribal governments are affected as discussed below.
By definition, a POTW is owned by a municipality, state, intermunicipal
or interstate agency, or any department, agency, or instrumentality of
the federal government (see 40 CFR 63.1595 of subpart VVV). To
determine whether your facility is affected, you should examine the
applicability criteria in the POTW NESHAP. Specifically, if a POTW is a
Group 2 POTW \1\ that is a major source of hazardous air pollutant
(HAP) emissions or a Group 1 POTW regardless of the HAP emissions, and
the POTW meets the criteria for development and implementation of a
pretreatment program according to 40 CFR 403.8, then the POTW is
affected by these standards. If you have any questions regarding the
applicability of any aspect of this NESHAP, please contact the
appropriate person listed in the preceding FOR FURTHER INFORMATION
CONTACT section of this preamble.
---------------------------------------------------------------------------
\1\ As discussed below in section III.D of this preamble, the
terms ``Group 1 POTW'' and ``Group 2 POTW'' are replacing the
previous terms ``industrial POTW'' and ``nonindustrial POTW. The
``Group 1'' and ``Group 2'' subcategories are described in the
regulatory text at 40 CFR 63.1581.
---------------------------------------------------------------------------
B. Where can I get a copy of this document and other related
information?
In addition to being available in the docket, an electronic copy of
this final action will also be available on the Internet. Following
signature by the EPA Administrator, the EPA will post a copy of this
final action at https://www.epa.gov/stationary-sources-air-pollution/publicly-owned-treatment-works-potw-national-emission-standards.
Following publication in the Federal Register, the EPA will post the
Federal Register version and key technical documents at this same Web
site.
Additional information is available on the RTR Web site at https://www.epa.gov/ttn/atw/rrisk/rtrpg.html. This information includes an
overview of the RTR program, links to project Web sites for the RTR
source categories, and detailed emissions and other data we used as
inputs to the risk assessments.
C. Judicial Review and Administrative Reconsideration
Under Clean Air Act (CAA) section 307(b)(1), judicial review of
this final action is available only by filing a petition for review in
the United States Court of Appeals for the District of Columbia Circuit
by December 26, 2017. Under CAA section 307(b)(2), the requirements
established by this final rule may not be challenged separately in any
civil or criminal proceedings brought by the EPA to enforce the
requirements.
Section 307(d)(7)(B) of the CAA further provides that only an
objection to a rule or procedure which was raised with reasonable
specificity during the period for public comment (including any public
hearing) may be raised during judicial review. This section also
provides a mechanism for the EPA to reconsider the rule if the person
raising an objection can demonstrate to the Administrator that it was
impracticable to raise such objection within the period for public
comment or if the grounds for such objection arose after the period for
public comment (but within the time specified for judicial review) and
if such objection is of central relevance to the outcome of the rule.
Any person seeking to make such a demonstration should submit a
Petition for Reconsideration to the Office of the Administrator, U.S.
EPA, Room 3000, EPA WJC South Building, 1200 Pennsylvania Ave. NW.,
Washington, DC 20460, with a copy to both the person(s) listed in the
preceding FOR FURTHER INFORMATION CONTACT section, and the Associate
General Counsel for the Air and Radiation Law Office, Office of General
Counsel (Mail Code 2344A), U.S. EPA, 1200 Pennsylvania Ave. NW.,
Washington, DC 20460.
II. Background
A. What is the statutory authority for this action?
Section 112 of the CAA establishes a two-stage regulatory process
to address emissions of HAP from stationary sources. In the first
stage, we must identify categories of sources emitting one or more of
the HAP listed in CAA section 112(b) and then promulgate technology-
based NESHAP for those sources. ``Major sources'' are those that emit,
or have the potential to emit, any single HAP at a rate of 10 tons per
year (tpy) or more, or 25 tpy or more of any combination of HAP. For
major sources, these standards are commonly referred to as maximum
achievable control technology (MACT) standards and must reflect the
maximum degree of emission reductions of HAP achievable (after
considering cost, energy requirements, and non-air quality health and
environmental impacts). In developing MACT standards, CAA section
112(d)(2) directs the EPA to consider the application of measures,
processes, methods, systems, or techniques, including but not limited
to those that reduce the volume of or eliminate HAP emissions through
process changes, substitution of materials, or other modifications;
enclose systems or
[[Page 49515]]
processes to eliminate emissions; collect, capture, or treat HAP when
released from a process, stack, storage, or fugitive emissions point;
are design, equipment, work practice, or operational standards; or any
combination of the above.
For these MACT standards, the statute specifies certain minimum
stringency requirements, which are referred to as MACT floor
requirements, and which may not be based on cost considerations. See
CAA section 112(d)(3). For new sources, the MACT floor cannot be less
stringent than the emission control achieved in practice by the best-
controlled similar source. The MACT standards for existing sources can
be less stringent than floors for new sources, but they cannot be less
stringent than the average emission limitation achieved by the best-
performing 12 percent of existing sources in the category or
subcategory (or the best-performing five sources for categories or
subcategories with fewer than 30 sources). In developing MACT
standards, we must also consider control options that are more
stringent than the floor under CAA section 112(d)(2). We may establish
standards more stringent than the floor, based on the consideration of
the cost of achieving the emissions reductions, any non-air quality
health and environmental impacts, and energy requirements.
In the second stage of the regulatory process, the CAA requires the
EPA to undertake two different analyses, which we refer to as the
technology review and the residual risk review. Under the technology
review, we must review the technology-based standards and revise them
``as necessary (taking into account developments in practices,
processes, and control technologies)'' no less frequently than every 8
years, pursuant to CAA section 112(d)(6). Under the residual risk
review, we must evaluate the risk to public health remaining after
application of the technology-based standards and revise the standards,
if necessary, to provide an ample margin of safety to protect public
health or to prevent, taking into consideration costs, energy, safety,
and other relevant factors, an adverse environmental effect. The
residual risk review is required within 8 years after promulgation of
the technology-based standards, pursuant to CAA section 112(f). In
conducting the residual risk review, if the EPA determines that the
current standards provide an ample margin of safety to protect public
health, it is not necessary to revise the MACT standards pursuant to
CAA section 112(f).\2\ For more information on the statutory authority
for this rule, see the proposed rule published on December 27, 2016 (81
FR 95352).
---------------------------------------------------------------------------
\2\ The U.S. Court of Appeals for the District of Columbia
Circuit has affirmed this approach of implementing CAA section
112(f)(2)(A): NRDC v. EPA, 529 F.3d 1077, 1083 (D.C. Cir. 2008)
(``If EPA determines that the existing technology-based standards
provide an `ample margin of safety,' then the Agency is free to
readopt those standards during the residual risk rulemaking.'').
---------------------------------------------------------------------------
B. What is the POTW source category and how does the NESHAP regulate
HAP emissions from the source category?
1. Definition of the POTW Source Category and the Affected Source
The EPA promulgated the NESHAP for the POTW source category
(henceforth referred to as the ``POTW NESHAP'') on October 26, 1999 (64
FR 57572). The standards are codified at 40 CFR part 63, subpart VVV.
The POTW NESHAP was amended on October 21, 2002 (67 FR 64742). As
amended in 2002, the POTW source category consists of new and existing
POTW treatment plants that are located at a POTW that is a major source
of HAP emissions and that meets the criteria for development and
implementation of a pretreatment program as defined by 40 CFR 403.8
under the Clean Water Act (CWA). Additional information about the
National Pretreatment Program can be found in the December 27, 2016,
RTR proposal (81 FR 95374). The source category covered by this MACT
standard currently includes thirteen facilities.
As used in this regulation, the term POTW refers to both any POTW
that is owned by a state, municipality, or intermunicipal or interstate
agency and, therefore, eligible to receive grant assistance under the
Subchapter II of the CWA, and any federally owned treatment works as
that term is described in section 3023 of the Solid Waste Disposal Act.
For more information see the December 27, 2016, RTR proposal (81 FR
95352). The source category includes any intercepting sewers, outfall
sewers, sewage collection systems, pumping, power, and other equipment.
The wastewater treated by these facilities is generated by industrial,
commercial, and domestic sources.
2. Applicability of the 2002 POTW NESHAP
The 2002 POTW NESHAP is subcategorized based on whether the POTW is
providing treatment for wastewaters received from an industrial user as
the means by which that industrial user complies with another NESHAP.
The 2002 POTW NESHAP defined an ``industrial POTW'' as ``a POTW that
accepts a waste stream regulated by another NESHAP and provides
treatment and controls as an agent for the industrial discharger. The
industrial discharger complies with its NESHAP by using the treatment
and controls located at the POTW. For example, an industry discharges
its benzene-containing waste stream to the POTW for treatment to comply
with 40 CFR part 61, subpart FF--National Emission Standards for
Benzene Waste Operations. This definition does not include POTW
treating waste streams not specifically regulated under another
NESHAP.'' An ``industrial POTW'' is subject to the 2002 POTW NESHAP
regardless of the HAP emissions (i.e., the POTW does not have to be a
major source). In contrast, a ``non-industrial POTW'' was defined in
the 2002 POTW NESHAP as ``a POTW that does not meet the definition of
an industrial POTW as defined above.'' A ``non-industrial POTW'' must
be a major source to be subject to the 2002 POTW NESHAP. For more
information, see the December 27, 2016, RTR proposal (81 FR 95357).
3. HAP Emitted and HAP Emission Points
The amount and type of HAP emitted from a POTW is dependent on the
composition of the wastewater streams discharged to a POTW by
industrial users. The primary HAP emitted from the POTW that were
identified as subject to the POTW NESHAP include acetaldehyde,
acetonitrile, chloroform, ethylene glycol, formaldehyde, methanol,
methylene chloride, tetratchloroethylene, toluene, and xylenes. The HAP
present in the wastewater entering a POTW can biodegrade, adhere to
sewage sludge, volatilize to the air, or pass through (remain in the
wastewater discharge) to receiving waters. Emissions can occur at any
point at the POTW, including collection systems and wastewater
treatment units located at the POTW treatment plant.
4. Regulation of HAP Emissions in the 2002 POTW NESHAP
The POTW NESHAP specifies requirements for the industial and non-
industrial POTW subcategories. Under the 2002 POTW NESHAP, an existing
``industrial POTW'' must meet the requirements of the industrial user's
NESHAP. A new or reconstructed ``industrial POTW'' must meet the
requirements of the industrial user's
[[Page 49516]]
NESHAP or the requirements for new or reconstructed non-industrial
POTW, whichever is more stringent.
There are no control requirements in the 2002 POTW NESHAP for
existing ``non-industrial POTW.'' However, new or reconstructed ``non-
industrial POTW'' must equip each treatment unit up to, but not
including, the secondary influent pumping station, with a cover. In
addition, all covered units, except the primary clarifier, must route
the air in the headspace above the surface of the wastewater to a
control device that meets the requirements for closed-vent systems and
control devices found in the NESHAP from Off-Site Waste and Recovery
Operations (40 CFR part 63, subpart DD). As an alternative, a new or
reconstructed ``non-industrial POTW'' can demonstrate that all units up
to, but not including, the secondary influent pumping station emit a
HAP fraction of 0.014 or less. The HAP fraction emitted is the fraction
of HAP in the wastewater entering the POTW that is emitted to the
atmosphere. For additional information, see the December 27, 2016, RTR
proposal (81 FR 95357).
C. What changes did we propose for the POTW source category in our
December 27, 2016, RTR proposal?
On December 27, 2016, the EPA published a proposed rule in the
Federal Register for the POTW NESHAP, 40 CFR part 63, subpart VVV, that
took into consideration the RTR analyses. In the proposed rule, we
proposed that the risks are acceptable and the current standards
provide an ample margin of safety to protect public health.
Additionally, we did not identify any developments in practices,
processes, and control technologies for the POTW source category as
part of the technology review. During this rulemaking, we evaluated
other revisions to the 2002 POTW NESHAP outside of the RTR. We proposed
to revise the names and definitions of the industrial and non-
industrial subcategories to be called Group 1 and Group 2 POTW. We also
proposed to include requirements to limit emissions from collection
systems and the POTW treatment plant; requirements for existing, new,
or reconstructed Group 1 POTW to comply with both the requirements in
the POTW NESHAP and those in the applicable NESHAP for which the POTW
acts as a control agent; and HAP emission limits for existing Group 2
POTW. In addition, we proposed to clarify the applicability criteria;
require initial notification for existing Group 1 and Group 2 POTW;
revise regulatory provisions pertaining to emissions during periods of
SSM; add requirements for electronic reporting; and make other
miscellaneous edits and technical corrections.
III. What is included in this final rule?
This action finalizes the EPA's determinations pursuant to the RTR
provisions of CAA section 112 for the POTW source category. This action
also finalizes other changes to the NESHAP, including revised names and
definitions of the subcategories, clarified applicability criteria,
revised regulatory provisions pertaining to emissions during periods or
SSM, initial notification requirements for existing Group 1 and Group 2
POTW, requirements for new or reconstructed Group 1 POTW to comply with
both the requirements in the POTW NESHAP and those in the applicable
NESHAP for which the POTW acts as a control agent, requirements for
electronic reporting, and other miscellaneous edits and technical
corrections. As explained in section IV of this preamble, we are not
taking final action at this time on several provisions that were
proposed, including standards for pretreatment, the inclusion of
collection systems in the major source determination, and the HAP
fraction emission limit for existing Group 1 and Group 2 POTW.
A. What are the final rule amendments based on the risk review for the
POTW source category?
We determined that risks resulting from emissions from the POTW
source category are acceptable. Specifically, the maximum individual
cancer risk (MIR) is 2-in-1 million based on allowable emissions and 1-
in-1 million based on actual emissions, well below the presumptive
limit of acceptability (100-in-1 million), and other health information
indicates there is no appreciable risk of adverse chronic or acute non-
cancer health effects due to HAP emissions from the source category.
Additionally, emissions of 2-methylnaphthalene, the only HAP emitted
from the POTW source category that is known to be persistent and bio-
accumulative in the environment (PB-HAP), did not exceed the worst-case
Tier I screening emission rate or any ecological benchmarks. Therefore,
revisions to the standards are not necessary to reduce risk to an
acceptable level or to prevent an adverse environmental effect.
Further, considering risk and non-risk factors, we determined that the
2002 POTW NESHAP requirements provide an ample margin of safety to
protect public health. Therefore, we are not finalizing revisions to
the standards under CAA section 112(f)(2).
B. What are the final rule amendments based on the technology review
for the POTW source category?
We determined that there are no developments in practices,
processes, and control technologies that warrant revisions to the MACT
standards for this source category. Therefore, we are not finalizing
revisions to the MACT standards under CAA section 112(d)(6).
C. What are the final rule amendments addressing emissions during
periods of startup, shutdown, and malfunction?
Consistent with Sierra Club v. EPA, 552 F.3d 1019 (D.C. Cir. 2008),
the EPA has established standards in this rule that apply at all times.
We have revised Table 1 to Subpart VVV of Part 63 (the General
Provisions applicability table) in several respects to eliminate the
incorporation of those General Provisions that stated or were tied to
the SSM exemption. These revisions to Table 1 are explained in detail
in the proposed rule preamble at 81 FR 95780-95782. Further, in
conjunction with the elimination of the incorporation of these General
Provisions requirements, we have (1) added a general duty to minimize
emissions in 40 CFR 63.1582(e) and 63.1586(e), see 81 FR at 95380 (col.
2-3); (2) incorporated performance testing requirements for control
devices in 40 CFR 63.694, see 81 FR at 95781 (col. 1); (3) added
language to Table 1 related to monitoring that is identical to 40 CFR
63.8(d)(3) (which is no longer incorporated) but with certain revisions
to reflect the ending of the SSM plan requirement, see 81 FR at 95381
(col. 2); (4) made the recordkeeping requirements in 40 CFR 63.696(h)
and 63.1589(d) applicable to periods that were previously covered by
SSM-related provisions, see 81 FR 95381 (col. 2-3); and (5) amended the
reporting requirements in 40 CFR 63.1590 which, in conjunction with the
existing reporting requirements in 40 CFR 63.693 and 63.1590(a), will
adequately provide for reporting that was previously governed by SSM-
related provisions, see 81 FR at 95382.
D. What other changes have been made to the NESHAP?
1. Applicability Criteria
The EPA is not revising the applicability of 40 CFR part 63,
subpart VVV as proposed on December 27, 2016. Instead, the EPA is
finalizing minor clarifying changes to the applicability criteria that
are in the 2002 POTW NESHAP. The renaming of the subcategories (from
``industrial'' to ``Group 1'' and from ``non-industrial'' to ``Group 2)
and the definitions of Group
[[Page 49517]]
1 and Group 2 POTW are being finalized as proposed, and as discussed
below. However, for clarification, the EPA has removed the statements
regarding ownership and operation of POTW in regards to which POTW are
required to develop and implement a pretreatment program as defined by
40 CFR 403.8. This change clarifies that any Group 1 POTW (regardless
of HAP emissions) or Group 2 POTW that is a major source of HAP is
subject to the POTW NESHAP if the POTW also meets the criteria for
development and implementation of a pretreatment program, regardless of
whether the POTW, state, or other entity implements the pretreatment
program.
2. Names and Definitions of the Subcategories
As proposed, the EPA is revising the names and definitions for the
subcategories identified in the POTW NESHAP. The EPA is renaming an
``industrial POTW treatment plant'' as a ``Group 1'' POTW treatment
plant and a ``non-industrial POTW treatment plant'' as a ``Group 2''
POTW treatment plant. The EPA expects that this clarification will
address any confusion that could have been caused by the previous
subcategory names ``industrial POTW treatment plant'' and ``non-
industrial treatment plant'' because POTW in both subcategories treat
wastewater from industrial users. The key difference between Group 1
and Group 2 is that a Group 1 POTW acts as an agent for an industrial
user by accepting and controling the industrial user's waste stream
regulated under another NESHAP. By contrast, a Group 2 POTW may treat
the waste stream from an industrial user, but does not act as the
industrial user's agent to comply with another NESHAP.
3. Initial Notification Requirements for Existing Group 1 and Group 2
POTW
In the final rule (40 CFR 63.1586(a)), existing Group 1 and Group 2
POTW treatment plants must comply with the initial notification
requirements in 40 CFR 63.1591(a) of subpart VVV. This notification
requirement was not required for these existing sources in the 2002
POTW NESHAP, but was proposed in the December 27, 2016, proposal, and
is consistent with notification requirements that were applicable to
new or reconstructed Group 2 sources under the 2002 POTW NESHAP.
4. Requirements for New Group 1 POTW
The EPA is finalizing, as proposed, the requirement that new Group
1 POTW comply with both the requirements of the other NESHAP for which
they act as an agent of control for an industrial user and the
requirements for new Group 2 POTW in this final rule. The requirements
for new Group 2 POTW are unchanged from the 2002 POTW NESHAP and
provide the option of complying with either (a) cover all primary
treatment units and route emissions through a closed vent system to a
control device or (b) meet a HAP fraction emission limit of 0.014 for
emissions from all primary treatment units.
5. Requirements for Electronic Reporting
The EPA is finalizing electronic reporting requirements for new
POTW consistent with the proposed rule. Specifically, new POTW must
electroncally submit all annual reports and certain performance test
reports. The EPA believes that the electronic submittal of these
reports will increase the usefulness of data contained in those
reports, is in keeping with current trends in data availability, will
further assist in the protection of public health and the environment,
and will ultimately result in less burden on the regulated community.
6. Other Miscellaneous Edits and Technical Corrections
The EPA is finalizing the following technical corrections as
proposed:
Revising all references to ``new or reconstructed POTW''
to refer to ``new POTW'' because the definition of ``new'' includes
reconstructed POTW.
Combining text from 40 CFR 63.1581 and 63.1582 because the
language was redundant and confusing. This includes revising 40 CFR
63.1581 to include all combined text and revising 40 CFR 63.1583(c) to
include the text from the current 40 CR 63.1582(c).
Revising 40 CFR 63.1586(b)(1) to require covers ``designed
and operated to prevent exposure of the wastewater to the atmosphere''
instead of ``designed and operated to minimize exposure of the
wastewater to the atmosphere.'' This clarification has also been made
to the definition of ``cover'' in 40 CFR 63.1595.
Revising 40 CFR 63.1587 to include compliance requirements
that are currently found in 40 CFR 64.1584 and 63.1587, and deleting 40
CFR 63.1584.
Clarifying the method for calculating the HAP fraction
emitted and moving the detailed instructions for calculating the HAP
fraction emitted from 40 CFR 63.1588(c)(4) to 40 CFR 63.1588(c)(3). The
requirements remaining in 40 CFR 63.1588(c)(4) address monitoring for
continuous compliance.
Revising 40 CFR 63.1588(a)(3) to clarify that a cover
defect must be repaired within 45 ``calendar'' days; currently the
paragraph says ``45 days.''
Adding definitions of existing source/POTW and new source/
POTW to 40 CFR 63.1595 to clarify the date that determines whether a
POTW is existing or new.
Renaming the title of 40 CFR 63.1588 to ``How do Group 1
and Group 2 POTW treatment plants demonstrate compliance?'' from ``What
inspections must I conduct?'' The new title better reflects the
contents of this section.
Removing the details on how to calculate the HAP fraction
emitted from the definition of HAP fraction emitted. The procedure for
how to calculate the HAP fraction emitted is provided within the text
of the rule. Having a summarized version of this procedure in the
definition could cause confusion.
Revising two references to dates to insert the actual
dates. The phrase ``six months after October 26, 1999'' was replaced
with ``April 26, 2000''; and the phrase ``60 days after October 26,
1999'' was replaced with ``December 27, 1999.'' These changes do not
result in a change in the date, but only clarify the specific dates
being referenced.
Clarifying that the reports required in 40 CFR
63.1589(b)(1) include the records associated with the HAP loading and
not just the records associated with the HAP emissions determination.
Removing the definition of ``Reconstruction'' in 40 CFR
63.1595 as ``Reconstruction'' is already defined in the General
Provisions of 40 CFR 63.2.
E. What are the effective and compliance dates of the standards?
The revisions to the MACT standards being promulgated in this
action are effective on October 26, 2017.
The compliance date for existing Group 1 POTW is found in the
applicable NESHAP for which the industrial user is subject to
wastewater requirements. The compliance date for existing Group 2 POTW
constructed or reconstructed on or before December 1, 1998, remains
April 26, 2000. While we do not expect any additional existing Group 1
or Group 2 POTW beyond the 13 identified, we have chosen to include an
additional compliance date of October 26, 2018 for existing Group 1 and
Group 2 sources to submit their initial notification. We understand
from public comments that POTW are evaluating their potential emissions
and additional POTW may find they are subject to the rule. These POTW
are only required to submit a notification that they are subject to the
rule, and the additional time given for compliance of
[[Page 49518]]
this notification submittal will provide time for completion of the
necessary emission calculations. The 13 existing sources that are
subject to the rule and were previously identified have already met
this notification requirement and do not need to resubmit a
notification. New sources constructed or reconstructed after December
27, 2016, must comply with all of the standards immediately upon the
effective date of the standard, October 26, 2017, or upon startup,
whichever is later. While we did not identify any new sources that are
subject to the rule since the original rule was published in 1999, we
are including a transition period until October 26, 2020 for any new
sources constructed or reconstructed between December 1, 1998, and
December 27, 2016, to comply with the revisions in this rule.
F. What are the requirements for submission of annual reports and
performance test data to the EPA?
As we proposed, the EPA is finalizing the requirement for owners
and operators of POTW to submit electronic copies of certain required
performance test reports and annual reports through the EPA's Central
Data Exchange (CDX) using the Compliance and Emissions Data Reporting
Interface (CEDRI). The electronic submittal of the reports addressed in
this rulemaking will increase the usefulness of the data contained in
those reports, is in keeping with current trends in data availability
and transparency, will further assist in the protection of public
health and the environment, will improve compliance by facilitating the
ability of regulated facilities to demonstrate compliance with
requirements and by facilitating the ability of delegated state, local,
tribal, and territorial air agencies and the EPA to assess and
determine compliance, and will ultimately reduce burden on regulated
facilities, delegated air agencies, and the EPA. Electronic reporting
also eliminates paper-based, manual processes, thereby saving time and
resources, simplifying data entry, eliminating redundancies, minimizing
data reporting errors, and providing data quickly and accurately to the
affected facilities, air agencies, the EPA, and the public.
The EPA Web site that stores the submitted electronic data,
WebFIRE, is easily accessible and provides a user-friendly interface.
By making records, data, and reports addressed in this rulemaking
readily available, the EPA, the regulated community, and the public
will benefit when the EPA conducts its CAA-required technology reviews.
As a result of having reports readily accessible, our ability to carry
out comprehensive reviews will increase and be achieved within a
shorter period of time.
We anticipate fewer or less substantial Information Collection
Requests (ICRs) in conjunction with prospective CAA-required technology
reviews may be needed, which results in a decrease in time spent by
industry to respond to data collection requests. We also expect the
ICRs to contain less extensive stack testing provisions, as we will
already have stack test data electronically. Reduced testing
requirements would be a cost savings to industry. The EPA should also
be able to conduct these required reviews more quickly. While the
regulated community may benefit from a reduced burden of ICRs, the
general public benefits from the agency's ability to provide these
required reviews more quickly, resulting in increased public health and
environmental protection.
Air agencies, as well as the EPA, can benefit from more streamlined
and automated review of the electronically submitted data.
Standardizing report formats allows air agencies to review reports and
data more quickly. Having reports and associated data in electronic
format facilitates review through the use of software ``search''
options, as well as the downloading and analyzing of data in
spreadsheet format. Additionally, air agencies and the EPA can access
reports wherever and whenever they want or need, as long as they have
access to the Internet. The ability to access and review reports
electronically assists air agencies in determining compliance with
applicable regulations more quickly and accurately, potentially
allowing a faster response to violations, which could minimize harmful
air emissions. This benefits both air agencies and the general public.
For a more thorough discussion of electronic reporting required by
this rule, see the discussion in the preamble of the proposal. In
summary, in addition to supporting regulation development, control
strategy development, and other air pollution control activities,
having an electronic database populated with performance test data will
save industry, air agencies, and the EPA significant time, money, and
effort while improving the quality of emission inventories and air
quality regulations and enhancing the public's access to this important
information.
IV. What is the rationale for our final decisions and amendments for
the POTW source category?
For each decision or amendment, this section provides a description
of what we proposed and what we are finalizing, the EPA's rationale for
the final decisions and amendments, and a summary of key comments and
responses. Comments not discussed in this preamble, comment summaries,
and the EPA's responses can be found in the comment summary and
response document available in the docket (Docket ID No. EPA-HQ-OAR-
2016-0490).
A. Residual Risk Review for the POTW Source Category
Pursuant to CAA section 112(f), we conducted a residual risk review
and presented the results of the review, along with our proposed
decisions regarding risk acceptability and ample margin of safety, in
the December 27, 2016, RTR proposal (81 FR 95372). The residual risk
review for the POTW source category included assessment of cancer risk,
chronic non-cancer risk, and acute non-cancer risk due to inhalation
exposure, as well as multipathway exposure risk and environmental risk.
The results of the risk assessment are presented briefly in this
preamble and in more detail in the residual risk document, Residual
Risk Assessment for Publicly Owned Treatment Works Source Category in
Support of the October 2017 Risk and Technology Review Final Rule,\3\
which is available in the docket for this rulemaking.
---------------------------------------------------------------------------
\3\ This report is an update to the residual risk report
provided at proposal, Residual Risk Assessment for Publicly Owned
Treatment Works Source Category in Support of the December 2016 Risk
and Technology Review Proposed Rule, available in the docket.
---------------------------------------------------------------------------
The results indicated that maximum inhalation cancer risk to the
individual most exposed is 2-in-1 million based on allowable emissions
and 1-in-1 million based on actual emissions, which is well below the
presumptive limit of acceptability (i.e., 100-in-1 million). In
addition, the maximum chronic noncancer target organ specific hazard
index (TOSHI) due to inhalation exposures is less than 1. The
evaluation of acute noncancer risk, which was conservative, showed a
hazard quotient at or below 1 for all but one POTW. Based on the
results of the screening analyses for human multipathway exposure to,
and environmental impacts from, PB-HAP, we also concluded that the
cancer risk to the individual most exposed through ingestion is below
the level of concern and no ecological benchmarks are exceeded. The
facility-wide cancer and noncancer risks were estimated based on the
actual emissions from all sources at the identified POTW (both MACT and
non-MACT sources). The results indicated the cancer risk to
[[Page 49519]]
the individual most exposed is no greater than 10-in-1 million and the
noncancer TOSHI is less than 1. Considering the above information, as
well as other relevant non-health factors under the Benzene NESHAP
analysis codified in CAA 112(f)(2)(B), we proposed that the risk is
acceptable and the requirements in the 2002 POTW NESHAP provide an
ample margin of safety to protect public health and prevent an adverse
environmental effect.
The risk assessment conducted for the POTW proposal estimated
cancer, chronic noncancer, and acute noncancer risk for six of the 13
facilities in the source category and is summarized and referenced
above. We confirmed the existence of seven additional POTW subject to
the rule that were identified through public comments. For these seven
POTW, we conducted a facility-wide risk assessment of potential cancer
and chronic noncancer health effects. The results of this assessment
indicate that all seven POTW have a facility-wide noncancer TOSHI less
than 1, four of the POTW have a facility-wide cancer risk estimated
less than 1-in-1 million, and three of the POTW have a facility-wide
cancer risk estimated at or above 10-in-1 million. The highest
facility-wide MIR was 60-in-1 million driven by formaldehyde from
internal combustion engines which are covered under the NESHAP for the
Stationary Reciprocating Internal Combustion Engines source category.
For this POTW with the highest facility-wide MIR, the facility-wide
emissions of formaldehyde are 22 tpy while the source category
emissions of formaldehyde are 0.0026 tpy, which indicates that almost
100 percent of the estimated cancer risk is from emissions sources that
are not part of the POTW source category. This ratio of source category
emissions relative to facility-wide emissions of formaldehyde is the
same for the other two POTW with facility-wide cancer risk estimated at
or above 10-in-1 million. Therefore, it is reasonable to conclude that
all 13 POTW have estimated cancer risk close to or below 1-in-1 million
from source category emissions and we retain our proposed determination
that risk is acceptable. Further, as discussed in the December 27,
2016, RTR proposal (81 FR 95373), we retain our determination that,
considering the costs, economic impacts and technological feasibility
of additional standards to reduce risk further, the 2002 POTW NESHAP
provides an ample margin of safety to protect public health and
prevents an adverse environmental effect. Details of this risk
assessment are described in the Residual Risk Assessment for the
Publicly Owned Treatment Works Source Category in Support of the
October 2017 Risk and Technology Review Final Rule found in the docket
for this rulemaking.
Most of the commenters on the proposed risk review supported our
risk acceptability and ample margin of safety determinations for the
POTW NESHAP. Some commenters requested that we make changes to our
residual risk review approach. However, we evaluated the comments and
determined that no changes to our risk assessment methods or
conclusions are warranted. A summary of these comments and responses
are in the comment summary and response document, available in the
docket for this action (Docket ID No. EPA-HQ-OAR-2016-0490).
Since proposal, our risk assessment has been broadened to include
additional POTW; however, the conclusions of our risk assessment and
our determinations regarding risk acceptability, ample margin of
safety, and adverse environmental effects have not changed. For the
reasons explained in the proposed rule and discussed above, we
determined that the risks from the POTW source category are acceptable,
and that the current standards provide an ample margin of safety to
protect public health and prevent an adverse environmental effect.
B. Technology Review for the POTW Source Category
As described in the December 27, 2016, RTR proposal (81 FR 95373),
and as provided by CAA section 112(d)(6), our technology review focused
on identifying developments in the practices, processes, and control
technologies for the POTW source category. We concluded that there are
two different control options that may be used at a POTW to reduce HAP
emissions: pretreatment programs and add-on controls (i.e., covers or
covers vented to a control device). While we proposed specific
revisions to the standards, none of those revisions were the result of
any identified developments in practices, processes, or control
technologies beyond the programs and controls already in use at the
time of the promulgation of the original 40 CFR part 63, subpart VVV
rulemaking.
Comment: We received various comments related to the information
evaluated for the proposal. Two commenters stated that there is no
technical basis that requires the EPA to revise the standards since
there have been no technology advances since 1998 that warrant a change
in the original MACT analysis. Several commenters provided additional
information on specific control technologies, including biofilters,
caustic scrubbers, and carbon absorbers. One of these commenters stated
that biofilters are not reliable control devices in the context of a
POTW because they are designed for stable operating conditions. In
contrast, another commenter provided information that biofilters might
have the ability to reduce HAP in addition to hydrogen sulfide
(H2S) and volatile organic compounds (VOC). Additional
comments on the technology review can be found in section 3 of the
response to comments document in the docket for this rule (EPA-HQ-OAR-
2016-0490).
Response: The EPA conducted a literature review and evaluated
available studies and publications on the use of add-on controls and
process modifications that are used to reduce emissions from POTW
wastewater collection and treatment operations. As noted by the
commenters, these technologies include biotrickling filters, the use of
covers and ducting of the headspace vent stream to caustic scrubbers
and carbon adsorbers, and biofiltration/biofilters. These types of
technologies have been used historically at POTW where they provide a
relatively high degree of H2S control for the purpose of
preventing odor. As documented in the technology review memorandum and
reflected in the comments received on the proposed rule, the efficacy
of these technologies to reduce HAP emissions is highly variable and
dependent on site-specific operating parameters. Our conclusion is that
the experience with biofilters for controlling organics at POTW is at
the experimental and pilot scale and that this technology has not been
demonstrated to be commercially available and effective for controlling
the range of HAP emitted by POTW. Thus, we do not consider this
technology to be a development in practices, processes, or control
technologies for purposes of this technology review. Scrubbers are
generally not used to control emissions of organic constituents, and
while carbon adsorbers may be effective at HAP control in certain
applications, as used in POTW, they are generally not designed for HAP
control. Nevertheless, 40 CFR part 63, subpart VVV allows flexibility
for POTW to develop site-specific control strategies to meet any
applicable requirements, and such strategies could include the use of
biologic filters and carbon adsorbers
[[Page 49520]]
that can achieve the required control levels.
As stated in section III.B of this preamble, we did not identify
any developments in practices, processes, or control technology with
respect to programs and controls already in use when the 2002 POTW
NESHAP was promulgated that warrant revisions to the standards as part
of the technology review of the POTW NESHAP.
C. Applicability Criteria
The 2002 POTW NESHAP established three criteria (40 CFR
63.1580(a)(1), (2), and (3)) for determining what POTW are subject to
the rule. Specifically, the following criteria must all be true: (1)
You own or operate a POTW that includes a POTW treatment plant; (2) the
POTW is a major source of HAP emissions, or an industrial POTW
regardless of the HAP emissions; and (3) the POTW is required to
develop and implement a pretreatment program as defined by 40 CFR
403.8. The EPA proposed to revise the applicability criteria in order
to clarify the original intent of the rule. Specifically, we proposed
to revise the first and second criteria in 40 CFR 63.1580(a)(1) and (2)
to state that your POTW is subject to the POTW NESHAP if ``(1) You own
or operate a POTW that is a major source of HAP emissions; or (2) you
own or operate a Group 1 POTW regardless of whether or not it is a
major source of HAP.'' As stated in the proposal, we proposed this
revision because we found several instances where a POTW might not
realize they are subject to the standards, or where the applicability
criteria could be misinterpreted to exclude facilities that are covered
by the rule. See 81 FR 95377.
The third applicability criterion in the 2002 POTW NESHAP states
that ``(3) Your POTW is required to develop and implement a
pretreatment program as defined by 40 CFR 403.8 (for a POTW owned or
operated by a municipality, state, or intermunicipal or interstate
agency), or your POTW would meet the general criteria for development
and implementation of a pretreatment program (for a POTW owned or
operated by a department, agency, or instrumentality of the Federal
government).'' We proposed revising the third criterion in 40 CFR
63.1580(a)(3) to state ``You are subject to this subpart if your POTW
has a design capacity to treat at least 5 million gallons of wastewater
per day (MGD) and treats wastewater from an industrial user, and either
paragraph (a)(1) or (a)(2) is true.'' This proposed revision removed
the requirement that a POTW must already have a pretreatment program in
place in order to be subject to the rule. The proposed revisions were
intended to clarify the intent of the rule, which was to limit
applicability to POTW that treat at least 5 MGD and wastewater from
industrial users.
Comment: We received numerous comments that raised specific
concerns related to these proposed changes. First, commenters disagreed
that the proposed changes were necessary and stated that the proposed
changes created confusion and changed the scope of affected sources.
One commenter stated that the applicability of 40 CFR part 63, subpart
VVV has been well-defined for over 17 years, and if sources are
confused, the EPA has methods to correct any confusion without making
rule changes.
Several commenters specifically objected to the proposed change
that removed pretreatment from the third applicability criterion and
made it a requirement of the rule. These commenters stated that
removing pretreatment as an applicability criterion and making it a
requirement changes the source category that the EPA intended to
control. One state commented that this proposed change would cause an
additional 12 POTW in their state to become subject to the rule. The
commenter explained that because the state (not the POTW) implements
the National Pollutant Discharge Elimination System (NPDES)
pretreatment program, the original rule does not apply to any POTW in
that state.
Response: As stated in the proposal, the EPA did not intend to
expand the applicability criteria from the 2002 POTW NESHAP. After
consideration of the comments received, we agree that implementing the
proposed changes to rule applicability could have caused confusion
among the regulated community without a demonstrable environmental
benefit. Therefore, at this time, we are not making any substantive
change to the 2002 POTW NESHAP third applicability criterion and are
not adopting the proposed applicability criterion of 5 MGD. However, it
is important to note that the requirements in the National Pretreatment
Program do establish a 5 MGD threshold for applicability.
In response to the apparent potential for misinterpretation of the
regulatory text that is reflected in the state's comment, we are making
one minor change to clarify our interpretation and the intent of 40 CFR
63.1580(a)(3). In developing the 2002 POTW NESHAP, we wrote the rule to
apply to POTW that receive a significant amount of HAP-containing waste
from industrial or commercial facilities. In developing the rule
language, we sought to define such POTW by using a regulatory criterion
that was already established and well understood in the industry. We
selected the criterion that the POTW be subject to a pretreatment
program under the NPDES program because this criterion would encompass
industrial and commercial wastes with HAP that pass through the POTW
untreated and that could present a safety or health concern to POTW
workers. In adopting this criterion, we did not limit applicability
based on the entity that administers the program. In other words, the
criterion encompasses every POTW that receives a waste stream that is
subject to pretreatment standards, regardless of whether the standards
are prescribed by the POTW itself or by a state or federal regulatory
body. Thus, to make sure that the regulatory text is properly read, we
have revised 40 CFR 63.1581(a)(3) to make clear that a POTW is subject
to this rule if either (1) the POTW is required to develop and
implement a pretreatment program as defined by 40 CFR 403.8, or (2) the
POTW meets the general criteria for development and implementation of a
pretreatment program, even if does not develop and implement the
pretreatment program itself. Specifically, we have removed the
parenthetical text in 40 CFR 63.1580(a)(3) that limited the first part
of the third criterion to POTW owned or operated by a municipality,
state, or intermunicipal or interstate agency and limited the second
part of the third criterion to POTW owned or operated by a department,
agency, or instrumentality of the federal government.
D. Emissions From Collection Systems
In the 2016 proposal, we stated that HAP emissions from collection
systems should be included when determining whether the POTW is a major
source, and therefore, subject to the rule. Specifically, we stated
that the 2002 applicability criteria in 40 CFR 63.1580(a)(2) provided
that emissions from the entire POTW source category must be considered
when determining whether the POTW is a major source of HAP emissions,
and not just the emissions from the POTW treatment plant (i.e., the
portion of the POTW designed to provide treatment of municipal sewage
or industrial waste).
Comment: Several commenters opposed including emissions from
collection systems in the determination of whether a POTW is a major
source. The commenters stated that collection systems/sewers may
include hundreds or thousands of miles of sewers and other equipment,
are not always under
[[Page 49521]]
the jurisdiction of the POTW, and are typically owned by another
entity.
We also received comments that stated the inclusion of emissions
from collection systems for major source determination is inconsistent
with the federal definition of a major source. One commenter stated
that expansion of the major source definition to include collection
sewers as part of the affected source is not authorized under section
112 of the CAA. The commenter also stated that the equipment that
collect and convey wastewater to a POTW treatment plant do not
reasonably constitute a ``building, structure, facility, or
installation'' as specified in the definition of a stationary source in
section 112(a)(3) of the CAA, are clearly not within a contiguous area
under common control, and should not be considered a single source.
Commenters noted that the determination of a major source of HAP
emissions should be limited to emission sources within the fence line
of each treatment plant, which would be consistent with the fact that
the emission fraction requirement of the proposed POTW NESHAP is
limited to emissions within the treatment plant. Further, one commenter
contended that excluding collection system emissions in POTW major
source determinations is also supported by Alabama Power Co. v. Costle
and EPA's response to that decision.
Commenters also noted that the emission data reviewed by the EPA in
developing the proposed rule represented the HAP emissions from the
POTW treatment plant only. One commenter noted that the risk assessment
did not include emissions from collection systems. Several commenters
disagreed with the EPA's statement in the preamble to the proposed rule
that collection systems may have significant HAP emissions. Some
commenters suggested that emissions from collection systems are
insignificant and in some cases collection systems are operated under a
vacuum to control odors. However, none of the commenters provided data
to demonstrate the level of HAP emissions from collection systems.
Response: Considering these comments, the EPA is not taking final
action at this time on any changes to the emission sources that must be
considered when determining if a POTW is a major source of HAP
emissions. Specifically, the EPA is not taking action on whether
emissions from collection systems should be included in the total HAP
emissions from a POTW. The determination of source boundaries is a
site-specific and often a complex determination. Facilities work with
their permitting authority to consider factors such as whether
activities and equipment are in a contiguous area and whether they are
under common control. In contemplating the comments, the EPA has
decided that we do not have enough information on individual POTW,
including information on the jurisdiction of the control of collection
system equipment or information on whether this equipment should be
considered contiguous with the POTW treatment plant. Also, data on HAP
emissions from collection systems are not well understood, and we are
not aware of accepted methods for measuring or calculating emissions
from collection systems at this time. In addition, we understand that
these source boundary determinations have already been made for the
approximately 16,000 POTW through Title V applicability assessment. For
these reasons, we are not taking final action at this time to change
these determinations. We may take action in the future if we obtain
additional information on source boundary issues (i.e., common control,
contiguous area), HAP emissions, and other information related to the
issues described above.
With respect to new sources, we expect new sources to consult their
permitting authorities on these matters as they plan for new
construction. The EPA considers these determinations on source
boundaries to be appropriately under the jurisdiction of the permitting
authority. Accordingly, to avoid regulatory disruption, this final rule
takes no action to change the definition of POTW. The definition of
POTW remains the same as originally promulgated and continues to
include ``. . . any intercepting sewers, outfall sewers, sewage
collection systems, pumping, power and other equipment.'' Likewise, we
are not taking final action at this time to revise the originally
promulgated definition of the affected source. The definition of
affected source continues to mean the ``group of all equipment that
comprise the POTW treatment plant.''
E. Pretreatment Requirements
As stated in section IV.C of this preamble, the EPA proposed
removing pretreatment from the applicability criteria and making it a
control requirement for new and existing sources. We proposed adding
pretreatment requirements in the rule because pretreatment would reduce
HAP emissions from the entire source category (i.e., collection systems
and the treatment plant) by limiting the quantity of HAP in the
wastewater before it is discharged to the collection system. The intent
of this requirement was to reduce the pollutant loading into the POTW
in order to reduce emissions throughout all stages of treatment.
Comment: Several commenters objected to the EPA requiring a
pretreatment program for HAP emissions. Commenters disagreed with the
EPA's contention that a pretreatment program will reduce emissions of
HAP by reducing the presence of toxic gases. Specifically, commenters
noted that a ``pretreatment program under CAA Section 112 is not the
same as a pretreatment program under the Clean Water Act (CWA)'', as 40
CFR 403 authorizes POTW to set pretreatment requirements for air
contaminants for worker and plant safety, and to prevent interference
and pass through. One commenter contended that the proposed rule
expands the CAA regulatory framework into the CWA National Pretreatment
Program without a legal basis.
Additionally, several commenters opposed requiring POTW to develop
local limits and expressed concerns about the way in which local limits
should be determined. Instead, commenters suggested that the EPA
establish wastewater concentration limits for HAP to identify
pollutants that may need local limits. One commenter stated that the
EPA should either ``regulate industrial users directly for HAP or
provide technically-based wastewater concentrations for HAP that POTW
could use for screening (where analytical methods exist under 40 CFR
part 136)'' to determine the need for establishing local limits.
Commenters also expressed concerns about the costs related to
requiring pretreatment programs wherein POTW evaluate and set local
limits for volatile organic HAP. The commenters stated that developing
local limits to identify pollutants of concern, as well as identify
potential pretreatment controls, would require significant time and
that the significant costs these requirements would impose on POTW have
not been quantified or justified. In contrast, one commenter stated
that categorical limits set by the EPA pursuant to the CWA for certain
industries could merit consideration, but additional analysis is
required.
Response: In response to these comments, we are not taking final
action at this time to require pretreatment as a control requirement
for the revised NESHAP. As explained in section IV.C of this preamble,
we are not changing the applicability criteria for 40 CFR part 63,
subpart VVV. The existence of a
[[Page 49522]]
pretreatment program under the CWA will continue to be one of the three
rule applicability criteria.
The EPA Office of Water is responsible for administering the
pretreatment program and updates the requirements of the pretreatment
program based on the best available technology and taking into account
cost effectiveness. As the pretreatment requirements are modified
through future updates, additional HAP reductions may occur. Because
all of the POTW that are subject to the rule already have pretreatment
programs, specifically requiring pretreatment under the NESHAP would
not reduce HAP emissions further, but could cause confusion and
increase compliance costs. Thus, we are not finalizing any revisions at
this time to impose additional pretreatment requirements prior to
discharging a wastewater stream to a receiving POTW. Pretreatment will
continue to be handled under the authority of the CWA. By retaining the
existing regulatory structure of the NESHAP, the EPA avoids redundancy
and confusion in having pretreatment requirements included in both air
and water permits.
F. HAP Fraction Emitted for Existing Group 1 and Group 2 Sources
In the 2016 proposal, we proposed that existing Group 1 and Group 2
POTW operate with an annual rolling average HAP fraction emitted from
primary treatment units of 0.08 or less. As stated in the proposal, we
believed that the existing POTW we knew about could meet this standard
without the need for additional control.
Comment: We received numerous comments that opposed the proposed
HAP fraction emission limit, and we received additional data to suggest
the proposed 0.08 HAP fraction limit was not appropriate and did not
accurately account for variability in HAP loading at individual POTW.
Several commenters objected that merely doubling the single largest
HAP fractions from the two available sources was not a scientifically
or statistically valid method for setting the emission limit and stated
that the EPA had provided no support for using the 2x factor to account
for variability of emissions. For example, the commenters collectively
pointed out that the two POTW on which the proposed standard was based
were operating at half capacity, that the available data represent
merely a snapshot in time, that other potentially regulated POTW might
emit higher HAP fractions, and that the specific combination of HAP
measured by the two POTW might not be representative of HAP emitted by
other POTW. One commenter suggested that due to the uncertainty
associated with such a small data set, the EPA should use a larger
multiplier for setting a standard.
Additionally, commenters stated that the EPA had underestimated the
cost of achieving compliance with the 0.08 HAP fraction emitted
standard. Specifically, commenters stated that in order to comply, they
would incur capital and operating costs, in addition to the
recordkeeping and reporting costs that the EPA accounted for in the
proposal. One commenter stated that they would potentially need to
install covers and controls in order to meet the HAP fraction emitted
limit, which would be an expense of $20 to $30 million with negligible
emission reductions. Two commenters argued that the compliance cost for
the proposed standard was not warranted given the low public health
risk that the EPA estimated. Commenters further recommended that the
EPA gather more complete data from the universe of affected sources,
conduct statistical analysis of those data, and determine a suitable
standard based on an acceptable level of risk and variability of the
data.
Response: After reviewing public comments and re-evaluating our
analysis, we are not taking final action to adopt the 0.08 HAP fraction
emitted limit for existing Group 1 and Group 2 POTW at this time. The
proposed HAP fraction emitted limit did not reflect the performance or
application of a specific control technology. At proposal, we
envisioned this limit as an enforceable numerical limit that would
ensure performance consistent with that being achieved by existing
sources. However, after consideration of the information provided in
public comment, we now recognize that we do not have the comprehensive
data on existing POTW that are necessary to conduct a sufficiently
robust analysis. The HAP fraction emitted by different POTW is
influenced by individual HAP vapor pressures, pollutant loadings, HAP
concentrations, sample measurement and analytical techniques, and
ambient conditions, which differ from POTW to POTW. Testing of influent
loadings is limited by applicable test methods, by compounds identified
by dischargers, and by the HAP for which air permits require sampling.
Without sufficient data, we cannot determine an appropriate HAP
fraction emitted limit, considering the variability in operating
conditions that is likely to occur across even well-operated POTW.
Moreover, at this time, we are unable to analyze the control costs for
all affected sources or the emissions reductions that might be
achieved. For all of these reasons, we are not taking final action on
the proposed 0.08 HAP fraction at this time, but we may in the future
consider promulgating a limit if we obtain further information on the
issues discussed above.
G. New and Existing Group 1 POTW
In addition to proposing a HAP fraction for existing Group 1 POTW,
we also proposed other changes to the requirements for Group 1 POTW.
The 2002 POTW NESHAP required existing Group 1 POTW to comply only
with the requirements of the other NESHAP for which they are acting as
an agent of control for the industrial user. We proposed that existing
Group 1 POTW must meet both the requirements of the other NESHAP for
which they are acting as an agent of control for an industrial user and
the proposed requirements for existing Group 2 POTW in the POTW NESHAP
(i.e., the proposed 0.08 HAP fraction emitted limit discussed in IV.F,
above).
The 2002 POTW NESHAP required new and reconstructed (which we are
now referring to as ``new'') Group 1 POTW to comply with the more
stringent of the following: (1) The requirements of the other NESHAP
for which they are acting as an agent of control for the industrial
user; or (2) the requirements applicable to new Group 2 POTW, which
allowed the POTW to choose to meet either a requirement to (a) cover
all equipment and route emissions through a closed vent system to a
control device; or (b) meet a HAP fraction emission limit of 0.014 for
emissions from all primary treatment units. We proposed that new Group
1 POTW comply with the other NESHAP for which they are acting as an
agent of control for an industrial user and the requirements for new
Group 2 POTW in the 2002 POTW NESHAP. (Note that we did not propose,
and are not finalizing, any revisions to the requirements for new Group
2 POTW.)
1. Existing Group 1 POTW
Comment: We received comments from one of the existing Group 1 POTW
that expressed concern that by imposing the HAP fraction emitted limit
on the existing Group 1 POTW with no alternative compliance option, the
EPA had ignored existing POTW with covers and controls already in
place. The commenter stated that new Group 1 POTW have the option of
either installing covers or complying with the HAP fraction limit.
However, the EPA did not provide that flexibility to
[[Page 49523]]
existing Group 1 POTW, thereby imposing an additional HAP fraction
limit without a cover option and more onerous recordkeeping and
reporting requirements. The commenter stated that the EPA should
provide existing Group 1 POTW that already use covers the option of
adding controls in lieu of complying with a HAP fraction limit.
Response: The EPA is not taking final action on the proposed
changes for existing Group 1 sources at this time. As explained in
section IV.F of this preamble, we are not setting a HAP fraction limit
for existing Group 1 or Group 2 POTW at this time; therefore, no
additional requirements are being added for existing Group 1 POTW in
the POTW NESHAP. Thus, as required by the 2002 POTW NESHAP, an existing
Group 1 POTW must comply with the control requirements as specified in
the appropriate NESHAP for the industrial user(s).
2. New Group 1 POTW
We did not receive any comment on our proposed revision to the
requirements for new Group 1 POTW. We proposed, and are finalizing,
that new Group 1 POTW must (1) meet the requirements of the other
NESHAP for which they act as an agent of control for an industrial user
and (2) either (a) cover all equipment and route emissions through a
closed vent system to a control device or (b) meet a HAP fraction
emission limit of 0.014 for emissions from all primary treatment units.
See 81 FR 95375 for our rationale for this change. Because we received
no adverse comment on our proposal, we are finalizing these
requirements as proposed.
V. Summary of Cost, Environmental, and Economic Impacts and Additional
Analyses Conducted
A. What are the affected facilities?
The EPA estimates, based on the responses to the 2015 ICR, the 2011
and 2014 National Emissions Inventory (NEI), and public comments
received, that there are 13 POTW that are engaged in treatment of
industrial wastewater and are currently subject to the POTW NESHAP. Two
of these facilities are considered Group 1 POTW, while the remaining
eleven are considered Group 2 POTW. All 13 currently subject to the
POTW NESHAP have already met the notification requirements for existing
Group 1 and Group 2 POTW. The EPA is not currently aware of any planned
new Group 1 or Group 2 POTW that will be constructed or any existing
Group 1 or Group 2 POTW that will be reconstructed.
B. What are the air quality impacts?
The EPA estimates that annual organic HAP emissions from the 13
POTW subject to the rule are approximately 35 tpy. We expect no
emissions of inorganic HAP from this category. The EPA does not
anticipate any additional emission reductions from the final changes to
the rule, and there are no anticipated new or reconstructed facilities.
C. What are the cost impacts?
The 13 entities subject to this proposal will incur only minimal
costs related to familiarizing themselves with this rule--estimated to
be a one-time total cost of $790 for all 13 entities. For further
information on the requirements of this rule, see section IV of this
preamble. For further information on the costs associated with the
requirements of this rule, see the document titled Economic Impact
Analysis for the National Emission Standards for Hazardous Air
Pollutants: Publicly Owned Treatment Works Risk and Technology Review,
in the docket. The memorandum titled Technology Review Memorandum for
the Publicly Owned Treatment Works Source Category, in the docket for
this action, presents costs estimated associated with the regulatory
options that were not selected for inclusion in this final rule (Docket
ID No. EPA-HQ-OAR-2016-0490).
D. What are the economic impacts?
The economic impact analysis is designed to inform decision makers
about the potential economic consequences of a regulatory action. For
this rule, the EPA estimated the annual cost of recordkeeping and
reporting as a percentage of reported sewage fees received by the
affected POTW. For the revisions promulgated in this final rule, costs
are expected to be less than 0.001 percent of collected sewage fees,
based on publicly available financial reports from the fiscal year
ending in 2015 for the affected entities.
In addition, the EPA performed a screening analysis for impacts on
small businesses by comparing estimated population served by the
affected entities to the population limit set forth by the U.S. Small
Business Administration. The screening analysis found that the
population served for all affected entities is greater than the limit
qualifying a public entity as a small business.
More information and details of the EPA's analysis of the economic
impacts, including the conclusions stated above, are provided in the
technical document, Final Economic Impact Analysis for the Publicly
Owned Treatment Works National Emissions Standards for Hazardous Air
Pollutants Risk and Technology Review, which is available in the docket
for this final rule (Docket ID No. EPA-HQ-OAR-2016-0490).
E. What are the benefits?
We do not anticipate any significant reductions in HAP emissions as
a result of these final amendments. However, we think that the
amendments will help to enhance the clarity of the rule, which can
improve compliance and minimize emissions.
F. What analysis of environmental justice did we conduct?
We examined the potential for any environmental justice concerns
that might be associated with this source category by performing a
demographic analysis of the population close to the six POTW that were
modeled for source category risk.\4\ In this analysis, we evaluated the
distribution of HAP-related cancer and non-cancer risks from the POTW
source category across different social, demographic, and economic
groups within the populations living near facilities identified as
having the highest risks. The methodology and the results of the
demographic analyses are included in a technical report, Risk and
Technology Review--Analysis of Socio-Economic Factors for Populations
Living Near POTW Facilities, available in the docket for this action
(Docket ID No. EPA-HQ-OAR-2016-0490). The results for various
demographic groups are based on the estimated risks from actual
emissions levels for the population living within 50 kilometers (km) of
the facilities.
---------------------------------------------------------------------------
\4\ See section IV.A of this preamble for an explanation of the
residual risk assessment.
---------------------------------------------------------------------------
The results of the POTW source category demographic analysis
indicate that actual emissions from the source category expose no
person to a cancer risk at or above 1-in-1 million or to a chronic non-
cancer TOSHI greater than 1. Therefore, we conclude that this final
rule will not have disproportionately high and adverse human health or
environmental effects on minority or low-income populations because it
does not affect the level of protection provided to human health or the
environment. However, this final rule may provide additional benefits
to these demographic groups by improving the compliance and
implementation of the NESHAP. The demographics of the population living
within 50 km of POTW can be found in Table 2 of the document titled
Risk and Technology
[[Page 49524]]
Review--Analysis of Socio-Economic Factors for Populations Living Near
Publicly Owned Treatment Works, available in the docket for this final
rule (Docket ID No. EPA-HQ-OAR-2016-0490).
G. What analysis of children's environmental health did we conduct?
This action is not subject to Executive Order 13045 because it is
not economically significant as defined in Executive Order 12866, and
because the EPA does not believe the environmental health or safety
risks addressed by this action present a disproportionate risk to
children. The results of the POTW source category demographic analysis
indicate that actual emissions from the source category expose no
person to a cancer risk at or above 1-in-1 million or to a chronic non-
cancer TOSHI greater than 1. Therefore, the analysis shows that actual
emissions from the POTW source category are not expected to have an
adverse human health effect on children.
VI. Statutory and Executive Order Reviews
Additional information about these statutes and Executive Orders
can be found at https://www2.epa.gov/laws-regulations/laws-and-executive-orders.
A. Executive Order 12866: Regulatory Planning and Review and Executive
Order 13563: Improving Regulation and Regulatory Review
This action is not a significant regulatory action and was
therefore not submitted to the Office of Management and Budget (OMB)
for review.
B. Executive Order 13771: Reducing Regulations and Controlling
Regulatory Costs
This action is not an Executive Order 13771 regulatory action
because this action is not significant under Executive Order 12866.
C. Paperwork Reduction Act (PRA)
The information collection activities in this rule have been
submitted for approval to the OMB under the PRA. The ICR document that
the EPA prepared has been assigned EPA ICR number 1891.08. You can find
a copy of the ICR in the docket for this rule, and it is briefly
summarized here. The information collection requirements are not
enforceable until OMB approves them.
The information to be collected includes the initial notification
that the POTW is subject to the rule. However, as stated in this
preamble, the 13 sources that we already know about have already met
this initial notification requirement and are not required to submit an
additional notification. The information will be used to identify
sources subject to the standards.
Respondents/affected entities: The respondents to the recordkeeping
and reporting requirements are owners and operators of POTW. The NAICS
code for the respondents affected by the standard is 221320 (Sewage
Treatment Facilities), which corresponds to the United States Standard
Industrial Classification code 4952 (Sewerage Systems).
Respondent's obligation to respond: Respondents are obligated to
respond in accordance with the notification requirements under 40 CFR
63.1591(a).
Estimated number of respondents: Zero.
Frequency of response: One response.
Total estimated burden: 0 hours (per year). Burden is defined at 5
CFR 1320.3(b).
Total estimated cost: $0 (per year), includes $0 annualized capital
or operation and maintenance costs.
An agency may not conduct or sponsor, and a person is not required
to respond to, a collection of information unless it displays a
currently valid OMB control number. The OMB control numbers for the
EPA's regulations in 40 CFR are listed in 40 CFR part 9. When OMB
approves this ICR, the Agency will announce that approval in the
Federal Register and publish a technical amendment to 40 CFR part 9 to
display the OMB control number for the approved information collection
activities contained in this final rule.
D. Regulatory Flexibility Act (RFA)
I certify that this action will not have a significant economic
impact on a substantial number of small entities under the RFA. This
action will not impose any requirements on small entities. There are no
small entities affected in this regulated industry. See the technical
document, Final Economic Impact Analysis for the National Emission
Standards for Hazardous Air Pollutants: Publicly Owned Treatment Works
Risk and Technology Review, which is available in the docket for this
final rule (Docket ID No. EPA-HQ-OAR-2016-0490) for more detail.
E. Unfunded Mandates Reform Act (UMRA)
This action does not contain an unfunded mandate of $100 million or
more as described in UMRA, 2 U.S.C. 1531-1538, and does not
significantly or uniquely affect small governments. The action imposes
no enforceable duty on any state, local, or tribal governments or the
private sector.
F. Executive Order 13132: Federalism
This action does not have federalism implications. It will not have
substantial direct effects on the states, on the relationship between
the national government and the states, or on the distribution of power
and responsibilities among the various levels of government.
G. Executive Order 13175: Consultation and Coordination With Indian
Tribal Governments
This action does not have tribal implications as specified in
Executive Order 13175. As discussed in section II.B.1 of this preamble,
we have identified only 13 POTW that are subject to this final rule and
none of those POTW are owned or operated by tribal governments. Thus,
Executive Order 13175 does not apply to this action.
H. Executive Order 13045: Protection of Children From Environmental
Health Risks and Safety Risks
The action is not subject to Executive Order 13045 because it is
not economically significant as defined in Executive Order 12866, and
because the EPA does not believe the environmental health or safety
risks addressed by this action present a disproportionate risk to
children. This action's health and risk assessments are contained in
sections III.A and B and sections IV.A and B of this preamble and the
Residual Risk Report memorandum contained in the docket for this
rulemaking.
I. Executive Order 13211: Actions Concerning Regulations That
Significantly Affect Energy Supply, Distribution, or Use
This action is not subject to Executive Order 13211 because it is
not a significant regulatory action under Executive Order 12866.
J. National Technology Transfer and Advancement Act (NTTAA)
This rulemaking does not involve technical standards.
K. Executive Order 12898: Federal Actions To Address Environmental
Justice in Minority Populations and Low-Income Populations
The EPA believes that this action does not have disproportionately
high and adverse human health or environmental effects on minority
populations, low-income populations, and/or indigenous peoples, as
specified in Executive Order 12898 (59 FR 7629, February 16, 1994).
The documentation for this decision is contained in section III.A.6
of this preamble and in the corresponding
[[Page 49525]]
technical report, Risk and Technology Review--Analysis of Socio-
Economic Factors for Populations Living Near Publicly Owned Treatment
Works, available in the docket for this action. The proximity results
indicate, for eight of the 11 demographic categories, that the
population percentages within 5 km and 50 km of source category
emissions are greater than the corresponding national percentage for
those same demographics. However, the results of the risk analysis
presented in section III.A.6 of this preamble and in the corresponding
technical report indicate that actual emissions from the source
category expose no person to a cancer risk at or above 1-in-1 million
or to a chronic non-cancer TOSHI greater than 1.
L. Congressional Review Act (CRA)
This action is subject to the CRA, and the EPA will submit a rule
report to each House of the Congress and to the Comptroller General of
the United States. This action is not a ``major rule'' as defined by 5
U.S.C. 804(2).
List of Subjects in 40 CFR Part 63
Environmental protection, Administrative practice and procedures,
Air pollution control, Hazardous substances, Intergovernmental
relations, Reporting and recordkeeping requirements.
Dated: October 16, 2017.
E. Scott Pruitt,
Administrator.
For the reasons stated in the preamble, the Environmental
Protection Agency amends part 63 of title 40, chapter I, of the Code of
Federal Regulations as follows:
PART 63--NATIONAL EMISSION STANDARDS FOR HAZARDOUS AIR POLLUTANTS
FOR SOURCE CATEGORIES
0
1. The authority citation for part 63 continues to read as follows:
Authority: 42 U.S.C. 7401, et seq.
0
2. Part 63 is amended by revising subpart VVV to read as follows:
Subpart VVV--National Emission Standards for Hazardous Air Pollutants:
Publicly Owned Treatment Works
Applicability
Sec.
63.1580 Am I subject to this subpart?
63.1581 Does the subpart distinguish between different types of POTW
treatment plants?
Requirements for Group 1 POTW Treatment Plants
63.1582 [Reserved]
63.1583 What are the emission points and control requirements for a
Group 1 POTW treatment plant?
63.1584 [Reserved]
63.1585 How does a Group 1 POTW treatment plant demonstrate
compliance?
Requirements for Group 1 and Group 2 POTW Treatment Plants
63.1586 What are the emission points and control requirements for a
Group 1 or Group 2 POTW?
63.1587 When do I have to comply?
63.1588 How do Group 1 and Group 2 POTW treatment plants demonstrate
compliance?
63.1589 What records must I keep?
63.1590 What reports must I submit?
63.1591 What are my notification requirements?
63.1592 Which General Provisions apply to my POTW treatment plant?
63.1593 [Reserved]
63.1594 Who enforces this subpart?
63.1595 List of definitions.
Table 1 to Subpart VVV of Part 63--Applicability of 40 CFR part 63
General Provisions to Subpart VVV
Table 2 to Subpart VVV of Part 63--Compliance Dates and Requirements
Subpart VVV--National Emission Standards for Hazardous Air
Pollutants: Publicly Owned Treatment Works
Applicability
Sec. 63.1580 Am I subject to this subpart?
(a) You are subject to this subpart if the following are all true:
(1) You own or operate a publicly owned treatment works (POTW) that
includes an affected source (Sec. 63.1595);
(2) The affected source is located at a Group 2 POTW which is a
major source of HAP emissions, or at any Group 1 POTW regardless of
whether or not it is a major source of HAP; and
(3) Your POTW is required to develop and implement a pretreatment
program as defined by 40 CFR 403.8, or your POTW meets the general
criteria for development and implementation of a pretreatment program.
(b) If your existing POTW treatment plant is not located at a major
source as of October 26, 1999, but thereafter becomes a major source
for any reason other than reconstruction, then, for the purpose of this
subpart, your POTW treatment plant would be considered an existing
source.
Note to paragraph (b): See Sec. 63.2 of the National Emission
Standards for Hazardous Air Pollutants (NESHAP) General Provisions
in subpart A of this part for the definitions of major source and
area source.
(c) If you commence construction or reconstruction of your POTW
treatment plant after December 1, 1998, then the requirements for a new
POTW apply.
Sec. 63.1581 Does the subpart distinguish between different types of
POTW treatment plants?
Yes, POTW treatment plants are divided into two subcategories:
Group 1 POTW treatment plants and Group 2 POTW treatment plants, as
described in paragraphs (a) through (c) of this section.
(a) Your POTW is a Group 1 POTW treatment plant if an industrial
user complies with its NESHAP by using the treatment and controls
located at your POTW treatment plant. Your POTW treatment plant accepts
the regulated waste stream and provides treatment and controls as an
agent for the industrial user. Group 1 POTW treatment plant is defined
in Sec. 63.1595.
(b) Your POTW is a Group 2 POTW treatment plant if your POTW treats
wastewater that is not subject to control by another NESHAP or the
industrial user does not comply with its NESHAP by using the treatment
and controls located at your POTW treatment plant. ``Group 2 POTW
treatment plant'' is defined in Sec. 63.1595.
(c) If, in the future, an industrial user complies with its NESHAP
by using the treatment and controls located at your POTW treatment
plant, then your Group 2 POTW treatment plant becomes a Group 1 POTW
treatment plant on the date your POTW begins treating that regulated
industrial wastewater stream.
Requirements for Group 1 POTW Treatment Plants
Sec. 63.1582 [Reserved]
Sec. 63.1583 What are the emission points and control requirements
for a Group 1 POTW treatment plant?
(a) The emission points and control requirements for an existing
Group 1 POTW treatment plant are specified in the appropriate NESHAP
for the industrial user(s).
(b) The emission points and control requirements for a new Group 1
POTW treatment plant are both those specified by the appropriate NESHAP
which apply to the industrial user(s) who discharge their waste for
treatment to the POTW, and those emission points and control
requirements set forth in Sec. 63.1586(b) or (c), as applicable.
(c) If your existing or new Group 1 POTW treatment plant accepts
one or more specific regulated industrial waste streams as part of
compliance with one or more other NESHAP, then you are subject to all
the requirements of each appropriate NESHAP for each waste stream.
(d) At all times, the POTW must operate and maintain any affected
source, including associated air
[[Page 49526]]
pollution control equipment and monitoring equipment, in a manner
consistent with safety and good air pollution control practices for
minimizing emissions. The general duty to minimize emissions does not
require the POTW to make any further efforts to reduce emissions if
levels required by the applicable standard have been achieved.
Determination of whether a source is operating in compliance with
operation and maintenance requirements will be based on information
available to the Administrator, which may include, but is not limited
to, monitoring results, review of operation and maintenance procedures,
review of operation and maintenance records, and inspection of the
source.
Sec. 63.1584 [Reserved]
Sec. 63.1585 How does a Group 1 POTW treatment plant demonstrate
compliance?
(a) An existing Group 1 POTW treatment plant demonstrates
compliance by operating treatment and control devices which meet all
requirements specified in the appropriate NESHAP. Requirements may
include performance tests, routine monitoring, recordkeeping, and
reporting.
(b) A new Group 1 POTW treatment plant demonstrates compliance by
operating treatment and control devices which meet all requirements
specified in the appropriate NESHAP and by meeting the requirements
specified in Sec. 63.1586, as applicable, as well as the applicable
requirements in Sec. Sec. 63.1588 through 63.1595.
Requirements for Group 1 and Group 2 POTW Treatment Plants
Sec. 63.1586 What are the emission points and control requirements
for a Group 1 or Group 2 POTW?
(a) An existing Group 1 or Group 2 POTW treatment plant must comply
with the initial notification requirements in Sec. 63.1591(a).
(b) Cover and control standard. Except as provided in paragraph (c)
of this section, new Group 1 and Group 2 POTW treatment plants must
install covers on the emission points up to, but not including, the
secondary influent pumping station or the secondary treatment units.
These emission points are treatment units that include, but are not
limited to, influent waste stream conveyance channels, bar screens,
grit chambers, grinders, pump stations, aerated feeder channels,
primary clarifiers, primary effluent channels, and primary screening
stations. In addition, all covered units, except primary clarifiers,
must have the air in the headspace underneath the cover ducted to a
control device in accordance with the standards for closed-vent systems
and control devices in Sec. 63.693 of subpart DD--National Emission
Standards for Hazardous Air Pollutants from Off-site Waste and Recovery
Operations of this part, except you may substitute visual inspections
for leak detection rather than Method 21 of appendix A-7 of part 60 of
this chapter. Covers must meet the following requirements:
(1) Covers must be tightly fitted and designed and operated to
prevent exposure of the wastewater to the atmosphere. This includes,
but is not limited to, the absence of visible cracks, holes, or gaps in
the roof sections or between the roof and the supporting wall; broken,
cracked, or otherwise damaged seals or gaskets on closure devices; and
broken or missing hatches, access covers, caps, or other closure
devices.
(2) If wastewater is in a treatment unit, each opening in the cover
must be maintained in a closed, sealed position, unless plant personnel
are present and conducting wastewater or sludge sampling, or equipment
inspection, maintenance, or repair.
(c) HAP fraction emitted standard. As an alternative to the
requirements in paragraph (b) of this section, a new Group 1 and Group
2 POTW treatment plant may comply by demonstrating, for all emission
points up to, but not including, the secondary influent pumping station
or the secondary treatment units, that the annual rolling average HAP
fraction emitted (calculated as specified in Sec. 63.1588(c)(3)) does
not exceed 0.014. You must demonstrate that for your POTW treatment
plant, the sum of all HAP emissions from these units divided by the sum
of all HAP mass loadings to the POTW treatment plant results in an
annual rolling average of the HAP fraction emitted of no greater than
0.014. You may use any combination of pretreatment, wastewater
treatment plant modifications, and control devices to achieve this
performance standard.
(d) At all times, the POTW 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. The general duty
to minimize emissions does not require the POTW to make any further
efforts to reduce emissions if the requirements of the applicable
standard have been met. Determination of whether a source is operating
in compliance with operation and maintenance requirements will be based
on information available to the Administrator, which may include, but
is not limited to, monitoring results, review of operation and
maintenance procedures, review of operation and maintenance records,
and inspection of the source.
Sec. 63.1587 When do I have to comply?
Sources subject to this subpart are required to achieve compliance
on or before the dates specified in table 2 of this subpart.
Sec. 63.1588 How do Group 1 and Group 2 POTW treatment plants
demonstrate compliance?
(a) If you are complying with Sec. 63.1586(b) by using covers, you
must conduct the following inspections:
(1) You must visually check the cover and its closure devices for
defects that could result in air emissions. Defects include, but are
not limited to, visible cracks, holes, or gaps in the roof sections or
between the roof and the supporting wall; broken, cracked, or otherwise
damaged seals or gaskets on closure devices; and broken or missing
hatches, access covers, caps, or other closure devices.
(2) You must perform an initial visual inspection within 60
calendar days of becoming subject to this NESHAP and perform follow-up
inspections at least once per year, thereafter.
(3) In the event that you find a defect on a cover on a treatment
unit in use, you must repair the defect within 45 calendar days. If you
cannot repair within 45 calendar days, you must notify the EPA or the
delegated authority immediately and report the reason for the delay and
the date you expect to complete the repair. If you find a defect on a
cover on a treatment unit that is not in service, you must repair the
defect prior to putting the treatment unit back in wastewater service.
(b) If you own or operate a control device used to meet the
requirements for Sec. 63.1586(b), you must comply with the inspection
and monitoring requirements of Sec. 63.695(c) of subpart DD of this
part.
(c) To comply with the HAP fraction emitted standard specified in
Sec. 63.1586(c), you must develop, to the satisfaction of the
Administrator, an Inspection and Monitoring Plan. This Inspection and
Monitoring Plan must include, at a minimum, the following:
(1) A method to determine the influent HAP mass loading, i.e., the
annual mass quantity for each HAP entering the wastewater treatment
plant.
[[Page 49527]]
(2) A method to determine your POTW treatment plant's annual HAP
emissions for all units up to, but not including, the secondary
influent pumping station or the secondary treatment units. The method
you use to determine your HAP emissions, such as modeling or direct
source measurement, must:
(i) Be approved by the Administrator for use at your POTW;
(ii) Account for all factors affecting emissions from your POTW
treatment plant including, but not limited to, emissions from
wastewater treatment units; emissions resulting from inspection,
maintenance, and repair activities; fluctuations (e.g., daily, monthly,
annual, seasonal) in your influent wastewater HAP concentrations;
annual industrial loading; performance of control devices; or any other
factors that could affect your annual HAP emissions; and
(iii) Include documentation that the values and sources of all
data, operating conditions, assumptions, etc., used in your method
result in an accurate estimation of annual emissions from your POTW
treatment plant.
(3) A method to demonstrate that your POTW treatment plant meets
the HAP fraction emitted standard specified in Sec. 63.1586(c), i.e.,
the sum of all HAP emissions from paragraph (c)(2) of this section
divided by the sum of all HAP mass loadings from paragraph (c)(1) of
this section results in a fraction emitted of 0.014 or less to
demonstrate compliance with Sec. 63.1586(c). The Inspection and
Monitoring Plan must require, at a minimum, that you perform the
calculations shown in paragraphs (c)(3)(i) through (viii) of this
section within 90 days of the end of each month. This calculation shall
demonstrate that your annual rolling average of the HAP fraction
emitted is 0.014 or less when demonstrating compliance with Sec.
63.1586(c).
(i) Determine the average daily flow in million gallons per day
(MGD) of the wastewater entering your POTW treatment plant for the
month;
(ii) Determine the flow-weighted monthly concentration of each HAP
listed in Table 1 to subpart DD of this part that is reasonably
anticipated to be present in your influent;
(iii) Using the information in paragraphs (c)(3)(i) and (ii) of
this section, determine a total annual flow-weighted loading in pounds
per day (lbs/day) of each HAP entering your POTW treatment plant;
(iv) Sum up the values for each individual HAP loading in paragraph
(c)(3)(iii) of this section and determine a total annual flow-weighted
loading value (lbs/day) for all HAP entering your POTW treatment plant
for the current month;
(v) Based on the current month's information in paragraph
(c)(3)(iii) of this section along with source testing and emission
modeling, for each HAP, determine the annual emissions (lbs/day) from
all wastewater units up to, but not including, secondary treatment
units;
(vi) Sum up the values in paragraph (c)(3)(v) of this section and
calculate the total annual emissions value for the month for all HAP
from all wastewater treatment units up to, but not including, secondary
treatment units;
(vii) Calculate the HAP fraction emitted value for the month, using
Equation 1 of this section as follows:
[GRAPHIC] [TIFF OMITTED] TR26OC17.018
Where:
femonthly = HAP fraction emitted for the previous month
[sum]E = Total HAP emissions value from paragraph (c)(3)(vi) of this
section
[sum]L = Total annual loading from paragraph (c)(3)(iv) of this
section
(viii) Average the HAP fraction emitted value for the month
determined in paragraph (c)(3)(vii) of this section, with the values
determined for the previous 11 months, to calculate an annual rolling
average of the HAP fraction emitted.
(4) A method to demonstrate, to the satisfaction of the
Administrator, that your POTW treatment plant is in continuous
compliance with the requirements of Sec. 63.1586(c). Continuous
compliance means that your emissions, when averaged over the course of
a year, do not exceed the level of emissions that allows your POTW to
comply with Sec. 63.1586(c). For example, you may identify a
parameter(s) that you can monitor that assures your emissions, when
averaged over the entire year, will meet the requirements in Sec.
63.1586(c). Some example parameters that may be considered for
monitoring include your wastewater influent HAP concentration and flow,
industrial loading from your permitted industrial users, and your
control device performance criteria. Where emission reductions are due
to proper operation of equipment, work practices, or other operational
procedures, your demonstration must specify the frequency of
inspections and the number of days to completion of repairs.
(d) Prior to receiving approval on the Inspection and Monitoring
Plan, you must follow the plan submitted to the Administrator as
specified in Sec. 63.1590(f).
Sec. 63.1589 What records must I keep?
(a) To comply with the cover and control standard specified in
Sec. 63.1586(b), you must prepare and maintain the records required in
paragraphs (a)(1) through (4) of this section:
(1) A record for each treatment unit inspection required by Sec.
63.1588(a). You must include a treatment unit identification number (or
other unique identification description as selected by you) and the
date of inspection.
(2) For each defect detected during inspections required by Sec.
63.1588(a), you must record the location of the defect, a description
of the defect, the date of detection, the corrective action taken to
repair the defect, and the date the repair to correct the defect is
completed.
(3) If repair of the defect is delayed as described in Sec.
63.1588(a)(3), you must also record the reason for the delay and the
date you expect to complete the repair.
(4) If you own or operate a control device used to meet the
requirements for Sec. 63.1586(b), you must comply with the
recordkeeping requirements of Sec. 63.696(a), (b), (g), and (h).
(b) To comply with the HAP fraction emitted standard specified in
Sec. 63.1586(c), you must prepare and maintain the records required in
paragraphs (b)(1) through (3) of this section:
(1) A record of the methods and data used to determine your POTW
treatment plant's annual HAP loading and HAP emissions as determined in
Sec. 63.1588(c)(1) and (2) as part of your Inspection and Monitoring
Plan;
(2) A record of the methods and data used to determine that your
POTW treatment plant meets the HAP fraction emitted standard of 0.014
or less, as determined in Sec. 63.1588(c)(3) as part of your
Inspection and Monitoring Plan; and
(3) A record of the methods and data that demonstrates that your
POTW treatment plant is in continuous compliance with the requirements
of Sec. 63.1588(c)(4) to calculate annual emissions as specified in
your Inspection and Monitoring Plan.
(c) The POTW must record the malfunction information specified in
paragraphs (c)(1) through (3) of this section.
(1) In the event that an affected unit fails to meet an applicable
standard, record the number of failures. For each failure, record the
date, time, and duration of the failure.
(2) For each failure to meet an applicable standard, record and
retain a list of the affected sources or equipment,
[[Page 49528]]
an estimate of the tons per year of each regulated pollutant emitted
over any emission limit and a description of the method used to
estimate the emissions.
(3) Record actions taken to minimize emissions in accordance with
Sec. 63.1583(d) or Sec. 63.1586(d) and any corrective actions taken
to return the affected unit to its normal or usual manner of operation.
(d) Any records required to be maintained by this part that are
submitted electronically via the EPA's Compliance and Emissions Data
Reporting Interface (CEDRI) may be maintained in electronic format.
This ability to maintain electronic copies does not affect the
requirement for facilities to make records, data, and reports available
upon request to a delegated air agency or the EPA as part of an on-site
compliance evaluation.
Sec. 63.1590 What reports must I submit?
(a) An existing Group 1 POTW must meet the reporting requirements
specified in the appropriate NESHAP for the industrial user(s).
(b) A new Group 1 or Group 2 POTW must submit annual reports
containing the information specified in paragraphs (b)(1) through (4)
of this section, if applicable. You must submit annual reports
following the procedure specified in paragraph (b)(5) of this section.
For new units, the initial annual report is due 15 months after your
POTW becomes subject to the requirements in this subpart and must cover
the first 12 months of operation after your POTW becomes subject to the
requirements of this subpart. Subsequent annual reports are due by the
same date each year as the initial annual report and must contain
information for the 12-month period following the 12-month period
included in the previous annual report.
(1) The general information specified in paragraphs (b)(1)(i) and
(ii) of this section must be included in all reports.
(i) The company name, POTW treatment plant name, and POTW treatment
plant address, including county where the POTW is located; and
(ii) Beginning and ending dates of the reporting period.
(2) If you use covers to comply with the requirements of Sec.
63.1586(b), you must submit the following:
(i) The dates of each visual inspection conducted;
(ii) The defects found during each visual inspection; and
(iii) For each defect found during a visual inspection, how the
defects were repaired, whether the repair has been completed, and
either the date each repair was completed or the date each repair is
expected to be completed.
(3) If you comply with the HAP fraction emitted standard in Sec.
63.1586(c), you must submit each value of the annual rolling average
HAP fraction emitted as calculated in Sec. 63.1588(c)(3)(vii) for the
period covered by the annual report. Identify each value by the final
month included in the calculation.
(4) If a source fails to meet an applicable standard, report such
events in the annual report. Report the number of failures to meet an
applicable standard. For each instance, report the start date, start
time, and duration of each failure, as well as a list of the affected
sources or equipment. If you comply with the cover and control standard
in Sec. 63.1586(b), for each failure, the report must include the
percent control achieved. If you comply with the HAP fraction emitted
standard in Sec. 63.1586(c), for each failure, the report must include
the HAP fraction emitted. You must include an estimate of the tons per
year of each regulated pollutant emitted over the emission limit and a
description of the method used to estimate the emissions in the report.
(5) You must submit the report to the Administrator at the
appropriate address listed in Sec. 63.13, unless the Administrator
agrees to or species an alternate reporting method. Beginning on
October 28, 2019 or once the reporting form has been available in CEDRI
for 1 year, whichever is later, you must submit subsequent annual
reports to the EPA via CEDRI. (CEDRI can be accessed through the EPA's
Central Data Exchange (CDX)(https://cdx.epa.gov/)). You must use the
appropriate electronic report template on the CEDRI Web site for this
subpart or an alternate electronic file format consistent with the
extensible markup language (XML) schema listed on the CEDRI Web site
(https://www.epa.gov/electronic-reporting-air-emissions/compliance-and-emissions-data-reporting-interface-cedri). The date report templates
become available in CEDRI will be listed on the CEDRI Web site. The
reports must be submitted by the deadline specified in this subpart,
regardless of the method in which the reports are submitted. If you
claim that some of the information required to be submitted via CEDRI
is confidential business information (CBI), you shall submit a complete
report generated using the appropriate form in CEDRI or an alternate
electronic file consistent with the extensible markup language (XML)
schema listed on the EPA's CEDRI Web site, including information
claimed to be CBI, on a compact disc, flash drive, or other commonly
used electronic storage medium to the EPA. The electronic medium shall
be clearly marked as CBI and mailed to U.S. EPA/OAQPS/CORE CBI Office,
Attention: Group Leader, Measurement Policy Group, MD C404-02, 4930 Old
Page Rd., Durham, NC 27703. The same file with the CBI omitted shall be
submitted to the EPA via the EPA's CDX as described earlier in this
paragraph.
(c) If you own or operate a control device used to meet the cover
and control standard in Sec. 63.1586(b), you must submit the
notifications and reports required by Sec. 63.697(b), including a
notification of performance tests; a performance test report; a
malfunction report; and a summary report. These notifications and
reports must be submitted to the Administrator, except for performance
test reports. Within 60 calendar days after the date of completing each
performance test (as defined in Sec. 63.2) required by subpart DD of
this part, you must submit the results of the performance test
following the procedure specified in paragraphs (c)(1) through (3) of
this section.
(1) For data collected using test methods supported by the EPA's
Electronic Reporting Tool (ERT) as listed on the EPA's ERT Web site
(https://www.epa/gov/electronic-reporting-air-emissions/electronic-reporting-tool-ert) at the time of the test, you must submit the
results of the performance test to the EPA via CEDRI. Performance test
data must be submitted in a file format generated through the use of
the EPA's ERT or an alternate electronic file format consistent with
the XML schema listed on the EPA's ERT Web site.
(2) For data collected using test methods that are not supported by
the EPA's ERT as listed on the EPA's ERT Web site at the time of the
test, you must submit the results of the performance test to the
Administrator at the appropriate address listed in Sec. 63.13 of
subpart A of this part, unless the Administrator agrees to or specifies
an alternate reporting method.
(3) If you claim that some of the performance test information
being submitted under paragraph (b)(1) of this section is CBI, you must
submit a complete file generated through the use of the EPA's ERT or an
alternate electronic file consistent with the XML schema listed on the
EPA's ERT Web site, including information claimed to be CBI, on a
compact disc, flash drive, or other commonly used electronic storage
medium to the EPA. The electronic medium must be clearly marked as CBI
and mailed to U.S. EPA/
[[Page 49529]]
OAQPS/CORE CBI Office, Attention: Group Leader, Measurement Policy
Group, MD C404-02, 4930 Old Page Rd., Durham, NC 27703. The same ERT or
alternate file with the CBI omitted must be submitted to the EPA via
the EPA's CDX as described in paragraph (c)(1) of this section.
(d) You must comply with the delay of repair reporting required in
Sec. 63.1588(a)(3).
(e) You may apply to the Administrator for a waiver of
recordkeeping and reporting requirements by complying with the
requirements of Sec. 63.10(f). Electronic reporting to the EPA cannot
be waived.
(f) To comply with the HAP fraction emitted standard specified in
Sec. 63.1586(c), you must submit, for approval by the Administrator,
an Inspection and Monitoring Plan explaining your compliance approach
90 calendar days prior to beginning operation of your new POTW or by
April 24, 2018, whichever is later.
(g) If you are required to electronically submit a report through
the CEDRI in the EPA's CDX, and due to a planned or actual outage of
either the EPA's CEDRI or CDX systems within the period of time
beginning 5 business days prior to the date that the submission is due,
you will be or are precluded from accessing CEDRI or CDX and submitting
a required report within the time prescribed, you may assert a claim of
EPA system outage for failure to timely comply with the reporting
requirement. You must submit notification to the Administrator in
writing as soon as possible following the date you first knew, or
through due diligence should have known, that the event may cause or
caused a delay in reporting. You must provide to the Administrator a
written description identifying the date, time and length of the
outage; a rationale for attributing the delay in reporting beyond the
regulatory deadline to the EPA system outage; describe the measures
taken or to be taken to minimize the delay in reporting; and identify a
date by which you propose to report, or if you have already met the
reporting requirement at the time of the notification, the date you
reported. In any circumstance, the report must be submitted
electronically as soon as possible after the outage is resolved. The
decision to accept the claim of EPA system outage and allow an
extension to the reporting deadline is solely within the discretion of
the Administrator.
(h) If you are required to electronically submit a report through
CEDRI in the EPA's CDX and a force majeure event is about to occur,
occurs, or has occurred or there are lingering effects from such an
event within the period of time beginning five business days prior to
the date the submission is due, the owner or operator may assert a
claim of force majeure for failure to timely comply with the reporting
requirement. For the purposes of this section, a force majeure event is
defined as an event that will be or has been caused by circumstances
beyond the control of the affected facility, its contractors, or any
entity controlled by the affected facility that prevents you from
complying with the requirement to submit a report electronically within
the time period prescribed. Examples of such events are acts of nature
(e.g., hurricanes, earthquakes, or floods), acts of war or terrorism,
or equipment failure or safety hazard beyond the control of the
affected facility (e.g., large scale power outage). If you intend to
assert a claim of force majeure, you must submit notification to the
Administrator in writing as soon as possible following the date you
first knew, or through due diligence should have known, that the event
may cause or caused a delay in reporting. You must provide to the
Administrator a written description of the force majeure event and a
rationale for attributing the delay in reporting beyond the regulatory
deadline to the force majeure event; describe the measures taken or to
be taken to minimize the delay in reporting; and identify a date by
which you propose to report, or if you have already met the reporting
requirement at the time of the notification, the date you reported. In
any circumstance, the reporting must occur as soon as possible after
the force majeure event occurs. The decision to accept the claim of
force majeure and allow an extension to the reporting deadline is
solely within the discretion of the Administrator.
Sec. 63.1591 What are my notification requirements?
(a) You must submit an initial notification that your POTW
treatment plant is subject to these standards as specified in
paragraphs (a)(1) and (2) of this section.
(1) If you have an existing Group 1 or Group 2 POTW treatment
plant, you must submit an initial notification by October 26, 2018.
(2) If you have a new Group 1 or Group 2 POTW treatment plant, you
must submit an initial notification upon startup.
(b) The initial notification must include the information included
in paragraphs (b)(1) through (4) of this section.
(1) Your name and address;
(2) The address (i.e., physical location) of your POTW treatment
plant;
(3) An identification of these standards as the basis of the
notification and your POTW treatment plant's compliance date; and
(4) A brief description of the nature, size, design, and method of
operation of your POTW treatment plant, including its operating design
capacity and an identification of each point of emission for each HAP,
or if a definitive identification is not yet possible, a preliminary
identification of each point of emission for each HAP.
(c) You must submit a notification of compliance status as required
in Sec. 63.9(h), as specified below:
(1) If you comply with Sec. 63.1586(b) and use covers on the
emission points and route air in the headspace underneath the cover to
a control device, you must submit a notification of compliance status
as specified in Sec. 63.9(h) that includes a description of the POTW
treatment units and installed covers, as well as the information
required for control devices including the performance test results.
(2) If you comply with Sec. 63.1586(c) by meeting the HAP fraction
emitted standard, submission of the Inspection and Monitoring Plan as
required in Sec. 63.1588(c) and Sec. 63.1590(f) meets the requirement
for submitting a notification of compliance status report in Sec.
63.9(h).
(d) You must notify the Administrator, within 30 calendar days of
discovering that you are out of compliance with an applicable
requirement of this subpart, including the following:
(1) The requirement to route the air in the headspace underneath
the cover of all units equipped with covers, except primary clarifiers,
to a control device as specified in Sec. 63.1586(b).
(2) The HAP fraction emitted standard as specified in Sec.
63.1586(c).
(3) The requirement to operate and maintain the affected source as
specified in Sec. 63.1586(d).
(4) The requirement to inspect covers annually and repair defects
as specified in Sec. 63.1588(a).
(5) The requirement to comply with the inspection and monitoring
requirements of Sec. 63.695(c) as specified in Sec. 63.1588(b).
(6) The procedures specified in an Inspection and Monitoring Plan
prepared as specified in Sec. 63.1588(c).
(7) The requirements specified in an appropriate NESHAP for which
the Group 1 POTW treatment plan treats regulated industrial waste as
specified in Sec. 63.1583(a) or (b), as applicable.
[[Page 49530]]
Sec. 63.1592 Which General Provisions apply to my POTW treatment
plant?
(a) Table 1 to this subpart lists the General Provisions (40 CFR
part 63, subpart A) which do and do not apply to POTW treatment plants.
(b) Unless a permit is otherwise required by law, the owner or
operator of a Group 1 POTW treatment plant which is not a major source
is exempt from the permitting requirements established by 40 CFR part
70.
Sec. 63.1593 [Reserved]
Sec. 63.1594 Who enforces this subpart?
(a) This subpart can be implemented and enforced by the U.S. EPA,
or a delegated authority such as the applicable state, local, or tribal
agency. If the U.S. EPA Administrator has delegated authority to a
state, local, or tribal agency, then that agency, in addition to the
U.S. EPA, has the authority to implement and enforce this subpart.
Contact the applicable U.S. EPA Regional Office to find out if
implementation and enforcement of this subpart is delegated to a state,
local, or tribal agency.
(b) In delegating implementation and enforcement authority of this
subpart to a state, local, or tribal agency under subpart E of this
part, the authorities contained in paragraphs (b)(1) through (5) of
this section are retained by the Administrator of U.S. EPA and cannot
be delegated to the state, local, or tribal agency.
(1) Approval of alternatives to the requirements in Sec. Sec.
63.1580, 63.1583, and 63.1586 through 63.1588.
(2) Approval of major alternatives to test methods under Sec.
63.7(e)(2)(ii) and (f), as defined in Sec. 63.90, and as required in
this subpart.
(3) Approval of major alternatives to monitoring under Sec.
63.8(f), as defined in Sec. 63.90, and as required in this subpart.
(4) Approval of major alternatives to recordkeeping and reporting
under Sec. 63.10(f), as defined in Sec. 63.90, and as required in
this subpart.
(5) Approval of an alternative to any electronic reporting to the
EPA required by this subpart.
Sec. 63.1595 List of definitions.
As used in this subpart:
Affected source means the group of all equipment that comprise the
POTW treatment plant.
Cover means a device that prevents or reduces air pollutant
emissions to the atmosphere by forming a continuous barrier over the
waste material managed in a treatment unit. A cover may have openings
(such as access hatches, sampling ports, gauge wells) that are
necessary for operation, inspection, maintenance, and repair of the
treatment unit on which the cover is used. A cover may be a separate
piece of equipment which can be detached and removed from the treatment
unit, or a cover may be formed by structural features permanently
integrated into the design of the treatment unit. The cover and its
closure devices must be made of suitable materials that will prevent
exposure of the waste material to the atmosphere and will maintain the
integrity of the cover and its closure devices throughout its intended
service life.
Existing source or existing POTW means a POTW that commenced
construction on or before December 1, 1998, and has not been
reconstructed after December 1, 1998.
Fraction emitted means the fraction of the mass of HAP entering the
POTW wastewater treatment plant which is emitted prior to secondary
treatment.
Group 1 POTW means a POTW that accepts a waste stream regulated by
another NESHAP and provides treatment and controls as an agent for the
industrial user. The industrial user complies with its NESHAP by using
the treatment and controls located at the POTW. For example, an
industry discharges its benzene-containing waste stream to the POTW for
treatment to comply with 40 CFR part 61, subpart FF--National Emission
Standard for Benzene Waste Operations. This definition does not include
POTW treating waste streams not specifically regulated under another
NESHAP.
Group 2 POTW means a POTW that does not meet the definition of a
Group 1 POTW. A Group 2 POTW can treat a waste stream that is either:
(1) Not specifically regulated by another NESHAP, or
(2) From an industrial user that complies with the specific
wastewater requirements in their applicable NESHAP prior to discharging
the waste stream to the POTW.
Industrial user means a nondomestic source introducing any
pollutant or combination of pollutants into a POTW. Industrial users
can be commercial or industrial facilities whose wastes enter local
sewers.
New source or new POTW means any POTW that commenced construction
or reconstruction after December 1, 1998.
Publicly owned treatment works (POTW) means a treatment works, as
that term is defined by section 112(e)(5) of the Clean Air Act, which
is owned by a municipality (as defined by section 502(4) of the Clean
Water Act), a state, an intermunicipal or interstate agency, or any
department, agency, or instrumentality of the federal government. This
definition includes any intercepting sewers, outfall sewers, sewage
collection systems, pumping, power, and other equipment. The wastewater
treated by these facilities is generated by industrial, commercial, and
domestic sources. As used in this subpart, the term POTW refers to both
any publicly owned treatment works which is owned by a state,
municipality, or intermunicipal or interstate agency and, therefore,
eligible to receive grant assistance under the Subchapter II of the
Clean Water Act, and any federally owned treatment works as that term
is described in section 3023 of the Solid Waste Disposal Act.
POTW treatment plant means that portion of the POTW which is
designed to provide treatment (including recycling and reclamation) of
municipal sewage and industrial waste.
Secondary treatment means treatment processes, typically
biological, designed to reduce the concentrations of dissolved and
colloidal organic matter in wastewater.
Waste and wastewater means a material, or spent or used water or
waste, generated from residential, industrial, commercial, mining, or
agricultural operations or from community activities that contain
dissolved or suspended matter, and that is discarded, discharged, or is
being accumulated, stored, or physically, chemically, thermally, or
biologically treated in a publicly owned treatment works.
Table 1 to Subpart VVV of Part 63--Applicability of 40 CFR Part 63 General Provisions to Subpart VVV
----------------------------------------------------------------------------------------------------------------
General provisions reference Applicable to subpart VVV Explanation
----------------------------------------------------------------------------------------------------------------
Sec. 63.1....................... ............................................. Applicability.
Sec. 63.1(a)(1)................. Yes.......................................... Terms defined in the Clean
Air Act.
Sec. 63.1(a)(2)................. Yes.......................................... General applicability
explanation.
Sec. 63.1(a)(3)................. Yes.......................................... Cannot diminish a stricter
NESHAP.
[[Page 49531]]
Sec. 63.1(a)(4)................. Yes.......................................... Not repetitive. Doesn't apply
to section 112(r).
Sec. 63.1(a)(5)................. Yes.......................................... Section reserved.
Sec. 63.1(a)(6)-(8)............. Yes.......................................... Contacts and authorities.
Sec. 63.1(a)(9)................. Yes.......................................... Section reserved.
Sec. 63.1(a)(10)................ Yes.......................................... Time period definition.
Sec. 63.1(a)(11)................ Yes.......................................... Postmark explanation.
Sec. 63.1(a)(12)-(14)........... Yes.......................................... Time period changes.
Regulation conflict. Force
and effect of subpart A.
Sec. 63.1(b)(1)................. Yes.......................................... Initial applicability
determination of subpart A.
Sec. 63.1(b)(2)................. Yes.......................................... Section reserved.
Sec. 63.1(b)(3)................. No........................................... Subpart VVV specifies
recordkeeping of records of
applicability determination.
Sec. 63.1(c)(1)................. Yes.......................................... Requires compliance with both
subparts A and subpart VVV.
Sec. 63.1(c)(2)(i).............. No........................................... State options regarding title
V permit. Unless required by
the State, area sources
subject to subpart VVV are
exempted from permitting
requirements.
Sec. 63.1(c)(2)(ii)-(iii)....... No........................................... State options regarding title
V permit.
Sec. 63.1(c)(3)................. Yes.......................................... Section reserved.
Sec. 63.1(c)(4)................. Yes.......................................... Extension of compliance.
Sec. 63.1(c)(5)................. No........................................... Subpart VVV addresses area
sources becoming major due
to increase in emissions.
Sec. 63.1(d).................... Yes.......................................... Section reserved.
Sec. 63.1(e).................... Yes.......................................... Title V permit before a
relevant standard is
established.
Sec. 63.2....................... Yes.......................................... Definitions.
Sec. 63.3....................... Yes.......................................... Units and abbreviations.
Sec. 63.4....................... ............................................. Prohibited activities and
circumvention.
Sec. 63.4(a)(1)-(3)............. Yes.......................................... Prohibits operation in
violation of subpart A.
Sec. 63.4(a)(4)................. Yes.......................................... Section reserved.
Sec. 63.4(a)(5)................. Yes.......................................... Compliance dates.
Sec. 63.4(b).................... Yes.......................................... Circumvention.
Sec. 63.4(c).................... Yes.......................................... Severability.
Sec. 63.5....................... ............................................. Preconstruction review and
notification requirements.
Sec. 63.5(a)(1)................. Yes.......................................... Construction and
reconstruction.
Sec. 63.5(a)(2)................. Yes.......................................... New source--effective dates.
Sec. 63.5(b)(1)................. Yes.......................................... New sources subject to
relevant standards.
Sec. 63.5(b)(2)................. Yes.......................................... Section reserved.
Sec. 63.5(b)(3)................. Yes.......................................... No new major sources without
Administrator approval.
Sec. 63.5(b)(4)................. Yes.......................................... New major source
notification.
Sec. 63.5(b)(5)................. Yes.......................................... New major sources must
comply.
Sec. 63.5(b)(6)................. Yes.......................................... New equipment added
considered part of major
source.
Sec. 63.5(c).................... Yes.......................................... Section reserved.
Sec. 63.5(d)(1)................. Yes.......................................... Implementation of section
112(I)(2)--application of
approval of new source
construction.
Sec. 63.5(d)(2)................. Yes.......................................... Application for approval of
construction for new sources
listing and describing
planned air pollution
control system.
Sec. 63.5(d)(3)................. Yes.......................................... Application for
reconstruction.
Sec. 63.5(d)(4)................. Yes.......................................... Administrator may request
additional information.
Sec. 63.5(e).................... Yes.......................................... Approval of reconstruction.
Sec. 63.5(f)(1)................. Yes.......................................... Approval based on State
review.
Sec. 63.5(f)(2)................. Yes.......................................... Application deadline.
Sec. 63.6....................... ............................................. Compliance with standards and
maintenance requirements.
Sec. 63.6(a).................... Yes.......................................... Applicability of compliance
with standards and
maintenance requirements.
Sec. 63.6(b).................... Yes.......................................... Compliance dates for new and
reconstructed sources.
Sec. 63.6(c).................... Yes.......................................... Compliance dates for existing
sources apply to existing
Group 1 POTW treatment
plants.
Sec. 63.6(d).................... Yes.......................................... Section reserved.
Sec. 63.6(e).................... Yes, except as noted below................... Operation and maintenance
requirements apply to new
sources.
Sec. 63.6(e)(1)(i).............. No........................................... General duty; See Sec.
63.1583(d) and Sec.
63.1586(d) for general duty
requirements.
Sec. 63.6(e)(1)(ii)............. No........................................... Requirement to correct
malfunctions.
Sec. 63.6(e)(3)................. No........................................... SSM plans are not required
for POTW.
Sec. 63.6(f).................... Yes, except as noted below................... Compliance with non-opacity
emission standards applies
to new sources.
Sec. 63.6(f)(1)................. No........................................... The POTW standards apply at
all times.
Sec. 63.6(g).................... Yes.......................................... Use of alternative non-
opacity emission standards
applies to new sources.
Sec. 63.6(h).................... No........................................... POTW treatment plants do not
typically have visible
emissions.
Sec. 63.6(i).................... Yes.......................................... Extension of compliance with
emission standards applies
to new sources.
Sec. 63.6(j).................... Yes.......................................... Presidential exemption from
compliance with emission
standards.
Sec. 63.7....................... ............................................. Performance testing
requirements.
Sec. 63.7(a).................... Yes.......................................... Performance testing is
required for new sources.
Sec. 63.7(b).................... Yes.......................................... New sources must notify the
Administrator of intention
to conduct performance
testing.
Sec. 63.7(c).................... Yes.......................................... New sources must comply with
quality assurance program
requirements.
Sec. 63.7(d).................... Yes.......................................... New sources must provide
performance testing
facilities at the request of
the Administrator.
Sec. 63.7(e).................... Yes, except as noted below................... Requirements for conducting
performance tests apply to
new sources.
Sec. 63.7(e)(1)................. No........................................... The performance testing
provisions of Sec. 63.694
for control devices are
incorporated by reference
into subpart DD of this
part.
[[Page 49532]]
Sec. 63.7(f).................... Yes.......................................... New sources may use an
alternative test method.
Sec. 63.7(g).................... Yes.......................................... Requirements for data
analysis, recordkeeping, and
reporting associated with
performance testing apply to
new sources.
Sec. 63.7(h).................... Yes.......................................... New sources may request a
waiver of performance tests.
Sec. 63.8....................... ............................................. Monitoring requirements.
Sec. 63.8(a).................... Yes.......................................... Applicability of monitoring
requirements.
Sec. 63.8(b).................... Yes.......................................... Monitoring shall be conducted
by new sources.
Sec. 63.8(c).................... Yes, except as noted below................... New sources shall operate and
maintain continuous
monitoring systems (CMS).
Sec. 63.8(c)(1)(i).............. No........................................... See Sec. 63.1583(d) for
general duty requirement
with respect to minimizing
emissions and continuous
monitoring requirements.
Sec. 63.8(c)(1)(iii)............ No........................................... See the applicable CMS
quality control requirements
under Sec. 63.8(c) and
(d).
Sec. 63.8(d).................... Yes, except as noted below................... New sources must develop and
implement a CMS quality
control program.
Sec. 63.8(d)(3)................. No........................................... The owner or operator must
keep these written
procedures on record for the
life of the affected source
or until the affected source
is no longer subject to the
provisions of this part, and
make them available for
inspection, upon request, by
the Administrator. If the
performance evaluation plan
is revised, the owner or
operator must keep previous
(i.e., superseded) versions
of the performance
evaluation plan on record to
be made available for
inspection, upon request, by
the Administrator, for a
period of 5 years after each
revision of the plan. The
program of corrective action
should be included in the
plan required under Sec.
63.8(d)(2).
Sec. 63.8(e).................... Yes.......................................... New sources may be required
to conduct a performance
evaluation of CMS.
Sec. 63.8(f).................... Yes.......................................... New sources may use an
alternative monitoring
method.
Sec. 63.8(g).................... Yes.......................................... Requirements for reduction of
monitoring data.
Sec. 63.9....................... ............................................. Notification requirements.
Sec. 63.9(a).................... Yes.......................................... Applicability of notification
requirements.
Sec. 63.9(b).................... Yes, except as noted below................... Initial notification due
February 23, 2000 or 60 days
after becoming subject to
this subpart.
Sec. 63.9(c).................... Yes.......................................... Request for extension of
compliance with subpart VVV.
Sec. 63.9(d).................... Yes.......................................... Notification that source is
subject to special
compliance requirements as
specified in Sec.
63.6(b)(3) and (4).
Sec. 63.9(e).................... Yes.......................................... Notification of performance
test.
Sec. 63.9(f).................... No........................................... POTW treatment plants do not
typically have visible
emissions.
Sec. 63.9(g).................... Yes.......................................... Additional notification
requirements for sources
with continuous emission
monitoring systems.
Sec. 63.9(h).................... Yes, except as noted......................... Notification of compliance
status when the source
becomes subject to subpart
VVV. See exceptions in Sec.
63.1591(b).
Sec. 63.9(i).................... Yes.......................................... Adjustments to time periods
or postmark deadlines or
submittal and review of
required communications.
Sec. 63.9(j).................... Yes.......................................... Change of information already
provided to the
Administrator.
Sec. 63.10...................... ............................................. Recordkeeping and reporting
requirements.
Sec. 63.10(a)................... Yes.......................................... Applicability of notification
and reporting requirements.
Sec. 63.10(b)(1)-(2)............ Yes, except as noted below................... General recordkeeping
requirements.
Sec. 63.10(b)(2)(i)............. No........................................... Recordkeeping for occurrence
and duration of startup and
shutdown.
Sec. 63.10(b)(2)(ii)............ No........................................... Recordkeeping for failure to
meet a standard, see Sec.
63.696.
Sec. 63.10(b)(2)(iii)........... Yes.......................................... Maintenance records.
Sec. 63.10(b)(2)(iv)............ No........................................... Actions taken to minimize
emissions during SSM.
Sec. 63.10(b)(2)(v)............. No........................................... Action taken to minimize
emissions during SSM.
Sec. 63.10(b)(2)(vi)............ Yes.......................................... Recordkeeping for CMS
malfunctions.
Sec. 63.10(b)(2)(vii)-(ix)...... Yes.......................................... Other CMS requirements.
Sec. 63.10(b)(3)................ No........................................... Recording requirement for
applicability determination.
Sec. 63.10(c)................... Yes, except as noted below................... Additional recordkeeping
requirements for sources
with continuous monitoring
systems.
Sec. 63.10(c)(7)................ No........................................... See Sec. 63.696(h) for
recordkeeping of (1) date,
time, and duration; (2)
listing of affected source
or equipment, and an
estimate of the tons per
year of each regulated
pollutant emitted over the
standard; and (3) actions to
minimize emissions and
correct the failure.
Sec. 63.10(c)(8)................ No........................................... See Sec. 63.696(h) for
recordkeeping of (1) date,
time, and duration; (2)
listing of affected source
or equipment, and an
estimate of the tons per
year of each regulated
pollutant emitted over the
standard; and (3) actions to
minimize emissions and
correct the failure.
Sec. 63.10(c)(15)............... No........................................... Use of SSM plan.
Sec. 63.10(d)................... Yes, except as noted below................... General reporting
requirements.
Sec. 63.10(d)(5)................ No........................................... See Sec. 63.697(b) for
malfunction reporting
requirements.
Sec. 63.10(e)................... Yes.......................................... Additional reporting
requirements for sources
with continuous monitoring
systems.
Sec. 63.10(f)................... Yes, except as noted......................... Waiver of recordkeeping and
reporting requirements.
Electronic reporting to the
EPA cannot be waived.
Sec. 63.11...................... Yes.......................................... Control device and equipment
leak work practice
requirements.
Sec. 63.11(a) and (b)........... Yes.......................................... If a new source uses flares
to comply with the
requirements of subpart VVV,
the requirements of Sec.
63.11 apply.
Sec. 63.11(c), (d) and (e)...... Yes.......................................... Alternative work practice for
equipment leaks.
[[Page 49533]]
Sec. 63.12...................... Yes.......................................... State authority and
designation.
Sec. 63.13...................... Yes.......................................... Addresses of State air
pollution control agencies
and EPA Regional Offices.
Sec. 63.14...................... Yes.......................................... Incorporation by reference.
Sec. 63.15...................... Yes.......................................... Availability of information
and confidentiality.
----------------------------------------------------------------------------------------------------------------
Table 2 to Subpart VVV of Part 63--Compliance Dates and Requirements
------------------------------------------------------------------------
And the owner or
If the construction/ Then the owner or operator must
reconstruction date is operator must comply achieve
with compliance
------------------------------------------------------------------------
Group 1 POTW:
(1) After December 27, 2016... (i) New source Upon initial
requirements in Sec. startup.
Sec. 63.1583(b);
63.1586(b) or (c);
and 63.1588 through
63.1591.
(2) After December 1, 1998 but (i) New source Upon initial
on or before December 27, requirements in Sec. startup through
2016. 63.1583(b) but October 26,
instead of complying 2020.
with both
requirements
(industrial user(s)
NESHAP and the POTW
standards in Sec.
Sec. 63.1586(b) or
(c)), you must comply
with the most
stringent
requirement\1\.
(ii) New source On or before
requirements in Sec. October 26,
Sec. 63.1586(b) or 2020.
(c); and 63.1588
through 63.1591.
(3) On or before December 1, (i) Existing source By the
1998. requirements in Sec. compliance date
Sec. 63.1583(a). specified in
the other
applicable
NESHAP.
(ii) Existing source On or before
requirements in Sec. October 26,
Sec. 63.1588 2018.
through 63.1591.
Group 2 POTW:
(4) After December 27, 2016... (i) New source Upon initial
requirements in Sec. startup.
Sec. 63.1586(b) or
(c); and 63.1588
through 63.1591.
(5) After December 1, 1998 but (i) New source Upon initial
on or before December 27, requirements in Sec. startup through
2016. 63.1586(b) or (c)\1\. October 26,
2020.
(ii) New source On or before
requirements in Sec. October 26,
Sec. 63.1586(b) or 2020.
(c); and 63.1588
through 63.1591.
(6) On or before December 1, (i) Existing source On or before
1998. requirements in Sec. October 26,
Sec. 63.1586(a); 2018.
and 63.1591(a).
------------------------------------------------------------------------
\1\ Note: This represents the new source requirements in the original
1999 NESHAP, which are applicable until October 26, 2020. Between
October 26, 2017 and October 26, 2020, you must transition to the new
requirements in Table 2 (2)(ii) and (5)(ii) for Group 1 and Group 2
POTW, respectively.
[FR Doc. 2017-23067 Filed 10-25-17; 8:45 am]
BILLING CODE 6560-50-P