National Emission Standards for Hazardous Air Pollutants for Area Sources: Polyvinyl Chloride and Copolymers Production, Primary Copper Smelting, Secondary Copper Smelting, and Primary Nonferrous Metals: Zinc, Cadmium, and Beryllium, 2930-2961 [E7-532]
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Federal Register / Vol. 72, No. 14 / Tuesday, January 23, 2007 / Rules and Regulations
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 63
[EPA–HQ–OAR–2006–0510; FRL–8257–4]
RIN 2060–AN45
National Emission Standards for
Hazardous Air Pollutants for Area
Sources: Polyvinyl Chloride and
Copolymers Production, Primary
Copper Smelting, Secondary Copper
Smelting, and Primary Nonferrous
Metals: Zinc, Cadmium, and Beryllium
Environmental Protection
Agency (EPA).
ACTION: Final rules.
AGENCY:
SUMMARY: EPA is issuing national
emission standards for hazardous air
pollutants (NESHAP) for four area
source categories. These final NESHAP
include emissions limits and/or work
practice standards that reflect the
generally available control technologies
(GACT) and/or management practices in
each of these area source categories.
DATES: These final rules are effective on
January 23, 2007. The incorporation by
reference of certain publications listed
in these rules is approved by the
Director of the Federal Register as of
January 23, 2007.
ADDRESSES: The EPA has established a
docket for this action under Docket ID
No. EPA–HQ–OAR–2006–0510. All
documents in the docket are listed in
the Federal Docket Management System
index at https://www.regulations.gov.
Although listed in the index, some
information is not publicly available,
e.g., confidential business information
or other information whose disclosure is
restricted by statute. Certain other
material, such as copyrighted material,
is not placed on the Internet and will be
publicly available only in hard copy
form. Publicly available docket
materials are available either
electronically through
www.regulations.gov or in hard copy at
the EPA Docket Center, Public Reading
Room, EPA West, Room 3334, 1301
Constitution Ave., NW., Washington,
DC. The Public Reading Room is open
from 8:30 a.m. to 4:30 p.m., Monday
through Friday, excluding legal
holidays. The telephone number for the
Public Reading Room is (202) 566–1744,
and the telephone number for the Air
Docket is (202) 566–1742.
FOR FURTHER INFORMATION CONTACT: Ms.
Sharon Nizich, U.S. EPA, Office of Air
Quality Planning and Standards, Sector
Policies and Programs Division, Metals
and Minerals Group (D243–02),
Research Triangle Park, North Carolina
27711, telephone number: (919) 541–
2825, fax number (919) 541–3207,
e-mail address: nizich.sharon@epa.gov.
SUPPLEMENTARY INFORMATION:
Outline
The information presented 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?
C. Judicial Review
II. Background Information for Final Area
Source Standards
NAICS
code 1
Category
Industry:
Polyvinyl chloride and copolymers production.
Primary copper smelting ......................
325211
331411
Secondary copper smelting .................
2 331423
Primary nonferrous metals—zinc, cadmium, and beryllium.
331419
Federal government ....................................
State/local/tribal government .......................
..................
..................
III. Summary of Final Rule and Changes
Since Proposal
A. NESHAP for Polyvinyl Chloride and
Copolymers Production Area Sources
B. NESHAP for Primary Copper Smelting
Area Sources
C. NESHAP for Secondary Copper
Smelting Area Sources
D. NESHAP for Primary Nonferrous
Metals—Zinc, Cadmium, and Beryllium
Area Sources
IV. Summary of Comments and Responses
A. Existing Area Source Facilities
B. Part 63 General Provisions
C. Primary Copper Smelters
D. Primary Zinc Smelters
E. Basis for Area Source Standards
F. Compliance Date
V. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory
Planning and Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
G. Executive Order 13045: Protection of
Children From Environmental Health
and Safety Risks
H. Executive Order 13211: Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use
I. National Technology Transfer
Advancement Act
J. Congressional Review Act
I. General Information
A. Does this action apply to me?
The regulated categories and entities
potentially affected by these final
standards include:
Examples of regulated entities
Area source facilities that polymerize vinyl chloride monomer to produce vinyl chloride
and/or copolymer products.
Area source facilities that produce copper from copper sulfide ore concentrates using
pyrometallurgical techniques.
Area source facilities that process copper scrap in a blast furnace and converter or
use another pyrometallurgical purification process to produce anode copper from
copper scrap, including low-grade copper scrap.
Area source facilities that produce zinc, zinc oxide, cadmium, or cadmium oxide from
zinc sulfide ore concentrates using pyrometallurgical techniques and area source
facilities that produce beryllium metal, alloy, or oxide from beryllium ore.
Not affected.
Not affected.
1 North
American Industry Classification System.
final rule applies only to secondary copper smelters and does not apply to copper, brass, and bronze ingot makers or remelters that may
also be included under this NAICS code.
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2 This
This table is not intended to be
exhaustive, but rather provides a guide
for readers regarding entities likely to be
affected by this action. To determine
whether your facility is regulated by this
action, you should examine the
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applicability criteria in 40 CFR 63.11140
of subpart DDDDDD (NESHAP for
Polyvinyl Chloride and Copolymers
Production Area Sources), 40 CFR
63.11146 of subpart EEEEEE (NESHAP
for Primary Copper Smelting Area
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Sources), 40 CFR 63.11153 of subpart
FFFFFF (NESHAP for Secondary
Copper Smelting Area Sources), or 40
CFR 63.11160 of subpart GGGGGG
(NESHAP for Primary Nonferrous
Metals—Zinc, Cadmium, and Beryllium
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Area Sources). If you have any questions
regarding the applicability of this action
to a particular entity, consult either the
air permit authority for the entity or
your EPA regional representative as
listed in 40 CFR 63.13 of subpart A
(General Provisions).
B. Where can I get a copy of this
document?
In addition to being available in the
docket, an electronic copy of this final
action will also be available on the
Worldwide Web (WWW) through the
Technology Transfer Network (TTN).
Following signature, a copy of this final
action will be posted on the TTN’s
policy and guidance page for newly
proposed or promulgated rules at the
following address: https://www.epa.gov/
ttn/oarpg/. The TTN provides
information and technology exchange in
various areas of air pollution control.
C. Judicial Review
Under section 307(b)(1) of the Clean
Air Act (CAA), judicial review of these
final rules is available only by filing a
petition for review in the U.S. Court of
Appeals for the District of Columbia
Circuit by March 26, 2007. Under
section 307(d)(7)(B) of the CAA, only an
objection to these final rules that was
raised with reasonable specificity
during the period for public comment
can be raised during judicial review.
Moreover, under section 307(b)(2) of the
CAA, the requirements established by
these final rules may not be challenged
separately in any civil or criminal
proceedings brought by EPA to enforce
these requirements.
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II. Background Information for Final
Area Source Standards
Sections 112(c)(3) and 112(k)(3)(B) of
the CAA instruct EPA to identify not
less than 30 HAP which, as a result of
emissions from area sources, present the
greatest threat to public health in the
largest number of urban areas, and to
list sufficient area source categories 1 to
ensure that sources representing 90
percent or more of the emissions of each
of the 30 listed HAP (‘‘area source
HAP’’) are subject to regulation. Sierra
Club sued EPA, alleging a failure to
complete standards for the source
categories listed pursuant to CAA
sections 112(c)(3) and (k)(3)(B) within
the timeframe specified by the statute.
1 Under section 112(a) of the Clean Air Act, an
area source is defined as a stationary source that is
not a major source. A major source is defined as a
stationary source or a group of stationary sources
located within a contiguous area and under
common control that emits or has the potential to
emit considering controls, in the aggregate, 10 tons
per year or more of any HAP or 25 tons per year
or more of any combination of HAP.
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See Sierra Club v. Johnston, No. 01–
1537, (D.D.C.). On March 31, 2006, the
court issued an order requiring EPA to
promulgate standards under CAA
section 112(d) for those area source
categories listed pursuant to CAA
sections 112(c)(3) and (k)(3)(B).
Among other things, the order
requires that, by December 15, 2006,
EPA complete standards for four of the
listed area source categories. On October
6, 2006 (71 FR 59302) we proposed
NESHAP for the following four listed
area source categories that we have
selected to meet the December 15, 2006
deadline: (1) Primary Copper Smelting;
(2) Secondary Copper Smelting; (3)
Polyvinyl Chloride and Copolymers
Production; and (4) Primary Nonferrous
Metals—Zinc, Cadmium, and Beryllium.
These final NESHAP complete the
required regulatory action for four area
source categories.
Under CAA section 112(d)(5), the
Administrator may, in lieu of standards
requiring maximum achievable control
technology (MACT) under section
112(d)(2), elect to promulgate standards
or requirements for area sources ‘‘which
provide for the use of generally
available control technologies or
management practices by such sources
to reduce emissions of hazardous air
pollutants.’’ Under section 112(d)(5), the
Administrator has the discretion to use
generally available control technology
(GACT) or management practices in lieu
of MACT. As mentioned in the
proposed NESHAP for these four area
source categories, we have decided not
to issue MACT standards and concluded
that requirements that provide for the
use of GACT or generally available
management practices are appropriate
for these four source categories (71 FR
59302, 59304, October 6, 2006).
III. Summary of Final Rules and
Changes Since Proposal
A. NESHAP for Polyvinyl Chloride and
Copolymers Production Area Sources
As proposed, we are adopting the
requirements in 40 CFR part 61, subpart
F that apply to polyvinyl chloride (PVC)
plants as the NESHAP for the Polyvinyl
Chloride and Copolymer Production
area source category. The only change
since the proposed rule is that this final
rule does not adopt either the startup,
shutdown, and malfunction (SSM)
requirements in 40 CFR 63.6(e)(3) or the
preconstruction notification
requirements in 40 CFR 63.5. As
discussed in more detail in section IV.B
of this preamble, under the construct of
part 61 standards, sources must comply
with the standards at all times,
including periods of SSM. Because in
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this final rule we are adopting the part
61 standards for PVC plants as the area
source standard, separate requirements
governing SSM are not necessary. We
have also determined that the
preconstruction notification
requirements at 40 CFR 63.5 are not
necessary because a comparable
preconstruction notification is already
required under the part 61 General
Provisions (40 CFR part 61, subpart A),
which apply to this NESHAP.
1. Applicability and Compliance Dates
This final rule applies to both new
and existing PVC and copolymer plants
that are area sources of HAP. The owner
or operator of an existing source must
comply with all the requirements of this
area source NESHAP by January 23,
2007. The owner or operator of a new
source must comply with this area
source NESHAP by January 23, 2007 or
at startup, whichever is later.
2. Emissions Limits and Work Practice
Standards
The Polyvinyl Chloride and
Copolymers Production area source
category was listed for its contribution
to the emissions of the area source HAP
vinyl chloride. As proposed, we are
adopting the requirements in 40 CFR
part 61, subpart F that are applicable to
PVC plants as the NESHAP for the
Polyvinyl Chloride and Copolymer
Production area source category. These
requirements in subpart F include
numerical emissions limits for reactors;
strippers; mixing, weighing, and
holding containers; monomer recovery
systems; emissions sources following
the stripper(s); and reactors used as
strippers. In addition, they include
emissions limits and work practice
requirements that apply to discharges
from manual vent valves on a PVC
reactor and relief valves in vinyl
chloride service, fugitive emissions
sources, and equipment leaks. Subpart F
also requires a new or existing source to
comply with the requirements at 40 CFR
part 61, subpart V for the control of
equipment leaks. As discussed in the
proposal preamble, we have determined
that these requirements represent GACT
for sources in this area source category.
3. Compliance Requirements
We are including in this NESHAP the
monitoring, testing, recordkeeping, and
reporting requirements in 40 CFR part
61, subpart F. This final NESHAP
requires a vinyl chloride continuous
emissions monitoring system (CEMS)
for the regulated emissions sources
(except for sources following the
stripper) and for any control system to
which reactor emissions or fugitive
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emissions must be ducted. Plants using
a stripper to comply with this NESHAP
must also determine the daily average
vinyl chloride concentration for each
type of resin. The owner or operator
must submit quarterly reports
containing information on emissions or
resin concentrations that exceed the
applicable limits. Records are required
to demonstrate compliance, including a
daily operating log for each reactor.
Plants are required to comply with the
testing, monitoring, recordkeeping, and
reporting requirements in the part 61
General Provisions (40 CFR part 61,
subpart A). For the reasons discussed in
sections III.A and IV.B of this preamble,
this final NESHAP does not require that
the owner or operator comply with the
SSM requirements at 40 CFR 63.6(e)(3)
and the preconstruction notification
requirements at 40 CFR 63.5.
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4. Exemption From Title V Permit
Requirements
Section 502(a) of the CAA provides
that EPA may exempt one or more area
sources from the requirements of title V
if EPA finds that compliance with such
requirements is ‘‘impracticable,
infeasible, or unnecessarily
burdensome’’ on such area sources. EPA
must determine whether to exempt an
area source from title V at the time we
issue the relevant section 112 standard
(40 CFR 70.3(b)(2)). For the reasons
discussed in the preamble to the
proposed rule, we are exempting PVC
and copolymers production area sources
from the requirements of title V. PVC
and copolymers production area sources
are not required to obtain title V permits
solely as a function of being the subject
of the NESHAP; however, if they were
otherwise required to obtain title V
permits, such requirement(s) would not
be affected by this exemption. We
received no comments on our proposal
to exempt PVC and copolymer
production area sources from the
requirements of title V.
B. NESHAP for Primary Copper
Smelting Area Sources
The Primary Copper Smelting area
source category was listed for its
contribution to the emissions of the area
source HAP arsenic, cadmium,
chromium, lead, and nickel. As
discussed in more detail in section IV.C
of this preamble, the major change since
the proposed rule is that we established
a subcategory of primary copper
smelters that use the batch converting
technology and developed separate
standards for this subcategory. At the
time of the proposed rule, we were not
aware of any area sources using the
batch converting technology. Since
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then, we received comments indicating
that there may or will be primary copper
smelting area sources that use the batch
converting technology. Because batch
technology is quite different from the
continuous converting technology we
used to develop the proposed standards
for the Primary Copper Smelting area
source category in terms of process
operation, emissions points, and
achievable levels of control, we believe
that the proposed standards do not
represent GACT for existing primary
copper smelting area sources that use
the batch converting technology.
Accordingly, we developed a separate
standard for existing sources that use
the batch converting technology, and we
developed that standard based on the
title V permit of one batch converting
facility that we have determined to be
effectively controlling its HAP
emissions by complying with its permit
terms and conditions.
In response to comments, we also
made several changes to the proposed
rule for primary copper smelters that do
not use the batch converting technology.
As explained in the preamble to the
proposed rule, we have determined that
certain terms and conditions in the title
V permit of the only area source primary
smelter of which we are aware provide
effective control of HAP emissions and
represent GACT for these sources. We
made changes in the proposed rule to
more accurately capture the relevant
terms and conditions in this existing
area source’s title V permit. Specifically,
we clarified that capture and control
systems are not required for anode
casting and holding operations; that the
sampler required for existing sources is
a continuous PM sampler; that the
emissions limit is expressed as PM less
than 10 microns in aerodynamic
diameter (PM10) rather than PM; and
that a single gas collection system could
serve multiple process vessels.
As discussed in section IV.B of this
preamble, we allow new and existing
sources to comply with either the SSM
requirements in 40 CFR 63.6(e)(3) or the
detailed SSM requirements in the final
rule that were developed from the
existing sources’ title V permits, which
are substantially equivalent to the SSM
requirements in 40 CFR part 63.
1. Applicability and Compliance Dates
This final rule applies to each new or
existing primary copper smelter that is
an area source of HAP. The owner or
operator of an existing affected source
must comply by January 23, 2007. The
owner or operator of a new affected
source must comply by January 23, 2007
or upon initial startup, whichever is
later. An affected source is new if
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construction or reconstruction of the
affected source was commenced on or
after October 6, 2006.
2. Emissions Limits and Work Practice
Standards
As previously mentioned, we have
developed separate standards for
existing sources that use the batch
converting technology and for those that
do not. However, the standards for new
sources apply to all new area source
primary copper smelters irrespective of
the converting technology utilized.
Under this final rule, the owner or
operator of an existing area source using
any converting technology is required to
control HAP emissions from copper
concentrate drying, copper concentrate
smelting, copper matte drying and
grinding, copper matte converting, and
copper anode refining. As discussed in
the proposal preamble, we are using PM
as a surrogate for HAP metals. Gases and
fumes generated by these processes
must be captured and vented through
one or more PM control devices. For
existing primary copper smelters that do
not use the batch converting process,
the total emissions of PM10 from the
captured gas streams from all of these
processes is limited to 89.5 pounds per
hour (lb/hr) as determined on a 24-hour
average basis.
For existing primary copper smelters
using the batch converting technology,
the exhaust gases from each smelter
vessel and each converter must be
collected and sent to a PM control
device and to a sulfuric acid plant. A
secondary gas collection system must be
installed on each smelting vessel and
converter, and PM emissions from the
secondary capture and control system
must not exceed 0.02 grains per dry
standard cubic foot (gr/dscf). The PM
emissions from each copper concentrate
dryer must not exceed 0.022 gr/dscf.
Similarly, the owner or operator of a
new area source using any converting
technology must control HAP emissions
from all primary copper smelting
processes, including but not limited to
those processes mentioned above that
are applicable to the new source’s
smelter design. Gases and fumes
generated by these processes at a new
source must be captured and vented
through one or more PM control
devices. We are requiring a new source
to achieve a facility input-based
emissions rate for total PM no greater
than a daily (24-hour) average of 0.6
pounds per ton (lb/ton) of copper
concentrate feed charged to the smelting
vessel.
This final rule for new area source
primary copper smelters also requires a
secondary gas system for each smelting
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vessel and converting vessel that
collects the gases and fumes released
during the molten material transfer
operations and conveys the collected
gas stream to a control device. Capture
systems that collect gas and fumes and
convey them to a control device also are
required for operations in the anode
refining. These capture and control
requirements apply to all new and
existing area sources using any copper
smelting technology.
3. Compliance Requirements
In this final rule, we have adopted the
testing, monitoring, operation and
maintenance, recordkeeping, and
reporting requirements for PM
emissions that are in the title V permits
of the existing area source smelters.
Compliance with the emissions limit for
existing area sources not using the batch
converting technology is based on the
daily average PM10 emissions measured
by a continuous PM sampler. For
smelters using the batch conversion
technology, compliance is based on
performance tests at least every 2.5
years and continuous monitoring using
continuous opacity monitoring systems
(COMS) for electrostatic precipitators
and bag leak detection systems for
baghouses.
The operation and maintenance
requirements in this final rule for
existing sources using any converting
technology are based on the existing
sources’ title V permits. At all times, the
owner or operator must to the extent
practicable, maintain and operate any
affected source, including associated air
pollution control equipment, in a
manner consistent with good air
pollution control practice for
minimizing emissions. In addition, all
pollution control equipment must be
installed, maintained, and operated
properly. Instructions from the vendor
or established maintenance practices
that maximize pollution control must be
followed. Maintenance records must be
made available to the permitting
authority upon request.
This final rule allows any new or
existing source to meet the SSM
requirements specified in this final rule
or the SSM requirements in 40 CFR
63.6(e)(3). The SSM requirements that
are specified in this final rule were
developed from the existing sources’
title V permit requirements, and we
believe these requirements are equally
applicable to new and existing area
sources irrespective of the converting
technology used. Sources may
nevertheless choose to comply with the
SSM provisions in 40 CFR 63.6(e)(3), in
lieu of the SSM requirements specified
in this final rule. The SSM provisions in
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this final rule require that all
malfunctions be reported within two
working days of the event. The report
must include a description of the
malfunction, steps taken to mitigate
emissions, and corrective actions taken.
In addition, the owner or operator must
show through signed contemporaneous
logs or other relevant evidence that: (1)
A malfunction occurred and the
probable cause can be identified, (2) the
facility was being operated properly at
the time the malfunction occurred, and
(3) all reasonable steps were taken to
minimize emissions that exceeded the
emission standards. A malfunction or
emergency does not include events
caused by improperly designed
equipment, lack of preventative
maintenance, careless or improper
operation, or operator error.
The owner or operator of an existing
area source using any copper smelting
technology must comply with
notification requirements in 40 CFR
63.9 of the General Provisions (40 CFR
part 63, subpart A). In the notification
of compliance status required in 40 CFR
63.9(h), the owner or operator may
certify initial compliance with the
emissions limit based on monitoring
data collected during a previous
compliance test. The owner or operator
also must certify initial compliance with
the work practice standards.
The owner or operator of a new
primary copper smelter must install,
operate, and maintain a CEMS to
measure and record PM concentrations
and gas stream flow rates for each
emissions source subject to the
emissions limit. The standard requires
that the PM CEMS meet EPA
Performance Specification 11 (40 CFR
part 60, appendix B). A device to
measure and record the weight of the
copper concentrate feed charged to the
smelting furnace each day also is
required. The owner or operator must
continuously monitor PM emissions,
determine and record the daily (24hour) value for each day, and calculate
and record the daily average pounds of
total PM per ton of copper concentrate
feed charged to the smelting furnace. A
monthly summary report of the daily
averages of PM per ton of copper
concentrate feed charged to the smelting
vessel also is required. All notification,
monitoring, testing, operation and
maintenance, recordkeeping, and
reporting requirements of the part 63
General Provisions apply to the owner
or operator of a new source. This final
rule allows a new source to meet the
specific SSM requirements that were
developed from the title V permit
requirements for existing sources or the
SSM requirements in 40 CFR 63.6(e)(3).
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C. NESHAP for Secondary Copper
Smelting Area Sources
We did not receive any comments on
our determination of GACT for
secondary copper smelters, and we are
promulgating the standard as proposed
without any changes.
1. Applicability and Compliance Dates
This final rule applies to each new
secondary copper smelter that is an area
source of HAP. The owner or operator
of a new affected source is required to
comply by January 23, 2007 or upon
initial startup, whichever is later.
2. Emissions Limit and Work Practice
Standards
This final rule does not include
requirements for existing area sources of
secondary copper smelters. As we
explained in the preamble to the
proposed rule, currently there are no
existing major or area sources of
secondary copper smelters. Therefore,
there is not any, nor would there ever
be, an existing secondary copper smelter
that would be subject to this rule. In this
circumstance, we are not issuing
standards for existing area sources of
secondary copper smelters. However,
this final rule contains requirements for
new area sources of secondary copper
smelters. The Secondary Copper
Smelting area source category was listed
for its contribution to the emissions of
the area source HAP cadmium, lead and
dioxin. We have established
requirements for new sources in this
category to ensure that any potential
emission of these area source HAP from
future secondary copper smelting area
sources will be appropriately controlled.
We are requiring that the owner or
operator of any new secondary copper
smelter operate a capture and control
system for PM emissions from any
process operation that melts copper
scrap, alloys, or other metals or that
processes molten material. Emissions of
PM from the control device must not
exceed 0.002 gr/dscf. The owner or
operator must also prepare and follow a
written plan for the selection,
inspection, and pretreatment of copper
scrap to minimize, to the extent
practicable, the amount of oil and
plastics in the scrap that is charged to
smelting or melting furnaces. As we
explained in the proposal preamble, we
are using PM as a surrogate for
establishing standards for metal HAP,
which are cadmium and lead in this
case. The United Nations Environmental
Programme (UNEP) has also
recommended using control devices
with high efficiency PM removal to
reduce dioxin emissions. The pollution
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prevention measure described above
(i.e., presorting and pretreating
materials) is another UNEP
recommendation for reducing dioxin
emissions. We have determined that
these requirements represent GACT for
new sources of secondary copper
smelters and requested comments on
this determination in the proposed rule.
We did not receive any comments on
this determination.
3. Compliance Requirements
Fabric filters (baghouses) are expected
to be needed to meet the NESHAP
emissions limit. Consequently, the
monitoring requirements include bag
leak detection systems when baghouses
are used. For additional information on
bag leak detection systems that operate
on the triboelectric effect, see ‘‘Fabric
Filter Bag Leak Detection Guidance’’,
U.S. Environmental Protection Agency,
Office of Air Quality Planning and
Standards, September 1997, EPA–454/
R–98–015, NTIS publication number
PB98164676. This document is available
from the National Technical Information
Service (NTIS), 5385 Port Royal Road,
Springfield, VA 22161. The owner or
operator must prepare a written plan for
the selection, inspection, and
pretreatment of copper scrap and keep
records to document conformance with
the requirements in the written plan. If
a control device other than a baghouse
is used, the owner or operator must
submit a monitoring plan to the
permitting authority for approval. The
monitoring plan must include
performance test results showing
compliance with the PM emissions
limit, a plan for operation and
maintenance of the control device, a list
of operating parameters that will be
monitored, and operating parameter
limits that were established during the
performance test.
The owner or operator must conduct
a performance test to demonstrate initial
compliance with the PM emissions limit
and report the results in the notification
of compliance status required by 40 CFR
63.9(h) of the General Provisions. If a
baghouse is used, the PM concentration
is to be determined using EPA Method
5 (for negative pressure baghouses) or
Method 5D (for positive pressure
baghouses) in 40 CFR part 60, appendix
A. Repeat performance tests are required
every 5 years to demonstrate
compliance with the PM emissions
limit. All requirements of the part 63
General Provisions apply to the owner
or operator of a new source, including
the notification, monitoring, testing,
operation and maintenance, SSM,
recordkeeping, and reporting
requirements.
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D. NESHAP for Primary Nonferrous
Metals—Zinc, Cadmium, and Beryllium
Area Sources
1. NESHAP for Primary Zinc Production
In this final rule, we have adopted a
limit in grains per dry standard cubic
foot (gr/dscf) for certain melting
furnaces at existing zinc production area
sources in addition to the proposed
pound per hour (lb/hr) limits for these
furnaces at existing sources. This gr/dscf
limit is the limit that we proposed for
the same furnaces at new sources. Both
the gr/dscf limit and the lb/hr limits
reflect the level of emission control that
can be achieved based on the
technology we identified as GACT for
these furnaces (i.e., a well-operated and
well-maintained baghouse). However,
whereas the lb/hr limits were based on
the specific operations at the two
existing sources of which we are aware,
the gr/dscf emission limit is not
operation specific and can apply to
these furnaces at any primary zinc
production area source irrespective of
its operation. For this reason, we
proposed this gr/dscf emissions limit for
these furnaces at new sources. In this
final rule, we similarly allow an existing
source to meet this gr/dscf limit for
these furnaces. This final rule provides
existing sources the option of meeting
either the lb/hr limits or the gr/dscf
limit for these furnaces. We believe that
including both the lb/hr and gr/dscf
limits in this final rule will ensure
effective control of these furnaces at all
existing primary zinc production area
sources in the event that there are
facilities other than the two we know
and with very different operations from
the two known sources.
In addition, as discussed in section
IV.B of this preamble, we allow new and
existing sources to comply with either
the SSM requirements in 40 CFR
63.6(e)(3) or with the detailed SSM
requirements in the final rule that were
developed from the existing sources’
title V permits, which are substantially
equivalent to the SSM requirements in
part 63.
Applicability and compliance dates.
This final rule applies to each new or
existing primary zinc production facility
that is an area source of HAP. The
owner or operator of an existing affected
source must comply by January 23,
2007. The owner or operator of a new
affected source must comply by January
23, 2007 or upon initial startup,
whichever is later.
Emissions limits and work practice
standards. Primary zinc production
facilities were included as part of the
Primary Nonferrous Metals area source
category due to their contributions to
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the emissions of the area source HAP
arsenic, cadmium, lead, manganese, and
nickel, all of which are metal HAP. As
we mentioned in the proposal preamble,
cadmium is produced as a by-product of
zinc smelting processes. There are no
primary cadmium smelters in the
United States. Accordingly, the
requirements for area sources of zinc
production in this final rule also
address emissions associated with any
cadmium production at these zinc
production facilities.
As previously mentioned, we are
using PM as a surrogate for establishing
standards for metal HAP. Under this
final rule, the owner or operator of an
area source of zinc production is
required to exhaust roaster off-gases to
PM removal equipment and a sulfuric
acid plant. Bypassing the sulfuric acid
plant during charging of the roaster is
prohibited.
Emissions limits apply to the different
types of melting furnaces at primary
zinc production facilities. For existing
sources, this NESHAP limit PM
emissions to 0.93 lb/hr for zinc cathode
melting furnaces; 0.1 lb/hr for furnaces
that melt zinc dust, chips, and offspecification zinc materials; and 0.228
lb/hr for the combined exhaust from
furnaces that melt zinc scrap and alloys.
As an alternative to the lb/hr limits for
these furnaces at existing sources, the
owner or operator may elect to meet a
limit of 0.005 gr/dscf. For new sources,
the PM limit is 0.005 gr/dscf for the
furnaces mentioned above. Other PM
limits are 0.014 gr/dscf for anode casting
furnaces and 0.015 gr/dscf for cadmium
melting furnaces at new and existing
sources.
Emissions limits also apply to any
sintering machine at a new or existing
area source facility. If there is a sintering
machine, the owner or operator must
comply with the PM limit at 40 CFR
60.172 and the opacity limit at 40 CFR
60.174(a) of the new source performance
standard (NSPS) for primary zinc
smelters (40 CFR part 60, subpart Q).
Compliance requirements. We are
adopting for existing area sources
certain monitoring, recordkeeping, and
reporting requirements in the title V
permits of the two existing facilities that
relate to PM emissions control. The
owner or operator of an existing area
source must monitor baghouse pressure
drop, perform routine baghouse
maintenance, and keep records to
document compliance. In addition, we
are requiring repeat performance tests
(at least once every 5 years) for existing
sources. This final rule also requires a
continuous opacity monitoring system
(COMS) for any sintering machine in
accordance with 40 CFR 60.175.
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The owner or operator of an existing
area source must comply with initial
notification requirements in 40 CFR
63.9 of the General Provisions. In the
notification of compliance status
required by 40 CFR 63.9(h), the owner
or operator may certify initial
compliance with the HAP emissions
limits based on the results of a PM
performance test for each of the
regulated emissions sources conducted
within the past 5 years. The owner or
operator must also certify initial
compliance with the work practice
standards.
If an existing source has not
conducted a performance test to
demonstrate compliance with the
emissions limits for a furnace, the
facility must conduct a test according to
the requirements at 40 CFR 63.7 using
EPA Method 5 (40 CFR part 60,
appendix A) to determine the PM
concentration or an alternative method
previously approved by the permitting
authority. For a sintering machine, the
owner or operator must conduct a
performance test according to the
procedures in 40 CFR 60.176(b) using
EPA Method 5 to determine the PM
concentration and EPA Method 9 (40
CFR part 60, appendix B) to determine
the opacity of emissions.
The operation and maintenance
requirements in the final rule for
existing sources are based on the
sources’ title V permits. The owner or
operator must maintain all equipment
covered under the subpart in such a
manner that the performance or
operation of the equipment does not
cause a deviation from the applicable
requirements. A maintenance record
must be kept for each item of air
pollution control equipment. At a
minimum, this record must show the
dates of performing maintenance and
the nature of preventative maintenance
activities.
This final rule allows any existing
source to meet the specific SSM
requirements that were developed from
the title V permit requirements for
existing sources or the SSM
requirements in 40 CFR 63.6(e)(3). The
specific SSM provisions in this final
rule require that all malfunctions be
reported within two working days of the
event. The report must include a
description of the malfunction, steps
taken to mitigate emissions, and
corrective actions taken. In addition, the
owner or operator must show through
signed contemporaneous logs or other
relevant evidence that: (1) A
malfunction occurred and the probable
cause can be identified, (2) the facility
was being operated properly at the time
the malfunction occurred, and (3) all
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reasonable steps were taken to minimize
emissions that exceeded the emission
standards. A malfunction or emergency
does not include events caused by
improperly designed equipment, lack of
preventative maintenance, careless or
improper operation, or operator error.
As required in the existing permits,
the owner or operator must submit a
notification to the permitting authority
of any deviation from the requirements
of this final NESHAP. The notification
must describe the probable cause of the
deviation and any corrective actions or
preventative measures taken. Existing
facilities are also required to submit
semiannual monitoring reports which
clearly describe any deviations. Records
of baghouse maintenance, all required
monitoring data, and support
information also are required. The
owner or operator of an existing area
source must also comply with the
notification requirements in 40 CFR
63.9 of the General Provisions.
The owner or operator of a new area
source is required to install and operate
a bag leak detection system for each
baghouse used to comply with a PM
emissions limit. For additional
information on bag leak detection
systems that operate on the triboelectric
effect, see ‘‘Fabric Filter Bag Leak
Detection Guidance’’, U.S.
Environmental Protection Agency,
Office of Air Quality Planning and
Standards, September 1997, EPA–454/
R–98–015, NTIS publication number
PB98164676. This document is available
from the National Technical Information
Service (NTIS), 5385 Port Royal Road,
Springfield, VA 22161. In addition, we
are requiring repeat PM performance
tests (once every 5 years) for each
furnace at a new source. The owner or
operator must also install, operate, and
maintain a COMS for each sintering
machine according to EPA Performance
Specification 1 (40 CFR part 60,
appendix B).
The owner or operator of a new
affected source must demonstrate initial
compliance with the applicable
emissions limits by conducting a
performance test according to the
requirements at 40 CFR 63.7 and using
EPA 5 or 5D (40 CFR part 60, appendix
A), as applicable, to determine the PM
concentration. An initial performance
test is also required for a sintering
machine according to the methods and
procedures in 40 CFR 60.176(b). All of
the notification, testing, monitoring,
operation and maintenance,
recordkeeping, and reporting
requirements of the part 63 General
Provisions apply to a new area source.
This final rule allows a new source to
meet the specific SSM requirements in
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2935
this final rule or the SSM requirements
in 40 CFR 63.6(e)(3).
2. NESHAP for Primary Beryllium
Production Area Sources
The only change since proposal is that
this final rule does not adopt the SSM
requirements in 40 CFR 63.6(e)(3) and
the preconstruction notification
requirements in 40 CFR 63.5. As
discussed in more detail in section IV.B
of this preamble, we have determined
that the SSM requirements are not
necessary for standards under part 61
that must be met at all times, and the
preconstruction notification is already
required under the part 61 General
Provisions.
Applicability and compliance dates.
For this final rule, we are adopting all
of the requirements in the National
Emission Standard for Beryllium at 40
CFR part 61, subpart C. The owner or
operator of an existing area source must
comply with this NESHAP by January
23, 2007. The owner or operator of a
new area source must comply by
January 23, 2007 or at startup,
whichever is later.
Emissions limits. Primary beryllium
production facilities were included as
part of the Primary Nonferrous Metals
area source category due to their
contributions to the emissions of the
area source HAP arsenic, cadmium,
lead, manganese, and nickel, all of
which are metal HAP. As discussed in
the proposal preamble, we are using
beryllium as a surrogate for HAP metals.
We are adopting the 40 CFR part 61,
subpart C standard as the requirements
for both new and existing primary
beryllium production facilities in this
final rule. The part 61, subpart C
standard limits emissions from
extraction plants (i.e., primary
beryllium production facilities) to 10
grams (0.022 lb) of beryllium over a 24hour period. Alternatively, the owner or
operator of a beryllium production
facility may request to meet an ambient
concentration limit instead of the
emissions limit. As discussed in the
preamble to the proposed rule, the part
61 standard is highly effective in
controlling PM and metal HAP
emissions from the only existing
beryllium production facility known to
us at the time of the proposal. We have
determined that these requirements
reflect GACT for area sources of
beryllium production. We did not
receive any comments on this
determination.
Compliance requirements. This final
rule requires the owner or operator to
comply with the testing, monitoring,
recordkeeping, and reporting
requirements in 40 CFR part 61, subpart
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C. An owner or operator subject to the
ambient concentration limit must
operate air sampling sites to
continuously monitor the
concentrations of beryllium in the
ambient air according to an EPAapproved plan.
The owner or operator must comply
with recordkeeping requirements in 40
CFR part 61, subpart C, as well as the
testing, monitoring, recordkeeping, and
reporting requirements in the part 61
General Provisions in 40 CFR part 61,
subpart A. For the reasons discussed in
section IV.B of this preamble, this final
rule does not require that the owner or
operator comply with the requirements
for SSM plans and reports in 40 CFR
63.6(e)(3) or the preconstruction
notification requirements in 40 CFR
63.5.
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IV. Summary of Comments and
Responses
A. Existing Area Source Facilities
At proposal, we stated that we did not
know of any existing sources in the
Polyvinyl Chloride and Copolymer area
source category, and we requested
comments on whether there are or ever
will be any area sources in this area
source category. We also stated that
currently there is only one area source
of primary copper production in
operation in the United States and that
there are no primary beryllium
production area sources.
Comment: One commenter informed
us of an area source PVC plant in
Alabama. In addition, two commenters
stated that there are a few (at least three)
PVC plants that they believe may
qualify as area sources. According to the
commenters, these were once major
sources that have reduced HAP
emissions significantly or that are
currently shut down but are expected to
start up again with significantly less
emissions than from previous
operations as major sources. The
commenters requested that EPA clarify
the meaning of ‘‘potential to emit’’ in its
definition of an ‘‘area source’’ in the
proposed rule, as well as the proposed
rule’s applicability to plants that have
obtained or, for the ones that are not
currently operating, will obtain permits
that limit emissions to levels below the
major source thresholds. In addition, the
commenters requested clarification of
the proposed rule’s applicability to PVC
plants co-located at chemical complexes
that are major sources.
One commenter notified us of an area
source primary beryllium plant in Utah.
The commenter sought clarification of
the proposed rule’s applicability to a
primary beryllium plant that is a major
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Jkt 211001
source because of perchloroethylene
emissions and that may become an area
source in the future by eliminating the
use of perchloroethylene.
We also received comments that there
are two operating primary copper
smelters that are area sources rather
than just one, as EPA stated in the
proposed rule. The company operating
this second source reported that it was
an area source (synthetic minor) based
on a determination by the permitting
authority. The company also stated that
it is planning to restart a primary copper
smelter in Texas that has been
shutdown and under ‘‘care and
maintenance’’ for several years. This
facility will incorporate feedstock
limitations to remain below major
source thresholds, and the company
expects that this facility will qualify as
an area source when the renewed
permits are issued. The commenter
sought clarification of the applicability
of the proposed rule to the two primary
copper smelters described above.
Response: Section 112(a) of the CAA
defines the terms ‘‘major source’’ and
‘‘area source.’’ An ‘‘area source’’ is
defined as any stationary source that is
not a major source. In the proposed rule,
we included a definition for ‘‘area
source’’ and that definition attempted to
summarize the statutory definitions of
‘‘major source’’ and ‘‘area source.’’
Commenters sought clarification of the
meaning of the term ‘‘potential to emit’’
contained in the proposed definition of
‘‘area source.’’ Based on the comment, it
appears that the proposed definition of
‘‘area source’’ has caused confusion.
Because the proposed definition of
‘‘area source’’ was merely intended to
summarize the statutory definitions of
‘‘major source’’ and ‘‘area source’’ and is
redundant of the definition of ‘‘area
source’’ contained in the General
Provisions (40 CFR part 63, subpart A),
we have decided not to finalize the
proposed ‘‘area source’’ definition.
Instead, as noted in the NESHAP for
each of these four area source categories,
the definitions of ‘‘major source,’’ ‘‘area
source,’’ and ‘‘potential to emit’’ in 40
CFR 63.2 apply to this final rule.2 To the
2 In 1995, the Court of Appeals for the District of
Columbia Circuit reviewed the definition of
‘‘potential to emit’’ (PTE) contained in 40 CFR in
40 CFR 63.2 (National Mining Ass’n v. EPA, 59 F.3d
1351 (D.C. Cir. 1995)). In July 2005, the D.C. Circuit
remanded the definition to EPA to the extent the
definition required that physical or operational
limitations be ‘‘federally enforceable’’ (National
Mining Ass’n v. EPA, 59 F.3d 1351 (D.C. Cir. 1995)).
The court did not vacate the 40 CFR part 63
regulations and therefore the definition of
‘‘potential to emit’’ in 40 CFR part 63 remains in
place. EPA is currently in the process of developing
a proposed rule that responds to the court’s remand.
EPA has a transitional policy that relates to PTE.
See ‘‘Options for Limiting the Potential to Emit
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extent the commenters have questions
as to whether their facility is a major
source or an area source, EPA cannot
answer these site-specific applicability
questions in the context of this national
rulemaking. We refer the commenters to
the definitions of ‘‘major source,’’ ‘‘area
source,’’ and ‘‘potential to emit’’ found
in 40 CFR 63.2, and recommend that the
commenters consult with the relevant
permitting authority or submit a request
for an applicability determination to the
EPA regional office in the region where
the source is located.
In addition, we want to clarify that a
plant that is co-located with other
facilities that together qualify as a major
source is part of that major source and
not an area source.
B. Part 63
General Provisions
Comment: One commenter
representing the two beryllium plants
objected to the part 63 SSM
requirements in the proposed NESHAP
for the Primary Beryllium Production
area source category. The commenter
stated that these two beryllium plants
are already subject to 40 CFR part 61,
subpart C, which EPA has adopted in
this final rule, as well as the SSM
requirements in State implementation
plans (SIP), State laws, and title V
permits. According to the comment,
because these plants are subject to a
strict ambient air standard for beryllium
under the part 61 NESHAP, which
requires that the plants monitor
continuously and meet the required
limits under all conditions, the part 63
SSM requirements are not necessary.
Commenters representing facilities in
the PVC industry provided similar
comments. In addition, they stated that
by requiring compliance with part 61
and the SSM provisions in 40 CFR 63.6,
the proposed rule would impose two
different SSM schemes in one standard.
It would also impose more burdensome
reporting and recordkeeping obligations
on the lower emitting (area) sources.
Representatives of two primary
copper companies also stated that the
SSM requirements are unnecessary and
duplicative of existing requirements and
should be deleted. Their title V permits
contain existing functionally equivalent
(PTE) of a Stationary Source Under Section 112 and
Title V of the Clean Air Act (Act)’’ (Jan. 25, 1995),
available at https://www.epa.gov/Region7/programs/
artd/air/title5/t5memos/ptememo.pdf. EPA has
extended the transition policy several times. See
‘‘Third Extension of January 25, 1995 Potential to
Emit Transition Policy’’ (December 20, 1999),
available at https://www.epa.gov/Region7/programs/
artd/air/title5/t5memos/4thext.pdf. Under the Third
Extension, sources can rely on State-only
enforceable PTE limits until we finalize our
response to the remand.
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SSM provisions, including requirements
for timely notification and reporting.
Response: We agree that the SSM
requirements in the 40 CFR part 63
General Provisions need not be included
in the NESHAP for the PVC and
Copolymer Production and the Primary
Beryllium Production area source
categories, both of which adopted the
relevant part 61 standards for these
categories. Under the construct of the
part 61 standards, sources must comply
with the standards at all times,
including periods of SSM. Therefore,
separate requirements governing SSM
are not necessary. Accordingly, we have
revised the proposed rule to eliminate
the part 63 SSM requirements for new
and existing primary beryllium and PVC
plants.
We also examined the SSM
requirements that are in title V permits
for other source categories. The primary
copper smelters and primary zinc
production plants have similar
requirements in their permits. Our
review indicates that these requirements
are substantially equivalent to the part
63 SSM requirements. For example, the
title V permits for these plants require
that all malfunctions be reported within
two working days of the event. The
report must include a description of the
malfunction, steps taken to mitigate
emissions, and corrective actions taken.
In addition, the permittee must show
through signed contemporaneous logs or
other relevant evidence that: (1) A
malfunction occurred and the permittee
can identify the probable cause, (2) the
facility was being operated properly at
the time the malfunction occurred, and
(3) all reasonable steps were taken to
minimize emissions that exceeded the
emission standards or other
requirements of the permit. The permit
also makes it clear that a malfunction or
emergency does not include events
caused by improperly designed
equipment, lack of preventative
maintenance, careless or improper
operation, or operator error.
Based on the comments and our
review of title V permits, we are
including in this final rule alternative
SSM requirements that we have
formulated based on our review of the
title V permits mentioned above. Under
this final rule, a new or existing primary
copper smelter or primary zinc
production facility may choose to meet
the SSM requirements in 40 CFR
63.6(e)(3) or the alternative SSM
requirements provided in this final rule.
This final rule also includes operation
and maintenance requirements for
existing sources that are based on the
permits. For primary copper smelters,
the owner or operator must to the extent
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practicable, maintain and operate any
affected source, including associated air
pollution control equipment, in a
manner consistent with good air
pollution control practice for
minimizing emissions. In addition, all
pollution control equipment must be
installed, maintained, and operated
properly. Instructions from the vendor
or established maintenance practices
that maximize pollution control must be
followed. All necessary equipment
control and operating devices, such as
pressure gauges, ampere meters, volt
meters, flow rate indicators, temperature
gauges, continuous emissions
monitoring systems, etc., must be
installed, operated properly and easily
accessible to compliance inspectors. A
copy of all manufacturers’ operating
instructions for pollution control
equipment and pollution emitting
equipment must be maintained at the
facility site. These instructions must be
available to all employees who operate
the equipment and must be made
available to the permitting authority
upon request. Maintenance records
must be made available to the
permitting authority upon request.
Comment: One commenter stated that
we should not adopt the
preconstruction notification
requirements in the part 63 General
Provisions (40 CFR part 63, subpart A)
because they were unnecessary and
duplicate the very similar requirements
already in the part 61 General
Provisions (40 CFR part 61, subpart A).
EPA should not impose the additional
burden of submitting and processing
two duplicative applications and should
just rely on the provisions already in the
part 61 General Provisions.
Response: We agree that if a
preconstruction notification is
submitted under the part 61 General
Provisions (40 CFR 61.07), it is not
necessary to submit another
preconstruction notification under the
part 63 General Provisions. We have
revised the proposed rule to reflect this
change.
Comment: One commenter stated that
EPA should not incorporate any of the
part 63 General Provisions into area
source standards that adopt the part 61
NESHAP. These provisions, including
those in 40 CFR 63.1 (Applicability), are
already addressed in the part 61 General
Provisions and enhanced by SIP
requirements and title V permits.
Response: We have previously
addressed the SSM requirements and
preconstruction notifications for
facilities subject to part 61 standards.
The only other section of the part 63
General Provisions that we have
included for these sources deals with
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2937
applicability in 40 CFR 63.1
(§§ 63.1(a)(1) through (10), 63.1(b)(1),
63.1(c), and 63.1(d)). The provisions on
applicability impose no burden on the
facility and provide clarity and useful
information related to the applicability
of standards under part 63.
Consequently, the final rule includes
portions of § 63.1 from the part 63
General Provisions.
C. Primary Copper Smelters
Comment: Two commenters
identified two primary copper smelters
as area sources in addition to the one
smelter identified as an area source in
the proposal preamble. One of these
smelters is operating, and the company
stated that the facility is an area source
(i.e., a synthetic minor source). The
other smelter has been shut down for
several years, but it is in the process of
obtaining permits to re-start and expects
to be an area source. Both of these
smelters use the batch converting
process, whereas the smelter that was
identified as an area source at proposal
and was the basis for GACT uses flash
continuous converting technology. The
company pointed to the process
descriptions in the proposal preamble
that noted the numerous differences in
the two technologies. The company
suggested that their two smelters fit into
a separate subcategory (batch converting
technology) and should have rule
requirements based on that technology.
The requirements in the proposed rule
are not appropriate for their smelters
because the proposed rule is based on
the flash continuous converting
technology.
Response: The commenters asserted
that there are two area source primary
copper smelters that use the batch
converting technology. As we described
in the proposal preamble (71 FR 59308,
October 6, 2006), there are numerous
differences in process operation,
emissions points, and achievable levels
of control. We believe that our proposed
standard for existing sources, which is
based on flash continuous converting
technology, would not be appropriate
for existing sources of primary copper
smelting that use the batch converting
technology and that separate standards
are needed to address the different
technology used by these existing
smelters. Solely for purposes of this
analysis, we accept, as true, the
commenter’s assertion that there are
existing area source facilities that use
batch processing. As explained above, to
the extent the commenter has any
question as to whether the smelters
identified above are major or area
sources, they should consult with the
relevant permitting authority or submit
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a request for an applicability
determination to the EPA regional office
in the region where the source is
located.
In developing the requirements for
sources using the batch converting
technology, we reviewed the title V
permit of the currently operating source
identified in the comment. The
emissions from this facility are
controlled as a result of its title V permit
requirements to capture and control
emissions of PM. The vast majority of
the gases from the smelting furnace and
converter are collected by a primary
capture system, sent to control
equipment to remove PM, and then
processed in a sulfuric acid plant.
Fugitive emissions are collected by a
secondary capture system and sent to a
baghouse for control of PM emissions.
We determined that these current
permit requirements represent GACT for
existing primary copper smelters using
the batch converting process and have
included these requirements in this
final rule as the requirements for
existing primary copper smelting area
sources that use batch converting
technology.
According to these requirements,
plants that use batch converting
technology must operate primary
capture systems on each smelting vessel
and each copper converter. Secondary
capture systems must be installed to
capture emissions from tapping copper
matte and slag from the smelting vessel
and emissions from charging, skimming,
pouring, and holding when the
converter mouth is partially rotated out
from the primary collection hood. All of
the collected gases must be routed to an
emissions control system. In addition,
emissions from the primary collection
system for the smelting vessel and
converter must be routed to a sulfuric
acid plant after PM removal.
Emissions from each copper
concentrate dryer must be controlled
and must not exceed 0.022 gr/dscf.
Emissions from secondary capture
systems that are not vented to a sulfuric
acid plant must not exceed 0.02 gr/dscf.
We also examined the monitoring
requirements in the title V permit of this
primary smelter using the batch
technology and found that they would
ensure that control devices are working
properly on a continuous basis. We
therefore included these monitoring
requirements in this final rule as
requirements for primary copper
smelting area sources that use the batch
converting technology. Under these
requirements, a COMS meeting
Performance Specification 1 (40 CFR
part 60, appendix B) must be installed
on each electrostatic precipitator. If the
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24-hour rolling average opacity exceeds
15 percent, the plant must investigate
the cause of the problem and take
corrective action. Each baghouse must
be equipped with and monitored by a
bag leak detection system to ensure
proper operation. We have also required
performance tests every 2.5 years to
determine compliance with PM limits.
Comment: A commenter representing
the primary copper plant that was the
basis for GACT stated that EPA did not
properly capture the facility’s title V
permit requirements in some cases. The
commenter supplied additional details
and clarifications. Clarification is
needed for the requirements for anode
casting and holding operations, the
emissions limit should not be referred to
as ‘‘smelter wide’’ but as the limit for
the main stack, the limit should be
expressed as PM10 rather than PM, and
the continuous PM sampler should not
be referred to as a CEMS. The
commenter also asked that EPA modify
the proposed rule to clearly state that a
single secondary gas collection system
can capture and control emissions from
multiple processing vessels (i.e., each
vessel does not have to have its own
separate collection system). The
commenter also requested more
flexibility in the monitoring
requirements so that the permitting
authority could approve improved
monitoring technology should it become
available in the future.
Response: We agree with the
commenter and will make most of the
suggested changes. The facility’s title V
permit was the basis for our GACT
determination, and we intended that the
proposed area source rule incorporate
the permit requirements of this wellcontrolled facility. We understand that
in some cases, a gas collection system
may be applied to multiple process
vessels, and we have included this
clarification in this final rule. We
understand that flexibility in monitoring
is important, especially as improved
monitoring techniques become
commercially available and
demonstrated in metallurgical
operations. That said, it is not necessary
to revise the proposed rule to allow a
facility to request approval of an
alternative monitoring method because
the procedure for making such requests
is contained in 40 CFR 63.8, which
applies to the NESHAP for the Primary
Copper Smelting area source category in
this final rule.
Comment: One commenter noted that
the new source standard for primary
copper was based on the newer flash
continuous converter technology and
would not be appropriate for new plants
using the batch converting technology.
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The commenter stated that continuous
converting has more limited
applicability to ore concentrates that
have high impurities levels than does
batch converting. The commenter stated
that because a new smelter could use
either of the technologies, the emission
standards for new sources should be
reflective of the performance of either of
these technologies. This can be achieved
by providing flexibility in the emission
limits that are adopted. The commenter
recommended that the standard for new
smelters using the batch converting
technology be based on the best
performing existing facility with the
technology. In addition, a provision
should be made to allow an alternate
emissions limit to be authorized by
either EPA or the permitting authority
that is equally protective.
Response: The emissions limit that we
proposed for new primary copper
smelters is in lb/ton of copper
concentrate feed and is applied on a
facility wide basis. The format and
requirements of the standard can be
applied to and achieved by a facility
using any primary copper smelting
technology if it is well controlled. The
format of the standard also provides
flexibility because multiple process
vessels can have different levels of
emissions as long as they collectively
meet the overall lb/ton limit. The limit
has been demonstrated as achievable by
an existing area source that uses a
continuous converting process. Unlike
existing sources, new sources using any
smelting technology have the
opportunity to incorporate state-of-theart capture and control systems into
their design, construction, and
operation. Based on our engineering
experience with capture and control
systems that have been applied to
primary copper processes and also those
that have been applied to similar
processes in other metallurgical
industries, we believe that the emissions
limit for new sources can be achieved
by primary copper smelters using any
processing technology, including both
the continuous and batch converting
processes. The standard for new
primary copper smelters represents a
level of control that is generally
available for new sources.
Consequently, we chose to promulgate
the limit as proposed as GACT for new
primary copper smelters.
Comment: Three commenters objected
to the requirement of using a PM CEMS
for monitoring at new primary copper
smelter area sources. Although
improvements in PM CEMS have been
made as they continue to be developed,
there is not sufficient operating history
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to prove its feasibility for continuous
monitoring at primary copper smelters.
Response: The PM CEMS have been
demonstrated in many different
applications, including processes with
exhaust gases similar to those from
primary copper smelters (e.g., at electric
utilities where the temperatures and
exhaust gas compositions are similar).
The commenters did not provide any
information that the exhaust gases from
primary copper smelting are uniquely
different. We have included PM CEMS
as the monitoring technology for new
sources in this final rule.
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D. Primary Zinc Smelters
Comment: One commenter asked if
the proposed rule was meant to apply to
any zinc refinery that processes any
amount of zinc sulfide concentrate. If
so, what is the timeframe for using zinc
sulfide concentrate and its percentage of
the feed that qualifies a facility as a
primary zinc smelter? Is EPA really
trying to regulate zinc refineries, which
produce cathodes in a cathode melting
furnace and use zinc sulfide concentrate
as a feed material, and not regulate
thermal zinc smelters, who do not
produce cathodes and do not currently
use zinc sulfide concentrate?
Response: The commenter is correct
in that this final rule applies to any area
source facility that produces zinc
products from any amount of zinc
sulfide ore concentrates using
pyrometallurgical processes (i.e., a
‘‘primary zinc smelter’’). This final rule
does not apply to thermal zinc smelters
if they do not process zinc sulfide
concentrate. (Facilities processing only
zinc scrap and residues containing zinc
would be classified as secondary zinc
smelters.) If a facility meets the
definition of primary zinc smelter and is
an area source on the compliance date,
it is subject to this final rule. If the
facility is not processing zinc sulfide
concentrate but subsequently begins
processing it, meets the definition of
primary zinc smelter, and is an area
source, it is subject to this final rule
when it begins processing the zinc
sulfide concentrate. Under these facts,
such a facility would be subject to the
standards for new sources if
construction or reconstruction of the
primary zinc smelter (the affected
source) commenced on or after October
6, 2006.
We are not making a distinction
between zinc refineries and thermal
zinc smelters as described by the
commenter. Either type of facility is
subject to this final rule if it is an area
source and meets the definition of
primary zinc smelter.
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Comment: One commenter noted that
the proposed rule requires
demonstrating compliance by stack
testing within 180 days after the
compliance date. Their plant has a
process that is not operating, it is
subject to the rule, but it may not restart
until more than 180 days after the
compliance date. As the proposed rule
reads, they would have to demonstrate
compliance by a stack test even though
the process is not operating.
Response: We have clarified the
proposed rule to indicate that if a
process subject to this final rule is not
operating on the compliance date and
subsequently starts up, compliance
testing must be performed within 180
days after startup of the process.
Comment: One commenter noted that
the proposed rule requires that initial
compliance must be demonstrated ‘‘for
each furnace at your facility.’’ A zinc
smelter may have other types of
furnaces that are not subject to emission
limits. The commenter assumes that this
requirement will have no impact on
these furnaces.
Response: The commenter is correct.
We have clarified the proposed rule to
state that initial compliance must be
demonstrated ‘‘for each furnace at your
facility that is subject to an emissions
limit under this subpart.’’
Comment: One commenter stated that
the emissions limit of 0.005 gr/dscf for
certain furnaces at new sources is
greater than the emissions limit for the
same furnaces at existing sources. The
commenter suggested that the greater of
the two values be applied in this case
to provide a level playing field for new
and existing sources.
Response: We disagree with the
comment that the emissions limit of
0.005 gr/dscf for certain furnaces at new
sources is greater than the emissions
limits for the same furnaces at existing
sources. The emissions limit of 0.005 gr/
dscf for new sources is applied to the
exhaust vent of a zinc cathode melting
furnace; scrap zinc melting furnace;
furnace melting zinc dust, zinc chips,
and other materials containing zinc; and
alloy melting furnace. For existing
sources, the limits are 0.1 lb/hr from the
exhaust vent of a furnace that melts zinc
dust, zinc chips, and/or other materials
containing zinc; and 0.228 lb/hr from
the vent for the combined exhaust from
a furnace melting zinc scrap and an
alloy furnace. Although the limits for
the furnaces mentioned above are
expressed in different formats for new
and existing sources, both formats
reflect the level of emission control that
can be achieved based on the
technology we identified as GACT for
these furnaces (i.e., a well-operated and
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well-maintained baghouse). However,
whereas the lb/hr limits for the abovenoted furnaces in the proposed rule
were based on the specific operations at
the two existing sources of which we are
aware, the gr/dscf emission limit is not
operation specific and can apply to
these furnaces at any primary zinc
production area source. We have
therefore adopted the gr/dscf limit in
addition to the proposed lb/hr limit, and
sources can meet either the limit
expressed in lb/hr or the limit expressed
in gr/dscf.
E. Basis for Area Source Standards
Comment: We received a comment
from the National Association of Clean
Air Agencies (NACAA) expressing
concern with EPA’s establishment of
area source standards under section 112
of the CAA by adopting existing Federal
and/or State area source standards. In
the comment, the NACAA stated that
the existence of State and local
regulations does not relieve EPA of its
obligation to establish area source
standards under the CAA. The NACAA
expressed concern that some States
cannot have requirements more
stringent than those of the Federal
government and may, therefore, be
required to change their regulations of
area sources to be consistent with EPA’s
area source standards. The NACAA
stated that, if the permit requirements
that make these sources ‘‘well
controlled’’ are not contained within the
Federal rule, the nonfederal rules could
be relaxed. The NACAA further stated
that, in the absence of Federal
requirements, there would be nothing to
prevent ‘‘backsliding’’ by these sources.
The NACAA was particularly
concerned with EPA’s proposed PVC
rule, which adopted the part 61
standards for PVC plants. According to
the NACAA, the part 61 standards for
PVC plants are outdated and
inappropriate as a model for GACT. The
NACAA submitted with its comment a
recommendation for the standards for
area sources of PVC plants. The NACAA
previously recommended these limits to
EPA as the MACT standards for major
sources of PVC plants. The NACAA
believes the submittal contains valuable
information for EPA in developing PVC
regulations for area sources as well.
Response: We have traditionally
reviewed operating permits and current
standards in the standards development
process, and we used this approach in
developing the NESHAP for the four
area source categories in this final rule.
The NACAA did not explain why it
would be inappropriate for EPA to
adopt existing Federal, State or local
standards that EPA has determined to be
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effective in controlling HAP emissions.
Contrary to the commenter’s assertions,
EPA is setting final area source
standards for the four source categories
at issue in this rule. The emissions
limits and/or work practice standards in
each of the four NESHAP in this final
rule have been reviewed, determined by
EPA to be the appropriate standards for
the relevant area source category, and
established by EPA in this final rule as
the Federal requirements for that
category pursuant to section 112 of the
CAA.
It is conceivable that for those States
with laws that preclude the State from
issuing regulations that are more
stringent than EPA’s regulations, a State
may need to change its existing area
source regulation in response to this
final rule. However, the NACAA has not
identified any existing State regulation
that would require modification in this
regard. Further, as previously
mentioned, we established the area
source standards in this final rule based
on GACT, which may or may not be
reflected by more stringent State or local
requirements. The NACAA also asserted
that the part 61 standards for PVC plants
are outdated and inappropriate as GACT
for area source PVC plants. NACAA’s
statement was apparently based on the
fact that the part 61 standards were
issued prior to the 1990 Amendments to
the Clean Air Act and were based on
risk. However, the fact that these are
risk-based standards are not per se
evidence that they do not reflect GACT
for area sources of PVC plants. We
believe that the record supports our
determination as to what constitutes
GACT for the four categories at issue
here.
Moreover, we reviewed the
information submitted by the
commenter that contained their
‘‘presumptive’’ determination of MACT
that they issued as guidance to State and
local agencies. These recommended
limits were based on the best-controlled
plants, most if not all of which are major
sources.3 We believe that these
recommended limits may represent
MACT or something beyond MACT, but
we do not believe that they are
appropriate for these particular area
source categories. As previously
mentioned, we have decided to
establish the standards for the PVC and
Copolymer Production area source
category based on GACT. We do not
believe that NACAA’s recommended
limits represent GACT for area sources
3 It is not clear whether the one polyvinyl
chloride area source plant known to the National
Association of Clean Air Agencies (NACAA) was
among the plants that the NACAA analyzed in
developing the recommended limits.
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of PVC plants. Because we expect PVC
plants to be operating in accordance
with the part 61 standards for PVC
plants, we believe that these standards
represent a level of control that is
generally available and is therefore a
reasonable representation of GACT for
area sources in this source category.
Comment: One commenter stated that
area source standards are not needed for
primary beryllium plants. All of these
plants, including major and area
sources, are already subject to NESHAP
under 40 CFR part 61. In addition, the
proposed area source standard will not
achieve any reduction in HAP
emissions. A second commenter stated
that absent EPA’s statutory obligation to
establish standards for area sources,
there would be no need to regulate PVC
and copolymer plants because they are
already governed by the existing
NESHAP. However, the commenter
recognizes EPA’s obligation to regulate
PVC and copolymer area sources and
supports the adoption of the part 61
NESHAP as the area source standard.
Response: The second commenter has
captured the issue and provides the
response to the first commenter: EPA
has a statutory obligation to establish
area source NESHAP for primary
beryllium plants.
F. Compliance Date
Comment: Two commenters stated
that requiring compliance on the date of
publication of the final rule in the
Federal Register does not allow
sufficient time for existing sources to
develop a SSM plan.
Response: We believe that we have
addressed the commenter’s concern
regarding existing sources’ abilities to
develop SSM plans by the compliance
date. With respect to primary copper
smelting and primary zinc production
area sources, this final rule allows
existing sources in these two area source
categories to address SSM according to
the relevant requirements in their title V
permits, which do not require a SSM
plan. As previously discussed in our
response to the comments on the
necessity of the part 63 SSM
requirements (section IV.B of this
preamble), we have reviewed the SSM
requirements in the title V permits for
the existing sources of primary copper
smelting and primary zinc production
area sources and have determined that
these provisions are adequate to replace
the SSM requirements in the General
Provisions, which require a SSM plan.
See 40 CFR 63.6(e)(3). We have
therefore included in the final NESHAP
for primary copper smelting and
primary zinc production area sources
requirements that are based on these
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title V permit terms and conditions. To
provide flexibility, sources can comply
with the SSM requirements specified in
this final rule or comply with the
provisions contained in the General
Provisions at 40 CFR 63.6(e).
Accordingly, the existing sources in
these two area source categories are not
required to develop SSM plans and may
instead continue to follow their title V
permit requirements regarding SSM.
In addition, as previously mentioned,
we are not requiring SSM plans and
reports in 40 CFR 63.6(e)(3) for area
source PVC plants and beryllium
production facilities. Because the
NESHAP for these source categories in
this final rule adopt part 61 standards,
which require compliance at all times,
specific provisions governing SSM are
unnecessary. For all of the reasons
stated above, we believe that the
concern expressed in this comment has
been addressed.
V. Statutory and Executive Order
Reviews
A. Executive Order 12866: Regulatory
Planning and Review
Under Executive Order 12866 (58 FR
51735, October 4, 1993), this action is a
‘‘significant regulatory action’’ because
it may raise novel legal or policy issues.
Accordingly, EPA submitted this action
to the Office of Management and Budget
(OMB) for review under Executive
Order 12866, and any changes made in
response to OMB recommendations
have been documented in the docket for
this action.
B. Paperwork Reduction Act
The NESHAP for Polyvinyl and
Copolymers Production Area Sources do
not impose any new information
collection burden. New and existing
plants that are area sources are required
to comply with the same testing,
monitoring, reporting, and
recordkeeping requirements as those in
the National Emission Standards for
Vinyl Chloride (40 CFR part 61, subpart
F), to which these area sources are
currently subject, and the information
collection requirements in the part 61
NESHAP General Provisions (40 CFR
part 61, subpart A), which are
incorporated into the NESHAP. The
OMB has previously approved the
information collection requirements in
40 CFR part 61, subpart F, under the
provisions of the Paperwork Reduction
Act, 44 U.S.C. 3501 et seq. and has
assigned OMB control number 2060–
0071, EPA Information Collection
Request (ICR) number 0186.10.
A copy of the OMB-approved ICR for
the National Emission Standards for
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Vinyl Chloride may be obtained from
Susan Auby, Collection Strategies
Division, U.S. EPA (2822T), 1200
Pennsylvania Ave., NW., Washington,
DC 20460, by e-mail at
auby.susan@epa.gov, or by calling (202)
566–1672.
The requirements for primary
beryllium production facilities in the
NESHAP for Primary Nonferrous Metals
Area Sources do not impose any new
information collection burden. New and
existing plants that are area sources are
required to comply with the same
testing, monitoring, recordkeeping, and
reporting requirements as those in the
National Emission Standards for
Beryllium (40 CFR part 61, subpart C),
to which these area sources are
currently subject, and the information
collection requirements in the part 61
General Provisions (40 CFR part 61,
subpart A), which are incorporated into
the NESHAP for these sources. The
OMB has previously approved the
information collection requirements in
40 CFR part 61, subpart C, under the
provisions of the Paperwork Reduction
Act, 44 U.S.C. 3501 et seq. and has
assigned OMB control number 2060–
0092, EPA ICR number 0193.08.
A copy of the OMB-approved ICR for
the National Emission Standards for
Beryllium may be obtained from Susan
Auby, Collection Strategies Division,
U.S. EPA (2822T), 1200 Pennsylvania
Ave., NW., Washington, DC 20460, by email at auby.susan@epa.gov, or by
calling (202) 566–1672.
The information requirements in the
NESHAP for Polyvinyl Chloride and
Copolymers Production Area Sources,
Primary Copper Smelting Area Sources,
Secondary Copper Smelting Area
Sources, and Primary Nonferrous
Metals—Zinc, Cadmium, and Beryllium
Area Sources have been submitted for
approval to OMB under the Paperwork
Reduction Act, 44 U.S.C. 3501 et seq.
The information collection requirements
are not enforceable until OMB approves
them.
The information collection
requirements for primary copper
smelting and primary zinc production
are based on the current title V
permitting requirements for existing
sources and the information collection
requirements in the part 63 General
Provisions (40 CFR part 63, subpart A),
most of which are incorporated into the
NESHAP for new sources. The ICR
document includes the burden estimates
for all applicable General Provisions.
These recordkeeping and reporting
requirements are mandatory pursuant to
section 114 of the CAA (42 U.S.C. 7414).
All information submitted to EPA
pursuant to the information collection
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requirements for which a claim of
confidentiality is made is safeguarded
according to CAA section 114(c) and the
Agency’s implementing regulations at
40 CFR part 2, subpart B.
The PM testing, monitoring,
recordkeeping, and reporting
requirements with which existing
primary copper smelting and primary
zinc smelting area sources must comply
are the same as the requirements that
are in these facilities’ current title V
operating permits. The only new
information collection requirements that
apply to these area sources consist of
initial notifications. There are no
existing secondary copper smelting
facilities, and there are no requirements
for existing secondary copper smelting
area sources.
Any new primary zinc production
facility, primary copper smelter, or
secondary copper smelter area source is
subject to all information collection
requirements in the part 63 General
Provisions. No costs or burden hours are
estimated for new primary copper
smelters, secondary copper smelters, or
primary zinc production area sources
because no new sources are estimated
during the 3-year period of the ICR. No
new sources have been constructed in
more than 10 years, no new
construction has been announced, and
we have no indication there will be any
new sources in the next 3 years.
The annual burden for this
information collection (including all
four source categories) averaged over the
first 3 years of this ICR is estimated to
total 23 labor hours per year at a cost of
$1,948 for the three existing primary
copper smelting area sources and 15.4
labor hours per year at a cost of $1,305
for the two existing primary zinc
smelting area sources. No capital/
startup costs or operation and
maintenance costs are associated with
the requirements.
Burden means the total time, effort, or
financial resources expended by persons
to generate, maintain, retain, disclose, or
provide information to or for a Federal
agency. This includes the time needed
to review instructions; develop, acquire,
install, and utilize technology and
systems for the purposes of collecting,
validating, and verifying information,
processing and maintaining
information, and disclosing and
providing information; adjust the
existing ways to comply with any
previously applicable instructions and
requirements; train personnel to be able
to respond to a collection of
information; search data sources;
complete and review the collection of
information; and transmit or otherwise
disclose the information.
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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 EPA’s regulations in 40
CFR part 63 are listed in 40 CFR part 9.
When this ICR is approved by OMB, the
Agency will publish a technical
amendments for the approved
information collection requirements
contained in the final rules.
C. Regulatory Flexibility Act
The Regulatory Flexibility Act (RFA)
generally requires an agency to prepare
a regulatory flexibility analysis of any
rule subject to notice and comment
rulemaking requirements under the
Administrative Procedure Act or any
other statute unless the agency certifies
that the rule would not have a
significant economic impact on a
substantial number of small entities.
Small entities include small businesses,
small not-for-profit enterprises, and
small governmental jurisdictions.
For the purposes of assessing the
impacts of the area source NESHAP on
small entities, small entity is defined as:
(1) A small business that meets the
Small Business Administration size
standards for small businesses at 13 CFR
121.201 (less than 1,000 employees for
primary copper smelting and less than
750 employees for PVC and copolymers
production, secondary copper smelting,
and primary nonferrous metals
manufacturing); (2) a small
governmental jurisdiction that is a
government of a city, county, town,
school district, or special district with a
population of less than 50,000; and (3)
a small organization that is any not-forprofit enterprise which is independently
owned and operated and is not
dominant in its field.
After considering the economic
impacts of these final rules on small
entities, I certify that this action will not
have a significant economic impact on
a substantial number of small entities.
The small entities directly regulated by
these final rules are small businesses.
We have determined that existing small
businesses in these area source
categories will not incur any adverse
impacts on existing area sources of PVC
and copolymer production facilities,
primary copper smelters, and nonferrous metal production facilities
because the rules do not create any new
requirements or burdens other than
minimal notification requirements.
There will be no adverse impacts on
existing secondary copper area sources
because there are no existing sources in
the category. Although these final
NESHAP contain emission control
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requirements for new area sources in all
four source categories, we are not aware
of any new sources being constructed
now or planned in the near future, and
consequently, we did not estimate any
impacts for new sources.
Although this final rule will not have
a significant economic impact on a
substantial number of small entities,
EPA nonetheless has tried to reduce the
impact of this rule on small entities.
These final rules are designed to
harmonize with existing State or local
requirements. In addition, we have
deleted the proposed requirements for
SSM plans and reports.
D. Unfunded Mandates Reform Act
Title II of the Unfunded Mandates
Reform Act of 1995 (UMRA), Public
Law 104–4, establishes requirements for
Federal agencies to assess the effects of
their regulatory actions on State, local,
and tribal governments and the private
sector. Under section 202 of the UMRA,
EPA generally must prepare a written
statement, including a cost-benefit
analysis, for proposed and final rules
with ‘‘Federal mandates’’ that may
result in expenditures by State, local,
and tribal governments, in the aggregate,
or to the private sector, of $100 million
or more in any 1 year. Before
promulgating an EPA rule for which a
written statement is needed, section 205
of the UMRA generally requires EPA to
identify and consider a reasonable
number of regulatory alternatives and
adopt the least costly, most costeffective, or least burdensome
alternative that achieves the objectives
of the rule. The provisions of section
205 do not apply when they are
inconsistent with applicable law.
Moreover, section 205 allows EPA to
adopt an alternative other than the least
costly, most cost-effective, or least
burdensome alternative if the
Administrator publishes with the final
rule an explanation why that alternative
was not adopted. Before EPA establishes
any regulatory requirements that may
significantly or uniquely affect small
governments, including tribal
governments, it must have developed
under section 203 of the UMRA a small
government agency plan. The plan must
provide for notifying potentially
affected small governments, enabling
officials of affected small governments
to have meaningful and timely input in
the development of EPA regulatory
proposals with significant Federal
intergovernmental mandates, and
informing, educating, and advising
small governments on compliance with
the regulatory requirements.
EPA has determined that the final
rules do not contain a Federal mandate
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that may result in expenditures of $100
million or more for State, local, and
tribal governments, in the aggregate, or
the private sector in any one year. The
estimated expenditures for the private
sector in any one year are less than
$2,500. Thus, the final rules are not
subject to the requirements of sections
202 and 205 of the UMRA. In addition,
the final rules do not significantly or
uniquely affect small governments. The
final rules contain no requirements that
apply to such governments, impose no
obligations upon them, and will not
result in expenditures by them of $100
million or more in any one year or any
disproportionate impacts on them.
Therefore, the final rules are not subject
to section 203 of the UMRA.
E. Executive Order 13132: Federalism
Executive Order 13132 (64 FR 43255,
August 10, 1999) requires EPA to
develop an accountable process to
ensure ‘‘meaningful and timely input by
State and local officials in the
development of regulatory policies that
have federalism implications.’’ ‘‘Policies
that have federalism implications’’ are
defined in the Executive Order to
include regulations that 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.’’
These final rules do not have
federalism implications. They will not
have substantial direct effects on the
States, on the relationship between the
national government and the States, or
on the distribution of power and
responsibilities among the various
levels of government, as specified in
Executive Order 13132. These final
rules impose requirements on owners
and operators of specified area sources
and not State and local governments.
Thus, Executive Order 13132 does not
apply to these final rules.
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
Executive Order 13175 (65 FR 67249,
November 6, 2000), requires EPA to
develop an accountable process to
ensure ‘‘meaningful and timely input by
tribal officials in the development of
regulatory policies that have tribal
implications.’’ These final rules do not
have tribal implications, as specified in
Executive Order 13175. They will not
have substantial direct effects on tribal
governments, on the relationship
between the Federal government and
Indian tribes, or on the distribution of
power and responsibilities between the
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Federal government and Indian tribes,
as specified in Executive Order 13175.
These final rules impose requirements
on owners and operators of specified
area sources and not tribal governments.
Thus, Executive Order 13175 does not
apply to these final rules.
G. Executive Order 13045: Protection of
Children From Environmental Health
and Safety Risks
Executive Order 13045 (62 FR 19885,
April 23, 1997) applies to any rule that:
(1) Is determined to be ‘‘economically
significant,’’ as defined under Executive
Order 12866, and (2) concerns an
environmental health or safety risk that
EPA has reason to believe may have a
disproportionate effect on children. If
the regulatory action meets both criteria,
EPA must evaluate the environmental
health or safety effects of the planned
rule on children, and explain why the
planned regulation is preferable to other
potentially effective and reasonably
feasible alternatives considered by EPA.
EPA interprets Executive Order 13045
as applying only to those regulatory
actions that are based on health or safety
risks, such that the analysis required
under section 5–501 of the Executive
Order has the potential to influence the
regulation. These final rules are not
subject to the Executive Order. They are
based on control technology and not on
health or safety risks.
H. Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution, or Use
These final rules are not a ‘‘significant
energy action’’ as defined in Executive
Order 13211 (66 FR 28355, May 22,
2001) because they are not likely to have
a significant adverse effect on the
supply, distribution, or use of energy.
Further, we have concluded that these
final rules are not likely to have any
adverse energy effects because energy
requirements would remain at existing
levels. No additional pollution controls
or other equipment that consume energy
are required by these final rules.
I. National Technology Transfer
Advancement Act
Section 12(d) of the National
Technology Transfer and Advancement
Act (NTTAA) of 1995 (Pub. L. 104–113,
section 12(d), 15 U.S.C. 272 note)
directs EPA to use voluntary consensus
standards (VCS) in its regulatory
activities, unless to do so would be
inconsistent with applicable law or
otherwise impractical. The VCS are
technical standards (e.g., materials
specifications, test methods, sampling
procedures, and business practices) that
are developed or adopted by VCS
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bodies. The NTTAA directs EPA to
provide Congress, through OMB,
explanations when the Agency does not
use available and applicable VCS.
This rule involves technical
standards. The EPA cites the following
standards: EPA Methods 1, 1A, 2, 2A,
2C, 2D, 2F, 2G, 3, 3A, 3B, 4, 5, 5D, and
9 in 40 CFR part 60, appendix A; and
Performance Specifications 1 and 11 in
40 CFR part 60, appendix B. The search
identified one VCS as an acceptable
alternative to EPA Method 3B. The
method ASME PTC 19.10–1981, ‘‘Flue
and Exhaust Gas Analyses,’’ is cited in
two of these final rules for its manual
method for measuring the oxygen,
carbon dioxide, and carbon monoxide
content of the exhaust gas. This part of
ASME PTC 19.10–1981 is an acceptable
alternative to EPA Method 3B.
The standard ASTM D6216 (1998),
‘‘Standard Practice for Opacity Monitor
Manufacturers to Certify Conformance
with Design and Performance
Specifications,’’ was designated an
acceptable alternative for the design
specifications given in EPA’s
Performance Specification 1. As a result,
EPA incorporated ASTM D6216–98 by
reference into Performance
Specification 1 as the design
specifications for opacity monitors in
August 2000.
The search for emissions
measurement procedures identified 13
other VCS. The EPA determined that
these 13 standards identified for
measuring emissions of the HAP or
surrogates subject to emission standards
in these final rules were impractical
alternatives to EPA test methods for the
purposes of the rules. Therefore, EPA
does not intend to adopt these standards
for this purpose. The reasons for the
determinations for the 13 methods are
in the docket for these rules.
For the methods required or
referenced by these rules, a source may
apply to EPA for permission to use
alternative test methods or alternative
monitoring requirements in place of any
required testing methods, performance
specifications, or procedures under
§§ 63.7(f) and 63.8(f) of subpart A of the
General Provisions.
J. Congressional Review Act
The Congressional Review Act, 5
U.S.C. 801, et seq., as added by the
Small Business Regulatory Enforcement
Fairness Act of 1996, generally provides
that before a rule may take effect, the
agency promulgating the rule must
submit a rule report, which includes a
copy of the rule, to each House of
Congress and to the Comptroller General
of the United States. The EPA will
submit a report containing these final
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rules and other required information to
the U.S. Senate, the U.S. House of
Representatives, and the Comptroller
General of the United States prior to
publication of the final rules in the
Federal Register. A major rule cannot
take effect until 60 days after it is
published in the Federal Register. This
action is not a ‘‘major rule’’ as defined
by 5 U.S.C. 804(2). These final rules will
be effective on January 23, 2007.
Standards and Compliance Requirements
63.11142 What are the standards and
compliance requirements for new and
existing sources?
List of Subjects in 40 CFR Part 63
Applicability and Compliance Dates
Environmental protection, Air
pollution control, Hazardous
substances, Incorporation by reference,
Reporting and recordkeeping
requirements.
§ 63.11140
Dated: December 11, 2006.
Stephen L. Johnson,
Administrator.
For the reasons stated in the preamble,
title 40, chapter I, part 63 of the Code
of Federal Regulations is amended as
follows:
I
PART 63—[AMENDED]
1. The authority citation for part 63
continues to read as follows:
I
Authority: 42 U.S.C. 7401 et seq.
Subpart A—[Amended]
2. Section 63.14 is amended by
revising paragraph (i)(1) to read as
follows:
I
§ 63.14
Incorporations by reference.
*
*
*
*
*
(i) * * *
(1) ANSI/ASME PTC 19.10–1981,
‘‘Flue and Exhaust Gas Analyses [Part
10, Instruments and Apparatus],’’ IBR
approved for §§ 63.309(k)(1)(iii),
63.865(b), 63.3166(a)(3),
63.3360(e)(1)(iii), 63.3545(a)(3),
63.3555(a)(3), 63.4166(a)(3),
63.4362(a)(3), 63.4766(a)(3),
63.4965(a)(3), 63.5160(d)(1)(iii),
63.9307(c)(2), 63.9323(a)(3),
63.11148(e)(3)(iii), 63.11155(e)(3),
63.11162(f)(3)(iii) and (f)(4),
63.11163(g)(1)(iii) and (g)(2), and Table
5 of subpart DDDDD of this part.
*
*
*
*
*
I 3. Part 63 is amended by adding
subpart DDDDDD to read as follows:
Subpart DDDDDD—National Emission
Standards for Hazardous Air Pollutants
for Polyvinyl Chloride and Copolymers
Production Area Sources
Sec.
Applicability and Compliance Dates
63.11140 Am I subject to this subpart?
63.11141 What are my compliance dates?
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Other Requirements and Information
63.11143 What General Provisions apply to
this subpart?
63.11144 What definitions apply to this
subpart?
63.11145 Who implements and enforces
this subpart?
Am I subject to this subpart?
(a) You are subject to this subpart if
you own or operate a plant specified in
40 CFR 61.61(c) that produces polyvinyl
chloride (PVC) or copolymers and is an
area source of hazardous air pollutant
(HAP) emissions.
(b) This subpart applies to each new
or existing affected source. The affected
source is the collection of all equipment
and activities in vinyl chloride service
necessary to produce PVC and
copolymers. An affected source does not
include portions of your PVC and
copolymers production operations that
meet the criteria in 40 CFR 61.60(b) or
(c).
(1) An affected source is existing if
you commenced construction or
reconstruction of the affected source
before October 6, 2006.
(2) An affected source is new if you
commenced construction or
reconstruction of the affected source on
or after October 6, 2006.
(c) This subpart does not apply to
research and development facilities, as
defined in section 112(c)(7) of the Clean
Air Act (CAA).
(d) You are exempt from the
obligation to obtain a permit under 40
CFR part 70 or 40 CFR part 71, provided
you are not otherwise required by law
to obtain a permit under 40 CFR 70.3(a)
or 40 CFR 71.3(a). Notwithstanding the
previous sentence, you must continue to
comply with the provisions of this
subpart.
§ 63.11141
dates?
What are my compliance
(a) If you own or operate an existing
affected source, you must achieve
compliance with the applicable
provisions in this subpart by January 23,
2007.
(b) If you own or operate a new
affected source, you must achieve
compliance with the applicable
provisions in this subpart by the dates
in paragraphs (b)(1) and (2) of this
section.
(1) If you start up a new affected
source on or before January 23, 2007,
you must achieve compliance with the
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applicable provisions in this subpart not
later than January 23, 2007.
(2) If you start up a new affected
source after January 23, 2007, you must
achieve compliance with the provisions
in this subpart upon startup of your
affected source.
Standards and Compliance
Requirements
§ 63.11142 What are the standards and
compliance requirements for new and
existing sources?
You must meet all the requirements in
40 CFR part 61, subpart F, except for 40
CFR 61.62 and 40 CFR 61.63.
Other Requirements and Information
§ 63.11143 What General Provisions apply
to this subpart?
(a) All the provisions in 40 CFR part
61, subpart A, apply to this subpart.
(b) The provisions in 40 CFR part 63,
subpart A, applicable to this subpart are
specified in paragraphs (b)(1) and (2) of
this section.
(1) § 63.1(a)(1) through (10).
(2) § 63.1(b) except paragraph (b)(3),
§ 63.1(c), and § 63.1(e).
§ 63.11144
subpart?
What definitions apply to this
The terms used in this subpart are
defined in the CAA; 40 CFR 61.02; 40
CFR 61.61; and § 63.2 for terms used in
the applicable provisions of part 63,
subpart A, as specified in § 63.11143(b).
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§ 63.11145 Who implements and enforces
this subpart?
(a) This subpart can be implemented
and enforced by the U.S. EPA or a
delegated authority such as a State,
local, or tribal agency. If the U.S. EPA
Administrator has delegated authority to
a State, local, or tribal agency, then that
Agency has the authority to implement
and enforce this subpart. You should
contact your U.S. EPA Regional Office
to find out if this subpart is delegated
to a State, local, or tribal agency within
your State.
(b) In delegating implementation and
enforcement authority of this subpart to
a State, local, or tribal agency under 40
CFR part 63, subpart E, the approval
authorities contained in paragraphs
(b)(1) through (4) of this section are
retained by the Administrator of the
U.S. EPA and are not transferred to the
State, local, or tribal agency.
(1) Approval of an alternative means
of emissions imitation under 40 CFR
61.12(d).
(2) Approval of a major change to test
methods under 40 CFR 61.13(h). A
‘‘major change to test method’’ is
defined in § 63.90.
(3) Approval of a major change to
monitoring under 40 CFR 61.14(g). A
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‘‘major change to monitoring’’ is defined
in § 63.90.
(4) Approval of a major change to
recordkeeping/reporting under 40 CFR
61.10. A ‘‘major change to
recordkeeping/reporting’’ is defined in
§ 63.90.
I 4. Part 63 is amended by adding
subpart EEEEEE to read as follows:
Subpart EEEEEE—National Emission
Standards for Hazardous Air Pollutants
for Primary Copper Smelting Area
Sources
Sec.
Applicability and Compliance Dates
63.11146 What are the applicability
provisions and compliance dates?
Standards and Compliance Requirements
63.11147 What are the standards and
compliance requirements for existing
sources not using batch copper
converters?
63.11148 What are the standards and
compliance requirements for existing
sources using batch copper converters?
63.11149 What are the standards and
compliance requirements for new
sources?
Other Requirements and Information
63.11150 What General Provisions apply to
this subpart?
63.11151 What definitions apply to this
subpart?
63.11152 Who implements and enforces
this subpart?
Table 1 to Subpart EEEEEE of Part 63—
Applicability of General Provisions to
Subpart EEEEEE
Applicability and Compliance Dates
§ 63.11146 What are the applicability
provisions and compliance dates?
(a) You are subject to this subpart if
you own or operate a primary copper
smelter that is an area source of
hazardous air pollutant (HAP)
emissions.
(b) This subpart applies to each new
or existing affected source. The affected
source is each primary copper smelter.
(1) An affected source is existing if
you commenced construction or
reconstruction of the affected source
before October 6, 2006.
(2) An affected source is new if you
commenced construction or
reconstruction of the affected source on
or after October 6, 2006.
(c) This subpart does not apply to
research and development facilities, as
defined in section 112(c)(7) of the Clean
Air Act (CAA).
(d) If you own or operate an area
source subject to this subpart, you must
obtain a permit under 40 CFR part 70 or
40 CFR part 71.
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(e) If you own or operate an existing
affected source, you must achieve
compliance with the applicable
provisions of this subpart by January 23,
2007.
(f) If you own or operate a new
affected source, you must achieve
compliance with the applicable
provisions of this subpart by the dates
in paragraphs (f)(1) and (2) of this
section.
(1) If you startup a new affected
source on or before January 23, 2007,
you must achieve compliance with the
applicable provisions of this subpart not
later than January 23, 2007.
(2) If you startup a new affected
source after January 23, 2007, you must
achieve compliance with the applicable
provisions of this subpart upon startup
of your affected source.
Standards and Compliance
Requirements
§ 63.11147 What are the standards and
compliance requirements for existing
sources not using batch copper
converters?
(a) Emissions limits and work practice
standards. (1) You must not discharge to
the atmosphere through any
combination of stacks or other vents
captured process exhaust gases from the
copper concentrate dryers, smelting
vessels, converting vessels, matte drying
and grinding plants, secondary gas
systems, and anode refining department
that contain particulate matter less than
10 microns in aerodynamic diameter
(PM10) in excess of 89.5 pounds per
hour (lb/hr) on a 24-hour average basis.
(2) You must operate a capture system
that collects the gases and fumes
released during the transfer of molten
materials from smelting vessels and
converting vessels and conveys the
collected gas stream to a control device.
(3) You must operate one or more
capture systems that collect the gases
and fumes released from each vessel
used to refine blister copper, remelt
anode copper, or remelt anode scrap
and convey each collected gas stream to
a control device. One control device
may be used for multiple collected gas
streams.
(b) Compliance requirements. For
purposes of determining compliance
with the emissions limit in paragraph
(a)(1) of this section, you must comply
with the requirements in paragraphs
(b)(1) through (7) of this section.
(1) You must calibrate, maintain and
operate a system to continuously
measure emissions of particulate matter
(PM) from the smelter’s main stack.
(2) All PM collected by the smelter
main stack continuous PM sampling
system is reported as PM10 unless you
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demonstrate to the satisfaction of the
permitting authority that, due to an
infrequent event, the measured PM
contains a large fraction of particles
greater than 10 microns in diameter.
(3) To determine the mass emissions
rate, the PM10 concentration as
determined by the smelter main stack
continuous PM sampling system is
multiplied by the volumetric flow rate
for the smelter main stack and any
necessary conversion factors.
(4) Compliance with the PM10
emissions limit is demonstrated based
on the average mass PM10 emissions rate
for each 24-hour period.
(5) The results of the PM monitoring
and calculated average mass PM10
emissions rate for each 24-hour period
must be recorded and the records
maintained for at least 5 years. Collected
data must be available for inspection
when the required laboratory analysis is
completed.
(6) You must submit to the permitting
authority by the 20th day of each month
a report summarizing the 24-hour
average mass PM10 emissions rates for
the previous month.
(7) You may certify initial compliance
with the emissions limit in paragraph
(a)(1) of this section based on the results
of PM sampling conducted during the
previous month.
(c) Operation and maintenance
requirements. (1) At all times, including
periods of startup, shutdown, and
malfunction, you must to the extent
practicable, maintain and operate any
affected source, including associated air
pollution control equipment, in a
manner consistent with good air
pollution control practice for
minimizing emissions. Determination of
whether acceptable operating and
maintenance procedures are being used
will be based on information available
to the permitting authority which may
include, but is not limited to,
monitoring results, opacity
observations, review of operating and
maintenance procedures, and inspection
of the source.
(2) All pollution control equipment
must be installed, maintained, and
operated properly. Instructions from the
vendor or established maintenance
practices that maximize pollution
control must be followed. All necessary
equipment control and operating
devices, such as pressure gauges, amp
meters, volt meters, flow rate indicators,
temperature gauges, continuous
emission monitors, etc., must be
installed, operated properly, and easily
accessible to compliance inspectors. A
copy of all manufacturers’ operating
instructions for pollution control
equipment and pollution emitting
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equipment must be maintained at your
facility site. These instructions must be
available to all employees who operate
the equipment and must be made
available to the permitting authority
upon request. Maintenance records
must be made available to the
permitting authority upon request.
(3) You must document the activities
performed to assure proper operation
and maintenance of the air pollution
control equipment and monitoring
systems or devices.
(4) Except as provided in paragraph
(c)(5) of this section, in the event of an
emergency situation the owner or
operator must comply with the
requirements in paragraphs (c)(4)(i)
through (iii) of this section. For the
purposes of complying with this
paragraph, an emergency situation is
any situation arising from sudden and
reasonably unforeseeable events beyond
the control of the facility owner or
operator that requires immediate
corrective action to restore normal
operation, and that causes the affected
source to exceed an applicable
emissions limitation under this subpart,
due to unavoidable increases in
emissions attributable to the emergency.
An emergency must not include
noncompliance to the extent it is caused
by improperly designed equipment, lack
of preventive maintenance, careless or
improper operation, or operator error.
(i) During the period of the
emergency, you must implement all
reasonable steps to minimize levels of
emissions that exceed the emissions
standards or other applicable
requirements in this subpart.
(ii) You must document through
signed contemporaneous logs or other
relevant evidence that an emergency
occurred and you can identify the
probable cause, your facility was being
operated properly at the time the
emergency occurred, and the corrective
actions taken to minimize emissions as
required by paragraph (c)(4)(i) of this
section.
(iii) You must submit a notice of the
emergency to the permitting authority
within two working days of the time
when emissions limitations were
exceeded due to the emergency (or an
alternate timeframe acceptable to the
permitting authority). This notice must
contain a description of the emergency,
any steps taken to mitigate emissions,
and corrective actions taken.
(5) As an alternative to the
requirements in paragraph (c)(4) of this
section, you must comply with the
startup, shutdown, and malfunction
requirements in 40 CFR 63.6(e)(3).
(d) Deviations. You must submit
written notification to the permitting
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authority of any deviation from the
requirements of this subpart, including
the probable cause of such deviations
and any corrective actions or
preventative measures taken. You must
submit this notification within 14 days
of the date the deviation occurred.
(e) Reports. You must submit
semiannual monitoring reports to your
permitting authority. All instances of
deviations from the requirements of this
subpart must be clearly identified in the
reports.
(f) Records. (1) You must retain
records of all required monitoring data
and support information. Support
information includes all calibration and
maintenance records, all original strip
charts or appropriate recordings for
continuous monitoring instrumentation,
and copies of all reports required by this
subpart. For all monitoring
requirements, the owner or operator
must record, where applicable, the date,
place, and time of sampling or
measurement; the date analyses were
performed; the company or entity that
performed the analyses; the analytical
techniques or methods used; the results
of such analyses; and the operating
conditions existing at the time of
sampling or measurement.
(2) You must maintain records of the
activities performed to assure proper
operation and maintenance of the air
pollution control equipment and
monitoring systems or devices. Records
of these activities must be maintained
for at least 5 years.
§ 63.11148 What are the standards and
compliance requirements for existing
sources using batch copper converters?
(a) Emissions limits and work practice
standards. (1) For each copper
concentrate dryer, you must not
discharge to the atmosphere from the
dryer vent any gases that contain total
particulate matter (PM) in excess of
0.022 grains per dry standard cubic foot
(gr/dscf).
(2) You must exhaust the process off
gas from each smelting vessel to a
control device according to the
requirements in paragraphs (a)(2)(i) and
(ii) of this section.
(i) During periods when copper ore
concentrate feed is charged to and
smelted to form molten copper matte
and slag layers in the smelting vessel,
you must exhaust the process off gas
from the smelting vessel to a gas
cleaning system controlling PM and to
a sulfuric acid plant prior to discharge
to the atmosphere.
(ii) During periods when no copper
ore concentrate feed is charged to or
molten material tapped from the
smelting vessel but the smelting vessel
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remains in operation to temporarily
hold molten material in the vessel
before resuming copper production, you
must exhaust the process off gas from
the smelting vessel to an electrostatic
precipitator or baghouse prior to
discharge to the atmosphere.
(3) You must control the process
emissions released when tapping copper
matte or slag from a smelting vessel
according to paragraphs (a)(3)(i) and (ii)
of this section.
(i) You must operate a capture system
that collects the gases and fumes
released when copper matte or slag is
tapped from the smelting vessel. The
design and placement of this capture
system must be such that the tapping
port opening, launder, and receiving
vessel (e.g., ladle, slag pot) are
positioned within the confines or
influence of the capture system’s
ventilation draft during those times
when the copper matte or slag is flowing
from the tapping port opening.
(ii) You must not cause to be
discharged to the atmosphere from the
capture system used to comply with
paragraph (a)(3)(i) of this section any
gases that contain total PM in excess of
0.022 gr/dscf.
(4) For each batch copper converter,
you must meet the requirements in
paragraphs (a)(4)(i) through (iv) of this
section.
(i) You must operate a primary
capture system that collects the process
off gas vented when one or more batch
copper converters are blowing. If you
operate a batch copper converter that
does not use a ‘‘U’’-shaped side flue
located at one end of the converter, then
the capture system design must include
use of a primary hood that covers the
entire mouth of each batch copper
converter vessel when the copper
converter is positioned for blowing. The
capture system may use multiple intake
and duct segments through which the
ventilation rates are controlled
independently of each other.
(ii) If you operate a batch copper
converter that does not use a ‘‘U’’shaped side flue located at one end of
the converter, then you must operate a
secondary capture system that collects
gases and fumes released from the batch
copper converter when the converter
mouth is rotated out partially or totally
from within the confines or influence of
the primary capture system’s ventilation
draft during charging, skimming,
pouring, or holding. The capture system
design must use additional hoods (e.g.,
sliding secondary hoods, air curtain
hoods) or other capture devices (e.g.,
building evacuation systems). The
capture system may use multiple intake
and duct segments through which the
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ventilation rates are controlled
independently of each other, and
individual duct segments may be
connected to separate PM control
devices.
(iii) You must exhaust the process off
gas captured by the primary capture
system that is used to comply with
paragraph (a)(4)(i) of this section to a gas
cleaning system controlling PM and to
a sulfuric acid plant prior to discharge
to the atmosphere.
(iv) For each secondary capture
system that is used to comply with
paragraph (a)(4)(ii) of this section and is
not vented to a gas cleaning system
controlling PM and a sulfuric acid plant,
you must not cause to be discharged to
the atmosphere any gases that contain
total particulate matter in excess of 0.02
grains/dscf.
(b) Monitoring requirements for
electrostatic precipitators. To monitor
the performance of each electrostatic
precipitator used to comply with the PM
emissions limits in paragraph (a) of this
section, you must use a continuous
opacity monitoring system (COMS) that
is installed at the outlet of each
electrostatic precipitator or a common
duct at the outlet of multiple
electrostatic precipitators.
(1) Each COMS must meet
Performance Specification 1 in 40 CFR
part 60, appendix B.
(2) You must comply with the quality
assurance requirements in paragraphs
(b)(2)(i) through (v) of this section.
(i) You must automatically (intrinsic
to the opacity monitor) check the zero
and upscale (span) calibration drifts at
least once daily. For a particular COMS,
the acceptable range of zero and upscale
calibration materials is as defined in the
applicable version of Performance
Specification 1 in 40 CFR part 60,
appendix B.
(ii) You must adjust the zero and span
whenever the 24-hour zero drift or 24hour span drift exceeds 4 percent
opacity. The COMS must allow for the
amount of excess zero and span drift
measured at the 24-hour interval checks
to be recorded and quantified. The
optical surfaces exposed to the effluent
gases must be cleaned prior to
performing the zero and span drift
adjustments, except for systems using
automatic zero adjustments. For systems
using automatic zero adjustments, the
optical surfaces must be cleaned when
the cumulative automatic zero
compensation exceeds 4 percent
opacity.
(iii) You must apply a method for
producing a simulated zero opacity
condition and an upscale (span) opacity
condition using a certified neutral
density filter or other related technique
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to produce a known obscuration of the
light beam. All procedures applied must
provide a system check of the analyzer
internal optical surfaces and all
electronic circuitry including the lamp
and photodetector assembly.
(iv) Except during periods of system
breakdowns, repairs, calibration checks,
and zero and span adjustments, the
COMS must be in continuous operation
and must complete a minimum of one
cycle of sampling and analyzing for
each successive 10 second period and
one cycle of data recording for each
successive 6-minute period.
(v) You must reduce all data from the
COMS to 6-minute averages. Six-minute
opacity averages must be calculated
from 36 or more data points equally
spaced over each 6-minute period. Data
recorded during periods of system
breakdowns, repairs, calibration checks,
and zero and span adjustments must not
be included in the data averages. An
arithmetic or integrated average of all
data may be used.
(3) You must evaluate opacity
measurements from the COMS on a 24hour rolling average excluding periods
of startup, shutdown, and malfunction.
If the 24-hour rolling average opacity
exceeds 15 percent, you must initiate
investigation of the relevant controls or
equipment within 24 hours of the first
discovery of the high opacity incident
and, if necessary, take corrective action
as soon as practicable to adjust or repair
the controls or equipment to reduce the
opacity average to below the 15 percent
level.
(4) You must log in ink or electronic
format and maintain a record of 24-hour
opacity measurements performed in
accordance with paragraph (b)(3) of this
section and any corrective actions taken,
if any. A record of corrective actions
taken must include the date and time
during which the 24-hour rolling
average opacity exceeded 15 percent
and the date, time and type of the
corrective action.
(c) Monitoring requirements for
baghouses. To monitor the performance
of each baghouse used to comply with
PM emissions limits in paragraph (a) of
this section, you must use a bag leak
detection system according to the
requirements in paragraphs (c)(1)
through (4) of this section.
(1) You must install, calibrate,
maintain, and continuously operate a
bag leak detection system for the
baghouse to monitor the baghouse
performance.
(2) The baghouse leak detection
system must meet the specifications and
requirements in paragraphs (c)(2)(i)
through (v) of this section.
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(i) The bag leak detection system must
be certified by the manufacturer to be
capable of detecting particulate matter
emissions at concentrations that can
effectively discern any dysfunctional
leaks of the baghouse.
(ii) The bag leak detection system
sensor must provide output of relative
or absolute particulate matter loadings.
(iii) The bag leak detection system
must be equipped with an alarm system
that will sound automatically when an
increase in relative particulate
emissions over a preset level is detected.
The alarm must be located where it is
easily heard by plant operating
personnel.
(iv) The bag leak detection system
must be installed downstream of the
baghouse.
(v) The bag leak detection system
must be installed, operated, calibrated,
and maintained in a manner consistent
with the manufacturer’s written
specifications and recommendations.
The calibration of the system must, at a
minimum, consist of establishing the
relative baseline output level by
adjusting the sensitivity and the
averaging period of the device and
establishing the alarm set points and the
alarm delay time.
(3) If the bag leak detection system
alarm sounds, you must initiate
investigation of the baghouse within 24
hours of the first discovery of the alarm
and, if necessary, take corrective action
as soon as practicable to adjust or repair
the baghouse to minimize possible
exceedances of the applicable PM
emissions limits in paragraph (a) of this
section.
(4) You must log in ink or electronic
format and maintain a record of
installation, calibration, maintenance,
and operation of the bag leak detection
system. If the bag leak detection system
alarm sounds, the records must include
an identification of the date and time of
all bag leak detection alarms, their
cause, and an explanation of the
corrective actions taken, if any.
(d) Alternative monitoring
requirements for baghouses. As an
alternative to the requirements in
paragraph (c) of this section for bag leak
detection systems, you must monitor the
performance of each baghouse used to
comply with a PM emissions limit in
paragraph (a) of this section using a
COMS that is installed at the outlet on
the baghouse or a common duct at the
outlet of multiple baghouses. Each
COMS must meet the requirements in
paragraphs (b)(1) through (4) of this
section.
(e) Performance testing. (1) You must
demonstrate initial compliance with the
applicable PM emissions limits in
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paragraph (a) of this section based on
the results of a performance test for each
affected source.
(i) You may certify initial compliance
for an affected source based on the
results of a previous performance test
conducted within the past 12 months
before your compliance date.
(ii) If you have not conducted a
performance test to demonstrate
compliance with the applicable
emissions limits within the past 12
months before your compliance date,
you must conduct a performance test
within 180 days of your compliance
date and report the results in your
notification of compliance status.
(2) You must demonstrate subsequent
compliance with the applicable PM
emissions limits in paragraph (a) of this
section based on the results of repeat
performance tests conducted at least
every 2.5 years for each affected source.
(3) You must conduct each
performance test according to
§ 63.7(e)(1) using the test methods and
procedures in paragraphs (e)(3)(i)
through (v) of this section.
(i) Method 1 or 1A (40 CFR part 60,
appendix A) to select sampling port
locations and the number of traverse
points in each stack or duct. Sampling
sites must be located at the outlet of the
control device (or at the outlet of the
emissions source if no control device is
present) prior to any releases to the
atmosphere.
(ii) Method 2, 2A, 2C, 2D, 2F, or 2G
(40 CFR part 60, appendix A) to
determine the volumetric flow rate of
the stack gas.
(iii) Method 3, 3A, or 3B (40 CFR part
60, appendix A) to determine the dry
molecular weight of the stack gas. You
may use ANSI/ASME PTC 19.10–1981,
‘‘Flue and Exhaust Gas Analyses’’
(incorporated by reference—see § 63.14)
as an alternative to EPA Method 3B.
(iv) Method 4 (40 CFR part 60,
appendix A) to determine the moisture
content of the stack gas.
(v) Method 5 (40 CFR part 60,
appendix A) to determine the PM
concentration for negative pressure
baghouses or Method 5D (40 CFR part
60, appendix A) for positive pressure
baghouses. A minimum of three valid
test runs are needed to comprise a PM
performance test.
(f) Operation and maintenance
requirements. (1) At all times, including
periods of startup, shutdown, and
malfunction, you must to the extent
practicable, maintain and operate any
affected source, including associated air
pollution control equipment, in a
manner consistent with good air
pollution control practice for
minimizing emissions. Determination of
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whether acceptable operating and
maintenance procedures are being used
will be based on information available
to the permitting authority which may
include, but is not limited to,
monitoring results, opacity
observations, review of operating and
maintenance procedures, and inspection
of the source.
(2) All pollution control equipment
must be installed, maintained, and
operated properly. Instructions from the
vendor or established maintenance
practices that maximize pollution
control must be followed. All necessary
equipment control and operating
devices, such as pressure gauges, amp
meters, volt meters, flow rate indicators,
temperature gauges, continuous
emissions monitor, etc., must be
installed, operated properly and easily
accessible to compliance inspectors. A
copy of all manufacturers’ operating
instructions for pollution control
equipment and pollution emitting
equipment must be maintained at your
facility site. These instructions must be
available to all employees who operate
the equipment and must be made
available to the permitting authority
upon request. Maintenance records
must be made available to the
permitting authority upon request.
(3) You must document the activities
performed to assure proper operation
and maintenance of the air pollution
control equipment and monitoring
systems or devices. Records of these
activities must be maintained as
required by the permitting authority.
(4) Except as specified in paragraph
(f)(5) of this section, in the event of an
emergency situation, you must comply
with the requirements specified in
paragraphs (f)(4)(i) through (iii) of this
section. For the purpose of complying
with this paragraph, an emergency
situation is any situation arising from
sudden and reasonably unforeseeable
events beyond the control of the facility
owner or operator that requires
immediate corrective action to restore
normal operation and that causes the
affected source to exceed applicable
emission limitation under this subpart
due to unavoidable increases in
emissions attributable to the emergency.
An emergency must not include
noncompliance to the extent it is caused
by improperly designed equipment, lack
of preventive maintenance, careless or
improper operation, or operator error.
(i) During the period of the emergency
you must implement all reasonable
steps to minimize levels of emissions
that exceeded the emission standards or
other applicable requirements in this
subpart.
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(ii) You must document through
signed contemporaneous logs or other
relevant evidence that an emergency
occurred and you can identify the
probable cause, your facility was being
operated properly at the time the
emergency occurred, and the corrective
actions taken to minimize emissions as
required by paragraph (f)(4)(i) of this
section.
(iii) You must submit a notice of the
emergency to the permitting authority
within two working days of the time
when emission limitations were
exceeded due to the emergency (or an
alternate timeframe acceptable to the
permitting authority). This notice must
contain a description of the emergency,
any steps taken to mitigate emissions,
and corrective actions taken.
(5) As an alternative to the
requirements in paragraph (f)(4) of this
section, you must comply with the
startup, shutdown, and malfunction
requirements in 40 CFR 63.6(e)(3).
(g) Recordkeeping requirements. (1)
You must maintain records of the
occurrence and duration of any startup,
shutdown, or malfunction in the
operation of an affected source subject
to this subpart; any malfunction of the
air pollution control equipment; or any
periods during which a continuous
monitoring system or monitoring device
is inoperative.
(2) You must maintain a file of all
measurements, including continuous
monitoring system, monitoring device,
and performance testing measurements;
all continuous monitoring system
performance evaluations; all continuous
monitoring system or monitoring device
calibration checks; adjustments and
maintenance performed on these
systems or devices; and all other
information required by this section
recorded in a permanent form suitable
for inspection. The file must be retained
for at least 5 years following the date of
such measurements, maintenance,
reports.
(h) Reporting requirements. (1) You
must prepare and submit to the
permitting authority an excess
emissions and monitoring systems
performance report and summary report
every calendar quarter. A less frequent
reporting interval may used for either
report as approved by the permitting
authority.
(2) The summary report must include
the information in paragraphs (h)(2)(i)
through (iv) of this section.
(i) The magnitude of excess emissions
computed, any conversion factor(s)
used, and the date and time of
commencement and completion of each
time period of excess emissions. The
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process operating time during the
reporting period.
(ii) Specific identification of each
period of excess emissions that occurs
during startups, shutdowns, and
malfunctions of the affected facility. The
nature and cause of any malfunction (if
known), the corrective action taken or
preventative measures adopted.
(iii) The date and time identifying
each period during which the
continuous monitoring system was
inoperative except for zero and span
checks and the nature of the system
repairs or adjustments.
(iv) When no excess emissions have
occurred or the continuous monitoring
system(s) have not been inoperative,
repaired, or adjusted, such information
must be stated in the report.
§ 63.11149 What are the standards and
compliance requirements for new sources?
(a) Emissions limits and work practice
standards. (1) You must not discharge to
the atmosphere exhaust gases that
contain total PM in excess of 0.6 pound
per ton of copper concentrate feed
charged on a 24-hour average basis from
any combination of stacks, vents, or
other openings on furnaces, reactors, or
other types of process vessels used for
the production of anode copper from
copper sulfide ore concentrates by
pyrometallurgical techniques. Examples
of such process equipment include, but
are not limited to, copper concentrate
dryers, smelting flash furnaces, smelting
bath furnaces, converting vessels,
combined smelting and converting
reactors, anode refining furnaces, and
anode shaft furnaces.
(2) You must operate a capture system
that collects the gases and fumes
released during the transfer of molten
materials from smelting vessels and
converting vessels and conveys the
collected gas stream to a baghouse or
other PM control device.
(3) You must operate one or more
capture systems that collect the gases
and fumes released from each vessel
used to refine blister copper, remelt
anode copper, or remelt anode scrap
and convey each collected gas stream to
a baghouse or other PM control device.
One control device may be used for
multiple collected gas streams.
(b) Monitoring requirements. (1) You
must install, operate, and maintain a PM
continuous emissions monitoring
system (CEMS) to measure and record
PM concentrations and gas stream flow
rates for the exhaust gases discharged to
the atmosphere from each affected
source subject to the emissions limit in
paragraph (a)(1) of this section. A single
PM CEMS may be used for the
combined exhaust gas streams from
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multiple affected sources at a point
before the gases are discharged to the
atmosphere. For each PM CEMS used to
comply with this paragraph, you must
meet the requirements in paragraphs
(b)(1)(i) through (iii) of this section.
(i) You must install, certify, operate,
and maintain the PM CEMS according
to EPA Performance Specification 11 in
40 CFR part 60, appendix B, and the
quality assurance requirements of
Procedure 2 in 40 CFR part 60,
appendix F.
(ii) You must conduct an initial
performance evaluation of the PM
CEMS according to the requirements of
Performance Specification 11 in 40 CFR
part 60, appendix B. Thereafter, you
must perform the performance
evaluations as required by Procedure 2
in 40 CFR part 60, appendix F.
(iii) You must perform quarterly
accuracy determinations and daily
calibration drift tests for the PM CEMS
according to Procedure 2 in 40 CFR part
60, appendix F.
(2) You must install, operate, and
maintain a weight measurement system
to measure and record the weight of the
copper concentrate feed charged to the
smelting vessel on a daily basis.
(c) Compliance requirements. (1) You
must demonstrate initial compliance
with the emissions limit in paragraph
(a)(1) of this section using the
procedures in paragraph (c)(2) this
section within 180 days after startup
and report the results in your
notification of compliance status no
later than 30 days after the end of the
compliance demonstration.
(2) You must demonstrate continuous
compliance with the emissions limit in
paragraph (a)(1) of this section using the
procedures in paragraph (c)(2)(i)
through (iii) of this section whenever
your facility is producing copper from
copper concentrate.
(i) You must continuously monitor
and record PM emissions, determine
and record the daily (24-hour) value for
each day, and calculate and record the
daily average pounds of total PM per ton
of copper concentrate feed charged to
the smelting vessel according to the
requirements in paragraph (b) of this
section.
(ii) You must calculate the daily
average at the end of each calendar day
for the preceding 24-hour period.
(iii) You must maintain records of the
calculations of daily averages with
supporting information and data,
including measurements of the weight
of copper concentrate feed charged to
the smelting vessel. Collected PM CEMS
data must be made available for
inspection.
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(d) Alternative startup, shutdown, and
malfunction requirements. You must
comply with the requirements specified
in this paragraph as an alternative to the
requirements in 40 CFR 63.6(e)(3). In
the event of an emergency situation, you
must comply with the requirements
specified in paragraphs (d)(1) through
(3) of this section. For the purpose of
complying with this paragraph, an
emergency situation is any situation
arising from sudden and reasonably
unforeseeable events beyond the control
of the facility owner or operator that
requires immediate corrective action to
restore normal operation, and that
causes the affected source to exceed an
applicable emissions limitation under
this subpart, due to unavoidable
increases in emissions attributable to
the emergency. An emergency must not
include noncompliance to the extent it
is caused by improperly designed
equipment, lack of preventive
maintenance, careless or improper
operation, or operator error.
(1) During the period of the
emergency, you must implement all
reasonable steps to minimize levels of
emissions that exceeded the emission
standards or other applicable
requirements in this subpart.
(2) You must document through
signed contemporaneous logs or other
relevant evidence that an emergency
occurred and you can identify the
probable cause, your facility was being
operated properly at the time the
emergency occurred, and the corrective
actions taken to minimize emissions as
required by paragraph (d)(1) of this
section.
(3) You must submit a notice of the
emergency to the permitting authority
within two working days of the time
when emissions limitations were
exceeded due to the emergency (or an
alternate timeframe acceptable to the
permitting authority). This notice must
contain a description of the emergency,
any steps taken to mitigate emissions,
and corrective actions taken.
(e) Reports. You must submit to the
permitting authority by the 20th day of
each month a summary of the daily
average PM per ton of copper
concentrate feed charged to the smelting
vessel for the previous month.
Other Requirements and Information
jlentini on PROD1PC65 with RULES2
§ 63.11150 What General Provisions apply
to this subpart?
(a) If you own or operate a new or
existing affected source, you must
comply with the requirements of the
General Provisions (40 CFR part 63,
subpart A) as specified in Table 1 to this
subpart.
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(b) If you own or operate an existing
affected source subject to § 63.11147,
your notification of compliance status
required by § 63.9(h) must include the
information specified in paragraphs
(b)(1) through (4) of this section.
(1) If you certify initial compliance
with the PM emissions limit in
§ 63.11147(a)(1) based on monitoring
data from the previous month, your
notification of compliance status must
include this certification of compliance,
signed by a responsible official: ‘‘This
facility complies with the PM emissions
limit in § 63.11147(a)(1) based on
monitoring data that were collected
during the previous month.’’
(2) If you conduct a new performance
test to demonstrate initial compliance
with the PM emissions limit in
§ 63.11147(a)(1), your notification of
compliance status must include the
results of the performance test,
including required monitoring data.
(3) Your notification of compliance
status must include this certification of
compliance, signed by a responsible
official, for the work practice standard
in § 63.11147(a)(2): ‘‘This facility
complies with the requirement to
capture gases from transfer of molten
materials from smelting vessels and
converting vessels and convey them to
a control device in accordance with
§ 63.11147(a)(2).’’
(4) Your notification of compliance
status must include this certification of
compliance, signed by a responsible
official, for the work practice standard
in § 63.11147(a)(3): ‘‘This facility
complies with the requirement to
capture gases from operations in the
anode refining department and convey
them to a PM control device in
accordance with § 63.11147(a)(3).’’
(c) If you own or operate an existing
affected source subject to § 63.11148,
your notification of compliance status
required by § 63.9(h) must include the
information specified in paragraphs
(c)(1) through (4) of this section.
(1) If you certify initial compliance
with the PM emissions limit in
§ 63.11148(a)(1), (a)(3)(ii), and (a)(4)(iv)
based on the results of a previous
performance test conducted within the
past 12 months before your compliance
date, your notification of compliance
status must include this certification of
compliance, signed by a responsible
official: ‘‘This facility complies with the
PM emissions limit in § 63.11148(a)(1)
based on the results of a previous
performance test.’’
(2) If you conduct a new performance
test to demonstrate initial compliance
with the PM emissions limits in
§ 63.11148(a)(1), (a)(3)(ii), and (a)(4)(iv),
your notification of compliance status
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must include the results of the
performance test, including required
monitoring data.
(3) Your notification of compliance
status must include this certification of
compliance, signed by a responsible
official, for the work practice standards
in § 63.11148(a)(2), and (a)(4)(iii): ‘‘This
facility complies with the requirement
to vent captured process gases to a gas
cleaning system controlling PM and to
a sulfuric acid plant in accordance with
§ 63.11148(a)(2) and (a)(4)(iii).’’
(3) Your notification of compliance
status must include this certification of
compliance, signed by a responsible
official, for the work practice standard
in § 63.11148(a)(3)(i): ‘‘This facility
complies with the requirement to
operate capture systems to collect gases
and fumes released when copper matte
or slag is tapped from the smelting
vessel in accordance with
§ 63.11148(a)(3)(i).’’
(4) Your notification of compliance
status must include this certification of
compliance, signed by a responsible
official, for the work practice standard
in § 63.11148(a)(4): ‘‘This facility
complies with the requirement to
operate capture systems to collect gases
and fumes released during batch copper
converter operations in accordance with
§ 63.11148(a)(4).’’
(d) If you own or operate a new
affected source, your notification of
compliance status required by § 63.9(h)
must include the information in
paragraphs (d)(1) through (3) of this
section.
(1) Your notification of compliance
status must include the results of the
initial performance test and monitoring
data collected during the test that
demonstrate compliance with the
emissions limit in § 63.11149(a)(1).
(2) Your notification of compliance
status must include this certification of
compliance, signed by a responsible
official, for the work practice standard
in § 63.11149(a)(2): ‘‘This facility
complies with the requirement to
capture gases from transfer of molten
materials from smelting vessels and
converting vessels and convey them to
a PM control device in accordance with
§ 63.11149(a)(2).’’
(3) Your notification of compliance
status must include this certification of
compliance, signed by a responsible
official, for the work practice standard
in § 63.11149(a)(3): ‘‘This facility
complies with the requirement to
capture gases from each vessel used to
refine blister copper, remelt anode
copper, or remelt anode scrap, and
convey them to a PM control device in
accordance with § 63.11149(a)(3).’’
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§ 63.11151
subpart?
Federal Register / Vol. 72, No. 14 / Tuesday, January 23, 2007 / Rules and Regulations
What definitions apply to this
Terms used in this subpart are
defined in the CAA, in 40 CFR 63.2, and
in this section as follows:
Anode refining department means the
area at a primary copper smelter in
which anode copper refining operations
are performed. Emissions sources in the
anode refining department include
anode refining furnaces and anode shaft
furnaces.
Baghouse means a control device that
collects particulate matter by filtering
the gas stream through bags. A baghouse
is also referred to as a ‘‘fabric filter.’’
Bag leak detection system means a
system that is capable of continuously
monitoring relative particulate matter
(dust) loadings in the exhaust of a
baghouse in order to detect bag leaks
and other upset conditions. A bag leak
detection system includes, but is not
limited to, an instrument that operates
on triboelectric, light scattering,
transmittance or other effect to
continuously monitor relative
particulate matter loadings.
Batch copper converter means a
converter in which molten copper matte
is charged and then oxidized to form
blister copper by a process that is
performed in discrete batches using a
sequence of charging, blowing,
skimming, and pouring.
Capture system means the collection
of components used to capture gases
and fumes released from one or more
emissions points and then convey the
captured gas stream to a control device.
A capture system may include, but is
not limited to, the following
components as applicable to a given
capture system design: Duct intake
devices, hoods, enclosures, ductwork,
dampers, manifolds, plenums, and fans.
Charging means the operating mode
for a batch copper converter during
which molten or solid material is added
into the vessel.
Control device means air pollution
control equipment used to remove PM
from a gas stream.
Converting vessel means a furnace,
reactor, or other type of vessel in which
copper matte is oxidized to form blister
copper.
Copper concentrate means copper ore
that has been beneficiated to increase its
copper content.
Copper concentrate dryer means a
vessel in which copper concentrates are
heated in the presence of air to reduce
the moisture content of the material.
Supplemental copper-bearing feed
materials and fluxes may be added or
mixed with the copper concentrates fed
to a copper concentrate dryer.
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Copper concentrate feed means the
mixture of copper concentrate,
secondary copper-bearing materials,
recycled slags and dusts, fluxes, and
other materials blended together for
feeding to the smelting vessel.
Copper matte means a material
predominately composed of copper and
iron sulfides produced by smelting
copper ore concentrates.
Deviation means any instance in
which an affected source subject to this
subpart, or an owner or operator of such
a source:
(1) Fails to meet any requirement or
obligation established by this subpart,
including but not limited to any
emissions limitation or work practice
standard;
(2) Fails to meet any term or condition
that is adopted to implement an
applicable requirement in this subpart
and that is included in the operating
permit for any affected source required
to obtain such a permit; or
(3) Fails to meet any emissions
limitation or work practice standard in
this subpart during startup, shutdown,
or malfunction, regardless of whether or
not such failure is permitted by this
subpart.
Holding means the operating mode for
a batch copper converter or a holding
furnace associated with a smelting
furnace during which the molten bath is
maintained in the vessel but no blowing
or smelting is performed nor is material
added into or removed from the vessel.
Matte drying and grinding plant
means the area at a primary copper
smelter in which wet granulated matte
copper is ground in a mill, dried by
blowing heated air through the mill, and
then separated from the drying air
stream using a control device such as a
baghouse.
Pouring means the operating mode for
a batch copper converter during which
molten copper is removed from the
vessel.
Primary copper smelter means any
installation or any intermediate process
engaged in the production of copper
from copper sulfide ore concentrates
through the use of pyrometallurgical
techniques.
Responsible official means
responsible official as defined at 40 CFR
70.2.
Secondary gas system means a
capture system that collects the gases
and fumes released when removing and
transferring molten materials from one
or more vessels using tapping ports,
launders, and other openings in the
vessels. Examples of molten material
include, but are not limited to: Copper
matte, slag, and blister copper.
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Skimming means the batch copper
converter operating mode during which
molten slag is removed from the vessel.
Smelting vessel means a furnace,
reactor, or other type of vessel in which
copper ore concentrate and fluxes are
smelted to form a molten mass of
material containing copper matte and
slag. Other copper-bearing materials
may also be charged to the smelting
vessel.
Work practice standard means any
design, equipment, work practice, or
operational standard, or combination
thereof.
§ 63.11152 Who implements and enforces
this subpart?
(a) This subpart can be implemented
and enforced by the U.S. EPA, or a
delegated authority such as a State,
local, or tribal agency. If the U.S. EPA
Administrator has delegated authority to
a State, local, or tribal agency, then that
Agency has the authority to implement
and enforce this subpart. You should
contact your U.S. EPA Regional Office
to find out if this subpart is delegated
to a State, local, or tribal agency within
your State.
(b) In delegating implementation and
enforcement authority of this subpart to
a State, local, or tribal agency under 40
CFR part 63, subpart E, the authorities
contained in paragraph (c) of this
section are retained by the
Administrator of the U.S. EPA and are
not transferred to the State, local, or
tribal agency.
(c) The authorities that will not be
delegated to State, local, or tribal
agencies are listed in paragraphs (c)(1)
through (5) of this section.
(1) Approval of an alternative nonopacity emissions standard under
§ 63.6(g).
(2) Approval of an alternative opacity
emissions standard under § 63.6(h)(9).
(3) Approval of a major change to a
test method under § 63.7(e)(2)(ii) and (f).
A ‘‘major change to test method’’ is
defined in § 63.90.
(4) Approval of a major change to
monitoring under § 63.8(f). A ‘‘major
change to monitoring’’ is defined in
§ 63.90.
(5) Approval of a major change to
recordkeeping/reporting under
§ 63.10(f). A ‘‘major change to
recordkeeping/reporting’’ is defined in
§ 63.90.
As required in § 63.11150(a), you
must comply with the requirements of
the NESHAP General Provisions (40
CFR part 63, subpart A) as shown in the
following table.
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2951
TABLE 1 TO SUBPART EEEEEE OF PART 63.—APPLICABILITY OF GENERAL PROVISIONS TO SUBPART EEEEEE
Applies to subpart EEEEEE?
Citation
Subject
63.1(a)(1), (a)(2), (a)(3), (a)(4), (a)(6),
(a)(10)–(a)(12) (b)(1), (b)(3), (c)(1),
(c)(2), (c)(5), (e).
63.1(a)(5), (a)(7)–(a)(9), (b)(2), (c)(3),
(c)(4), (d).
63.2 ..........................................................
63.3 ..........................................................
63.4 ..........................................................
63.5 ..........................................................
Applicability ............................................
Yes.
Reserved ................................................
No.
Definitions ..............................................
Units and Abbreviations .........................
Prohibited Activities and Circumvention
Preconstruction Review and Notification
Requirements.
Compliance with Standards and Maintenance
Requirements—Applicability
and Compliance Dates.
Operation and Maintenance Requirements.
Yes.
Yes.
Yes.
No.
Compliance with Nonopacity Emission
Standards.
Reserved ................................................
Yes.
................................................................
Yes/No ..............
Performance Testing Requirements ......
................................................................
Yes.
Yes/No ..............
63.8(a)(1), (a)(2), (b), (c), (f), (g) .............
63.8(a)(3) .................................................
63.8(a)(4) .................................................
Monitoring Requirements .......................
Reserved ................................................
................................................................
Yes.
No.
No .....................
63.8(d), (e) ...............................................
................................................................
Yes/No ..............
63.9(a), (b)(1), (b)(2), (b)(5), (c), (d),
(h)(1)–(h)(3), (h)(5), (h)(6), (i), (j).
63.9(b)(3), (h)(4) ......................................
63.9(b)(4), (f) ...........................................
63.9(e), (g) ...............................................
Notification Requirements ......................
Yes.
Reserved ................................................
................................................................
................................................................
No.
No.
Yes/No ..............
63.10(a), (b)(1), (d)(1), (d)(2), (d)(4),
(d)(5), (f).
63.10(b)(2), (b)(3), (c)(1) (c)(5)–(c)(8),
(c)(10)–(c)(15), (e)(1), (e)(2).
63.10(c)(2)–(c)(4), (c)(9) ..........................
63.10(d)(3), (e)(4) ....................................
Recordkeeping and Reporting Requirements.
................................................................
Yes/No ..............
Reserved ................................................
................................................................
No.
No .....................
63.10(e)(3) ...............................................
................................................................
Yes/No ..............
63.11 ........................................................
Control Device Requirements ................
No .....................
63.12
63.13
63.14
63.15
State Authorities and Delegations .........
Addresses ..............................................
Incorporations by Reference ..................
Availability of Information and Confidentiality.
Performance Track Provisions ...............
Yes.
Yes.
Yes.
Yes.
63.6(a), (b)(1)–(b)(5),
(c)(2), (c)(5).
(b)(7),
(c)(1),
63.6(e) .....................................................
63.6(f), (g), (i), (j) .....................................
jlentini on PROD1PC65 with RULES2
63.6(b)(6), (c)(3), (c)(4), (d), (e)(2),
(e)(3)(ii), (h)(3), (h)(5)(iv).
63.6(h)(1)–(h)(4),
(h)(5)(i)–(h)(5)(iii),
(h)(6)–(h)(9).
63.7(a), (e), (f), (g), (h) ............................
63.7(b), (c) ...............................................
........................................................
........................................................
........................................................
........................................................
63.16 ........................................................
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Explanation
Yes.
Yes/No ..............
Operation and maintenance requirements do not apply to existing
sources except that the startup, shutdown, and malfunction requirements
in § 63.6(e)(3) are allowed as an alternative to the rule requirements for
emergency situations. Operation and
maintenance requirements apply to
new sources except that the rule requirements for emergency situations
are allowed as an alternative to the
startup, shutdown, and malfunction
requirements in § 63.6(e)(3).
No.
Yes/No ..............
Requirements apply to new sources but
not existing sources.
Notification of performance tests and
quality assurance program apply to
new sources but not existing sources.
Subpart EEEEEE does not require
flares.
Requirements for quality control program and performance evaluations
apply to new sources but not existing
sources.
Notification requirements for performance test and use of continuous monitoring systems apply to new sources
but not existing sources.
Recordkeeping requirements apply to
new sources but not existing sources.
Recordkeeping requirements apply to
new sources but not existing sources.
Reporting requirements apply to new
sources but not existing sources.
Reporting requirements apply to new
sources but not existing sources.
Subpart EEEEEE does not require
flares.
Yes.
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Federal Register / Vol. 72, No. 14 / Tuesday, January 23, 2007 / Rules and Regulations
5. Part 63 is amended by adding
subpart FFFFFF to read as follows:
I
Subpart FFFFFF—National Emission
Standards for Hazardous Air Pollutants
for Secondary Copper Smelting Area
Sources
Sec.
Applicability and Compliance Dates
63.11153 Am I subject to this subpart?
63.11154 What are my compliance dates?
Standards and Compliance Requirements
63.11155 What are the standards and
compliance requirements for new
sources?
63.11156 [Reserved]
Other Requirements and Information
63.11157 What General Provisions apply to
this subpart?
63.11158 What definitions apply to this
subpart?
63.11159 Who implements and enforces
this subpart?
Table 1 to Subpart FFFFFF of Part 63—
Applicability of General Provisions to
Subpart FFFFFF
Applicability and Compliance Dates
§ 63.11153
Am I subject to this subpart?
(a) You are subject to this subpart if
you own or operate a new secondary
copper smelter that is an area source of
hazardous air pollutant (HAP)
emissions.
(b) This subpart applies to each new
affected source. The affected source is
each secondary copper smelter. Your
secondary copper smelter is a new
affected source if you commenced
construction or reconstruction of the
affected source before October 6, 2006.
(c) This subpart does not apply to
research and development facilities, as
defined in section 112(c)(7) of the CAA.
(d) If you own or operate an area
source subject to this subpart, you must
obtain a permit under 40 CFR part 70 or
40 CFR part 71.
§ 63.11154
dates?
What are my compliance
jlentini on PROD1PC65 with RULES2
(a) If you startup a new affected
source on or before January 23, 2007,
you must achieve compliance with the
applicable provisions of this subpart not
later than January 23, 2007.
(b) If you startup a new affected
source after January 23, 2007, you must
achieve compliance with the applicable
provisions of this subpart upon startup
of your affected source.
Standards and Compliance
Requirements
§ 63.11155 What are the standards and
compliance requirements for new sources?
(a) You must not discharge to the
atmosphere any gases which contain
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particulate matter (PM) in excess of
0.002 grains per dry standard cubic foot
(gr/dscf) from the exhaust vent of any
capture system for a smelting furnace,
melting furnace, or other vessel that
contains molten material and any
capture system for the transfer of molten
material.
(b) For each smelting furnace, melting
furnace, or other vessel that contains
molten material, you must install and
operate a capture system that collects
the gases and fumes from the vessel and
from the transfer of molten material and
convey the collected gas stream to a
control device.
(c) You must prepare and operate at
all times according to a written plan for
the selection, inspection, and
pretreatment of copper scrap to
minimize, to the extent practicable, the
amount of oil and plastics in the scrap
that is charged to the smelting furnace.
Your plan must include a training
program for scrap inspectors. You must
keep records to demonstrate continuous
compliance with the requirements of
your plan. You must keep a current
copy of your pollution prevention plan
onsite and available for inspection.
(d) You must install, operate, and
maintain a bag leak detection system on
all baghouses used to comply with the
PM emissions limit in paragraph (a) of
this section according to paragraph
(d)(1) of this section, prepare and
operate by a site-specific monitoring
plan according to paragraph (d)(2) of
this section, take corrective action
according to paragraph (d)(3) of this
section, and record information
according to paragraph (d)(4) of this
section.
(1) Each bag leak detection system
must meet the specifications and
requirements in paragraphs (d)(1)(i)
through (viii) of this section.
(i) The bag leak detection system must
be certified by the manufacturer to be
capable of detecting PM emissions at
concentrations of 1 milligram per actual
cubic meter (0.00044 grains per actual
cubic foot) or less.
(ii) The bag leak detection system
sensor must provide output of relative
PM loadings. The owner or operator
must continuously record the output
from the bag leak detection system using
electronic or other means (e.g., using a
strip chart recorder or a data logger.)
(iii) The bag leak detection system
must be equipped with an alarm system
that will sound when the system detects
an increase in relative particulate
loading over the alarm set point
established according to paragraph
(d)(1)(iv) of this section, and the alarm
must be located such that it can be
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heard by the appropriate plant
personnel.
(iv) In the initial adjustment of the bag
leak detection system, you must
establish, at a minimum, the baseline
output by adjusting the sensitivity
(range) and the averaging period of the
device, the alarm set points, and the
alarm delay time.
(v) Following initial adjustment, you
must not adjust the averaging period,
alarm set point, or alarm delay time
without approval from the
Administrator or delegated authority
except as provided in paragraph
(d)(1)(vi) of this section.
(vi) Once per quarter, you may adjust
the sensitivity of the bag leak detection
system to account for seasonal effects,
including temperature and humidity,
according to the procedures identified
in the site-specific monitoring plan
required by paragraph (d)(2) of this
section.
(vii) You must install the bag leak
detection sensor downstream of the
baghouse and upstream of any wet
scrubber.
(viii) Where multiple detectors are
required, the system’s instrumentation
and alarm may be shared among
detectors.
(2) You must develop and submit to
the Administrator or delegated authority
for approval a site-specific monitoring
plan for each bag leak detection system.
You must operate and maintain the bag
leak detection system according to the
site-specific monitoring plan at all
times. Each monitoring plan must
describe the items in paragraphs (d)(2)(i)
through (vi) of this section.
(i) Installation of the bag leak
detection system;
(ii) Initial and periodic adjustment of
the bag leak detection system, including
how the alarm set-point will be
established;
(iii) Operation of the bag leak
detection system, including quality
assurance procedures;
(iv) How the bag leak detection
system will be maintained, including a
routine maintenance schedule and spare
parts inventory list;
(v) How the bag leak detection system
output will be recorded and stored; and
(vi) Corrective action procedures as
specified in paragraph (d)(3) of this
section. In approving the site-specific
monitoring plan, the Administrator or
delegated authority may allow owners
and operators more than 3 hours to
alleviate a specific condition that causes
an alarm if the owner or operator
identifies in the monitoring plan this
specific condition as one that could lead
to an alarm, adequately explains why it
is not feasible to alleviate this specific
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condition within 3 hours of the time the
alarm occurs, and demonstrates that the
requested time will ensure alleviation of
this condition as expeditiously as
practicable.
(3) For each bag leak detection
system, you must initiate procedures to
determine the cause of every alarm
within 1 hour of the alarm. Except as
provided in paragraph (d)(2)(vi) of this
section, you must alleviate the cause of
the alarm within 3 hours of the alarm by
taking whatever corrective action(s) are
necessary. Corrective actions may
include, but are not limited to the
following:
(i) Inspecting the baghouse for air
leaks, torn or broken bags or filter
media, or any other condition that may
cause an increase in particulate
emissions;
(ii) Sealing off defective bags or filter
media;
(iii) Replacing defective bags or filter
media or otherwise repairing the control
device;
(iv) Sealing off a defective baghouse
compartment;
(v) Cleaning the bag leak detection
system probe or otherwise repairing the
bag leak detection system; or
(vi) Shutting down the process
producing the particulate emissions.
(4) You must maintain records of the
information specified in paragraphs
(d)(4)(i) through (iii) of this section for
each bag leak detection system.
(i) Records of the bag leak detection
system output;
(ii) Records of bag leak detection
system adjustments, including the date
and time of the adjustment, the initial
bag leak detection system settings, and
the final bag leak detection system
settings; and
(iii) The date and time of all bag leak
detection system alarms, the time that
procedures to determine the cause of an
alarm were initiated, whether
procedures were initiated within 1 hour
of the alarm, the cause of the alarm, an
explanation of the actions taken, the
date and time the cause of the alarm was
alleviated, and whether the alarm was
alleviated within 3 hours of the alarm.
(e) You must conduct a performance
test to demonstrate initial compliance
with the PM emissions limit within 180
days after startup and report the results
in your notification of compliance
status. You must conduct each PM test
according to § 63.7(e)(1) using the test
methods and procedures in paragraphs
(e)(1) through (5) of this section.
(1) Method 1 or 1A (40 CFR part 60,
appendix A) to select sampling port
locations and the number of traverse
points in each stack or duct. Sampling
sites must be located at the outlet of the
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17:01 Jan 22, 2007
Jkt 211001
control device (or at the outlet of the
emissions source if no control device is
present) prior to any releases to the
atmosphere.
(2) Method 2, 2A, 2C, 2D, 2F, or 2G
(40 CFR part 60, appendix A) to
determine the volumetric flow rate of
the stack gas.
(3) Method 3, 3A, or 3B (40 CFR part
60, appendix A) to determine the dry
molecular weight of the stack gas. You
may use ANSI/ASME PTC 19.10–1981,
‘‘Flue and Exhaust Gas Analyses
(incorporated by reference—see § 63.14)
as an alternative to EPA Method 3B.
(4) Method 4 (40 CFR part 60,
appendix A) to determine the moisture
content of the stack gas.
(5) Method 5 (40 CFR part 60,
appendix A) to determine the PM
concentration for negative pressure
baghouses and Method 5D (40 CFR part
60, appendix A) for positive pressure
baghouses. The sampling time and
volume for each run must be at least 60
minutes and 0.85 dry standard cubic
meters (30 dry standard cubic feet). A
minimum of three valid test runs are
needed to comprise a PM performance
test.
(f) You must conduct subsequent
performance tests to demonstrate
compliance with the PM emissions limit
at least once every 5 years.
(g) If you use a control device other
than a baghouse, you must prepare and
submit a monitoring plan to the
Administrator for approval. Each plan
must contain the information in
paragraphs (g)(1) through (5) of this
section.
(1) A description of the device;
(2) Test results collected in
accordance with paragraph (e) of this
section verifying the performance of the
device for reducing PM to the levels
required by this subpart;
(3) Operation and maintenance plan
for the control device (including a
preventative maintenance schedule
consistent with the manufacturer’s
instructions for routine and long-term
maintenance) and continuous
monitoring system.
(4) A list of operating parameters that
will be monitored to maintain
continuous compliance with the
applicable emission limits; and
(5) Operating parameter limits based
on monitoring data collected during the
performance test.
§ 63.11156
[Reserved]
Other Requirements and Information
§ 63.11157 What General Provisions apply
to this subpart?
(a) If you own or operate a new
affected source, you must comply with
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2953
the requirements of the General
Provisions in 40 CFR part 63, subpart A
as specified in Table 1 to this subpart.
(b) Your notification of compliance
status required by § 63.9(h) must
include the following:
(1) The results of the initial
performance tests and monitoring data
collected during the test.
(2) This certification of compliance,
signed by a responsible official, for the
work practice standard in § 63.1155(b):
‘‘This facility complies with the
requirement for a capture system for
each smelting furnace, melting furnace,
or other vessel that contains molten
material in accordance with
§ 63.11155(b).’’
(3) This certification of compliance,
signed by a responsible official, for the
work practice standard in § 63.11155(c):
‘‘This facility complies with the
requirement for a written plan for the
selection, inspection, and pretreatment
of copper scrap in accordance with
§ 63.11155(c).’’
(4) This certification of compliance,
signed by a responsible official, for the
work practice standard in
§ 63.11155(d)(2): ‘‘This facility has an
approved monitoring plan in
accordance with § 63.11155(d)(2).’’
(5) This certification of compliance,
signed by a responsible official, for the
work practice standard in § 63.11157(g):
‘‘This facility has an approved
monitoring plan in accordance with
§ 63.11157(g).’’
§ 63.11158
subpart?
What definitions apply to this
Terms used in this subpart are
defined in the CAA, in 40 CFR 63.2, and
in this section as follows:
Anode copper means copper that is
cast into anodes and refined in an
electrolytic process to produce high
purity copper.
Capture system means the collection
of components used to capture gases
and fumes released from one or more
emissions points and then convey the
captured gas stream to a control device.
A capture system may include, but is
not limited to, the following
components as applicable to a given
capture system design: duct intake
devices, hoods, enclosures, ductwork,
dampers, manifolds, plenums, and fans.
Melting furnace means any furnace,
reactor, or other type of vessel that heats
solid materials and produces a molten
mass of material.
Secondary copper smelter means a
facility that processes copper scrap in a
blast furnace and converter or that uses
another pyrometallurgical purification
process to produce anode copper from
copper scrap, including low-grade
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Federal Register / Vol. 72, No. 14 / Tuesday, January 23, 2007 / Rules and Regulations
copper scrap. A facility where recycled
copper scrap or copper alloy scrap is
melted to produce ingots or for direct
use in a manufacturing process is not a
secondary copper smelter.
Smelting furnace means any furnace,
reactor, or other type of vessel in which
copper scrap and fluxes are melted to
form a molten mass of material
containing copper and slag.
Work practice standard means any
design, equipment, work practice, or
operational standard, or combination
thereof.
§ 63.11159 Who implements and enforces
this subpart?
(a) This subpart can be implemented
and enforced by the U.S. EPA, or a
delegated authority such as a State,
local, or tribal agency. If the U.S. EPA
Administrator has delegated authority to
a State, local, or tribal agency, then that
Agency has the authority to implement
and enforce this subpart. You should
contact your U.S. EPA Regional Office
to find out if 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 40
CFR part 63, subpart E, the authorities
contained in paragraph (c) of this
section are retained by the
Administrator of the U.S. EPA and are
not transferred to the State, local, or
tribal agency.
(c) The authorities that will not be
delegated to State, local, or tribal
agencies are listed in paragraphs (c)(1)
through (4) of this section.
(1) Approval of an alternative nonopacity emissions standard under
§ 63.6(g).
(2) Approval of a major change to test
methods under § 63.7(e)(2)(ii) and (f). A
‘‘major change to test method’’ is
defined in § 63.90.
(3) Approval of a major change to
monitoring under § 63.8(f). A ‘‘major
change to monitoring’’ is defined in
§ 63.90.
(4) Approval of a major change to
recordkeeping/ reporting under
§ 63.10(f). A ‘‘major change to
recordkeeping/reporting’’ is defined in
§ 63.90.
As required in § 63.11157(a), you
must comply with the requirements of
the General Provisions (40 CFR part 63,
subpart A) as shown in the following
table.
TABLE 1 TO SUBPART FFFFFF OF PART 63.—APPLICABILITY OF GENERAL PROVISIONS TO SUBPART FFFFFF
Applies to subpart FFFFFF?
Citation
Subject
63.1(a)(1), (a)(2), (a)(3), (a)(4), (a)(6),
(a)(10)–(a)(12), (b)(1), (b)(3), (c)(1),
(c)(2), (c)(5), (e).
63.1(a)(5), (a)(7)–(a)(9), (b)(2), (c)(3),
(c)(4), (d).
63.2 ..........................................................
63.3 ..........................................................
63.4 ..........................................................
63.5 ..........................................................
Applicability ............................................
Yes.
Reserved ................................................
No.
Definitions ..............................................
Units and Abbreviations .........................
Prohibited Activities and Circumvention
Preconstruction Review and Notification
Requirements.
Compliance with Standards and Maintenance Requirements.
Yes.
Yes.
Yes.
No.
Reserved ................................................
No.
................................................................
No .....................
Performance Testing Requirements ......
Monitoring Requirements .......................
Reserved ................................................
................................................................
Yes.
Yes.
No.
No .....................
63.8(a)(4) .................................................
................................................................
No .....................
63.9(a), (b)(1), (b)(2), (b)(5), (c), (d), (e),
(f), (g), (h)(1)–(h)(3), (h)(5), (h)(6), (i),
(j).
63.9(b)(3), (h)(4) ......................................
63.9(b)(4) .................................................
63.9(f) ......................................................
Notification Requirements ......................
Yes.
Reserved ................................................
................................................................
................................................................
No.
No.
No .....................
63.9(g) .....................................................
................................................................
No .....................
63.10(a), (b)(2)(i)–(b)(2)(v), (b)(2)(xiv),
(d)(1), (d)(2), (d)(4), (d)(5), (e)(1),
(e)(2), (f).
63.10(c)(2)–(c)(4), (c)(9) ..........................
63.10(b)(2)(vi)–(b)(2)(xiii), (c)(1), (c)(5)–
(c)(14), (e)(1)–(e)(2), (e)(4).
63.10(d)(3) ...............................................
Recordkeeping and Reporting Requirements.
Yes.
Reserved ................................................
................................................................
No.
...........................
................................................................
No .....................
63.10(e)(3) ...............................................
63.11 ........................................................
................................................................
Control Device Requirements ................
Yes.
No .....................
63.12 ........................................................
63.13 ........................................................
63.14 ........................................................
State Authorities and Delegations .........
Addresses ..............................................
Incorporations by Reference ..................
Yes.
Yes.
Yes.
jlentini on PROD1PC65 with RULES2
63.6(a), (b)(1)–(b)(5), (b)(7), (c)(1),
(c)(2), (c)(5), (e)(3)(i), (e)(3)(iii)–
(e)(3)(ix), (f), (g), (i), (j).
63.6(b)(6), (c)(3), (c)(4), (d), (e)(2),
(e)(3)(ii), (h)(3), (h)(5)(iv).
63.6(h)(1)–(h)(4),
(h)(5)(i)–(h)(5)(iii),
(h)(6)–(h)(9).
63.7 ..........................................................
63.8(a)(1), (a)(2), (b), (f)(1)–(5) ...............
63.8(a)(3) .................................................
63.8(c), (d), (e), (f)(6), (g) ........................
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Explanation
Yes.
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Subpart FFFFFF does not include opacity or visible emissions standards.
Subpart FFFFFF does not require a
continuous monitoring system.
Subpart FFFFFF does not require
flares.
Subpart FFFFFF does not include opacity or visible emissions standards.
Subpart FFFFFF does not require a
continuous monitoring system.
Subpart FFFFFF does not require a
continuous monitoring system.
Subpart FFFFFF does not include opacity or visible emissions standards.
Subpart FFFFFF
flares.
23JAR2
does
not
require
Federal Register / Vol. 72, No. 14 / Tuesday, January 23, 2007 / Rules and Regulations
2955
TABLE 1 TO SUBPART FFFFFF OF PART 63.—APPLICABILITY OF GENERAL PROVISIONS TO SUBPART FFFFFF—
Continued
Applies to subpart FFFFFF?
Citation
Subject
63.15 ........................................................
Availability of Information and Confidentiality.
Performance Track Provisions ...............
63.16 ........................................................
6. Part 63 is amended by adding
subpart GGGGGG to read as follows:
I
Subpart GGGGGG—National Emission
Standards for Hazardous Air Pollutants
for Primary Nonferrous Metals Area
Sources—Zinc, Cadmium, and
Beryllium
Sec.
Applicability and Compliance Dates
63.11160 Am I subject to this subpart?
63.11161 What are my compliance dates?
Primary Zinc Production Facilities
63.11162 What are the standards and
compliance requirements for existing
sources?
63.11163 What are the standards and
compliance requirements for new
sources?
63.11164 What General Provisions apply to
primary zinc production facilities?
Primary Beryllium Production Facilities
63.11165 What are the standards and
compliance requirements for new and
existing sources?
63.11166 What General Provisions apply to
primary beryllium production facilities?
Other Requirements and Information
63.11167 What definitions apply to this
subpart?
63.11168 Who implements and enforces
this subpart?
Table 1 to Subpart GGGGGG of Part 63—
Applicability of General Provisions to
Primary Zinc Production Area Sources
Applicability and Compliance Dates
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§ 63.11160
Am I subject to this subpart?
(a) You are subject to this subpart if
you own or operate a primary zinc
production facility or primary beryllium
production facility that is an area source
of hazardous air pollutant (HAP)
emissions.
(b) The affected source is each
existing or new primary zinc production
facility or primary beryllium production
facility.
(1) An affected source is existing if
you commenced construction or
reconstruction of the affected source
before October 6, 2006.
(2) An affected source is new if you
commenced construction or
reconstruction of the affected source on
or after October 6, 2006.
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Yes.
Yes.
(c) If you own or operate a new or
existing affected source, you must
obtain a permit under 40 CFR part 70 or
71.
§ 63.11161
dates?
What are my compliance
(a) If you have an existing affected
source, you must achieve compliance
with applicable provisions in this
subpart by January 23, 2007. If you
startup a new sintering machine at an
existing affected source after January 23,
2007, you must achieve compliance
with the applicable provisions in this
subpart not later than 180 days after
startup.
(b) If you have a new affected source,
you must achieve compliance with
applicable provisions in this subpart
according to the dates in paragraphs
(b)(1) and (2) of this section.
(1) If you startup a new affected
source on or before January 23, 2007,
you must achieve compliance with
applicable provisions in this subpart not
later than January 23, 2007.
(2) If you startup a new affected
source after January 23, 2007, you must
achieve compliance with applicable
provisions in this subpart upon initial
startup.
Primary Zinc Production Facilities
§ 63.11162 What are the standards and
compliance requirements for existing
sources?
(a) You must exhaust the off-gases
from each roaster to a particulate matter
(PM) control device and to a sulfuric
acid plant, including during the
charging of the roaster.
(b) Except as provided in paragraph
(b)(6) of this section, you must not
discharge to the atmosphere any gases
which contain PM in excess of the
emissions limits in paragraphs (b)(1)
through (5) of this section.
(1) 0.93 pound per hour (lb/hr) from
the exhaust vent of a zinc cathode
melting furnace.
(2) 0.1 lb/hr from the exhaust vent of
a furnace that melts zinc dust, zinc
chips, and/or other materials containing
zinc.
(3) 0.228 lb/hr from the vent for the
combined exhaust from a furnace
melting zinc scrap and an alloy furnace.
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Explanation
(4) 0.014 grains per dry standard
cubic foot (gr/dscf) from the exhaust
vent of an anode casting furnace.
(5) 0.015 gr/dscf from the exhaust
vent of a cadmium melting furnace.
(6) You may elect to meet an
emissions limit of 0.005 gr/dscf as an
alternative to the emissions limits in lb/
hr in paragraphs (b)(1) through (3) of
this section.
(c) You must establish an operating
range for pressure drop for each
baghouse applied to a furnace subject to
an emissions limit in paragraph (b) of
this section based on the minimum and
maximum values recorded during a
performance test that demonstrates
compliance with the applicable PM
emissions limit. Alternatively, you may
use an operating range that has been
previously established and approved by
your permitting authority within the
past 5 years. You must monitor the
pressure drop daily, maintain the
pressure drop for each baghouse within
the established operating range, and
record the pressure drop measurement
in a daily log. You must perform routine
maintenance on each baghouse and
record maintenance activities in a
baghouse maintenance log. Baghouse
maintenance logs must include, but are
not limited to, inspections, criteria for
changing bag filters, and dates on which
the bag filters are replaced. Both logs
must be maintained in a suitable
permanent form and kept available for
inspection.
(d) If you own or operate a sintering
machine at your facility, you must
comply with the PM emissions limit in
40 CFR 60.172(a) and the opacity
emissions limit in 40 CFR 60.174(a) for
that sintering machine.
(e) If you own or operate a sintering
machine at your facility, you must
install and operate a continuous opacity
monitoring system (COMS) for each
sintering machine according to the
requirements in 40 CFR 60.175(a). Each
COMS must meet Performance
Specification 1 (40 CFR part 60,
appendix B).
(f) For each furnace at your facility
subject to an emissions limit in
paragraph (b) of this section, you must
demonstrate initial compliance with the
applicable PM emissions limit in
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paragraph (b) of this section based on
the results of a performance test for that
furnace. If you own or operate a
sintering machine, you must also
demonstrate initial compliance with the
PM and opacity emissions limits in
paragraph (d) of this section based on
the results of a performance test for that
sintering machine.
(1) You may certify initial compliance
for a furnace (and sintering machine, if
applicable) based on the results of a
previous performance test conducted
during the past 5 years.
(2) If you have not conducted a
performance test to demonstrate
compliance with the applicable
emissions limits during the past 5 years,
you must conduct a performance test
within 180 days of your compliance
date and report the results in your
notification of compliance status. If a
furnace subject to an emissions limit in
paragraph (b) of this section is not
operating on the compliance date and
subsequently resumes operation, you
must conduct a performance test within
180 days of startup and report the
results in your notification of
compliance status.
(3) You must conduct each PM test for
a furnace according to § 63.7(e)(1) using
the test methods and procedures in
paragraphs (f)(3)(i) through (v) of this
section.
(i) Method 1 or 1A (40 CFR part 60,
appendix A) to select sampling port
locations and the number of traverse
points in each stack or duct. Sampling
sites must be located at the outlet of the
control device (or at the outlet of the
emissions source if no control device is
present) prior to any releases to the
atmosphere.
(ii) Method 2, 2A, 2C, 2D, 2F, or 2G
(40 CFR part 60, appendix A) to
determine the volumetric flow rate of
the stack gas.
(iii) Method 3, 3A, or 3B (40 CFR part
60, appendix A) to determine the dry
molecular weight of the stack gas. You
may use ANSI/ASME PTC 19.10–1981,
‘‘Flue and Exhaust Gas Analyses
(incorporated by reference—see § 63.14)
as an alternative to EPA Method 3B.
(iv) Method 4 (40 CFR part 60,
appendix A) to determine the moisture
content of the stack gas.
(v) Method 5 (40 CFR part 60,
appendix A) to determine the PM
concentration for a negative pressure
baghouse, Method 5D (40 CFR part 60,
appendix A) for a positive pressure
baghouse, or an alternative method
previously approved by your permitting
authority. A minimum of three valid test
runs are needed to comprise a PM
performance test.
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(4) You must conduct each PM test for
a sintering machine according to
§ 63.7(e)(1) and 40 CFR 60.176(b)(1)
using the test methods in paragraph
(f)(3) of this section. You must
determine the PM concentration using
EPA Method 5 (40 CFR part 60,
appendix A). You may use ANSI/ASME
PTC 19.10–1981, ‘‘Flue and Exhaust Gas
Analyses’’ (incorporated by reference—
see § 63.14) as an alternative to EPA
Method 3B.
(5) You must conduct each opacity
test for a sintering machine according to
the requirements in § 63.6(h)(7). You
must determine the opacity of emissions
using EPA Method 9 (40 CFR part 60,
appendix A).
(g) For each furnace subject to an
emissions limit in paragraph (b) of this
section, you must conduct subsequent
performance tests according to the
requirements in paragraph (f)(3) of this
section to demonstrate compliance with
the applicable PM emissions limit for
the furnace every 5 years.
(h) You must submit a notification to
your permitting authority of any
deviation from the requirements of this
subpart within 30 days after the
deviation. The notification must
describe the probable cause of the
deviation and any corrective actions or
preventative measures taken.
(i) You must submit semiannual
monitoring reports to your permitting
authority containing the results for all
monitoring required by this subpart. All
deviations that occur during the
reporting period must be clearly
identified.
(j) You must keep records of all
required monitoring data and support
information. Support information
includes all calibration and
maintenance records and all original
strip chart recordings for continuous
monitoring instrumentation and copies
of all reports required by this subpart.
(k) You must comply with the
operation and maintenance
requirements specified in paragraphs
(k)(1) and (2) of this section and the
requirements for emergency situations
specified in paragraph (k)(3) or (4) of
this section.
(1) You must maintain all equipment
covered under this subpart in such a
manner that the performance or
operation of such equipment does not
cause a deviation from the applicable
requirements.
(2) You must keep a maintenance
record for each item of air pollution
control equipment. At a minimum, this
record must show the dates of
performing maintenance and the nature
of preventative maintenance activities.
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(3) Except as specified in paragraph
(k)(4) of this section, in the event of an
emergency situation you must comply
with the requirements in paragraphs
(k)(3)(i) through (iii) of this section. For
the purpose of complying with this
paragraph, an emergency situation is
any situation arising from sudden and
reasonably unforeseeable events beyond
the control of the facility owner or
operator that require immediate
corrective action to restore normal
operation, and that cause the affected
source to exceed applicable emission
limitation under this subpart, due to
unavoidable increases in emissions
attributable to the emergency. An
emergency must not include
noncompliance to the extent it is caused
by improperly designed equipment, lack
of preventive maintenance, careless or
improper operation, or operator error.
(i) During the period of the emergency
you must implement all reasonable
steps to minimize levels of emissions
that exceeded the emission standards or
other applicable requirements in this
subpart.
(ii) You must document through
signed contemporaneous logs or other
relevant evidence that an emergency
occurred and you can identify the
probable cause, your facility was being
operated properly at the time the
emergency occurred, and the corrective
actions taken to minimize emissions as
required by paragraph (k)(3)(i) of this
section.
(iii) You must submit a notice of the
emergency to the permitting authority
within two working days of the time
when emission limitations were
exceeded due to the emergency (or an
alternative timeframe acceptable to the
permitting authority). This notice must
contain a description of the emergency,
any steps taken to mitigate emissions,
and corrective actions taken.
(4) As an alternative to the
requirements in paragraph (k)(3) of this
section, you must comply with the
startup, shutdown, and malfunction
requirements in 40 CFR 63.6(e)(3).
§ 63.11163 What are the standards and
compliance requirements for new sources?
(a) You must exhaust the off-gases
from each roaster to a PM control device
and to a sulfuric acid plant, including
the charging of the roaster.
(b) You must not discharge to the
atmosphere any gases which contain PM
in excess of the emissions limits in
paragraphs (b)(1) through (3) of this
section.
(1) 0.005 gr/dscf from the exhaust
vent of a zinc cathode melting furnace;
scrap zinc melting furnace; furnace
melting zinc dust, zinc chips, and other
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materials containing zinc; and alloy
melting furnace.
(2) 0.014 gr/dscf from the exhaust
vent of an anode casting furnace.
(3) 0.015 gr/dscf from the exhaust
vent of a cadmium melting furnace.
(c) For each melting furnace, you
must install and operate a capture
system that collects gases and fumes
from the melting furnace and from the
transfer of molten materials and conveys
the collected gases to a control device.
(d) You must install, operate, and
maintain a bag leak detection system on
all baghouses used to comply with the
PM emissions limit in paragraph (b) of
this section according to paragraph
(d)(1) of this section, prepare and
operate by a site-specific monitoring
plan according to paragraph (d)(2) of
this section, take corrective action
according to paragraph (d)(3) of this
section, and record information
according to paragraph (d)(4) of this
section.
(1) Each bag leak detection system
must meet the specifications and
requirements in paragraphs (d)(1)(i)
through (viii) of this section.
(i) The bag leak detection system must
be certified by the manufacturer to be
capable of detecting PM emissions at
concentrations of 1 milligram per actual
cubic meter (0.00044 grains per actual
cubic foot) or less.
(ii) The bag leak detection system
sensor must provide output of relative
PM loadings. The owner or operator
must continuously record the output
from the bag leak detection system using
electronic or other means (e.g., using a
strip chart recorder or a data logger.)
(iii) The bag leak detection system
must be equipped with an alarm system
that will sound when the system detects
an increase in relative particulate
loading over the alarm set point
established according to paragraph
(d)(1)(iv) of this section, and the alarm
must be located such that it can be
heard by the appropriate plant
personnel.
(iv) In the initial adjustment of the bag
leak detection system, you must
establish, at a minimum, the baseline
output by adjusting the sensitivity
(range) and the averaging period of the
device, the alarm set points, and the
alarm delay time.
(v) Following initial adjustment, you
must not adjust the averaging period,
alarm set point, or alarm delay time
without approval from the
Administrator or delegated authority
except as provided in paragraph
(d)(1)(vi) of this section.
(vi) Once per quarter, you may adjust
the sensitivity of the bag leak detection
system to account for seasonal effects,
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including temperature and humidity,
according to the procedures identified
in the site-specific monitoring plan
required by paragraph (d)(2) of this
section.
(vii) You must install the bag leak
detection sensor downstream of the
baghouse and upstream of any wet
scrubber.
(viii) Where multiple detectors are
required, the system’s instrumentation
and alarm may be shared among
detectors.
(2) You must develop and submit to
the Administrator or delegated authority
for approval a site-specific monitoring
plan for each bag leak detection system.
You must operate and maintain the bag
leak detection system according to the
site-specific monitoring plan at all
times. Each monitoring plan must
describe the items in paragraphs (d)(2)(i)
through (vi) of this section.
(i) Installation of the bag leak
detection system;
(ii) Initial and periodic adjustment of
the bag leak detection system, including
how the alarm set-point will be
established;
(iii) Operation of the bag leak
detection system, including quality
assurance procedures;
(iv) How the bag leak detection
system will be maintained, including a
routine maintenance schedule and spare
parts inventory list;
(v) How the bag leak detection system
output will be recorded and stored; and
(vi) Corrective action procedures as
specified in paragraph (d)(3) of this
section. In approving the site-specific
monitoring plan, the Administrator or
delegated authority may allow owners
and operators more than 3 hours to
alleviate a specific condition that causes
an alarm if the owner or operator
identifies in the monitoring plan this
specific condition as one that could lead
to an alarm, adequately explains why it
is not feasible to alleviate this condition
within 3 hours of the time the alarm
occurs, and demonstrates that the
requested time will ensure alleviation of
this condition as expeditiously as
practicable.
(3) For each bag leak detection
system, you must initiate procedures to
determine the cause of every alarm
within 1 hour of the alarm. Except as
provided in paragraph (d)(2)(vi) of this
section, you must alleviate the cause of
the alarm within 3 hours of the alarm by
taking whatever corrective action(s) are
necessary. Corrective actions may
include, but are not limited to the
following:
(i) Inspecting the baghouse for air
leaks, torn or broken bags or filter
media, or any other condition that may
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2957
cause an increase in particulate
emissions;
(ii) Sealing off defective bags or filter
media;
(iii) Replacing defective bags or filter
media or otherwise repairing the control
device;
(iv) Sealing off a defective baghouse
compartment;
(v) Cleaning the bag leak detection
system probe or otherwise repairing the
bag leak detection system; or
(vi) Shutting down the process
producing the particulate emissions.
(4) You must maintain records of the
information specified in paragraphs
(d)(4)(i) through (iii) of this section for
each bag leak detection system.
(i) Records of the bag leak detection
system output;
(ii) Records of bag leak detection
system adjustments, including the date
and time of the adjustment, the initial
bag leak detection system settings, and
the final bag leak detection system
settings; and
(iii) The date and time of all bag leak
detection system alarms, the time that
procedures to determine the cause of the
alarm were initiated, if procedures were
initiated within 1 hour of the alarm, the
cause of the alarm, an explanation of the
actions taken, the date and time the
cause of the alarm was alleviated, and
if the alarm was alleviated within 3
hours of the alarm.
(e) If there is a sintering machine at
your primary zinc production facility,
you must comply with the PM
emissions limit in 40 CFR 60.172(a) and
the opacity emissions limit in 40 CFR
60.174(a) for that sintering machine.
(f) If there is a sintering machine at
your primary zinc production facility,
you must install and operate a COMS
for each sintering machine according to
the requirements in 40 CFR 60.175(a).
Each COMS must meet EPA
Performance Specification 1 (40 CFR
part 60, appendix B).
(g) For each furnace (and sintering
machine, if applicable) at your facility,
you must conduct a performance test to
demonstrate initial compliance with
each applicable PM emissions limit for
that furnace (and the PM and opacity
limits for a sintering machine, if
applicable) within 180 days after startup
and report the results in your
notification of compliance status.
(1) You must conduct each PM test for
a furnace according to § 63.7(e)(1) using
the test methods and procedures in
paragraphs (g)(1)(i) through (v) of this
section.
(i) Method 1 or 1A (40 CFR part 60,
appendix A) to select sampling port
locations and the number of traverse
points in each stack or duct. Sampling
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sites must be located at the outlet of the
control device (or at the outlet of the
emissions source if no control device is
present) prior to any releases to the
atmosphere.
(ii) Method 2, 2A, 2C, 2D, 2F, or 2G
(40 CFR part 60, appendix A) to
determine the volumetric flow rate of
the stack gas.
(iii) Method 3, 3A, or 3B (40 CFR part
60, appendix A) to determine the dry
molecular weight of the stack gas. You
may use ANSI/ASME PTC 19.10–1981,
‘‘Flue and Exhaust Gas Analyses’’
(incorporated by reference—see § 63.14)
as an alternative to EPA Method 3B.
(iv) Method 4 (40 CFR part 60,
appendix A) to determine the moisture
content of the stack gas.
(v) Method 5 (40 CFR part 60,
appendix A) to determine the PM
concentration for negative pressure
baghouses or Method 5D (40 CFR part
60, appendix A) for positive pressure
baghouses. A minimum of three valid
test runs are needed to comprise a PM
performance test.
(2) You must conduct each PM test for
a sintering machine according to
§ 63.7(e)(1) and 40 CFR 60.176(b)(1)
using the test methods in paragraph
(g)(1) of this section. You must
determine the PM concentration using
EPA Method 5 (40 CFR part 60,
appendix A). You may use ANSI/ASME
PTC 19.10–1981, ‘‘Flue and Exhaust Gas
Analyses’’ (incorporated by reference—
see § 63.14) as an alternative to EPA
Method 3B.
(3) You must conduct each opacity
test for a sintering machine according to
the requirements in § 63.6(h)(7). You
must determine the opacity of emissions
using EPA Method 9 (40 CFR part 60,
appendix A).
(h) You must conduct subsequent
performance tests according to the
requirements in paragraph (g)(1) of this
section for each furnace subject to an
emissions limit in paragraph (b) of this
section to demonstrate compliance at
least once every 5 years.
(i) If you use a control device other
than a baghouse, you must prepare and
submit a monitoring plan to the
Administrator for approval. Each plan
must contain the information in
paragraphs (i)(1) through (5) of this
section.
(1) A description of the device;
(2) Test results collected in
accordance with paragraph (g) of this
section verifying the performance of the
device for reducing PM and opacity to
the levels required by this subpart;
(3) Operation and maintenance plan
for the control device (including a
preventative maintenance schedule
consistent with the manufacturer’s
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instructions for routine and long-term
maintenance) and continuous
monitoring system;
(4) A list of operating parameters that
will be monitored to maintain
continuous compliance with the
applicable emission limits; and
(5) Operating parameter limits based
on monitoring data collected during the
performance test.
(i) As an alternative to the startup,
shutdown, and malfunction
requirements in 40 CFR 63.6(e)(3), you
must comply with the requirements
specified in this paragraph. In the event
of an emergency situation, you must
comply with the requirements in
paragraphs (i)(1) through (3) of this
section. For the purpose of complying
with this paragraph, an emergency
situation is any situation arising from
sudden and reasonably unforeseeable
events beyond the control of the facility
owner or operator that require
immediate corrective action to restore
normal operation, and that cause the
affected source to exceed applicable
emission limitation under this subpart,
due to unavoidable increases in
emissions attributable to the emergency.
An emergency must not include
noncompliance to the extent it is caused
by improperly designed equipment, lack
of preventive maintenance, careless or
improper operation, or operator error.
(1) During the period of the
emergency you must implement all
reasonable steps to minimize levels of
emissions that exceeded the emission
standards or other applicable
requirements in this subpart.
(2) You must document through
signed contemporaneous logs or other
relevant evidence that an emergency
occurred and you can identify the
probable cause, your facility was being
operated properly at the time the
emergency occurred, and the corrective
actions taken to minimize emissions as
required by paragraph (i)(1) of this
section.
(3) You must submit a notice of the
emergency to the permitting authority
within two working days of the time
when emission limitations were
exceeded due to the emergency (or an
alternative timeframe acceptable to the
permitting authority). This notice must
contain a description of the emergency,
any steps taken to mitigate emissions,
and corrective actions taken.
§ 63.11164 What General Provisions apply
to primary zinc production facilities?
(a) If you own or operate an existing
affected source, you must comply with
the requirements of the General
Provisions in 40 CFR part 63, subpart A,
according to Table 1 to this subpart and
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paragraphs (a)(1) through (3) of this
section.
(1) Your notification of compliance
status required by § 63.9(h) must
include this certification of compliance,
signed by a responsible official, for the
work practice standards in
§ 63.11162(a): ‘‘This facility complies
with the work practice standards in
§ 63.11162(a).’’
(2) If you certify compliance with the
PM emissions limits in § 63.11162(b)
based on a previous performance test,
your notification of compliance status
required by § 63.9(h) must include this
certification of compliance, signed by a
responsible official: ‘‘This facility
complies with the PM emissions limits
in § 63.11162(b) based on a previous
performance test.’’
(3) If you conduct a new performance
test to demonstrate compliance with the
PM emissions limits for a furnace in
§ 63.11162(b), your notification of
compliance status required by § 63.9(h)
must include the results of the
performance test, including required
monitoring data.
(b) If you own or operate a new
affected source, you must comply with
the requirements of the General
Provisions (40 CFR part 63, subpart A)
as provided in Table 1 to this subpart
and paragraphs (b)(1) through (4) of this
section.
(1) Your notification of compliance
status required in § 63.9(h) must include
the results of the initial performance
tests, including required monitoring
data.
(2) Your notification of compliance
status required by § 63.9(h) must
include this certification of compliance,
signed by a responsible official, for the
work practice standard in § 63.11163(a):
‘‘This facility complies with the work
practice standards in § 63.11163(a).’’
(3) Your notification of compliance
status required by § 63.9(h) must
include this certification of compliance,
signed by a responsible official, for the
capture system requirements in
§ 63.11163(c): ‘‘This facility has
installed capture systems according to
§ 63.11163(c).’’
(4) If you use a baghouse that is
subject to the requirements in
§ 63.11163(d), your notification of
compliance status required by § 63.9(h)
must include this certification of
compliance, signed by a responsible
official, for the bag leak detection
system requirements in § 63.11163(d):
‘‘This facility has an approved
monitoring plan in accordance with
§ 63.11163(d).’’
(5) If you use control devices other
than baghouses, your notification of
compliance status required by § 63.9(h)
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Federal Register / Vol. 72, No. 14 / Tuesday, January 23, 2007 / Rules and Regulations
must include this certification of
compliance, signed by a responsible
official for the monitoring plan
requirements in § 63.11163(i): ‘‘This
facility has an approved monitoring
plan in accordance with § 63.11163(i).’’
Primary Beryllium Production
Facilities
§ 63.11165 What are the standards and
compliance requirements for new and
existing sources?
You must comply with the
requirements in 40 CFR 61.32 through
40 CFR 61.34 of the National Emission
Standards for Beryllium (40 CFR part
61, subpart C).
§ 63.11166 What General Provisions apply
to primary beryllium production facilities?
(a) You must comply with all of the
requirements of the General Provisions
in 40 CFR part 61, subpart A.
(b) You must comply with the
requirements of the General Provisions
in 40 CFR part 63, subpart A, that are
specified in paragraphs (b)(1) and (2) of
this section.
(1) Section 63.1(a)(1) through (10).
(2) Section 63.1(b) except paragraph
(b)(3), § 63.1(c), and § 63.1(e).
Other Requirements and Information
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§ 63.11167
subpart?
What definitions apply to this
Terms used in this subpart are
defined in the CAA; 40 CFR 60.2;
60.171; 61.02; 61.31; 61.61; 63.2; and in
this section as follows:
Alloy furnace means any furnace used
to melt alloys or to produce zinc that
contains alloys.
Anode casting furnace means any
furnace that melts materials to produce
the anodes used in the electrolytic
process for the production of zinc.
Bag leak detection system means a
system that is capable of continuously
monitoring the relative particulate
matter (dust) loadings in the exhaust of
a baghouse to detect bag leaks and other
conditions that result in increases in
particulate loadings. A bag leak
detection system includes, but is not
limited to, an instrument that operates
on triboelectric, electrodynamic, light
scattering, light transmittance, or other
effect to continuously monitor relative
particulate matter loadings.
Cadmium melting furnace means any
furnace used to melt cadmium or
produce cadmium oxide from the
cadmium recovered in the zinc
production process.
Capture system means the collection
of equipment used to capture gases and
fumes released from one or more
emissions points and then convey the
captured gas stream to a control device.
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A capture system may include, but is
not limited to, the following
components as applicable to a given
capture system design: duct intake
devices, hoods, enclosures, ductwork,
dampers, manifolds, plenums, and fans.
Deviation means any instance in
which an affected source subject to this
subpart, or an owner or operator of such
a source:
(1) Fails to meet any requirement or
obligation established by this subpart,
including but not limited to any
emissions limitation or work practice
standard;
(2) Fails to meet any term or condition
that is adopted to implement an
applicable requirement in this subpart
and that is included in the operating
permit for any affected source required
to obtain such a permit; or
(3) Fails to meet any emissions
limitation or work practice standard in
this subpart during startup, shutdown,
or malfunction, regardless of whether or
not such failure is permitted by this
subpart.
Primary beryllium production facility
means any establishment engaged in the
chemical processing of beryllium ore to
produce beryllium metal, alloy, or
oxide, or performing any of the
intermediate steps in these processes. A
primary beryllium production facility
may also be known as an extraction
plant.
Primary zinc production facility
means an installation engaged in the
production, or any intermediate process
in the production, of zinc or zinc oxide
from zinc sulfide ore concentrates
through the use of pyrometallurgical
techniques.
Responsible official means
responsible official as defined in 40 CFR
70.2.
Roaster means any facility in which a
zinc sulfide ore concentrate charge is
heated in the presence of air to
eliminate a significant portion (more
than 10 percent) of the sulfur contained
in the charge.
Sintering machine means any furnace
in which calcines are heated in the
presence of air to agglomerate the
calcines into a hard porous mass called
sinter.
Sulfuric acid plant means any facility
producing sulfuric acid from the sulfur
dioxide (SO2) in the gases from the
roaster.
Work practice standard means any
design, equipment, work practice, or
operational standard, or combination
thereof.
Zinc cathode melting furnace means
any furnace used to melt the pure zinc
from the electrolytic process.
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2959
§ 63.11168 Who implements and enforces
this subpart?
(a) This subpart can be implemented
and enforced by the U.S. EPA or a
delegated authority such as a State,
local, or tribal agency. If the U.S. EPA
Administrator has delegated authority to
a State, local, or tribal agency, then that
Agency has the authority to implement
and enforce this subpart. You should
contact your U.S. EPA Regional Office
to find out if this subpart is delegated
to your State, local, or tribal agency.
(b) In delegating implementation and
enforcement authority of this subpart to
a State, local, or tribal agency under 40
CFR part 63, subpart E, the authorities
contained in paragraphs (c) and (d) of
this section are retained by the
Administrator of the U.S. EPA and are
not transferred to the State, local, or
tribal agency.
(c) For primary zinc production
facilities subject to this subpart, the
authorities that will not be delegated to
State, local, or tribal agencies are listed
in paragraphs (c)(1) through (5) of this
section.
(1) Approval of an alternative nonopacity emissions standard under
§ 63.6(g).
(2) Approval of an alternative opacity
emissions standard under § 63.6(h)(9).
(3) Approval of a major change to test
methods under § 63.7(e)(2)(ii) and (f). A
‘‘major change to test method’’ is
defined in § 63.90
(4) Approval of a major change to
monitoring under § 63.8(f). A ‘‘major
change to monitoring’’ is defined in
§ 63.90.
(5) Approval of a major change to
recordkeeping/reporting under
§ 63.10(f). A ‘‘major change to
recordkeeping/reporting’’ is defined in
§ 63.90.
(d) For primary beryllium
manufacturing facilities subject to this
subpart, the authorities that will not be
delegated to State, local, or tribal
agencies are listed in paragraphs (d)(1)
through (4) of this section.
(1) Approval of an alternative nonopacity emissions standard under 40
CFR 61.12(d).
(2) Approval of a major change to test
methods under 40 CFR 61.13(h). A
‘‘major change to test method’’ is
defined in § 63.90.
(3) Approval of a major change to
monitoring under 40 CFR 61.14(g). A
‘‘major change to monitoring’’ is defined
in § 63.90.
(4) Approval of a major change to
recordkeeping/reporting under 40 CFR
61.10. A ‘‘major change to
recordkeeping/reporting’’ is defined in
§ 63.90.
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Federal Register / Vol. 72, No. 14 / Tuesday, January 23, 2007 / Rules and Regulations
As required in § 63.11164(a) and (b),
you must comply with the requirements
of the NESHAP General Provisions (40
CFR part 63, subpart A) as shown in the
following table.
TABLE 1 TO SUBPART GGGGGG OF PART 63.—APPLICABILITY OF GENERAL PROVISIONS TO PRIMARY ZINC PRODUCTION
AREA SOURCES
Applies to subpart GGGGGG
Citation
Subject
63.1(a)(1), (a)(2), (a)(3), (a)(4), (a)(6),
(a)(10)–(a)(12), (b)(1), (b)(3), (c)(1),
(c)(2), (c)(5), (e).
63.1(a)(5), (a)(7)–(a)(9), (b)(2), (c)(3),
(c)(4), (d).
63.2 ..........................................................
63.3 ..........................................................
63.4 ..........................................................
63.5 ..........................................................
Applicability ............................................
Yes.
Reserved ................................................
No.
Definitions ..............................................
Units and Abbreviations .........................
Prohibited Activities and Circumvention
Preconstruction Review and Notification
Requirements.
Compliance with Standards and Maintenance
Requirements—Applicability
Compliance Dates.
Operation and Maintenance Requirements.
Yes.
Yes.
Yes.
No.
Compliance with Nonopacity Emission
Standards.
Reserved ................................................
Yes.
................................................................
Yes.
Performance Testing Requirements ......
................................................................
Yes.
Yes/No ..............
63.8(a)(1), (a)(2), (b), (c), (f), (g) .............
Monitoring Requirements .......................
Yes ...................
63.8(a)(3) .................................................
63.8(a)(4) .................................................
Reserved ................................................
................................................................
No.
No .....................
63.8(d), (e) ...............................................
................................................................
Yes/No ..............
63.9(a), (b)(1), (b)(2), (b)(5), (c), (d), (f),
(g), (h)(1)–(h)(3), (h)(5), (h)(6), (i), (j).
Notification Requirements ......................
Yes/No ..............
63.9(b)(3), (h)(4) ......................................
63.9(b)(4) .................................................
63.10(a), (b)(1), (b)(2)(i)–(v), (d)(4),
(d)(5)(i), (f).
63.10(b)(2), (b)(3), (c)(1), (c)(5)–(c)(8),
(c)(10)–(c)(15), (d)(1)–(d)(3), (d)(5)(ii),
(e)(1), (e)(2), (e)(4).
63.10(c)(2)–(c)(4), (c)(9) ..........................
63.10(e)(3) ...............................................
Reserved ................................................
................................................................
Recordkeeping and Reporting Requirements.
................................................................
No.
No.
Yes.
Reserved ................................................
................................................................
No.
Yes/No ..............
63.11 ........................................................
Control Device Requirements ................
No .....................
63.12 ........................................................
63.13 ........................................................
63.14 ........................................................
State Authorities and Delegations .........
Addresses ..............................................
Incorporations by Reference ..................
Yes.
Yes.
Yes.
63.6(a), (b)(1)–(b)(5),
(c)(2), (c)(5).
(b)(7),
(c)(1),
63.6(e) .....................................................
63.6(f), (g), (i), (j) .....................................
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63.6(b)(6), (c)(3), (c)(4), (d), (e)(2),
(e)(3)(ii), (h)(3), (h)(5)(iv).
63.6(h)(1)–(h)(4),
(h)(5)(i)–(h)(5)(iii),
(h)(6)–(h)(9).
63.7(a), (e), (f), (g), (h) ............................
63.7(b), (c) ...............................................
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Explanation
Yes.
Yes/No ..............
Operation and maintenance requirements do not apply to existing
sources except that the startup, shutdown, and malfunction requirements
in § 63.6(e)(3) are allowed as an alternative to the rule requirements for
emergency situations. Operation and
maintenance requirements apply to
new sources except that the rule requirements for emergency situations
are allowed as an alternative to the
startup, shutdown, and malfunction
requirements in § 63.6(e)(3).
No.
Yes/No ..............
E:\FR\FM\23JAR2.SGM
Notification of performance tests and
quality assurance program apply to
new sources but not existing sources.
Requirements
in
§ 63.6(c)(4)(i)–(ii),
(c)(5), (c)(6), (d), (e), (f)(6), and (g)
apply if a COMS is used.
Subpart GGGGGG does not require
flares.
Requirements for quality control program and performance evaluations
apply to new sources but not existing
sources.
Notification of performance tests and
opacity or visible emissions observations apply to new sources but not
existing sources.
Recordkeeping and reporting requirements apply to new sources but not
existing sources.
Reporting requirements apply to new
sources but not existing sources.
Subpart GGGGGG does not require
flares.
23JAR2
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2961
TABLE 1 TO SUBPART GGGGGG OF PART 63.—APPLICABILITY OF GENERAL PROVISIONS TO PRIMARY ZINC PRODUCTION
AREA SOURCES—Continued
Applies to subpart GGGGGG
Citation
Subject
63.15 ........................................................
Availability of Information and Confidentiality.
Performance Track Provisions ...............
63.16 ........................................................
Explanation
Yes.
Yes.
[FR Doc. E7–532 Filed 1–22–07; 8:45 am]
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BILLING CODE 6560–50–P
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23JAR2
Agencies
[Federal Register Volume 72, Number 14 (Tuesday, January 23, 2007)]
[Rules and Regulations]
[Pages 2930-2961]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E7-532]
[[Page 2929]]
-----------------------------------------------------------------------
Part II
Environmental Protection Agency
-----------------------------------------------------------------------
40 CFR Part 63
National Emission Standards for Hazardous Air Pollutants for Area
Sources: Polyvinyl Chloride and Copolymers Production, Primary Copper
Smelting, Secondary Copper Smelting, and Primary Nonferrous Metals:
Zinc, Cadmium, and Beryllium; Final Rule
Federal Register / Vol. 72, No. 14 / Tuesday, January 23, 2007 /
Rules and Regulations
[[Page 2930]]
=======================================================================
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 63
[EPA-HQ-OAR-2006-0510; FRL-8257-4]
RIN 2060-AN45
National Emission Standards for Hazardous Air Pollutants for Area
Sources: Polyvinyl Chloride and Copolymers Production, Primary Copper
Smelting, Secondary Copper Smelting, and Primary Nonferrous Metals:
Zinc, Cadmium, and Beryllium
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rules.
-----------------------------------------------------------------------
SUMMARY: EPA is issuing national emission standards for hazardous air
pollutants (NESHAP) for four area source categories. These final NESHAP
include emissions limits and/or work practice standards that reflect
the generally available control technologies (GACT) and/or management
practices in each of these area source categories.
DATES: These final rules are effective on January 23, 2007. The
incorporation by reference of certain publications listed in these
rules is approved by the Director of the Federal Register as of January
23, 2007.
ADDRESSES: The EPA has established a docket for this action under
Docket ID No. EPA-HQ-OAR-2006-0510. All documents in the docket are
listed in the Federal Docket Management System index at https://
www.regulations.gov. Although listed in the index, some information is
not publicly available, e.g., confidential business information or
other information whose disclosure is restricted by statute. Certain
other material, such as copyrighted material, is not placed on the
Internet and will be publicly available only in hard copy form.
Publicly available docket materials are available either electronically
through www.regulations.gov or in hard copy at the EPA Docket Center,
Public Reading Room, EPA West, Room 3334, 1301 Constitution Ave., NW.,
Washington, DC. The Public Reading Room is open from 8:30 a.m. to 4:30
p.m., Monday through Friday, excluding legal holidays. The telephone
number for the Public Reading Room is (202) 566-1744, and the telephone
number for the Air Docket is (202) 566-1742.
FOR FURTHER INFORMATION CONTACT: Ms. Sharon Nizich, U.S. EPA, Office of
Air Quality Planning and Standards, Sector Policies and Programs
Division, Metals and Minerals Group (D243-02), Research Triangle Park,
North Carolina 27711, telephone number: (919) 541-2825, fax number
(919) 541-3207, e-mail address: nizich.sharon@epa.gov.
SUPPLEMENTARY INFORMATION:
Outline
The information presented 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?
C. Judicial Review
II. Background Information for Final Area Source Standards
III. Summary of Final Rule and Changes Since Proposal
A. NESHAP for Polyvinyl Chloride and Copolymers Production Area
Sources
B. NESHAP for Primary Copper Smelting Area Sources
C. NESHAP for Secondary Copper Smelting Area Sources
D. NESHAP for Primary Nonferrous Metals--Zinc, Cadmium, and
Beryllium Area Sources
IV. Summary of Comments and Responses
A. Existing Area Source Facilities
B. Part 63 General Provisions
C. Primary Copper Smelters
D. Primary Zinc Smelters
E. Basis for Area Source Standards
F. Compliance Date
V. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory Planning and Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation and Coordination With
Indian Tribal Governments
G. Executive Order 13045: Protection of Children From
Environmental Health and Safety Risks
H. Executive Order 13211: Actions Concerning Regulations That
Significantly Affect Energy Supply, Distribution, or Use
I. National Technology Transfer Advancement Act
J. Congressional Review Act
I. General Information
A. Does this action apply to me?
The regulated categories and entities potentially affected by these
final standards include:
------------------------------------------------------------------------
NAICS code Examples of regulated
Category \1\ entities
------------------------------------------------------------------------
Industry:
Polyvinyl chloride and 325211 Area source facilities
copolymers production. that polymerize vinyl
chloride monomer to
produce vinyl chloride
and/or copolymer
products.
Primary copper smelting...... 331411 Area source facilities
that produce copper from
copper sulfide ore
concentrates using
pyrometallurgical
techniques.
Secondary copper smelting.... \2\ 331423 Area source facilities
that process copper
scrap in a blast furnace
and converter or use
another
pyrometallurgical
purification process to
produce anode copper
from copper scrap,
including low-grade
copper scrap.
Primary nonferrous metals-- 331419 Area source facilities
zinc, cadmium, and beryllium. that produce zinc, zinc
oxide, cadmium, or
cadmium oxide from zinc
sulfide ore concentrates
using pyrometallurgical
techniques and area
source facilities that
produce beryllium metal,
alloy, or oxide from
beryllium ore.
Federal government............... .......... Not affected.
State/local/tribal government.... .......... Not affected.
------------------------------------------------------------------------
\1\ North American Industry Classification System.
\2\ This final rule applies only to secondary copper smelters and does
not apply to copper, brass, and bronze ingot makers or remelters that
may also be included under this NAICS code.
This table is not intended to be exhaustive, but rather provides a
guide for readers regarding entities likely to be affected by this
action. To determine whether your facility is regulated by this action,
you should examine the applicability criteria in 40 CFR 63.11140 of
subpart DDDDDD (NESHAP for Polyvinyl Chloride and Copolymers Production
Area Sources), 40 CFR 63.11146 of subpart EEEEEE (NESHAP for Primary
Copper Smelting Area Sources), 40 CFR 63.11153 of subpart FFFFFF
(NESHAP for Secondary Copper Smelting Area Sources), or 40 CFR 63.11160
of subpart GGGGGG (NESHAP for Primary Nonferrous Metals--Zinc, Cadmium,
and Beryllium
[[Page 2931]]
Area Sources). If you have any questions regarding the applicability of
this action to a particular entity, consult either the air permit
authority for the entity or your EPA regional representative as listed
in 40 CFR 63.13 of subpart A (General Provisions).
B. Where can I get a copy of this document?
In addition to being available in the docket, an electronic copy of
this final action will also be available on the Worldwide Web (WWW)
through the Technology Transfer Network (TTN). Following signature, a
copy of this final action will be posted on the TTN's policy and
guidance page for newly proposed or promulgated rules at the following
address: https://www.epa.gov/ttn/oarpg/. The TTN provides information
and technology exchange in various areas of air pollution control.
C. Judicial Review
Under section 307(b)(1) of the Clean Air Act (CAA), judicial review
of these final rules is available only by filing a petition for review
in the U.S. Court of Appeals for the District of Columbia Circuit by
March 26, 2007. Under section 307(d)(7)(B) of the CAA, only an
objection to these final rules that was raised with reasonable
specificity during the period for public comment can be raised during
judicial review. Moreover, under section 307(b)(2) of the CAA, the
requirements established by these final rules may not be challenged
separately in any civil or criminal proceedings brought by EPA to
enforce these requirements.
II. Background Information for Final Area Source Standards
Sections 112(c)(3) and 112(k)(3)(B) of the CAA instruct EPA to
identify not less than 30 HAP which, as a result of emissions from area
sources, present the greatest threat to public health in the largest
number of urban areas, and to list sufficient area source categories
\1\ to ensure that sources representing 90 percent or more of the
emissions of each of the 30 listed HAP (``area source HAP'') are
subject to regulation. Sierra Club sued EPA, alleging a failure to
complete standards for the source categories listed pursuant to CAA
sections 112(c)(3) and (k)(3)(B) within the timeframe specified by the
statute. See Sierra Club v. Johnston, No. 01-1537, (D.D.C.). On March
31, 2006, the court issued an order requiring EPA to promulgate
standards under CAA section 112(d) for those area source categories
listed pursuant to CAA sections 112(c)(3) and (k)(3)(B).
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\1\ Under section 112(a) of the Clean Air Act, an area source is
defined as a stationary source that is not a major source. A major
source is defined as a stationary source or a group of stationary
sources located within a contiguous area and under common control
that emits or has the potential to emit considering controls, in the
aggregate, 10 tons per year or more of any HAP or 25 tons per year
or more of any combination of HAP.
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Among other things, the order requires that, by December 15, 2006,
EPA complete standards for four of the listed area source categories.
On October 6, 2006 (71 FR 59302) we proposed NESHAP for the following
four listed area source categories that we have selected to meet the
December 15, 2006 deadline: (1) Primary Copper Smelting; (2) Secondary
Copper Smelting; (3) Polyvinyl Chloride and Copolymers Production; and
(4) Primary Nonferrous Metals--Zinc, Cadmium, and Beryllium. These
final NESHAP complete the required regulatory action for four area
source categories.
Under CAA section 112(d)(5), the Administrator may, in lieu of
standards requiring maximum achievable control technology (MACT) under
section 112(d)(2), elect to promulgate standards or requirements for
area sources ``which provide for the use of generally available control
technologies or management practices by such sources to reduce
emissions of hazardous air pollutants.'' Under section 112(d)(5), the
Administrator has the discretion to use generally available control
technology (GACT) or management practices in lieu of MACT. As mentioned
in the proposed NESHAP for these four area source categories, we have
decided not to issue MACT standards and concluded that requirements
that provide for the use of GACT or generally available management
practices are appropriate for these four source categories (71 FR
59302, 59304, October 6, 2006).
III. Summary of Final Rules and Changes Since Proposal
A. NESHAP for Polyvinyl Chloride and Copolymers Production Area Sources
As proposed, we are adopting the requirements in 40 CFR part 61,
subpart F that apply to polyvinyl chloride (PVC) plants as the NESHAP
for the Polyvinyl Chloride and Copolymer Production area source
category. The only change since the proposed rule is that this final
rule does not adopt either the startup, shutdown, and malfunction (SSM)
requirements in 40 CFR 63.6(e)(3) or the preconstruction notification
requirements in 40 CFR 63.5. As discussed in more detail in section
IV.B of this preamble, under the construct of part 61 standards,
sources must comply with the standards at all times, including periods
of SSM. Because in this final rule we are adopting the part 61
standards for PVC plants as the area source standard, separate
requirements governing SSM are not necessary. We have also determined
that the preconstruction notification requirements at 40 CFR 63.5 are
not necessary because a comparable preconstruction notification is
already required under the part 61 General Provisions (40 CFR part 61,
subpart A), which apply to this NESHAP.
1. Applicability and Compliance Dates
This final rule applies to both new and existing PVC and copolymer
plants that are area sources of HAP. The owner or operator of an
existing source must comply with all the requirements of this area
source NESHAP by January 23, 2007. The owner or operator of a new
source must comply with this area source NESHAP by January 23, 2007 or
at startup, whichever is later.
2. Emissions Limits and Work Practice Standards
The Polyvinyl Chloride and Copolymers Production area source
category was listed for its contribution to the emissions of the area
source HAP vinyl chloride. As proposed, we are adopting the
requirements in 40 CFR part 61, subpart F that are applicable to PVC
plants as the NESHAP for the Polyvinyl Chloride and Copolymer
Production area source category. These requirements in subpart F
include numerical emissions limits for reactors; strippers; mixing,
weighing, and holding containers; monomer recovery systems; emissions
sources following the stripper(s); and reactors used as strippers. In
addition, they include emissions limits and work practice requirements
that apply to discharges from manual vent valves on a PVC reactor and
relief valves in vinyl chloride service, fugitive emissions sources,
and equipment leaks. Subpart F also requires a new or existing source
to comply with the requirements at 40 CFR part 61, subpart V for the
control of equipment leaks. As discussed in the proposal preamble, we
have determined that these requirements represent GACT for sources in
this area source category.
3. Compliance Requirements
We are including in this NESHAP the monitoring, testing,
recordkeeping, and reporting requirements in 40 CFR part 61, subpart F.
This final NESHAP requires a vinyl chloride continuous emissions
monitoring system (CEMS) for the regulated emissions sources (except
for sources following the stripper) and for any control system to which
reactor emissions or fugitive
[[Page 2932]]
emissions must be ducted. Plants using a stripper to comply with this
NESHAP must also determine the daily average vinyl chloride
concentration for each type of resin. The owner or operator must submit
quarterly reports containing information on emissions or resin
concentrations that exceed the applicable limits. Records are required
to demonstrate compliance, including a daily operating log for each
reactor. Plants are required to comply with the testing, monitoring,
recordkeeping, and reporting requirements in the part 61 General
Provisions (40 CFR part 61, subpart A). For the reasons discussed in
sections III.A and IV.B of this preamble, this final NESHAP does not
require that the owner or operator comply with the SSM requirements at
40 CFR 63.6(e)(3) and the preconstruction notification requirements at
40 CFR 63.5.
4. Exemption From Title V Permit Requirements
Section 502(a) of the CAA provides that EPA may exempt one or more
area sources from the requirements of title V if EPA finds that
compliance with such requirements is ``impracticable, infeasible, or
unnecessarily burdensome'' on such area sources. EPA must determine
whether to exempt an area source from title V at the time we issue the
relevant section 112 standard (40 CFR 70.3(b)(2)). For the reasons
discussed in the preamble to the proposed rule, we are exempting PVC
and copolymers production area sources from the requirements of title
V. PVC and copolymers production area sources are not required to
obtain title V permits solely as a function of being the subject of the
NESHAP; however, if they were otherwise required to obtain title V
permits, such requirement(s) would not be affected by this exemption.
We received no comments on our proposal to exempt PVC and copolymer
production area sources from the requirements of title V.
B. NESHAP for Primary Copper Smelting Area Sources
The Primary Copper Smelting area source category was listed for its
contribution to the emissions of the area source HAP arsenic, cadmium,
chromium, lead, and nickel. As discussed in more detail in section IV.C
of this preamble, the major change since the proposed rule is that we
established a subcategory of primary copper smelters that use the batch
converting technology and developed separate standards for this
subcategory. At the time of the proposed rule, we were not aware of any
area sources using the batch converting technology. Since then, we
received comments indicating that there may or will be primary copper
smelting area sources that use the batch converting technology. Because
batch technology is quite different from the continuous converting
technology we used to develop the proposed standards for the Primary
Copper Smelting area source category in terms of process operation,
emissions points, and achievable levels of control, we believe that the
proposed standards do not represent GACT for existing primary copper
smelting area sources that use the batch converting technology.
Accordingly, we developed a separate standard for existing sources that
use the batch converting technology, and we developed that standard
based on the title V permit of one batch converting facility that we
have determined to be effectively controlling its HAP emissions by
complying with its permit terms and conditions.
In response to comments, we also made several changes to the
proposed rule for primary copper smelters that do not use the batch
converting technology. As explained in the preamble to the proposed
rule, we have determined that certain terms and conditions in the title
V permit of the only area source primary smelter of which we are aware
provide effective control of HAP emissions and represent GACT for these
sources. We made changes in the proposed rule to more accurately
capture the relevant terms and conditions in this existing area
source's title V permit. Specifically, we clarified that capture and
control systems are not required for anode casting and holding
operations; that the sampler required for existing sources is a
continuous PM sampler; that the emissions limit is expressed as PM less
than 10 microns in aerodynamic diameter (PM10) rather than PM; and that
a single gas collection system could serve multiple process vessels.
As discussed in section IV.B of this preamble, we allow new and
existing sources to comply with either the SSM requirements in 40 CFR
63.6(e)(3) or the detailed SSM requirements in the final rule that were
developed from the existing sources' title V permits, which are
substantially equivalent to the SSM requirements in 40 CFR part 63.
1. Applicability and Compliance Dates
This final rule applies to each new or existing primary copper
smelter that is an area source of HAP. The owner or operator of an
existing affected source must comply by January 23, 2007. The owner or
operator of a new affected source must comply by January 23, 2007 or
upon initial startup, whichever is later. An affected source is new if
construction or reconstruction of the affected source was commenced on
or after October 6, 2006.
2. Emissions Limits and Work Practice Standards
As previously mentioned, we have developed separate standards for
existing sources that use the batch converting technology and for those
that do not. However, the standards for new sources apply to all new
area source primary copper smelters irrespective of the converting
technology utilized.
Under this final rule, the owner or operator of an existing area
source using any converting technology is required to control HAP
emissions from copper concentrate drying, copper concentrate smelting,
copper matte drying and grinding, copper matte converting, and copper
anode refining. As discussed in the proposal preamble, we are using PM
as a surrogate for HAP metals. Gases and fumes generated by these
processes must be captured and vented through one or more PM control
devices. For existing primary copper smelters that do not use the batch
converting process, the total emissions of PM10 from the captured gas
streams from all of these processes is limited to 89.5 pounds per hour
(lb/hr) as determined on a 24-hour average basis.
For existing primary copper smelters using the batch converting
technology, the exhaust gases from each smelter vessel and each
converter must be collected and sent to a PM control device and to a
sulfuric acid plant. A secondary gas collection system must be
installed on each smelting vessel and converter, and PM emissions from
the secondary capture and control system must not exceed 0.02 grains
per dry standard cubic foot (gr/dscf). The PM emissions from each
copper concentrate dryer must not exceed 0.022 gr/dscf.
Similarly, the owner or operator of a new area source using any
converting technology must control HAP emissions from all primary
copper smelting processes, including but not limited to those processes
mentioned above that are applicable to the new source's smelter design.
Gases and fumes generated by these processes at a new source must be
captured and vented through one or more PM control devices. We are
requiring a new source to achieve a facility input-based emissions rate
for total PM no greater than a daily (24-hour) average of 0.6 pounds
per ton (lb/ton) of copper concentrate feed charged to the smelting
vessel.
This final rule for new area source primary copper smelters also
requires a secondary gas system for each smelting
[[Page 2933]]
vessel and converting vessel that collects the gases and fumes released
during the molten material transfer operations and conveys the
collected gas stream to a control device. Capture systems that collect
gas and fumes and convey them to a control device also are required for
operations in the anode refining. These capture and control
requirements apply to all new and existing area sources using any
copper smelting technology.
3. Compliance Requirements
In this final rule, we have adopted the testing, monitoring,
operation and maintenance, recordkeeping, and reporting requirements
for PM emissions that are in the title V permits of the existing area
source smelters. Compliance with the emissions limit for existing area
sources not using the batch converting technology is based on the daily
average PM10 emissions measured by a continuous PM sampler.
For smelters using the batch conversion technology, compliance is based
on performance tests at least every 2.5 years and continuous monitoring
using continuous opacity monitoring systems (COMS) for electrostatic
precipitators and bag leak detection systems for baghouses.
The operation and maintenance requirements in this final rule for
existing sources using any converting technology are based on the
existing sources' title V permits. At all times, the owner or operator
must to the extent practicable, maintain and operate any affected
source, including associated air pollution control equipment, in a
manner consistent with good air pollution control practice for
minimizing emissions. In addition, all pollution control equipment must
be installed, maintained, and operated properly. Instructions from the
vendor or established maintenance practices that maximize pollution
control must be followed. Maintenance records must be made available to
the permitting authority upon request.
This final rule allows any new or existing source to meet the SSM
requirements specified in this final rule or the SSM requirements in 40
CFR 63.6(e)(3). The SSM requirements that are specified in this final
rule were developed from the existing sources' title V permit
requirements, and we believe these requirements are equally applicable
to new and existing area sources irrespective of the converting
technology used. Sources may nevertheless choose to comply with the SSM
provisions in 40 CFR 63.6(e)(3), in lieu of the SSM requirements
specified in this final rule. The SSM provisions in this final rule
require that all malfunctions be reported within two working days of
the event. The report must include a description of the malfunction,
steps taken to mitigate emissions, and corrective actions taken. In
addition, the owner or operator must show through signed
contemporaneous logs or other relevant evidence that: (1) A malfunction
occurred and the probable cause can be identified, (2) the facility was
being operated properly at the time the malfunction occurred, and (3)
all reasonable steps were taken to minimize emissions that exceeded the
emission standards. A malfunction or emergency does not include events
caused by improperly designed equipment, lack of preventative
maintenance, careless or improper operation, or operator error.
The owner or operator of an existing area source using any copper
smelting technology must comply with notification requirements in 40
CFR 63.9 of the General Provisions (40 CFR part 63, subpart A). In the
notification of compliance status required in 40 CFR 63.9(h), the owner
or operator may certify initial compliance with the emissions limit
based on monitoring data collected during a previous compliance test.
The owner or operator also must certify initial compliance with the
work practice standards.
The owner or operator of a new primary copper smelter must install,
operate, and maintain a CEMS to measure and record PM concentrations
and gas stream flow rates for each emissions source subject to the
emissions limit. The standard requires that the PM CEMS meet EPA
Performance Specification 11 (40 CFR part 60, appendix B). A device to
measure and record the weight of the copper concentrate feed charged to
the smelting furnace each day also is required. The owner or operator
must continuously monitor PM emissions, determine and record the daily
(24-hour) value for each day, and calculate and record the daily
average pounds of total PM per ton of copper concentrate feed charged
to the smelting furnace. A monthly summary report of the daily averages
of PM per ton of copper concentrate feed charged to the smelting vessel
also is required. All notification, monitoring, testing, operation and
maintenance, recordkeeping, and reporting requirements of the part 63
General Provisions apply to the owner or operator of a new source. This
final rule allows a new source to meet the specific SSM requirements
that were developed from the title V permit requirements for existing
sources or the SSM requirements in 40 CFR 63.6(e)(3).
C. NESHAP for Secondary Copper Smelting Area Sources
We did not receive any comments on our determination of GACT for
secondary copper smelters, and we are promulgating the standard as
proposed without any changes.
1. Applicability and Compliance Dates
This final rule applies to each new secondary copper smelter that
is an area source of HAP. The owner or operator of a new affected
source is required to comply by January 23, 2007 or upon initial
startup, whichever is later.
2. Emissions Limit and Work Practice Standards
This final rule does not include requirements for existing area
sources of secondary copper smelters. As we explained in the preamble
to the proposed rule, currently there are no existing major or area
sources of secondary copper smelters. Therefore, there is not any, nor
would there ever be, an existing secondary copper smelter that would be
subject to this rule. In this circumstance, we are not issuing
standards for existing area sources of secondary copper smelters.
However, this final rule contains requirements for new area sources of
secondary copper smelters. The Secondary Copper Smelting area source
category was listed for its contribution to the emissions of the area
source HAP cadmium, lead and dioxin. We have established requirements
for new sources in this category to ensure that any potential emission
of these area source HAP from future secondary copper smelting area
sources will be appropriately controlled.
We are requiring that the owner or operator of any new secondary
copper smelter operate a capture and control system for PM emissions
from any process operation that melts copper scrap, alloys, or other
metals or that processes molten material. Emissions of PM from the
control device must not exceed 0.002 gr/dscf. The owner or operator
must also prepare and follow a written plan for the selection,
inspection, and pretreatment of copper scrap to minimize, to the extent
practicable, the amount of oil and plastics in the scrap that is
charged to smelting or melting furnaces. As we explained in the
proposal preamble, we are using PM as a surrogate for establishing
standards for metal HAP, which are cadmium and lead in this case. The
United Nations Environmental Programme (UNEP) has also recommended
using control devices with high efficiency PM removal to reduce dioxin
emissions. The pollution
[[Page 2934]]
prevention measure described above (i.e., presorting and pretreating
materials) is another UNEP recommendation for reducing dioxin
emissions. We have determined that these requirements represent GACT
for new sources of secondary copper smelters and requested comments on
this determination in the proposed rule. We did not receive any
comments on this determination.
3. Compliance Requirements
Fabric filters (baghouses) are expected to be needed to meet the
NESHAP emissions limit. Consequently, the monitoring requirements
include bag leak detection systems when baghouses are used. For
additional information on bag leak detection systems that operate on
the triboelectric effect, see ``Fabric Filter Bag Leak Detection
Guidance'', U.S. Environmental Protection Agency, Office of Air Quality
Planning and Standards, September 1997, EPA-454/R-98-015, NTIS
publication number PB98164676. This document is available from the
National Technical Information Service (NTIS), 5385 Port Royal Road,
Springfield, VA 22161. The owner or operator must prepare a written
plan for the selection, inspection, and pretreatment of copper scrap
and keep records to document conformance with the requirements in the
written plan. If a control device other than a baghouse is used, the
owner or operator must submit a monitoring plan to the permitting
authority for approval. The monitoring plan must include performance
test results showing compliance with the PM emissions limit, a plan for
operation and maintenance of the control device, a list of operating
parameters that will be monitored, and operating parameter limits that
were established during the performance test.
The owner or operator must conduct a performance test to
demonstrate initial compliance with the PM emissions limit and report
the results in the notification of compliance status required by 40 CFR
63.9(h) of the General Provisions. If a baghouse is used, the PM
concentration is to be determined using EPA Method 5 (for negative
pressure baghouses) or Method 5D (for positive pressure baghouses) in
40 CFR part 60, appendix A. Repeat performance tests are required every
5 years to demonstrate compliance with the PM emissions limit. All
requirements of the part 63 General Provisions apply to the owner or
operator of a new source, including the notification, monitoring,
testing, operation and maintenance, SSM, recordkeeping, and reporting
requirements.
D. NESHAP for Primary Nonferrous Metals--Zinc, Cadmium, and Beryllium
Area Sources
1. NESHAP for Primary Zinc Production
In this final rule, we have adopted a limit in grains per dry
standard cubic foot (gr/dscf) for certain melting furnaces at existing
zinc production area sources in addition to the proposed pound per hour
(lb/hr) limits for these furnaces at existing sources. This gr/dscf
limit is the limit that we proposed for the same furnaces at new
sources. Both the gr/dscf limit and the lb/hr limits reflect the level
of emission control that can be achieved based on the technology we
identified as GACT for these furnaces (i.e., a well-operated and well-
maintained baghouse). However, whereas the lb/hr limits were based on
the specific operations at the two existing sources of which we are
aware, the gr/dscf emission limit is not operation specific and can
apply to these furnaces at any primary zinc production area source
irrespective of its operation. For this reason, we proposed this gr/
dscf emissions limit for these furnaces at new sources. In this final
rule, we similarly allow an existing source to meet this gr/dscf limit
for these furnaces. This final rule provides existing sources the
option of meeting either the lb/hr limits or the gr/dscf limit for
these furnaces. We believe that including both the lb/hr and gr/dscf
limits in this final rule will ensure effective control of these
furnaces at all existing primary zinc production area sources in the
event that there are facilities other than the two we know and with
very different operations from the two known sources.
In addition, as discussed in section IV.B of this preamble, we
allow new and existing sources to comply with either the SSM
requirements in 40 CFR 63.6(e)(3) or with the detailed SSM requirements
in the final rule that were developed from the existing sources' title
V permits, which are substantially equivalent to the SSM requirements
in part 63.
Applicability and compliance dates. This final rule applies to each
new or existing primary zinc production facility that is an area source
of HAP. The owner or operator of an existing affected source must
comply by January 23, 2007. The owner or operator of a new affected
source must comply by January 23, 2007 or upon initial startup,
whichever is later.
Emissions limits and work practice standards. Primary zinc
production facilities were included as part of the Primary Nonferrous
Metals area source category due to their contributions to the emissions
of the area source HAP arsenic, cadmium, lead, manganese, and nickel,
all of which are metal HAP. As we mentioned in the proposal preamble,
cadmium is produced as a by-product of zinc smelting processes. There
are no primary cadmium smelters in the United States. Accordingly, the
requirements for area sources of zinc production in this final rule
also address emissions associated with any cadmium production at these
zinc production facilities.
As previously mentioned, we are using PM as a surrogate for
establishing standards for metal HAP. Under this final rule, the owner
or operator of an area source of zinc production is required to exhaust
roaster off-gases to PM removal equipment and a sulfuric acid plant.
Bypassing the sulfuric acid plant during charging of the roaster is
prohibited.
Emissions limits apply to the different types of melting furnaces
at primary zinc production facilities. For existing sources, this
NESHAP limit PM emissions to 0.93 lb/hr for zinc cathode melting
furnaces; 0.1 lb/hr for furnaces that melt zinc dust, chips, and off-
specification zinc materials; and 0.228 lb/hr for the combined exhaust
from furnaces that melt zinc scrap and alloys. As an alternative to the
lb/hr limits for these furnaces at existing sources, the owner or
operator may elect to meet a limit of 0.005 gr/dscf. For new sources,
the PM limit is 0.005 gr/dscf for the furnaces mentioned above. Other
PM limits are 0.014 gr/dscf for anode casting furnaces and 0.015 gr/
dscf for cadmium melting furnaces at new and existing sources.
Emissions limits also apply to any sintering machine at a new or
existing area source facility. If there is a sintering machine, the
owner or operator must comply with the PM limit at 40 CFR 60.172 and
the opacity limit at 40 CFR 60.174(a) of the new source performance
standard (NSPS) for primary zinc smelters (40 CFR part 60, subpart Q).
Compliance requirements. We are adopting for existing area sources
certain monitoring, recordkeeping, and reporting requirements in the
title V permits of the two existing facilities that relate to PM
emissions control. The owner or operator of an existing area source
must monitor baghouse pressure drop, perform routine baghouse
maintenance, and keep records to document compliance. In addition, we
are requiring repeat performance tests (at least once every 5 years)
for existing sources. This final rule also requires a continuous
opacity monitoring system (COMS) for any sintering machine in
accordance with 40 CFR 60.175.
[[Page 2935]]
The owner or operator of an existing area source must comply with
initial notification requirements in 40 CFR 63.9 of the General
Provisions. In the notification of compliance status required by 40 CFR
63.9(h), the owner or operator may certify initial compliance with the
HAP emissions limits based on the results of a PM performance test for
each of the regulated emissions sources conducted within the past 5
years. The owner or operator must also certify initial compliance with
the work practice standards.
If an existing source has not conducted a performance test to
demonstrate compliance with the emissions limits for a furnace, the
facility must conduct a test according to the requirements at 40 CFR
63.7 using EPA Method 5 (40 CFR part 60, appendix A) to determine the
PM concentration or an alternative method previously approved by the
permitting authority. For a sintering machine, the owner or operator
must conduct a performance test according to the procedures in 40 CFR
60.176(b) using EPA Method 5 to determine the PM concentration and EPA
Method 9 (40 CFR part 60, appendix B) to determine the opacity of
emissions.
The operation and maintenance requirements in the final rule for
existing sources are based on the sources' title V permits. The owner
or operator must maintain all equipment covered under the subpart in
such a manner that the performance or operation of the equipment does
not cause a deviation from the applicable requirements. A maintenance
record must be kept for each item of air pollution control equipment.
At a minimum, this record must show the dates of performing maintenance
and the nature of preventative maintenance activities.
This final rule allows any existing source to meet the specific SSM
requirements that were developed from the title V permit requirements
for existing sources or the SSM requirements in 40 CFR 63.6(e)(3). The
specific SSM provisions in this final rule require that all
malfunctions be reported within two working days of the event. The
report must include a description of the malfunction, steps taken to
mitigate emissions, and corrective actions taken. In addition, the
owner or operator must show through signed contemporaneous logs or
other relevant evidence that: (1) A malfunction occurred and the
probable cause can be identified, (2) the facility was being operated
properly at the time the malfunction occurred, and (3) all reasonable
steps were taken to minimize emissions that exceeded the emission
standards. A malfunction or emergency does not include events caused by
improperly designed equipment, lack of preventative maintenance,
careless or improper operation, or operator error.
As required in the existing permits, the owner or operator must
submit a notification to the permitting authority of any deviation from
the requirements of this final NESHAP. The notification must describe
the probable cause of the deviation and any corrective actions or
preventative measures taken. Existing facilities are also required to
submit semiannual monitoring reports which clearly describe any
deviations. Records of baghouse maintenance, all required monitoring
data, and support information also are required. The owner or operator
of an existing area source must also comply with the notification
requirements in 40 CFR 63.9 of the General Provisions.
The owner or operator of a new area source is required to install
and operate a bag leak detection system for each baghouse used to
comply with a PM emissions limit. For additional information on bag
leak detection systems that operate on the triboelectric effect, see
``Fabric Filter Bag Leak Detection Guidance'', U.S. Environmental
Protection Agency, Office of Air Quality Planning and Standards,
September 1997, EPA-454/R-98-015, NTIS publication number PB98164676.
This document is available from the National Technical Information
Service (NTIS), 5385 Port Royal Road, Springfield, VA 22161. In
addition, we are requiring repeat PM performance tests (once every 5
years) for each furnace at a new source. The owner or operator must
also install, operate, and maintain a COMS for each sintering machine
according to EPA Performance Specification 1 (40 CFR part 60, appendix
B).
The owner or operator of a new affected source must demonstrate
initial compliance with the applicable emissions limits by conducting a
performance test according to the requirements at 40 CFR 63.7 and using
EPA 5 or 5D (40 CFR part 60, appendix A), as applicable, to determine
the PM concentration. An initial performance test is also required for
a sintering machine according to the methods and procedures in 40 CFR
60.176(b). All of the notification, testing, monitoring, operation and
maintenance, recordkeeping, and reporting requirements of the part 63
General Provisions apply to a new area source. This final rule allows a
new source to meet the specific SSM requirements in this final rule or
the SSM requirements in 40 CFR 63.6(e)(3).
2. NESHAP for Primary Beryllium Production Area Sources
The only change since proposal is that this final rule does not
adopt the SSM requirements in 40 CFR 63.6(e)(3) and the preconstruction
notification requirements in 40 CFR 63.5. As discussed in more detail
in section IV.B of this preamble, we have determined that the SSM
requirements are not necessary for standards under part 61 that must be
met at all times, and the preconstruction notification is already
required under the part 61 General Provisions.
Applicability and compliance dates. For this final rule, we are
adopting all of the requirements in the National Emission Standard for
Beryllium at 40 CFR part 61, subpart C. The owner or operator of an
existing area source must comply with this NESHAP by January 23, 2007.
The owner or operator of a new area source must comply by January 23,
2007 or at startup, whichever is later.
Emissions limits. Primary beryllium production facilities were
included as part of the Primary Nonferrous Metals area source category
due to their contributions to the emissions of the area source HAP
arsenic, cadmium, lead, manganese, and nickel, all of which are metal
HAP. As discussed in the proposal preamble, we are using beryllium as a
surrogate for HAP metals. We are adopting the 40 CFR part 61, subpart C
standard as the requirements for both new and existing primary
beryllium production facilities in this final rule. The part 61,
subpart C standard limits emissions from extraction plants (i.e.,
primary beryllium production facilities) to 10 grams (0.022 lb) of
beryllium over a 24-hour period. Alternatively, the owner or operator
of a beryllium production facility may request to meet an ambient
concentration limit instead of the emissions limit. As discussed in the
preamble to the proposed rule, the part 61 standard is highly effective
in controlling PM and metal HAP emissions from the only existing
beryllium production facility known to us at the time of the proposal.
We have determined that these requirements reflect GACT for area
sources of beryllium production. We did not receive any comments on
this determination.
Compliance requirements. This final rule requires the owner or
operator to comply with the testing, monitoring, recordkeeping, and
reporting requirements in 40 CFR part 61, subpart
[[Page 2936]]
C. An owner or operator subject to the ambient concentration limit must
operate air sampling sites to continuously monitor the concentrations
of beryllium in the ambient air according to an EPA-approved plan.
The owner or operator must comply with recordkeeping requirements
in 40 CFR part 61, subpart C, as well as the testing, monitoring,
recordkeeping, and reporting requirements in the part 61 General
Provisions in 40 CFR part 61, subpart A. For the reasons discussed in
section IV.B of this preamble, this final rule does not require that
the owner or operator comply with the requirements for SSM plans and
reports in 40 CFR 63.6(e)(3) or the preconstruction notification
requirements in 40 CFR 63.5.
IV. Summary of Comments and Responses
A. Existing Area Source Facilities
At proposal, we stated that we did not know of any existing sources
in the Polyvinyl Chloride and Copolymer area source category, and we
requested comments on whether there are or ever will be any area
sources in this area source category. We also stated that currently
there is only one area source of primary copper production in operation
in the United States and that there are no primary beryllium production
area sources.
Comment: One commenter informed us of an area source PVC plant in
Alabama. In addition, two commenters stated that there are a few (at
least three) PVC plants that they believe may qualify as area sources.
According to the commenters, these were once major sources that have
reduced HAP emissions significantly or that are currently shut down but
are expected to start up again with significantly less emissions than
from previous operations as major sources. The commenters requested
that EPA clarify the meaning of ``potential to emit'' in its definition
of an ``area source'' in the proposed rule, as well as the proposed
rule's applicability to plants that have obtained or, for the ones that
are not currently operating, will obtain permits that limit emissions
to levels below the major source thresholds. In addition, the
commenters requested clarification of the proposed rule's applicability
to PVC plants co-located at chemical complexes that are major sources.
One commenter notified us of an area source primary beryllium plant
in Utah. The commenter sought clarification of the proposed rule's
applicability to a primary beryllium plant that is a major source
because of perchloroethylene emissions and that may become an area
source in the future by eliminating the use of perchloroethylene.
We also received comments that there are two operating primary
copper smelters that are area sources rather than just one, as EPA
stated in the proposed rule. The company operating this second source
reported that it was an area source (synthetic minor) based on a
determination by the permitting authority. The company also stated that
it is planning to restart a primary copper smelter in Texas that has
been shutdown and under ``care and maintenance'' for several years.
This facility will incorporate feedstock limitations to remain below
major source thresholds, and the company expects that this facility
will qualify as an area source when the renewed permits are issued. The
commenter sought clarification of the applicability of the proposed
rule to the two primary copper smelters described above.
Response: Section 112(a) of the CAA defines the terms ``major
source'' and ``area source.'' An ``area source'' is defined as any
stationary source that is not a major source. In the proposed rule, we
included a definition for ``area source'' and that definition attempted
to summarize the statutory definitions of ``major source'' and ``area
source.'' Commenters sought clarification of the meaning of the term
``potential to emit'' contained in the proposed definition of ``area
source.'' Based on the comment, it appears that the proposed definition
of ``area source'' has caused confusion. Because the proposed
definition of ``area source'' was merely intended to summarize the
statutory definitions of ``major source'' and ``area source'' and is
redundant of the definition of ``area source'' contained in the General
Provisions (40 CFR part 63, subpart A), we have decided not to finalize
the proposed ``area source'' definition. Instead, as noted in the
NESHAP for each of these four area source categories, the definitions
of ``major source,'' ``area source,'' and ``potential to emit'' in 40
CFR 63.2 apply to this final rule.\2\ To the extent the commenters have
questions as to whether their facility is a major source or an area
source, EPA cannot answer these site-specific applicability questions
in the context of this national rulemaking. We refer the commenters to
the definitions of ``major source,'' ``area source,'' and ``potential
to emit'' found in 40 CFR 63.2, and recommend that the commenters
consult with the relevant permitting authority or submit a request for
an applicability determination to the EPA regional office in the region
where the source is located.
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\2\ In 1995, the Court of Appeals for the District of Columbia
Circuit reviewed the definition of ``potential to emit'' (PTE)
contained in 40 CFR in 40 CFR 63.2 (National Mining Ass'n v. EPA, 59
F.3d 1351 (D.C. Cir. 1995)). In July 2005, the D.C. Circuit remanded
the definition to EPA to the extent the definition required that
physical or operational limitations be ``federally enforceable''
(National Mining Ass'n v. EPA, 59 F.3d 1351 (D.C. Cir. 1995)). The
court did not vacate the 40 CFR part 63 regulations and therefore
the definition of ``potential to emit'' in 40 CFR part 63 remains in
place. EPA is currently in the process of developing a proposed rule
that responds to the court's remand. EPA has a transitional policy
that relates to PTE. See ``Options for Limiting the Potential to
Emit (PTE) of a Stationary Source Under Section 112 and Title V of
the Clean Air Act (Act)'' (Jan. 25, 1995), available at https://
www.epa.gov/Region7/programs/artd/air/title5/t5memos/ptememo.pdf.
EPA has extended the transition policy several times. See ``Third
Extension of January 25, 1995 Potential to Emit Transition Policy''
(December 20, 1999), available at https://www.epa.gov/Region7/
programs/artd/air/title5/t5memos/4thext.pdf. Under the Third
Extension, sources can rely on State-only enforceable PTE limits
until we finalize our response to the remand.
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In addition, we want to clarify that a plant that is co-located
with other facilities that together qualify as a major source is part
of that major source and not an area source.
B. Part 63 General Provisions
Comment: One commenter representing the two beryllium plants
objected to the part 63 SSM requirements in the proposed NESHAP for the
Primary Beryllium Production area source category. The commenter stated
that these two beryllium plants are already subject to 40 CFR part 61,
subpart C, which EPA has adopted in this final rule, as well as the SSM
requirements in State implementation plans (SIP), State laws, and title
V permits. According to the comment, because these plants are subject
to a strict ambient air standard for beryllium under the part 61
NESHAP, which requires that the plants monitor continuously and meet
the required limits under all conditions, the part 63 SSM requirements
are not necessary. Commenters representing facilities in the PVC
industry provided similar comments. In addition, they stated that by
requiring compliance with part 61 and the SSM provisions in 40 CFR
63.6, the proposed rule would impose two different SSM schemes in one
standard. It would also impose more burdensome reporting and
recordkeeping obligations on the lower emitting (area) sources.
Representatives of two primary copper companies also stated that
the SSM requirements are unnecessary and duplicative of existing
requirements and should be deleted. Their title V permits contain
existing functionally equivalent
[[Page 2937]]
SSM provisions, including requirements for timely notification and
reporting.
Response: We agree that the SSM requirements in the 40 CFR part 63
General Provisions need not be included in the NESHAP for the PVC and
Copolymer Production and the Primary Beryllium Production area source
categories, both of which adopted the relevant part 61 standards for
these categories. Under the construct of the part 61 standards, sources
must comply with the standards at all times, including periods of SSM.
Therefore, separate requirements governing SSM are not necessary.
Accordingly, we have revised the proposed rule to eliminate the part 63
SSM requirements for new and existing primary beryllium and PVC plants.
We also examined the SSM requirements that are in title V permits
for other source categories. The primary copper smelters and primary
zinc production plants have similar requirements in their permits. Our
review indicates that these requirements are substantially equivalent
to the part 63 SSM requirements. For example, the title V permits for
these plants require that all malfunctions be reported within two
working days of the event. The report must include a description of the
malfunction, steps taken to mitigate emissions, and corrective actions
taken. In addition, the permittee must show through signed
contemporaneous logs or other relevant evidence that: (1) A malfunction
occurred and the permittee can identify the probable cause, (2) the
facility was being operated properly at the time the malfunction
occurred, and (3) all reasonable steps were taken to minimize emissions
that exceeded the emission standards or other requirements of the
permit. The permit also makes it clear that a malfunction or emergency
does not include events caused by improperly designed equipment, lack
of preventative maintenance, careless or improper operation, or
operator error.
Based on the comments and our review of title V permits, we are
including in this final rule alternative SSM requirements that we have
formulated based on our review of the title V permits mentioned above.
Under this final rule, a new or existing primary copper smelter or
primary zinc production facility may choose to meet the SSM
requirements in 40 CFR 63.6(e)(3) or the alternative SSM requirements
provided in this final rule.
This final rule also includes operation and maintenance
requirements for existing sources that are based on the permits. For
primary copper smelters, the owner or operator must to the extent
practicable, maintain and operate any affected source, including
associated air pollution control equipment, in a manner consistent with
good air pollution control practice for minimizing emissions. In
addition, all pollution control equipment must be installed,
maintained, and operated properly. Instructions from the vendor or
established maintenance practices that maximize pollution control must
be followed. All necessary equipment control and operating devices,
such as pressure gauges, ampere meters, volt meters, flow rate
indicators, temperature gauges, continuous emissions monitoring
systems, etc., must be installed, operated properly and easily
accessible to compliance inspectors. A copy of all manufacturers'
operating instructions for pollution control equipment and pollution
emitting equipment must be maintained at the facility site. These
instructions must be available to all employees who operate the
equipment and must be made available to the permitting authority upon
request. Maintenance records must be made available to the permitting
authority upon request.
Comment: One commenter stated that we should not adopt the
preconstruction notification requirements in the part 63 General
Provisions (40 CFR part 63, subpart A) because they were unnecessary
and duplicate the very similar requirements already in the part 61
General Provisions (40 CFR part 61, subpart A). EPA should not impose
the additional burden of submitting and processing two duplicative
applications and should just rely on the provisions already in the part
61 General Provisions.
Response: We agree that if a preconstruction notification is
submitted under the part 61 General Provisions (40 CFR 61.07), it is
not necessary to submit another preconstruction notification under the
part 63 General Provisions. We have revised the proposed rule to
reflect this change.
Comment: One commenter stated that EPA should not incorporate any
of the part 63 General Provisions into area source standards that adopt
the part 61 NESHAP. These provisions, including those in 40 CFR 63.1
(Applicability), are already addressed in the part 61 General
Provisions and enhanced by SIP requirements and title V permits.
Response: We have previously addressed the SSM requirements and
preconstruction notifications for facilities subject to part 61
standards. The only other section of the part 63 General Provisions
that we have included for these sources deals with applicability in 40
CFR 63.1 (Sec. Sec. 63.1(a)(1) through (10), 63.1(b)(1), 63.1(c), and
63.1(d)). The provisions on applicability impose no burden on the
facility and provide clarity and useful information related to the
applicability of standards under part 63. Consequently, the final rule
includes portions of Sec. 63.1 from the part 63 General Provisions.
C. Primary Copper Smelters
Comment: Two commenters identified two primary copper smelters as
area sources in addition to the one smelter identified as an area
source in the proposal preamble. One of these smelters is operating,
and the company stated that the facility is an area source (i.e., a
synthetic minor source). The other smelter has been shut down for
several years, but it is in the process of obtaining permits to re-
start and expects to be an area source. Both of these smelters use the
batch converting process, whereas the smelter that was identified as an
area source at proposal and was the basis for GACT uses flash
continuous converting technology. The company pointed to the process
descriptions in the proposal preamble that noted the numerous
differences in the two technologies. The company suggested that their
two smelters fit into a separate subcategory (batch converting
technology) and should have rule requirements based on that technology.
The requirements in the proposed rule are not appropriate for their
smelters because the proposed rule is based on the flash continuous
converting technology.
Response: The commenters asserted that there are two area source
primary copper smelters that use the batch converting technology. As we
described in the proposal preamble (71 FR 59308, October 6, 2006),
there are numerous differences in process operation, emissions points,
and achievable levels of control. We believe that our proposed standard
for existing sources, which is based on flash continuous converting
technology, would not be appropriate for existing sources of primary
copper smelting that use the batch converting technology and that
separate standards are needed to address the different technology used
by these existing smelters. Solely for purposes of this analysis, we
accept, as true, the commenter's assertion that there are existing area
source facilities that use batch processing. As explained above, to the
extent the commenter has any question as to whether the smelters
identified above are major or area sources, they should consult with
the relevant permitting authority or submit
[[Page 2938]]
a request for an applicability determination to the EPA regional office
in the region where the source is located.
In developing the requirements for sources using the batch
converting technology, we reviewed the title V permit of the currently
operating source identified in the comment. The emissions from this
facility are controlled as a result of its title V permit requirements
to capture and control emissions of PM. The vast majority of the gases
from the smelting furnace and converter are collected by a primary
capture system, sent to control equipment to remove PM, and then
processed in a sulfuric acid plant. Fugitive emissions are collected by
a secondary capture system and sent to a baghouse for control of PM
emissions. We determined that these current permit requirements
represent GACT for existing primary copper smelters using the batch
converting process and have included these requirements in this final
rule as the requirements for existing primary copper smelting area
sources that use batch converting technology.
According to these requirements, plants that use batch converting
technology must operate primary capture systems on each smelting vessel
and each copper converter. Secondary capture systems must be installed
to capture emissions from tapping copper matte and slag from the
smelting vessel and emissions from charging, skimming, pouring, and
holding when the converter mouth is partially rotated out from the
primary collection hood. All of the collected gases must be routed to
an emissions control system. In addition, emissions from the primary
collection system for the smelting vessel and converter must be routed
to a sulfuric acid plant after PM removal.
Emissions from each copper concentrate dryer must be controlled and
must not exceed 0.022 gr/dscf. Emissions from secondary capture systems
that are not vented to a sulfuric acid plant must not exceed 0.02 gr/
dscf.
We also examined the monitoring requirements in the title V permit
of this primary smelter using the batch technology and found that they
would ensure that control devices are working properly on a continuous
basis. We therefore included these monitoring requirements in this
final rule as requirements for primary copper smelting area sources
that use the batch converting technology. Under these requirements, a
COMS meeting Performance Specification 1 (40 CFR part 60, appendix B)
must be installed on each electrostatic precipitator. If the 24-hour
rolling average opacity exceeds 15 percent, the plant must investigate
the cause of the problem and take corrective action. Each baghouse must
be equipped wit