National Emission Standards for Hazardous Air Pollutants: Area Source Standards for Prepared Feeds Manufacturing, 522-551 [E9-30498]
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Federal Register / Vol. 75, No. 2 / Tuesday, January 5, 2010 / Rules and Regulations
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 63
[EPA–HQ–OAR–2008–0080; FRL–9095–2]
RIN 2060–AO98
National Emission Standards for
Hazardous Air Pollutants: Area Source
Standards for Prepared Feeds
Manufacturing
AGENCY: Environmental Protection
Agency (EPA).
ACTION: Final rule.
SUMMARY: EPA is issuing national
emission standards for control of
hazardous air pollutants (HAP) for the
Prepared Feeds Manufacturing area
source category. The emissions
standards for new and existing sources
are based on EPA’s determination as to
what constitutes the generally available
control technology or management
practices for the area source category.
DATES: This final rule is effective on
January 5, 2010.
ADDRESSES: EPA has established a
docket for this action under Docket ID
No. EPA–HQ–OAR–2008–0080. All
documents in the docket are listed in
the Federal Docket Management System
index at https://
www.regulations.gov.index. Although
listed in the index, some information is
not publicly available, e.g., confidential
business information (CBI) or other
information whose disclosure is
restricted by statute. Certain other
material, such as copyrighted material,
will be publicly available only in hard
copy form. Publicly available docket
materials are available either
electronically in https://
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.
Jan King, Outreach and Information
Division, Office of Air Quality Planning
and Standards (C404–05), U.S.
Environmental Protection Agency,
Research Triangle Park, North Carolina
27711, telephone number: (919) 541–
5665; fax number: (919) 541–7674;
e-mail address: king.jan@epa.gov.
SUPPLEMENTARY INFORMATION: The
supplementary information in this
preamble is organized as follows:
I. General Information
A. Does This Action Apply to Me?
B. Where Can I Get a Copy of This
Document?
C. Judicial Review
II. Background Information for This Final
Rule
III. Summary of Changes Since Proposal
A. Applicability
B. Standards and Compliance
Requirements
C. Reporting and Recordkeeping
Requirements
D. Definitions
IV. Summary of Final Standards
A. What Are the Applicability Provisions
and Compliance Dates?
B. What Are the Final Standards?
C. What Are the Compliance
Requirements?
D. What Are the Notification,
Recordkeeping, and Reporting
Requirements?
V. Summary of Comments and Responses
NAICS code 1
Category
Industry:
Other Animal Foods Manufacturing .....................................
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1 North
311119
A. Rulemaking Process
B. Applicability
C. Emission Standards
D. Inspections and Compliance Provisions
E. Reporting and Recordkeeping
Requirements
F. Definitions
G. Impacts Assessment
H. Title V Requirements
VI. Impacts of the Final Standards
VII. 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. Executive Order 12898: Federal Actions
To Address Environmental Justice in
Minority Populations and Low-Income
Populations
K. Congressional Review Act
I. General Information
A. Does This Action Apply to Me?
The regulated categories and entities
potentially affected by the final
standards are prepared feeds
manufacturers who add chromium
compounds or manganese compounds
to their product. In general, the facilities
potentially affected by the rule are
covered under the North American
Industrial Classification System
(NAICS) code listed in the following
table.
Examples of regulated entities
Animal feeds, prepared (except dog and cat), manufacturing.
American Industry Classification System.
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 would be
regulated by this action, you should
examine the applicability criteria in 40
CFR 63.11619 of subpart DDDDDDD
(NESHAP for Area Sources: Prepared
Feeds Manufacturing). 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
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representative as listed in 40 CFR 63.13
of subpart A (General Provisions).
B. Where Can I Get a Copy of This
Document?
provides information and technology
exchange in various areas of air
pollution control.
C. Judicial Review
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 EPA’s
Technology Transfer Network (TTN). 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
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Under section 307(b)(1) of the Clean
Air Act (CAA), judicial review of this
final rule is available only by filing a
petition for review in the United States
Court of Appeals for the District of
Columbia Circuit by March 8, 2010.
Under section 307(b)(2) of the CAA, the
requirements established by this final
rule may not be challenged separately in
any civil or criminal proceedings
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brought by EPA to enforce these
requirements.
Section 307(d)(7)(B) of the CAA
further provides that ‘‘[o]nly an
objection to a rule or procedure which
was raised with reasonable specificity
during the period for public comment
(including any public hearing) may be
raised during judicial review.’’ This
section also provides a mechanism for
EPA to convene a proceeding for
reconsideration, ‘‘[i]f the person raising
an objection can demonstrate to EPA
that it was impracticable to raise such
objection within [the period for public
comment] or if the grounds for such
objection arose after the period for
public comment (but within the time
specified for judicial review) and if such
objection is of central relevance to the
outcome of the rule.’’ Any person
seeking to make such a demonstration to
us should submit a Petition for
Reconsideration to the Office of the
Administrator, U.S. EPA, Room 3000,
Ariel Rios Building, 1200 Pennsylvania
Ave., NW., Washington, DC 20460, with
a copy to both the person(s) listed in the
preceding FOR FURTHER INFORMATION
CONTACT section, and the Associate
General Counsel for the Air and
Radiation Law Office, Office of General
Counsel (Mail Code 2344A), U.S. EPA,
1200 Pennsylvania Ave., NW.,
Washington, DC 20460.
II. Background Information for This
Final Rule
Section 112(d) of the CAA requires
EPA to establish national emission
standards for hazardous air pollutants
(NESHAP) for both major and area
sources of HAP that are listed for
regulation under CAA section 112(c). A
major source emits or has the potential
to emit 10 tons per year (tpy) or more
of any single HAP or 25 tpy or more of
any combination of HAP. An area
source is a stationary source that is not
a major source.
Section 112(k)(3)(B) of the CAA calls
for EPA to identify at least 30 HAP
which, as the result of emissions from
area sources, pose the greatest threat to
public health in the largest number of
urban areas. EPA implemented this
provision in 1999 in the Integrated
Urban Air Toxics Strategy, (64 FR
38715, July 19, 1999). Specifically, in
the Strategy, EPA identified 30 HAP that
pose the greatest potential health threat
in urban areas, and these HAP are
referred to as the ‘‘30 urban HAP.’’
Section 112(c)(3) requires EPA to list
sufficient categories or subcategories of
area sources to ensure that area sources
representing 90 percent of the emissions
of the 30 urban HAP are subject to
regulation. We implemented these
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requirements through the Integrated
Urban Air Toxics Strategy (64 FR 38715,
July 19, 1999). A primary goal of the
Strategy is to achieve a 75 percent
reduction in cancer incidence
attributable to HAP emitted from
stationary sources.
Under CAA section 112(d)(5), we may
elect to promulgate standards or
requirements for area sources ‘‘which
provide for the use of generally
available control technologies or
management practices (GACT) by such
sources to reduce emissions of
hazardous air pollutants.’’ Additional
information on GACT is found in the
Senate report on the legislation (Senate
Report Number 101–228, December 20,
1989), which describes GACT as:
* * * methods, practices and techniques
which are commercially available and
appropriate for application by the sources in
the category considering economic impacts
and the technical capabilities of the firms to
operate and maintain the emissions control
systems.
Consistent with the legislative history,
we can consider costs and economic
impacts in determining GACT. This is
particularly important when developing
regulations for source categories, like
this one, that have many small
businesses, as defined by the Small
Business Administration.
Determining what constitutes GACT
involves considering the control
technologies and management practices
that are generally available to the area
sources in the source category. We also
consider the standards applicable to
major sources in the same industrial
sector to determine if the control
technologies and management practices
are transferable and generally available
to area sources. In appropriate
circumstances, we may also consider
technologies and practices at area and
major sources in similar categories to
determine whether such technologies
and practices could be considered
generally available for the area source
category at issue. Finally, as noted
above, in determining GACT for a
particular area source category, we
consider the costs and economic
impacts of available control
technologies and management practices
on that category.
We are promulgating these national
emission standards in response to a
court-ordered deadline that requires
EPA to sign final rules establishing
emission standards for two source
categories listed pursuant to section
112(c)(3) and (k) by December 16, 2009
(Sierra Club v. Johnson, no. 01–1537,
D.D.C., March 2006). We intend to
publish a separate rulemaking in the
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Federal Register for the other source
category due in December 2009.
III. Summary of Changes Since
Proposal
This final rule contains several
changes to the proposed rule as a result
of public comments. The following
sections present a summary of the
changes to the proposed rule. We
explain the reasons for these changes in
detail in the summary of comments and
responses (section V of this preamble).
A. Applicability
The final rule applies to any prepared
feeds manufacturing facility that
produces animal feed products (not
including cat and dog feed products)
and uses a material containing
chromium or a material containing
manganese. In light of questions raised
concerning the scope of sources covered
by this area source rule, we revised
several definitions in the rule and added
other definitions. The prepared feeds
manufacturing area source category is
identified by NAICS code 311119,
‘‘Other Animal Food Manufacturing.’’
This NAICS code includes
establishments primarily engaged in
manufacturing animal feed (except dog
and cat) from ingredients, such as
grains, oilseed mill products, and meat
products. The NAICS definition also
contains a list of over 40 specific animal
feed processes that are included in the
NAICS code. First, we added a
definition of ‘‘animal feed,’’ and defined
that term to include all of the products
in NAICS code 311119. This definition
also clarifies that dog and cat feed
products are not considered animal
feed, consistent with the NAICS
definition. The final rule, therefore,
applies not only to ‘‘traditional’’ feed
products, but also to animal feed
ingredients, supplements, premixes,
concentrates, and other products
included in the definition of NAICS
code 311119. Second, we revised the
definition of a ‘‘prepared feed
manufacturing facility’’ to include the
concept of ‘‘primarily engaged.’’ To
meet the definition of a prepared feeds
manufacturing facility, a facility must be
‘‘primarily engaged’’ in the production
of animal feed. We identified that
primarily engaged in the production of
animal feed means that the animal feed
makes up at least half of the facility’s
annual production of all products. The
definition of prepared feed
manufacturing facility explicitly states
that facilities primarily engaged in
feeding animals are not prepared feed
manufacturing facilities. We also added
definitions for ‘‘a material containing
chromium’’ and ‘‘a material containing
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manganese.’’ ‘‘A material containing
chromium’’ is defined as any material
that contains chromium in an amount
greater than 0.1 percent by weight, and
‘‘a material containing manganese’’ is
defined as any material that contains
manganese in an amount greater than 1
percent by weight. We added a
requirement to provide for the situation
where a facility starts using a material
containing chromium or manganese
after the applicable compliance date.
Specifically, facilities that are not
subject to the rule but start adding
materials containing chromium or
manganese in the future become subject
to the rule at the time they begin adding
these HAP. While the rule does not
apply to prepared feeds manufacturing
facilities that do not use any materials
containing chromium or manganese, we
added provisions that make it clear that
facilities that stop using all materials
containing chromium and manganese at
a later date are no longer subject to the
rule.
B. Standards and Compliance
Requirements
The final rule retains the specific
housekeeping management practices
discussed in the proposed rule. Those
management practices must reduce dust
(use industrial vacuum, remove dust
from walls and ledges, keep doors shut).
The only change we made to these
provisions was to require that doors be
kept shut except during normal ingress
and egress, rather than the proposed
requirement to keep doors shut ‘‘as
practicable.’’
The final rule requires that a device
be installed and operated at the loadout
end of each bulk loader that loads
products containing chromium or
manganese to lessen fugitive emissions
by reducing the distance between the
loading arm and the truck or railcar.
This is a change from the proposed
requirements, which specified that
‘‘drop filter socks’’ be used on bulk
loaders.
The final rule requires that emissions
from the pelleting process at facilities
with an average daily feed production
level exceeding 50 tons per day (tpd) be
collected and routed to a cyclone
designed to achieve 95 percent or
greater reduction in particulate matter
(PM) emissions. This is a change from
the proposed rule, which required a
cyclone designed to achieve a 95
percent reduction in particulate matter
emissions less than 10 microns in
diameter (PM10). To demonstrate that
your cyclone is designed to achieve a 95
percent reduction in PM emissions, the
final rule provides three different
options: (1) Manufacturer’s
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specifications certifying that the cyclone
is designed to achieve 95 percent PM
reduction, (2) certification by a
professional engineer or responsible
official that the cyclone is designed to
achieve a 95 percent reduction in PM
emissions, or (3) a Method 5
performance test to demonstrate that the
cyclone can achieve a 95 percent
reduction in PM emissions.
The proposed rule required that the
pressure drop across the cyclone be
monitored to demonstrate that the
device was in good condition and
operating properly. The final rule
expands the monitoring options to
include other measures that indicate
proper flow through the cyclone.
Specifically, the final rule allows
monitoring of inlet flow rate, inlet
velocity, pressure drop, or fan
amperage.
C. Reporting and Recordkeeping
Requirements
The final rule requires that all sources
that have an average daily feed
production level of 50 tpd or less to
keep production records. These
facilities must also submit their initial
average daily feed production level in
the Notification of Compliance Status
report.
We added recordkeeping and
reporting requirements associated with
the new options on demonstrating
cyclone performance efficiency
(certification by professional engineer or
responsible official, or testing). We also
added provisions that require facilities
that discontinue the use of all materials
containing chromium and manganese to
notify the Agency that they are no
longer subject to the rule.
D. Definitions
As discussed above, definitions for
animal feed, a material containing
chromium, a material containing
manganese, and prepared feeds
manufacturing facility were added or
modified. The definition of filter drop
sock was removed, as this term is no
longer used in the final rule.
IV. Summary of Final Standards
A. What Are the Applicability
Provisions and Compliance Dates?
Subpart DDDDDDD standards apply
to each new or existing prepared feeds
manufacturing facility that is an area
source and uses a material containing
chromium or a material containing
manganese. A prepared feeds
manufacturing facility is a facility where
animal feed (as defined in the rule)
makes up at least half of the facility’s
annual production of all products. A
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material containing chromium is any
material that contains chromium in an
amount greater than 0.1 percent by
weight, and a material containing
manganese is any material that contains
manganese in an amount greater than 1
percent by weight.
All existing area source facilities
subject to this rule are required to
comply with the rule requirements no
later than January 5, 2012. A new source
is any affected source that commenced
construction or reconstruction after July
27, 2009. All new sources are required
to comply with the rule requirements by
January 5, 2010 or upon startup,
whichever is later.
Prepared feeds manufacturing
facilities that do not use any materials
containing chromium or manganese are
not subject to this rule. If a facility starts
using a material containing chromium
or manganese after the applicable
compliance date, they will be required
to comply at the time that they start
using such materials. Also, if a facility
stops using all materials containing
chromium and manganese, they are no
longer subject to the rule and should
notify EPA or the delegated authority of
the change.
B. What Are the Final Standards?
The final requirements, which apply
to all new and existing sources, consist
of equipment standards and
management practices. There are two
general management practices that
apply in all areas where materials
containing chromium or manganese are
stored, used, or handled. The first is to
perform housekeeping measures to
minimize excess dust that could contain
chromium or manganese. The specific
measures required by the rule are: (1)
Use either an industrial vacuum system
or manual sweeping to reduce the
amount of dust, (2) at least once per
month, remove dust from walls, ledges,
and equipment using low pressure air or
by other means, and then sweep or
vacuum the area, and (3) keep doors
shut except during normal ingress and
egress.
The second general management
practice is the requirement to maintain
and operate all process equipment that
stores, processes, or contains chromium
or manganese in accordance with
manufacturers’ specifications and in a
manner to minimize dust creation.
There are also requirements that are
specific to certain areas of the plant or
processes at all new and existing
sources. These requirements are:
• For the storage area, all raw
materials containing chromium or
manganese must be stored in closed
containers.
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• For mixing operations, materials
containing chromium or manganese
must be added to the mixer in a manner
to reduce emissions, and the mixer must
be covered at all times when mixing is
occurring, except when materials are
being added.
• For bulk loading processes where
prepared feeds products containing
chromium or manganese are loaded into
trucks or railcars, you must use a device
at the loadout end of each bulk loader
to lessen fugitive emissions by reducing
the distance between the loading arm
and the truck or railcar.
In addition to the above requirements
that apply to all facilities, new and
existing facilities with average daily
feed production levels exceeding 50 tpd
are required to install and operate a
cyclone to reduce emissions from
pelleting and pellet cooling operations.
The average daily feed production level
means the average amount of prepared
feed product produced each operating
day over an annual period. The initial
determination of the average daily feed
production level is based on the oneyear period prior to the compliance date
for existing sources, or the design rate
for new sources. Subsequent average
daily feed production levels are then
determined annually and are based on
the amount of animal feed product
produced in the calendar year divided
by the number of days in which the
production processes were in operation.
Facilities with average daily feed
production levels of 50 tpd or less are
required to submit production
information in their Notification of
Compliance Status report and keep
records documenting their animal feed
production levels.
For the pelleting operations at
facilities with daily pelleting production
levels exceeding 50 tpd, the final rule
requires that PM emissions be collected
and routed to a cyclone that is designed
to achieve 95 percent or greater
reduction in PM. There are three ways
you can demonstrate that your cyclone
is designed to achieve 95 percent
reduction in PM: (1) Manufacturer
specifications that certifying the cyclone
is designed to achieve 95 percent
reduction in PM emissions; (2)
certification by a professional engineer
or responsible official that the cyclone
is designed to achieve a 95 or greater
percent reduction in PM emissions; or
(3) a one-time Method 5 performance
test to demonstrate that the cyclone can
achieve a 95 percent or greater
reduction in PM emissions.
In addition, the final rule requires that
you establish an operating parameter
range that indicates proper operation of
the cyclone and then monitor this
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parameter at least once per day. The
specific parameters allowed to be
monitored are inlet flow rate, inlet
velocity, pressure drop, or fan
amperage. The range that represents
proper operation of the cyclone must be
provided by the manufacturer,
determined as part of the engineering
calculations demonstrating the design
efficiency, or determined based on
monitoring conducted during the
performance test.
The final rule also requires that you
maintain the cyclone in accordance
with manufacturer specifications. If
manufacturer specifications are not
available, you must develop and follow
standard maintenance procedures.
C. What Are the Compliance
Requirements?
For all new and existing sources,
compliance with the final regulation is
demonstrated through installation of the
required equipment, adherence to the
management practices specified in the
rule, and keeping the required records
and submitting the required
notifications and reports described
below.
To ensure that the cyclone for the
pelleting and pellet cooling process is
operated properly at facilities with
average daily feed production levels
exceeding 50 tpd, the final rule requires
that the cyclone be inspected quarterly
for corrosion, erosion, or any other
damage that could result in air inleakage, and that the inlet flow rate,
inlet velocity, pressure drop, or fan
amperage be monitored and recorded
daily to ensure that it is being operated
in accordance with specified proper
operating range.
The final rule also requires that the
devices required at the loadout end of
a bulk loader to lessen fugitive
emissions by containing the unloaded
product within the device be inspected
monthly to ensure that they are in good
condition.
D. What Are the Notification,
Recordkeeping, and Reporting
Requirements?
All new and existing sources are
required to comply with some
requirements of the General Provisions
(40 CFR part 63, subpart A), which are
identified in Table 1 of the final rule.
The General Provisions include specific
requirements for notifications,
recordkeeping, and reporting. Each
facility is required to submit an Initial
Notification and a one-time Notification
of Compliance Status according to the
requirements in 40 CFR 63.9 in the
General Provisions. The Initial
Notification, which is required to be
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submitted by affected sources not later
than May 5, 2010, or 120 days after you
become subject to the rule, whichever is
later, must contain basic information
about the facility and its operations. The
Notification of Compliance Status,
which is required to be submitted 120
days after the compliance date, must
contain a statement that the source has
complied with all relevant standards.
The Notification of Compliance Status
also must include the inlet flow rate,
inlet velocity, pressure drop, or fan
amperage range that constitutes proper
operation of the cyclone used to reduce
emissions from the pelleting and pellet
cooling operations. Facilities not
required to install and operate cyclones
on their pelleting operations are
required to submit documentation of
their initial average daily feed
production level.
The final rule requires that records be
kept of all notifications of compliance.
The rule requires that records be kept
documenting each inspection of a
cyclone and each inspection of a device
at the loadout end of a bulk loader. It
also requires that the daily reading of
cyclone inlet flow rate, inlet velocity,
pressure drop, or fan amperage be
recorded. In addition, records are
required of any actions taken in
response to findings of the inspections
or monitoring results outside the proper
operating range. Facilities with average
daily feed production levels of 50 tpd or
less are required to keep records of the
annual production and the number of
days of operation.
The final rule includes the
requirement to prepare, by March 1 of
each year, and submit an annual
compliance certification, a copy of
which will need to be maintained on
site. This report must contain a
statement of whether the source has
complied with all relevant standards
and other requirements of the final rule.
If a deviation from the standard
occurred during the annual reporting
period, or if an instance occurred where
the cyclone inlet flow rate, inlet
velocity, pressure drop, or fan amperage
was outside of the proper operating
range submitted in the Notification of
Compliance Status report, this
information is required to be included
in the annual report and the report
needs to be submitted to the EPA
Administrator or the designated
authority. All records are required to be
maintained in a form suitable and
readily available for expeditious review,
and kept for at least five years, the first
two of which must be onsite.
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V. Summary of Comments and
Responses
EPA received 16 public comment
letters on the proposed rule. Five of
these comment letters were requests for
an extension to the comment period,1
leaving 11 comment letters that
provided comments on the proposed
rule. These comments were received
from industry representatives, trade
associations, state agencies, and an
environmental organization. Sections
V.A through V.G of this preamble
provide responses to the public
comments received on the proposed
NESHAP.
A. Rulemaking Process
Comment: Several commenters
requested that the comment period be
extended by 90 days. The commenters
had concerns about the inputs to the
impacts analysis and requested
additional time to collect and provide
factual information to the agency about
the proposed rule’s provisions and their
potential impact.
Response: Due to a court-ordered
deadline for promulgation of this rule
(which at the time of proposal was
November 16, 2009), we were unable to
extend the comment period in response
to these requests. Moreover, CAA
section 307(d) requires that EPA provide
a minimum of 30 days for public
comment, and we provided that period
for public comment. Furthermore,
consistent with section 307(d), the
proposed rule provided the public an
opportunity to request a public hearing,
and no party requested such a hearing.
See 307(d)(5) (record remains open 30
days after the date of the public
hearing).
Comment: One commenter expressed
their concerns about the process that
EPA used to develop its proposed
national emission standard for prepared
feeds manufacturers. The commenter
believes that EPA did not provide ample
due process in developing the proposed
rule. The commenter pointed out that
they requested a 90-day extension to the
proposed rule’s comment period so that
accurate information could be obtained
to respond to the assumptions and
estimates made by the agency. In this
request, the commenter indicated that
they highlighted five major areas of the
proposed rule in which they believed
EPA lacked critical information that
directly affects the provisions within the
proposed rule and its impact on
prepared feeds manufacturers. Since
1 We denied the requests for extension by letter,
copies of which are in the docket. These letters
explain the reasons for the denial. These reasons are
also provided in section V.A.
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EPA denied their request for extension
of the comment period, the commenter
indicated that they were left with what
they believe was an inappropriately
short 30-day comment period to
respond to a proposed rule that, if
promulgated as drafted, would have
very significant operational and
economic impacts on prepared feeds
manufacturers. While cognizant of
EPA’s court-ordered mandate to issue
this national emission standard, the
commenter believes that the agency’s
actions related to gathering industry
information, timing of the proposed rule
and its response to their request for
extension of the comment period are not
indicative of a constructive or
meaningful rulemaking process.
Response: EPA complied with the
requirements of 307(d) during this
rulemaking process. We engaged
industry prior to proposal by meeting
and by telephone to discuss our
rulemaking process and the information
we intended to obtain through the 114
survey. EPA strongly disagrees with the
commenters’ assertion that EPA did not
provide ample due process in
developing the rule.
CAA 307(d) requires EPA to publish
a notice of proposed rulemaking and
provide a minimum of 30 days for the
public to comment on the proposal, and
EPA complied with this requirement.
EPA also identified a date for public
hearing, if such hearing was requested
by any member of the public. No
member of the public requested a
hearing, and therefore, a public hearing
was not held.
In conclusion, we believe that lines of
communication with the industry were
well established and open throughout
the rulemaking process, and that the
commenters had ample opportunity to
participate.
B. Applicability
Comment: Two commenters stated
that the rule should clarify that a
prepared feeds manufacturing facility is
a facility that produces feeds, and not a
facility that manufactures feed
ingredients. One of the commenters
explained that although feed ingredient
companies may predominantly
manufacture ingredients for animal feed
and be classified under the NAICS Code
defining the Prepared Feeds
Manufacturing source category (NAICS
311119), they may also produce feed
ingredients for human and/or
companion animal consumption.
Response: EPA would like to clarify
that, in addition to facilities that
produce animal feed, facilities that
manufacture feed ingredients are part of
the prepared feeds manufacturing area
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source category. The category was
identified in the original section 112(k)
emissions inventory through the use of
the Standard Industrial Classification
(SIC) code 2048, Prepared Feeds
Manufacturing, except cat and dog feed.
As noted by the commenter, the NAICS
code that covers this area source
category is 311119, which is equivalent
to the SIC code used in the original
source category definition. The SIC/
NAICS code for the source category
includes many segments of the prepared
feed industry, including the production
of feed ingredients. Specifically, in
addition to many other segments of the
industry, NAICS code 311119, and thus
the prepared feeds manufacturing area
source category, includes:
• Feed concentrates, animal,
manufacturing;
• Feed premixes, animal,
manufacturing;
• Feed supplements, animal (except
cat, dog), manufacturing;
• Micro and macro premixes,
livestock, manufacturing;
• Mineral feed supplements (except
cat, dog) manufacturing; and
• Mineral supplements, animal
(except cat, dog), manufacturing.
Therefore, since facilities that
manufacture feed ingredients are subject
to the rule, we did not make the change
suggested by the commenter. We did,
however, make changes to the
applicability provisions and definitions
to clarify the various segments of the
prepared feeds industry that are
included in the source category and,
therefore, subject to the rule (provided
they use chromium or manganese).
These changes include adding a
definition of ‘‘animal feed,’’ which
includes a list of all the products
included under NAICS code 311119.
While we recognize that chromium and
manganese are not used in the
production of many of the animal feed
products in the definition, we believe
that a complete listing eliminates the
confusion of what types of processes are
included in the source category. We
would point out, however, that, even if
a facility produces a listed animal feed
product (e.g., earthworm feed and
bedding), it is not subject to the rule if
no chromium or manganese is used.
One of the commenters raised the
issue of a facility that produces a
product covered by the rule along with
other similar products that would not be
covered by the rule. Specifically, the
commenter mentions a facility that
produces animal feed ingredients along
with feed ingredients for humans and/
or cats and dogs. First, the NAICS code
only includes establishments ‘‘primarily
engaged in’’ manufacturing animal feed.
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We have revised the definition of
‘‘prepared feed manufacturing facility’’
to incorporate this concept. Specifically,
the final rule contains the following
definition.
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Prepared feeds manufacturing facility
means a facility that is primarily engaged in
manufacturing animal feed. A facility is
primarily engaged in manufacturing animal
feed if the production of animal feed
comprises greater than 50 percent of the total
production of the facility on an annual basis.
Facilities primarily engaged in raising or
feeding animals are not considered prepared
feeds manufacturing facilities.
Thus, a facility would be a prepared
feeds manufacturing facility subject to
the rule if the animal feed ingredients
(not including ingredients for dog, cat,
or human feed) make up more than half
of its production. In addition, the final
rule specifies that an affected source at
a prepared feeds manufacturing facility
only includes the collection of
equipment and activities necessary to
produce animal feed containing
chromium or manganese. Therefore, if
the ingredients for human and/or dog
and cat feed at a facility primarily
engaged in manufacturing animal feed
were produced in equipment that is
never used to produce ‘‘animal feed,’’
those production processes would not
be part of the affected source and would
not be subject to the requirements in the
rule. While not specifically mentioned
by the commenters, consideration of
these applicability issues, along with
comments related to the number of
facilities in the source category, caused
us to clarify that prepared feeds
manufacturing at farms and animal feed
lots is not part of this source category.
Facilities ‘‘primarily engaged’’ in raising
or feeding animals are listed under
different NAICS codes (e.g., 112210—
Hog and Pig Farming, 112112—Cattle
Feedlots, 112111—Beef Cattle Ranching
and Farming) and were not part of the
sources that formed the basis for the
listing of the prepared feed
manufacturing area source category.
Comment: Five commenters stated
that the rule should only apply to
prepared feeds manufacturing facilities
that use or emit chromium compounds
or manganese compounds above a
specified threshold. The commenters
claimed that such an approach would
focus attention on facilities that are
more significant emitters of chromium
and manganese and will avoid requiring
extremely small facilities to comply
with the rule with little environmental
benefit. The commenters suggested
several different threshold levels. One
commenter recommended a threshold
based on established Superfund
Amendments and Reauthorization Act
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of 1986 (SARA) Tier II threshold
quantities (10,000 pounds per year),
while another suggested 2,000 pounds
per year based on levels determined to
be insignificant under the title V
program. Another commenter noted that
Toxics Release Inventory (TRI)
regulations require a covered facility to
report only if it manufactures or
processes non-exempt chromium and/or
manganese compounds in quantities
exceeding 25,000 pounds per year, and
suggested that a threshold be
established at this 25,000 pounds per
year level. Still another commenter
suggested a level of 1,000 pounds per
day. One of the commenters
recommended that, if such a threshold
is established, compounds having a
concentration of less than 1 percent of
the chromium compounds or
manganese compounds need not be
counted by a facility when determining
whether it has used a sufficient quantity
to reach the threshold use level that
establishes whether a facility is subject
to the rule’s provisions.
Response: Although several
commenters advocated for a usage
threshold for chromium compounds and
manganese compounds, below which a
facility would be exempt, we are not
adopting any exemptions. Prepared
Feeds Manufacturing is one of the area
source categories needed to meet the
section 112(c)(3) requirement that we
subject to regulation, (i.e., area source
categories representing 90 percent of the
emissions of chromium and
manganese). We reviewed the listing
decision for this area source category
and did not identify any information
suggesting that small sources were not
included in the listing decision. As
such, we do not believe we can satisfy
our requirement to regulate sources
representing 90 percent of the emissions
of Prepared Feeds Manufacturing urban
HAP unless we subject all sources that
emit those HAP to the rule.
We recognize that the Prepared Feeds
Manufacturing source category is
comprised of a large number of
relatively small facilities. Although area
sources individually may be considered
low-emitting sources, collectively, they
are not. The commenter’s suggestion
fails to address the requirement of
section 112(c)(3), and, as discussed
above, we previously determined that
we need to subject the Prepared Feeds
Manufacturing area source category to
regulations in order to meet the
requirement that EPA regulate area
sources accounting for 90 percent of the
emissions of the 30 urban HAP.
Comment: One commenter suggested
that the applicability be changed to only
include facilities that utilize pelletizing
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527
operations. The commenter noted that
this would more adequately match the
original group of prepared feeds
manufacturers who were surveyed and
those in the same class. The commenter
also pointed out that the pelleting and
pellet cooling process is the most
significant source of pollutants, as it is
estimated to emit 90 percent or more of
the total chromium and manganese.
Response: The basis for the listing of
the area source category was not limited
to emissions from pelleting. Thus, we
conclude that the applicability should
remain as proposed.
C. Emission Standards
1. General
Comment: One commenter stated that
EPA based the proposed standard on
erroneous and misguided assumptions
and estimates of emissions of chromium
compounds and manganese compounds.
This commenter had numerous
objections to the impacts analyses (see
section V.G) and how these analyses
impacted EPA’s decision to regulate this
category and specific emission points.
Response: In section 112(c)(3) of the
CAA, EPA is required to list ‘‘sufficient
categories or subcategories of area
sources to ensure that area source
representing 90 percent of the emissions
of the 30 urban HAP are subject to
regulation.’’ An area source emissions
inventory was compiled for each of the
30 urban HAP and the area source
categories identified that comprised 90
percent of the emissions of each of these
HAP. For the prepared feeds
manufacturing source category, this
inventory was based on data from the
1990 TRI. The TRI is an EPA inventory
of annual emissions self-reported by
industry. Based on this information,
EPA determined that chromium
compounds emissions and manganese
compounds emissions from prepared
feeds manufacturing area sources
needed to be regulated to achieve the 90
percent requirement in CAA section
112(c)(3). Therefore, the decision to
regulate emissions of chromium
compounds and manganese compounds
from the prepared feeds manufacturing
industry was based on emissions data
submitted directly by the industry. The
information and analyses referred to by
the commenter were prepared to
evaluate potential impacts of regulatory
options. This information had no
bearing on the basic decision to develop
regulations for the prepared feeds
manufacturing area source category.
The commenter is also incorrect with
respect to how emission points were
identified for regulation. They assume
that the information compiled for the
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impacts analyses was used as the basis
to identify emission points for
regulation. Rather, chromium and
manganese emission points were
identified primarily based on
information submitted directly by the
industry. Specifically, we conducted a
survey of the industry, and responses
were received for over 100 prepared
feeds manufacturing facilities. In the
responses to this survey, prepared feeds
manufacturing facilities identified
potential emission sources and reported
controls and management practices that
were being used. This information
formed the basis for the decisions
regarding the emission points and
process areas for which standards were
proposed.
In conclusion, the commenter raised
several issues on the impacts analyses
(see section V.G below). However, the
issues associated with these analyses
did not influence the basic decision to
regulate this source category or the
decisions on the specific emission
sources that would be regulated.
Comment: One commenter asserted
that, ‘‘* * * The legislative history of
§ 112 explains that Congress intended
GACT standards to reflect ‘methods,
practices and techniques which are
commercially available and appropriate
for application by sources in the
category considering economic impacts
and technical capabilities of the firms to
operate and maintain emission control
systems’.’’
The commenter also asserted that,
although EPA used its discretion to
issue GACT standards and that
§ 112(d)(5) authorizes EPA to do so, that
decision is subject to administrative law
requirements. The commenter asserted
that EPA’s decision is arbitrary and
capricious because that decision was
not supported with a rational
explanation.
Response: As the commenter
recognizes, in CAA section 112(d)(5),
Congress gave EPA explicit authority to
issue alternative emission standards for
area sources. Specifically, CAA section
112(d)(5), which is entitled ‘‘Alternative
standard for area sources,’’ provides:
With respect only to categories and
subcategories of area sources listed pursuant
to subsection (c) of this section, the
Administrator may, in lieu of the authorities
provided in paragraph (2) and subsection (f)
of this section, elect to promulgate standards
or requirements applicable to sources in such
categories or subcategories which provide for
the use of generally available control
technologies or management practices by
such sources to reduce emissions of
hazardous air pollutants.
See CAA section 112(d)(5) (Emphasis
added).
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There are two critical aspects to CAA
section 112(d)(5). First, CAA section
112(d)(5) applies only to those
categories and subcategories of area
sources listed pursuant to CAA section
112(c). The commenter does not dispute
that EPA listed the area source category
noted above pursuant to CAA section
112(c)(3). Second, CAA section
112(d)(5) provides that, for area sources
listed pursuant to CAA section 112(c),
EPA ‘‘may, in lieu of’’ the authorities
provided in CAA section 112(d)(2) and
112(f), elect to promulgate standards
pursuant to CAA section 112(d)(5). CAA
Section 112(d)(2) provides that emission
standards established under that
provision ‘‘require the maximum degree
of reduction in emissions’’ of HAP (also
known as maximum achievable control
technology or MACT). CAA section
112(d)(3), in turn, defines what
constitutes the ‘‘maximum degree of
reduction in emissions’’ for new and
existing sources. See CAA section
112(d)(3).2 Webster’s dictionary defines
the phrase ‘‘in lieu of’’ to mean ‘‘in the
place of’’ or ‘‘instead of.’’ See Webster’s
II New Riverside University (1994).
Thus, CAA section 112(d)(5) authorizes
EPA to promulgate standards under
CAA section 112(d)(5) that provide for
the use of GACT, instead of issuing
MACT standards pursuant to CAA
section 112(d)(2) and (d)(3). The statute
does not set any condition precedent for
issuing standards under CAA section
112(d)(5) other than that the area source
category or subcategory at issue must be
one that EPA listed pursuant to CAA
section 112(c), which is the case here.3
We disagree with the commenter’s
assertion that we must provide a
rationale for issuing GACT standards
under section 112(d)(5), instead of
MACT standards. Had Congress
intended that EPA first conduct a MACT
2 Specifically, CAA section 112(d)(3) sets the
minimum degree of emission reduction that MACT
standards must achieve, which is known as the
MACT floor. For new sources, the degree of
emission reduction shall not be less stringent than
the emission control that is achieved in practice by
the best controlled similar source, and for existing
sources, the degree of emission reduction shall not
be less stringent than the average emission
limitation achieved by the best performing 12
percent of the existing sources for which the
Administrator has emissions information. CAA
Section 112(d)(2) directs EPA to consider whether
more stringent emission reductions (so called
beyond-the-floor limits) are technologically
achievable considering, among other things, the
cost of achieving the emission reduction.
3 CAA Section 112(d)(5) also references CAA
section 112(f). See CAA section 112(f)(5) (entitled
‘‘Area Sources’’ and providing that EPA is not
required to conduct a review or promulgate
standards under CAA section 112(f) for any area
source category or subcategory listed pursuant to
CAA section 112(c)(3), and for which an emission
standard is issued pursuant to CAA section
112(d)(5)).
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analysis for each area source category,
Congress would have stated so expressly
in section 112(d)(5). Congress did not
require EPA to conduct any MACT
analysis, floor analysis or beyond-thefloor analysis before the Agency could
issue a section 112(d)(5) standard.
Rather, Congress authorized EPA to
issue GACT standards for area source
categories listed under section 112(c),
and that is precisely what EPA has done
in this rulemaking.
Although EPA has no obligation to
justify why it is issuing a GACT
standard for an area source category as
opposed to a MACT standard, we did
explain at proposal that being able to
consider costs and economic impacts is
important when establishing standards
for a category like this with many small
sources. Furthermore, EPA must set a
GACT standard that is consistent with
the requirements of CAA section
112(d)(5) and have a reasoned basis for
its GACT determination. As explained
in the proposed rule and below. The
legislative history supporting section
112(d)(5) provides that GACT is to
encompass:
‘‘* * * methods, practices and techniques
which are commercially available and
appropriate for application by the sources in
the category considering economic impacts
and the technical capabilities of the firms to
operate and maintain the emissions control
systems.’’
The discussion in the Senate report
clearly provides that EPA may consider
costs in determining what constitutes
GACT for the area source category.
Congress plainly recognized that area
sources differ from major sources,
which is why Congress allowed EPA to
consider costs in setting GACT
standards for area sources under section
112(d)(5), but did not allow that
consideration in setting MACT floors for
major sources pursuant to section
112(d)(3). This important dichotomy
between section 112(d)(3) and section
112(d)(5) provides further evidence that
Congress sought to do precisely what
the title of section 112(d)(5) states, i.e.,
provide EPA the authority to issue
‘‘alternative standards for area sources.’’
Notwithstanding the commenter’s
claim, EPA properly issued standards
for the area source categories at issue
here under section 112(d)(5), and in
doing so provided a reasoned basis for
its selection of GACT for these area
source categories. As explained in the
proposed rule, EPA evaluated the
control technologies and management
practices that reduce HAP emissions at
Prepared Feeds Manufacturing area
source facilities. In its evaluation, EPA
used information on pollution
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prevention from industry trade
associations, and reviewed operating
permits to identify the emission controls
and management practices that are
currently used to control volatile and
particulate HAP emissions. We also
considered technologies and practices at
major and area sources in similar
categories.
Finally, even though not required,
EPA did provide a rationale for why it
set a GACT standard in the proposed
rule. In the proposal, we explained that
the facilities in the source categories at
issue are already well controlled for the
urban HAP for which the source
category was listed pursuant to section
112(c)(3). Consideration of costs and
economic impacts proves especially
important for the well-controlled area
sources at issue in this final action.
Given the current, well controlled
emission levels, a MACT floor
determination, where costs cannot be
considered, could result in only
marginal reductions in emissions at very
high costs for modest incremental
improvement in control for the area
source category.
Comment: One commenter questioned
why EPA was not considering
regulation for all HAP emissions. The
commenter explained that, as
documented in the record for this
rulemaking, that Prepared Feed
Manufacturing facilities often generate
emissions other than manganese, such
as arsenic and arsenic compounds,
benzene, beryllium and beryllium
compounds, cadmium and cadmium
compounds, chlorine, cobalt and cobalt
compounds, formaldehyde, hexane,
hydrochloric acid, hydrogen fluoride,
lead and lead compounds, mercury and
mercury compounds, naphthalene,
nickel and nickel compounds,
polycyclic organic matter, selenium and
selenium compounds, and toluene. The
commenter acknowledged that
management practices and PM controls
required by the rule will likely reduce
other metal HAP emissions to some
degree; however they indicated that the
Agency failed to quantify this benefit.
The commenter also indicated that EPA
should consider controls for other HAPs
that will not be co-controlled with the
manganese and chromium.
Response: Section 112(k)(3)(B) of the
CAA requires EPA to identify at least 30
HAP emitted from area sources that
pose the greatest threat to public health
in the largest number of urban areas (the
‘‘Urban HAP’’) and identify the area
source categories emitting such
pollutants that are or will be listed
pursuant to section 112(c)(3). Section
112(c)(3), in relevant part, provides:
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The Administrator shall * * *, pursuant to
subsection (k)(3)(B) of this section, list, based
on actual or estimated aggregate emissions of
a listed pollutant or pollutants, sufficient
categories or subcategories of area sources to
ensure that area sources representing 90
percent of the area source emissions of the
30 hazardous air pollutants that present the
greatest threat to public health in the largest
number of urban areas are subject to
regulation under this section.
Thus, section 112(c)(3) requires EPA to
list sufficient categories or subcategories
of area sources to ensure that area
sources representing 90 percent of the
area source emissions of the 30 urban
HAP are subject to regulation. Section
112(d)(1) requires the Administrator to
promulgate regulations establishing
emissions standards for each area source
category of HAP listed for regulation
pursuant to section 112(c).
EPA identified the 30 Urban HAP that
posed the greatest threat to public
health in the Integrated Urban Air
Toxics Strategy (Strategy). In the
Strategy and subsequent Federal
Register notices, EPA listed the area
source categories necessary to meet the
90 percent requirement in section
112(c)(3) and (k)(3)(B), and one of those
categories was the Prepared Feeds
Manufacturing area source category.
We have interpreted sections 112(c)(3)
and 112(k)(3)(B) together to require EPA
to regulate only those Urban HAP
emissions for which an area source
category is listed pursuant to section
112(c)(3), not all urban HAP or all
section 112(b) HAP emitted from a
listed area source category. As stated
above, section 112(k)(3)(B) addresses the
strategy to control HAP from area
sources in urban areas and the focus of
the strategy as it relates to control of
area sources is on the 30 HAP that pose
the greatest threat to public health in the
largest number of urban areas. Section
112(c)(3) specifically references section
112(k)(3)(B) as the basis for selecting
area sources for listing to satisfy the
Agency’s responsibility for regulating
urban HAP emissions from area sources.
Under these provisions, area sources
categories are listed because they emit
one or more of the 30 listed Urban HAP
and the Agency has identified the
category as one that is necessary to
satisfy the requirement to subject area
sources representing 90 percent of the
area source emissions of the 30 urban
HAP to regulation.
EPA listed the Prepared Feeds
Manufacturing area source category
pursuant to sections 112(c)(3) and
112(k)(3)(B). We must regulate only the
chromium and manganese emissions
from the Prepared Feeds Manufacturing
area source category, as these are the
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529
urban HAP emissions for which the
category was listed to meet the 90
percent requirement in sections
112(c)(3) and (k)(3)(B). See 112(c)(3)
(EPA must ‘‘ensure that area sources
representing 90 percent of the area
source emissions of the 30 hazardous air
pollutants * * * are subject to
regulation.’’). We recognize that the
source category emits other section
112(b) HAP, including other urban HAP;
however, as stated above, sections
112(c)(3) and 112(k)(3)(B) do not require
the Agency to regulate the area source
category for any HAP other than those
for which the category was listed. As to
the other urban HAP emitted from this
category, we have identified other area
source categories that emit these urban
HAP and subjecting those area source
categories to regulation will satisfy the
requirement to subject to regulation area
sources that account for 90 percent of
the area source emissions of those urban
HAP.
While the Agency is not required to
regulate all section 112(b) HAP from
area sources listed pursuant to section
112(c)(3) and 112(k)(3)(B), section 112
of the CAA does not preclude EPA from
regulating other HAP from these area
sources at our discretion and in
appropriate circumstances. Section
112(d)(5) states that, for area sources
listed pursuant to section 112(c), the
Administrator may, in lieu of section
112(d)(2) ‘‘MACT’’ standards,
promulgate standards or requirements
‘‘applicable to sources’’ which provide
for the use of GACT or management
practices ‘‘to reduce emissions of
hazardous air pollutants.’’ This
provision does not limit EPA’s authority
to regulate only those urban HAP
emissions for which the category is
needed to achieve the 90 percent
requirement in sections 112(k)(3)(B) and
112(c)(3). In fact, in two other area
source rules, in addition to regulating
the urban HAP that were necessary to
satisfy the 90 percent requirement in
sections 112(k)(3)(B) and 112(c)(3), we
regulated additional section 112(b)
HAP. Specifically, in the chemical
manufacturing area source rule and the
paint and allied products area source
rule, although not required, we
exercised our discretion to regulate
other section 112(b) HAP beyond the
urban HAP for which the categories
were listed under section 112(c)(3) and
(k)(3)(B), including non-urban section
112(b) HAP. The chemical
manufacturing area source rule and the
paints and allied products area source
rule both involve specific circumstances
which EPA believes justify regulating
organic and metal section 112(b) HAP in
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addition to the specific urban HAP
needed to meet the 90 percent
requirement in section 112(c)(3) and
(k)(3)(B), which served as the basis for
the listing of the categories. In the
chemical manufacturing area source
rule, which establishes standards for 9
area source categories, we regulated
such HAP because the emission
standards designed to control the urban
HAP for which the categories were
listed were equally effective at removing
other urban and non-urban metal and
organic HAP, and demonstrating
compliance for total HAP was less
burdensome than demonstrating
compliance for speciated HAP for those
sources required to install add-on
controls. In the paint and allied
products area source rule, we included
emission standards for HAP beyond the
urban HAP for which the category was
listed because the emission standards
designed to control those urban HAP
would also control other urban and nonurban metal and organic HAP.
In conclusion, we believe that we
have appropriately exercised our
discretion in regulating only the
chromium and manganese emissions
from the prepared feeds manufacturing
area source category. Therefore, we did
not make any changes in the final rule
based on this comment.
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2. Housekeeping Management Practices
Comment: One commenter claimed
that the Agency’s proposed
housekeeping practices are
‘‘overreaching,’’ ‘‘unfounded,’’ and
‘‘unnecessary.’’ The commenter
believed that EPA had no basis for
correlating housekeeping practices with
ambient air concentrations of chromium
compounds or manganese compounds.
The commenter also had concerns
with regard to two of the specific plantwide housekeeping requirements
proposed. The commenter argued that
the requirement that dust be removed
from walls, ledges and equipment at
least once per month is not
performance-orientated and fails to
consider individual facility operations
or existing management practices. The
commenter also disagreed with the
Agency’s assertion that air flow through
open doors ‘stirs-up’ dust and causes
chromium compounds and manganese
compounds to be emitted into the
atmosphere. Therefore, the commenter
opposed the proposed requirement that
affected facilities keep doors shut, as
practicable. In addition, the commenter
also expressed concern over the
facilities ability to comply with this
requirement as they questioned what
would be the parameters set/used to
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determine that having a door shut is not
practicable.
The commenter noted that prepared
feeds manufacturing facilities already
comply with Occupational Safety and
Health Administration’s (OSHA) Grain
Handling Standard (29 CFR 1910.272)
and the Food and Drug Administration’s
(FDA’s) Current Good Manufacturing
Practices (CGMPs) for Medicated Feeds
(21 CFR part 225), and that they are
regularly inspected by Federal and State
authorities. Because of this, the
commenter believed that EPA’s
proposed housekeeping practices are
unnecessary. The commenter provided
more detailed descriptions of these two
programs.
public health in the largest number of
urban areas. Section 112(c)(3) of the
CAA requires EPA to list sufficient
categories or subcategories of area
sources to ensure that there are sources
representing 90 percent of the emissions
of each of the 30 urban HAP are subject
to regulation. We determined that the
chromium and manganese emissions
from prepared feeds manufacturing area
sources need to be subject to regulation
to meet this 90 percent requirement for
these two HAP. Additionally, under
CAA section 112(d)(5), we may elect to
promulgate standards that represent
GACT. As cited above, the legislative
history supporting section 112(d)(5)
provides that GACT is to encompass:
Occupational Safety and Health
Administration’s (OSHA) Grain Handling
Standard (29 CFR 1910.272): This standard
requires facilities to ‘‘develop and implement
a written housekeeping program that
establishes the frequency and method(s)
determined best to reduce accumulations of
fugitive grain dust on ledges, floors,
equipment and other exposed surfaces’’
throughout the entire facility. OSHA’s
housekeeping requirements are performanceoriented, allowing facilities the flexibility to
design housekeeping programs to achieve
compliance through methods that are most
effective for individual facilities and
operations.
FDA’s Current Good Manufacturing
Practices (CGMPs) for Medicated Feeds (21
CFR 225): The vast majority of prepared feed
manufacturers are mandated to comply with
CGMPs that require buildings and equipment
be maintained and kept in a reasonably clean
and orderly manner to avoid the potential
adulteration of feed products. Regarding this
provision, FDA’s compliance program
guidance states, ‘‘Accumulated dust or
residue will be considered objectionable
when there is a likelihood that the material
could contribute to significant contamination
of animal feed.’’ Similar to the OSHA
requirement, FDA’s housekeeping standard
also is performance-orientated. The CGMP
regulations allow facilities to implement
those housekeeping practices that are
effective for their individual operations and
achieve compliance with the standard.
‘‘* * * methods, practices and techniques
which are commercially available and
appropriate for application by the sources in
the category considering economic impacts
and the technical capabilities of the firms to
operate and maintain the emissions control
systems.’’
Another commenter recommended
that instead of the specific
requirements, facilities be required to
maintain a management plan to
minimize excess dust. The commenter
said that this plan can be maintained on
site, available for review by the
delegated authority.
Response: The commenter claimed
that EPA has no basis for correlating
housekeeping practices with ambient air
concentrations. Under section
112(k)(3)(B) of the CAA, EPA
determined that chromium and
manganese were 2 of the 30 HAP which,
as the result of emissions from area
sources, pose the greatest threat to
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Section 112(d)(5) calls for EPA to
establish GACT standards that are
designed to reduce HAP emissions.
Nothing in these provisions requires
EPA to justify GACT regulations based
on a correlation between ambient
concentrations and emissions from a
specific emissions source.
We based our GACT determinations
on methods, practices, and techniques
commonly employed in the prepared
feeds manufacturing industry. Based on
the available information, we concluded
that every prepared feeds manufacturing
facility performed general housekeeping
practices and maintained equipment in
an effort to reduce dust and thus,
particulate emissions. We appreciate the
information provided by the commenter
that confirms this conclusion, along
with the details of the regulatory
programs that require these measures.
We disagree with the commenter that
including GACT housekeeping practices
is unnecessary. As noted above, section
112(d)(5) requires EPA to establish
national standards. The fact that OSHA
and FDA have similar requirements has
no relevance here, especially since they
allow facilities to establish individual
(and potentially dissimilar) standards.
Therefore, the final rule maintains
specific housekeeping requirements to
minimize dust and does not include a
requirement to develop site-specific
management practices.
As noted above, we had information
prior to proposal that made it clear that
housekeeping practices to minimize
dust were widespread. We concluded
that GACT was ‘‘continual
housekeeping practices to reduce dust
that can contain chromium compounds
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and manganese compounds.’’ (74 FR
36985) However, we did not have
information from a good cross section of
the industry on specific practices
employed. We solicited information
from one of the major prepared feeds
manufacturers to identify some specific
practices employed in the industry, and
included them in the proposed rule. At
proposal, we acknowledged the
potential limitations of the examples of
practices proposed, and specifically
requested comment on these measures.
We also requested additional general
management practices commonly
employed throughout the industry.
The commenter expressed concerns
with regard to the proposed
housekeeping practices, but they were
not responsive to our request for
additional practices used throughout the
industry. While the commenter did not
provide any suggestions to address their
concerns (other than the suggestion to
remove the practices entirely), we
recognize the issues raised in the
comments provided on the specific
management practices and have
considered them.
The commenter stated that the
requirement that dust be removed from
walls, ledges and equipment at least
once per month is not performanceorientated and fails to consider
individual facility operations or existing
management practices. It is clear that all
prepared feeds manufacturing facilities
must remove dust from walls, ledges,
and equipment periodically in order to
comply with the OSHA requirement.
The commenter did not provide any
alternative to the monthly requirement,
and our follow-up calls to feed
manufacturing facilities indicated that
monthly is a reasonable time frame. In
fact, these calls show that many areas of
the plant are cleaned more frequently
than monthly. Therefore, the final rule
retains the requirement to remove dust
from walls, ledges, and equipment on a
monthly basis.
The proposed requirement to keep
doors closed was the result of a
recommendation from a prepared feeds
manufacturer. However, we appreciate
the concerns regarding potential
compliance confusion with the
proposed requirement to keep doors
closed ‘‘as practicable.’’ Therefore, the
final rule states that doors must remain
closed ‘‘except during normal ingress
and egress.’’
Comment: One commenter expressed
concern that the general housekeeping
requirements would apply to all areas of
the affected facility, even though all
areas of the affected facility may not be
involved with the storage and/or use of
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chromium compounds or manganese
compounds.
Response: We agree with the
commenter that there is no need to
perform these management practices in
areas where chromium or manganese
are never present. Therefore, we have
changed this language in the final rule
to specify that the general management
practices apply in ‘‘all areas of the
affected source where materials
containing chromium or manganese are
stored, used, or handled.’’
3. Mixers
Comment: One commenter urged the
Agency to eliminate the requirement
that affected facilities cover the mixer
where materials containing chromium
compounds or manganese compounds
are added at all times when mixing is
occurring, except when the materials are
being added to the mixer. The
commenter suggested that this
requirement implies that chromium
compounds or manganese compounds
are being emitted into the atmosphere
directly from the mixer when mixing
occurs, and they do not believe that this
is true. The commenter stated that if
chromium and manganese are released
from a mixer, they are captured within
the facility in which the mixer is
operating and not directly released to
the atmosphere. The commenter
explained that the facilities themselves
are control devices. The commenter
claimed that there was a lack of
sufficient and compelling data to
support a contention that openings in
mixers are a source of emissions of
chromium compounds or manganese
compounds. The commenter believed
that the technical background
information considered by EPA in this
rulemaking produced an unfounded
correlation between mixer operation
and chromium and manganese
emissions. The commenter cited EPA’s
2002 National Emissions Inventory
(NEI) and noted that the data reviewed
indicated no emissions of chromium
compounds or manganese compounds
from source classification codes 31227
through 31237, which encompass
mixing/blending operations at feed
manufacturers.
Response: The commenter stated that
when chromium compounds or
manganese compounds are released
from the mixer they are not emitted to
the atmosphere because the facilities
themselves are control devices. We do
not disagree that there may be situations
where direct releases to the atmosphere
from the mixing operations do not
occur. In fact, of the facilities that
reported information for mixing in
response to our industry survey, over 60
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531
percent indicated that their processes
are ‘‘closed’’ without direct vents to the
atmosphere. However, the general
ventilation of the building can allow
chromium- and manganese-containing
dust from the building to be emitted.
Chromium and manganese dust created
in the mixer that accumulates in the
building could be emitted. Therefore,
any measures to reduce the amount of
dust in the building impacts emissions.
We believe that the proposed measures
to reduce dust generation from mixing
will result in lower dust levels and,
thus, lower emissions.
The commenter further claimed that
there was no evidence that openings in
mixers are a source of emissions of
chromium compounds or manganese
compounds, and that the technical
background information considered by
EPA in this rulemaking produced an
unfounded correlation between mixer
operation and chromium and
manganese emissions. However, we
identified mixers as a source of
emissions due to information submitted
directly by the industry. Specifically,
prepared feeds manufacturing facilities
identified mixing as a potential
emission source and reported associated
add-on control devices and management
practices in response to our industry
survey. We reviewed the material
submitted via this survey and agree that
it is accurate and representative.
Since some prepared feeds
manufacturing facilities reported that
emissions from mixing were vented to a
control device, we evaluated whether
add-on controls were GACT for mixing
operations. The commenter is correct
that no emissions were assigned directly
to mixing in the 2002 NEI. However, we
would note that over 60 percent of the
manganese emissions in the 2002 NEI,
and 90 percent of the chromium
emissions, were not assigned to any
specific operation, thus raising the
possibility that some of these emissions
are occurring from mixing operations.
In order to evaluate whether it was
cost effective to select add-on control as
GACT, it was necessary to make
assumptions based on engineering
judgment to estimate emissions from
mixing. While the commenter may
disagree with the assumptions that were
used to estimate these emissions, the
result was the rejection of add-on
control as GACT for mixing.
To reiterate, the emission estimates
that the commenter objects to were not
a factor in establishing the proposed
management practices as GACT. That
determination was directly based on the
information submitted in response to
the survey.
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In conclusion, the commenter
provided no information to suggest that
the proposed measures were not
generally available and commonly used
by the facilities to reduce chromium- or
manganese-containing dust from mixing
operations at prepared feeds
manufacturing facilities. The
commenter also provided no
information challenging our conclusion
that the costs of the GACT standards in
the final rule are reasonable. Therefore,
no changes were made to the proposed
requirements for mixing.
4. Pelleting and Pellet Cooling
Comment: One commenter supported
requiring the option to select add-on
control (cyclones) as GACT for facilities
that produce less than 50 tpd of
prepared feeds. The commenter points
out that EPA determined that
approximately 20 percent of existing
facilities already had cyclones installed,
and that the agency estimated that the
cost effectiveness of requiring the
remaining 80 percent to install controls
would be around $1 million per ton of
chromium and manganese compound
emission reduction, $4,000 per ton of
PM emission reduction, and $20,000 per
ton of PM2.5 reduction, and that the
annual cost of installing and operating
a cyclone at one of these facilities would
be around $58,000 per year. The
commenter recognizes that EPA
performed an economic impact
assessment, which indicated that these
annual costs could represent over 5
percent of the total annual sales for a
small facility, and that EPA concluded
that ‘‘the adverse economic impacts do
not justify a determination requiring
cyclones for the small prepared feeds
manufacturing subcategory.’’ The
commenter states that, although this
economic impact analysis is more
instructive than mere reliance on cost
effectiveness figures, the 5 percent of
total annual sales threshold is arbitrary.
The commenter states that EPA does not
explain why the benefits of further
reductions in PM, PM2.5, manganese
compounds and chromium compounds,
as well as other metal HAP emissions,
are not sufficient to justify the costs of
the controls. The commenter stated their
belief that the GACT provision’s
requirement of cost considerations does
not preclude the need to consider the
environmental benefits of the proposed
rule in determining whether those costs
are justified.
Response: As noted by the
commenter, we performed an economic
impact assessment that indicated that
the annual costs for fabric filters for
bagging could represent over 5 percent
of the total annual sales for a facility
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with less than 5 employees. We strongly
disagree that a decision to reject
controls that would result in costs that
represent 5 percent of the total annual
sales is arbitrary. This 5 percent value
was a direct calculation of the small
model plant cyclone costs divided by
the average shipments per facility for
facilities with less than 5 employees.
While each GACT decision includes a
variety of factors to take into account,
we generally consider costs in excess of
3 percent of sales to be significant and
potentially economically damaging.
Further, since we believe all of the
facilities in the small facility
subcategory are small businesses, we are
even more sensitive to potentially
detrimental economic impacts. We also
disagree that we did not consider the
environmental benefits. For this option,
we estimated and considered the
emission reductions of chromium,
manganese, PM, and PM2.5. However,
we determined that these emission
reductions are not justified given the
economic impacts. In conclusion, we
believe our decision to reject the option
to require add-on controls for pelleting
operations at prepared feed
manufacturers with daily production
rates of 50 tpd or less is justified.
Comment: Two commenters
recommended that, since the 50 tpd
production level determines if
emissions must be controlled from the
pelleting and pellet cooling operations,
this level should be related to the
amount of feed pelletized and not the
total amount of feed produced by the
entire facility. One of the commenters
indicated that they are aware of several
prepared feeds manufacturing facilities
that do not pelletize feed, or that only
pelletize a small percentage of the feed
produced.
Response: Under section 112(d)(1) of
the CAA, EPA ‘‘may distinguish among
classes, types, and sizes within a source
category or subcategory in establishing
such standards’’. As discussed at
proposal (74 FR 36985), we observed
differences between prepared feeds
manufacturing facilities based on
production levels and subcategorized
the Prepared Feeds Manufacturing
source category into ‘‘small’’ and
‘‘large’’ facilities. The threshold used to
distinguish between these subcategories
was an average feed production level of
50 tpd. We then independently
determined GACT standards for each
subcategory. Therefore, our
subcategorization and GACT
determinations were based on the
separation of facilities according to total
feed production levels, not pelleting
feed production. Since the change
suggested by the commenter is
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inconsistent with our subcategorization
decision and analyses, we retained the
proposed definition of the small and
large subcategories based on total feed
production levels.
Comment: One commenter
recommended that the 50 tpy threshold
be on an annual, rather than daily, basis.
The commenter said that this could be
the production level in a calendar year
or a rolling 12-month production level.
The commenter points out that an
annual production level of 13,000 tons
per year would be equivalent to 50 tpd,
assuming an operating schedule of 260
days per year. The commenter noted
that the proposed daily rate did not
appear to have any special significance,
as it was calculated as an average of
annual production. The commenter
believed that an annual production rate
would achieve the same objectives and
would be easier than a daily production
rate for facilities and for regulatory
agencies to track.
Response: We did not incorporate the
commenters’ suggestion to change the
threshold to an annual basis. In our
determination of GACT, the data on the
existence of controls were related to
daily production levels. To determine
an annual threshold from these data
would require an assumption regarding
the number of days of operation per
year. We do not believe that calculating
an annual rate based on a ‘‘typical’’
production schedule is reflective of
varying production schedules that exist
in the industry. Therefore, the final rule
maintains the daily production level
concept. Requiring owners and
operators to maintain annual production
data and the number of operating days,
and then dividing the annual
production by the number of operating
days is no more difficult or burdensome
for facilities or regulatory agencies than
the approach recommended by the
commenter.
Comment: Two commenters
maintained that the pelleting cyclones
would not be able to reach the proposed
design efficiency of 95 percent for
PM10. The commenters believed that
this level of efficiency would not be
attainable under the conditions of the
pelleting process. One commenter
suggested the efficiency requirement be
changed to 95 percent for total PM (up
to 35 micron). The commenter included
a chart from a cyclone manufacturer that
showed the efficiency in removal of
PM10 by a cyclone estimated at 90
percent. The commenter continued that
this level would not be expected to be
reached under the conditions of the
pelleting process with its high moisture
and high temperature conditions. The
commenter stated that a second control
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device such as a baghouse or a wet
scrubber would be necessary to reach a
capture efficiency of 95 percent for
PM10.
Response: In the proposed rule, GACT
for the pelleting operation was
determined to be the use of a cyclone to
control emissions of chromium and
manganese. We did not specify GACT as
a specific control efficiency,
concentration, or operating parameter.
However, in order to establish criteria
that represent a properly designed,
operated, and maintained control
device, it was necessary to establish
requirements in the proposed rule on
how the cyclone is designed and
operated. Many respondents to the
industry survey stated they use high
efficiency cyclones to control the
pelleting operations. The result is
reduced emissions to the air and the
capture of lost product that can be
returned to the manufacturing
operation.
As a follow up to the industry survey
responses, we contacted an industry
representative (Docket No. EPA–HQ–
OAR–2008–0080–0010) that responded
to our survey for several prepared feeds
manufacturing facilities and asked about
the level of efficiency that would be
expected with high efficiency cyclones
reported to be used to control the
pelleting process. The representatives
indicated that today’s high efficiency
cyclones can be expected to get 99
percent control of particulates, while
older ones can be expected to achieve
efficiencies in the ‘‘mid 90 percent’’
range. While background material
gathered prior to proposal from vendors
(Docket No. EPA–HQ–OAR–2008–0080–
0034) show that high efficiency
cyclones should be able to reach the
proposed 95 percent efficiency level for
PM10, we understand that the
conditions of the pelleting process are
not optimum. We contacted additional
cyclone manufacturers after proposal,
and some agreed with the commenters
that cyclones designed to achieve 95
percent efficiency level for PM10 for
pelleting operations are not available.
All of those contacted indicated that
many older cyclones still being used in
the industry would not meet the
proposed 95 percent PM10 design
requirement. It was not our intent to
force prepared feeds manufacturers to
replace older, well designed and
properly operating cyclones with new
high efficiency cyclones, particularly
since the incremental emission
reduction would be very low and the
costs would be high (our estimates are
that the capital cost of a new cyclone is
between $50,000 to $100,000). The
available information suggests that a 95
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percent efficiency design requirement is
achievable for total PM. Therefore, we
have changed the criterion in the final
rule to require cyclones designed to
achieve a 95 percent efficiency level for
total PM, rather than for PM10.
Comment: A commenter
recommended that the final rule provide
explicit compliance alternatives to the
requirement to operate a 95 percent
control efficient cyclone. The
commenter cites that other area source
NESHAP, such as the Nonferrous
Foundry NESHAP (Subpart ZZZZZZ),
establish a limit of either 99.0 percent
control for PM or an emission limit of
0.01 grains per dry standard cubic foot
(gr/dscf). The commenter is concerned
that having 95 percent control efficient
cyclone as the only compliance option
for pelletizing operations would
unfairly penalize a facility that has a
pelletizing process with low
uncontrolled emissions or a facility that
uses other control equipment to achieve
emissions reductions.
Response: The proposed rule required
that emissions from pelleting operations
be captured and routed to a cyclone
designed to reduce PM10 emissions by
95 percent. The format of the rule is an
equipment standard, and the 95 percent
criterion is a design value, not an
emission limitation. Therefore, there is
no penalty for a facility with low
uncontrolled emissions, provided that
they have a cyclone designed to achieve
95 percent reduction that is operated
and maintained properly.
Comment: A commenter requested
clarification of whether PM or PM10
emissions is considered a surrogate for
HAP emission in the proposed rule. The
commenter notes that the proposed rule
requires that pelletizing operations at
feed preparation facilities with daily
production levels greater than 50 tpd be
controlled by a cyclone designed to
reduce PM10 emissions by 95 percent or
greater, and that in several places in the
preamble to the proposed rule that EPA
indicates that PM emissions will be
considered the surrogate for chromium
and manganese. The commenter asked
whether PM or PM10 is the surrogate
pollutant for the proposed rule. The
commenter points out that several other
area source NESHAP consider PM to be
the surrogate pollutant for HAP
emissions such as Subpart ZZZZZZ
(Aluminum, Copper, Nonferrous
Foundries) and Subpart ZZZZZ (Iron
and Steel Foundries). The commenter
recommends that EPA clarify in the
final rule whether the surrogate
pollutant is PM or PM10 and include a
justification for the choice of surrogate.
Further, the commenter recommends
that, if EPA elects to use PM10 as the
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533
surrogate, EPA evaluate the required
control efficiency for the cyclone
control equipment.
Response: As stated in the preamble
to the proposed rule, PM is the surrogate
for chromium and manganese emitted
from this source category. However,
when specifying compliance conditions,
the proposed rule used the measure of
collection efficiency of PM10. Due to
other comments received (see above),
the final rule uses PM as the metric for
cyclone collection efficiency rather than
PM10, which should remove any
confusion about the surrogate.
Comment: A commenter notes that
the proposed rule requires the owner of
a cyclone at a feed preparation facility
with a daily production level of greater
than 50 tpd to keep a record from the
cyclone’s manufacturer of the control
efficiency. The commenter asks what
EPA’s expectations are for facilities if
the manufacturer’s specifications are not
available or do not show compliance
with the control efficiency? The
commenter also asked whether an
owner or operator would have the
option of demonstrating compliance
with the rule by testing the inlet/outlet
concentrations of the cyclone for
determining the control efficiency.
Finally, the commenter asked whether
other particulate control devices, such
as a baghouse or fabric filter, or control
equipment in series, such as a cyclone
and a baghouse, would be allowed? The
commenter indicated that if these
options are allowed that this should be
made clear in the final rule.
Response: The commenter asked what
EPA’s expectations are for facilities in
showing compliance with the rule if the
cyclone manufacturer’s design control
efficiency and operating and
maintenance procedures are not
available. We acknowledge that this
could be a problem, and have included
in the final rule options for
documenting that the cyclone is
designed to achieve 95 percent PM
reduction. The first option is to obtain
certification from the manufacturer, as
proposed. Under Option 2, the owner or
operator could have a registered
professional engineer or responsible
official certify that the cyclone is
designed in a manner capable of
achieving 95 percent or greater PM
reduction and keep a record of the
information used to make this
determination. The third option is to
conduct PM testing at the inlet and
outlet of the cyclone(s) to demonstrate
that an efficiency of 95 percent or
greater PM reduction is actually being
achieved. If either the certification or
testing option is used, the owner or
operator would be required to identify
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a parameter (inlet flow rate, inlet
velocity, pressure drop, or fan
amperage) operating range that
constitutes proper operation of the
device, and develop site-specific
cyclone maintenance procedures.
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5. Bulk Loading
Comment: Several commenters
objected to the proposed requirement
that emissions from bulk loading be
reduced through the use of drop filter
socks. Two of the commenters believe
that this is too costly and should not be
considered as GACT. One of the
commenters explained that, in order to
meet the proposed requirements, one of
their facilities would need to redesign
and purchase equipment for the entire
bin and bin loading system and
potentially redesign the entire mill,
which could cost hundreds of
thousands of dollars. Two commenters
disagreed with EPA’s claim that every
facility uses drop filter socks to reduce
dust and the loss of product during the
loading of railcars and trucks. One of
the commenters argued that EPA’s
conclusion that every affected facility
already uses drop filter socks to reduce
dust and the loss of product during the
loading of railcars and trucks
contradicts the background technical
information in the docket, which
indicates that the use of drop filter socks
was reported for around 70 percent of
the plants. The commenter noted that
they conducted a survey of 41 prepared
feed manufacturing companies
representing 306 plants to identify how
many facilities currently use drop filter
socks. The commenter’s survey results
were as follows:
1. The average number of loadingdischarge points is 14.3 per facility.
2. Only 53 percent of the responding
industry facilities currently have drop
filter socks installed at discharge points
where prepared feed products are
loaded into trucks or railcars.
3. The estimated average cost to
install each drop filter sock is $295.
4. The estimated average annual cost
to maintain each drop filter sock is
$215.
The commenter indicated that, based on
their survey results and the assumption
that there would be approximately 6,300
affected facilities, the cost to install
drop filter socks at loading discharge
points would be $12.5 million for the
entire industry, with an annual cost of
$9.1 million per year. The commenter
notes the stark contrast in these
estimates and EPA’s claim that the
proposed requirement to install drop
filter socks would not create additional
associated costs for facilities.
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Three of the commenters point out
other alternative methods that are
equally effective in reducing emissions
and should be allowed. One commenter
explained that many facilities have
discharge-loading points that already
are designed to limit the distance
between the feed-discharge point and
the conveyance, thereby minimizing
potential dust emissions. All three of
these commenters note that many loadout operations are conducted in
enclosed areas, which minimizes
emissions and eliminates the need for
drop filter socks. One of the commenters
asked that, if the requirements did not
apply to truck load-outs that occur
inside a building, EPA should clarify
this in the final rule.
Response: At proposal, we
determined that filter drop socks (or
drop filter socks, as we inadvertently
used the terms interchangeably)
represented GACT for bulk loading. As
evident in the definition of ‘‘filter drop
sock,’’ we intended that this term
represent any ‘‘device at the loadout end
of a bulk loader that lessens fugitive
emissions by containing the unloaded
product within the device thus
preventing windblown and drop caused
fugitive emissions.’’ We are confident in
our assumption that every prepared
feeds manufacturing facility uses some
device that meets the proposed broad
definition of filter drop sock. However,
these comments make it apparent that
the industry recognizes one specific
technology as filter drop socks, or drop
socks, and that it would not be accurate
to assume that every facility utilizes this
technology. Therefore, in order to avoid
confusion, we have removed the
definition of filter drop sock and revised
the standard to require that, for the bulk
loading process where prepared feeds
products containing chromium or
manganese are loaded into trucks or
railcars, a device must be used at the
loadout end of each bulk loader to
lessen fugitive emissions. Examples of
these devices include drop socks,
flexible spouts, and any device that
reduces the distance between the
loading arm and the truck or railcar to
a degree that avoids dust. We believe it
is important that these technologies be
used for all bulk loaders, whether they
are inside or outside. Therefore, this
requirement applies to all bulk loaders
that load products containing chromium
or manganese.
6. Bagging
Comment: One commenter disagreed
with the decision to reject add-on
controls for emissions from bagging
operations based solely on the cost
effectiveness of installing and operating
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those controls. The commenter
explained that the Agency’s decision
was made despite the widespread use of
these controls, as around 30 percent of
the smaller facilities and over 90
percent of the larger facilities controlled
emissions from bagging. The commenter
points out that EPA did not disagree or
reject the notion that control options are
appropriate or that the economic
impacts are too great. Rather, the
commenter points out that the decision
to reject the option was based solely on
the cost-effectiveness, and that no
economic analysis was performed. The
commenter indicated that basing this
GACT decision solely on cost
effectiveness was unlawful. The
commenter stated that the Agency is not
directed, under Section 112(d)(5), to set
standards based on what the agency
believes is cost effective. The
commenter noted that the Agency
themselves stated, ‘‘GACT must reflect
the ‘methods, practices and techniques
which are commercially available and
appropriate for application by the
sources in the category considering
economic impacts.’ 74 FR 36982
(quoting S. REP. NO. 101–228, at 171–
72).’’
Response: We disagree with the
commenter, as we believe that cost
effectiveness is an appropriate measure
to consider in the evaluation of GACT,
and that considering cost effectiveness
is not unlawful. We believe that by
rejecting add-on controls for bagging
operations because the cost
effectiveness was ‘‘too high to be
considered GACT,’’ clearly indicates
that we concluded the economic
impacts are too great. In the preamble to
the proposed rule (74 FR 36986), we
presented the estimates for both sizes of
facilities. For the facilities with daily
production levels of 50 tpd or less, the
estimates were over $7 million for the
total capital costs and over $16 million
per year for the total annual costs,
resulting in cost effectiveness estimates
for these controls of around $255
million per ton of chromium and
manganese reduction, over $750,000 per
ton of PM emission reduction, and $3.3
million per ton of PM2.5 reduction. For
the facilities with daily production
levels greater than 50 tpd, the estimates
were over $10 million for the total
capital costs and over $13 million per
year for the total annual costs, resulting
in cost effectiveness estimates of around
$37 million per ton of chromium and
manganese reduction, over $100,000 per
ton of PM emission reduction, and
around $500,000 per ton of PM2.5
reduction. Therefore, no changes were
made as a result of this comment.
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D. Inspections and Compliance
Provisions
Comment: Two commenters stated
that monitoring pressure drop would
not be the best way to ensure the proper
functioning of the pelleting cyclones.
The commenters noted that, due to high
moisture conditions (always near dew
point) of the dust laden air passing
through the cyclones on the pellet
cooler air system, accurately measuring
the pressure drop is problematic. The
commenters stated that moisture and
particulates in the duct (especially those
‘‘upstream’’ of the collectors) will
constantly compromise the accuracy of
the static pressure indicating
equipment. Secondly, the commenters
state that the collectors are quite
inaccessible and would require remote
readouts, which add to the cost and
maintenance of this equipment. One
commenter believed the best way to
ensure the proper functioning of their
collectors is to simply monitor the ampload of the fan. The commenter states
that if the amp-load on the fan motor
stays within the proper range then the
system is functioning properly. The
commenter also stated that, in their
operation, the cyclones are located
between the cooler and the fan and the
duct work is fully contained and sealed.
According to the commenter,
consequently, all the air that is
discharged from the fan has passed
through the collectors. The commenter
stated that, additionally, the fans on
their cooler air systems are electrically
interlocked with the pelleting system
(i.e., the pellet mill feeder will not
operate unless the fan is operating);
consequently, if the pelleting system is
operating, the fan will be operating and
the continuous monitoring of the fan
amps will ensure the collectors are
operating in the proper range.
One of these commenters believed
that the cost to industry to install
pressure-drop gauges and to monitor
cyclone pressure drop would be
extremely high. According to the
commenter, given the limited time
provided by EPA to respond to this
proposed requirement, they were unable
to receive actual price quotes from
vendors on the cost to install a pressuredrop gauge on a cyclone at various types
of facilities. The commenter anticipated
that such prices could vary depending
upon a facility’s equipment and
physical layout. However, according to
the commenter, based upon best
estimates from vendors, they believed
that an average conservative cost to
install a pressure-drop gauge is $1,500
to $2,000 per cyclone. This commenter
suggested that the rule be revised to
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include alternative management
practices and equipment controls as
follows:
1. Pellet cooling cyclones are to be
operated in accordance with the
parameters authorized by air-operating
permits issued by appropriate legal
authorities.
2. Pellet cooling cyclones are to be
maintained and operated in accordance
with the manufacturer’s
recommendations.
3. Once per day, affected facilities are
to perform a visual inspection of the
operating cyclone and the discharge air
stream to observe emissions.
4. Should an affected facility observe
an emission discharge that is not in
accordance with the parameters
authorized within its air-operating
permit, corrective actions are to be taken
immediately to correct the discharge
and bring it into compliance with its airoperating permit. The details of such
occurrences, if any, are to be recorded
in the facility’s maintenance records as
required by rule’s recordkeeping and
notification requirements.
Response: We believe that it is
necessary to have a reasonably frequent
indication that the cyclones are
operating properly. Cyclones are
relatively simple devices and generally
have no moving parts. A cyclone uses
an induced draft fan to move the gas
stream through the device. These fans
are sized to provide the maximum inlet
velocity possible for high separation
without excessive turbulence. The
primary indicators of the performance of
cyclones are the outlet opacity and inlet
velocity.
The commenter suggested the use of
outlet opacity to monitor performance;
however, monitoring outlet opacity
would require that trained off-site
contractors be used, or more likely, that
individuals at the plant be trained and
certified in determining opacity using
Method 9. We have estimated that a
single Method 9 test by an off-site
contractor costs around $2,000. While
the costs to train and certify on-site
employees to perform these required
daily tests would result in costs less
than $2,000 per day, we still believe that
the cost of using outlet opacity as an
indicator of performance would be too
high. Therefore, we elected to require
monitoring which provides an
indication of inlet velocity. Pressure
drop across the cyclone is a surrogate
for inlet velocity, and, contrary to the
commenters’ claims, it is an appropriate
measure to indicate proper operation of
a cyclone. Many cyclone manufacturers
link the design efficiency with a specific
pressure drop. However, other
parameters are appropriate surrogates
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535
for the inlet velocity. In particular,
monitoring either inlet flow rate, inlet
velocity, or fan amperage are acceptable
alternatives to monitoring pressure
drop. As a result of these comments, we
have added alternatives to the final rule
that allow an owner or operator to
monitor pressure drop on a daily basis,
or monitor either the inlet flow rate,
inlet velocity, or amperage load to the
fan, on a daily basis to show that the
cyclone is performing consistent with
its design specifications. The
commenter did not provide any
information to support their estimated
costs of monitoring equipment.
One of the commenters suggested that
cyclones be operated in accordance with
parameters authorized by operating
permits issued by appropriate legal
authorities. We disagree with the
commenter’s suggested approach. As an
initial matter, section 112(d)(5) requires
that the Administrator establish national
emission standards. To assure
compliance with these national
emission standards, EPA develops
monitoring, recordkeeping and
reporting requirements, as it did in this
rule. Indeed, one of the reasons
supporting EPA’s exemption of the
prepared feed manufacturing area
source category from the requirements
of title V is that this rule contains
sufficient monitoring, recordkeeping
and reporting requirements to assure
compliance with the requirements of the
final rule. Thus, section 112
contemplates not only that EPA will
establish national emission standards,
but that EPA will establish appropriate
monitoring, recordkeeping and
reporting requirements to assure
compliance with those requirements.
Furthermore, the monitoring and other
compliance provisions in State permits
can vary considerably, and some
prepared feeds manufacturing facilities
may not even have permits. If a source
would like to use an alternative
monitoring approach allowed by a state
permit, it should follow the
requirements of 40 CFR 63.8(f).
Therefore, we reject the commenter’s
suggestion to remove any specific
monitoring requirements from the rule.
Comment: Two commenters
expressed concern over the frequency of
record keeping for the pelleting control
devices. One of these commenters
suggested that weekly, rather than daily,
pressure drop readings would be
adequate. This commenter stated that,
while a monthly maintenance check on
the cyclone is a reasonable requirement,
daily pressure drop readings are
excessive because the pressure drop
readings would not be expected to vary
widely. The commenter also noted that
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many cyclones are installed in areas that
are not easily accessible so daily checks
can be time consuming to collect data
that they describe as a ‘‘maintenance
indicator.’’ The other commenter stated
that weekly recording of readings would
be adequate and that daily
recordkeeping was ‘‘overkill’’ (although
the commenter provided justification for
reduced recordkeeping specific to a
baghouse rather than the proposed
requirement for a cyclone).
Response: We proposed using the
maintenance indicator of pressure drop
in order to ensure that the cyclones are
operating correctly as an indicator of
compliance with the rule that can be
readily checked by an inspector. As
discussed above, the final rule includes
the option to daily monitor inlet flow
rate, inlet velocity, pressure drop, or fan
amperage. By providing multiple
options to indicate compliance, we
believe the facility will find an option
that can be completed from an
accessible area. Daily readings of these
parameters are considered appropriate
because, while a cyclone may be a
rather simple control device in terms of
moving parts, the system of ductwork
and fans impact the efficiency of the
unit. Each cyclone is designed for a
specific inlet velocity in order to
maximize the collection efficiency. We
believe that daily checks are necessary
to ensure the ductwork is not entraining
outside air and/or that the fan is
operating in the designed manner. As a
result, we have not changed the
requirement for daily monitoring and
recording of cyclone performance
measures.
Comment: A commenter also asked
that the rule specify which cyclone is
expected to have a pressure drop gauge
installed in cases where multiple
cyclones are installed in a line.
Specifically, would pressure drop
monitoring be required for the initial
cyclone, subsequent cyclones, or all
cyclones?
Response: The answer is dependent
on the design reduction efficiency of the
cyclones. If one cyclone in a series is
designed to achieve 95 percent or
greater PM removal, then monitoring
would only be necessary for that one
device. However, if the design
efficiencies for all the individual
cyclones in the series are less than 95
percent, but the combined design
efficiency is 95 percent or greater, then
the inlet flow rate, inlet velocity,
pressure drop, or fan amperage for all
the cyclones would need to be
monitored.
Comment: One commenter
recommended that the Agency consider
revising the proposed monitoring to
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specify that the pressure drop must be
monitored at least once per day when
the cyclone is in operation.
Response: We agree with the concept
of this comment. However, we want to
make clear that the cyclone is required
to be used at all times when the
pelleting process is in operation.
Therefore, the rule has been revised to
state that monitoring of the cyclone
operating parameters is required at least
once per day when the pelleting process
is in operation.
E. Reporting and Recordkeeping
Requirements
Comment: One commenter stated that
§ 63.11619(e)(1) of the proposed rule
indicated that facilities that do not add
any materials containing chromium or
manganese compounds are not subject
to the rule. The commenter interpreted
this to mean that facilities that do not
use chromium- or manganesecontaining materials would be excluded
from all aspects of the NESHAP,
including the requirement to submit an
Initial Notification. However, the
commenter noted that, during the
August 4, 2009 webinar (Docket Item
No. EPA–HQ–OAR–2008–0080–44), it
was suggested that these facilities would
be required to submit an initial
notification. The commenter indicated
that it seems unnecessary to require
submittal of initial notification from
facilities that do not use chromium or
manganese compounds, and requested
that EPA clarify whether this report is
required of these facilities.
Response: The commenter’s
interpretation is correct. Facilities that
do not add any materials containing
chromium or manganese to any product
manufactured at the facility are not
subject to the rule, including the
requirement to submit an initial
notification.
Comment: One commenter
recommended that the proposed
requirement to submit an annual
compliance certification report be
omitted from the final rule. The
commenter said that annual reporting is
burdensome and difficult for small
businesses to do year after year. The
commenter believes that annual
reporting creates excessive paperwork
for the facility and the delegated
authority with little environmental
benefit. The commenter also
recommended that the monthly record
certifying that a facility has complied
with the dust minimization
management practices be omitted, as
they believe it is very excessive.
Response: Provided that the facility is
in compliance, this annual compliance
certification report only needs to
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indicate that compliance has been
achieved. In the event that a
noncompliance event has occurred, this
report will need to provide information
about this event. We believe it is
important that there is clear
accountability regarding compliance
with the regulation, and we believe that
this is best accomplished by having a
responsible official certify that the
facility has complied with the
requirements in the rule. We disagree
with the commenter that this once per
year report is difficult and overly
burdensome. Therefore, the final rule
has retained the requirement to submit
annual certification reports.
However, we considered the
commenter’s request regarding the
monthly certifications and have
determined that they are not necessary.
We believe that accountability can be
maintained via the annual certifications
and required records. Therefore, the
proposed requirement to keep a
monthly record certifying compliance
with the management practices was not
maintained in the final rule.
Comment: One commenter pointed
out that the proposed rule did not
require a facility to keep records to
show that it was below or above the 50
tpd production level that determines
whether controls are required for
emissions from the pelleting and pellet
cooling operation. The commenter also
noted that the rule did not explain what
happens when a facility with a daily
production level less than 50 tpd
increases production such that they
would have a daily production level
greater than 50 tpd. The commenter
recommended that provisions be added
to eliminate these deficiencies.
Response: We agree with the
commenter, and added recordkeeping
and reporting requirements related to
the average daily feed production level.
We also clarified how this level is to be
determined. The final rule specifies that
the initial determination of the average
daily feed production level is based on
the one-year period prior to the
compliance date for existing sources, or
the design rate for new sources. The
final rule also requires that facilities
with average daily feed production
levels below 50 tpd report their initial
average daily feed production level in
their Notification of Compliance Status
report. These facilities would be
required to maintain average daily feed
production level records to demonstrate
that they do not exceed the 50 tpd
threshold in the future. At the end of
each calendar year, the facility will be
required to re-calculate the average
daily feed production level for the
previous year. If the average daily feed
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production level exceeds 50 tpd, the
facility would have to comply with the
requirement to collect emissions from
the pelleting and pellet cooling
operations and route them to a cyclone
by July 1 of that year.
Prepared feed mill owners or
operators with average daily feed
production levels less than 50 tpd that
elect to comply with the requirement to
collect emissions from the pelleting and
pellet cooling operations and route the
emissions to a cyclone would not be
required to maintain production
records.
F. Definitions
Comment: Three commenters
suggested that the EPA establish
definitions for chromium compounds
and manganese compounds. One of the
commenters suggested using criteria
consistent with that found within the
Agency’s TRI reporting requirements,
and noted that these regulations state
that: (1) Chromium compounds and
manganese compounds are exempt from
the TRI reporting requirements when
the concentration of such chemicals is
less than 1 percent of the total
compound; and (2) such an exemption
applies whether the facility received or
produced the compound. One of the
other commenters pointed out that, in
other area source NESHAP, materials
containing HAP are defined as materials
that contain chromium in amounts
greater than 0.1 percent by weight or
manganese in amounts greater than 1.0
percent by weight. The commenter cited
the definition of ‘‘Material containing
MFHAP’’ in § 63.1522 (40 CFR part 63,
subpart XXXXXX) as an example.
Response: The commenters are
confusing two concepts. A ‘‘chemical
compound’’ is a basic chemistry term to
indicate a substance composed of two or
more elements united chemically in
definite proportions by mass. Therefore,
any chemical compound containing the
element chromium would be a
‘‘chromium compound.’’ For example,
chromic oxide, chromium trioxide, and
potassium chromate are all chromium
compounds. Similarly, any compound
containing the element manganese is a
‘‘manganese compound.’’ Manganese
dioxide and manganese chloride are
examples of manganese compounds. In
the CAA, ‘‘chromium compounds’’ and
‘‘manganese compounds’’ two of the 30
Urban HAP. See Integrated Air Toxics
Strategy; see also CAA 112(b).
Therefore, any chemical compound that
contains chromium or manganese is
considered a HAP. We do not believe
that it is necessary to add language in
the rule to explain this standard
chemistry terminology.
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However, we agree with the
commenter that the addition of
definitions of ‘‘a material containing
chromium’’ and ‘‘a material containing
manganese’’ are appropriate. As we
have pointed out in several other area
source rulemakings, the CAA section
112(k) inventory was primarily based on
the 1990 TRI, and that is the case for the
Prepared Feeds Manufacturing source
category as well. The reporting
requirements for the TRI do not include
de minimis concentrations of toxic
chemicals in mixtures; therefore, the
CAA section 112(k) inventory would not
have included emissions from
operations involving chemicals below
these concentration levels. See 40 CFR
372.38, Toxic Chemical Release
Reporting: Community Right-To-Know
(Reporting Requirements). Accordingly,
the percentages noted above define the
scope of the listed source category; they
are not exemptions.
Therefore, we believe that it is also
appropriate to incorporate this into the
prepared feeds manufacturing area
source NESHAP. Specifically, we have
added the following definitions to the
final rule:
A material containing chromium
means a material that contains
chromium (Cr, atomic number 24) in
amounts greater than or equal to 0.1
percent by weight.
A material containing manganese
means a material that contains
manganese (Mn, atomic number 25) in
amounts greater than or equal to 1.0
percent by weight.
We also revised the applicability
provisions in § 63.11619(a) to specify
that the rule applies to prepared feeds
manufacturing facilities that use a
material containing chromium or a
material containing manganese and is
an area source of emissions of HAP.
Comment: One commenter suggested
that the EPA add the following
definition for prepared animal feeds: ‘‘a
mixture of ingredients and supplements
fortified with essential minerals,
intended to be fed directly to animals to
meet or exceed total daily nutrient
requirements.’’ The commenter also
suggested that the definition of prepared
feeds manufacturing facility be changed
to specify that the feeds produced must
be ‘‘fortified with essential minerals.’’
Response: As discussed earlier in
section B, the prepared feeds area
source category extends beyond those
facilities manufacturing only products
intended to be fed directly to animals.
Additionally, this definition is not
consistent with the NAICS code that
forms the basis for this source category.
Therefore, we did not incorporate the
changes suggested by the commenter.
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Comment: One commenter requested
that drop filter sock should be defined
and that it needs to specify the materials
of construction and how far into the
railcar or truck it needs to extend.
Another commenter recommended that
the Agency amend the term ‘‘drop filter
sock’’ to ‘‘drop sock, since the device
does not filter potential emissions in
any manner.’’
Response: As discussed in section
V.C.5, we have eliminated the use of the
term ‘‘filter drop sock’’ in the final rule.
Therefore, this definition has been
removed.
G. Impacts Assessment
Comment: One commenter believes
that EPA’s estimated number of
prepared feeds manufacturers affected
by the proposed rule is inaccurately
low. The commenter points out that
EPA states that approximately 1,800
area-source prepared feed
manufacturing facilities currently
operating add chromium compounds or
manganese compounds to their products
and therefore would be subject to the
proposed area source standards. In
contrast, the commenter believes that
the actual number of affected facilities
exceeds 6,300. The commenter notes
that the FDA’s bovine spongiform
encephalopathy inspection database
currently lists more than 6,300 feed
mills in which FDA has conducted
inspections. The commenter points out
that the actual number of facilities
subject to the proposed rule has a direct
impact on the agency’s stated benefits
and costs of the rule.
Response: We agree that the number
of facilities subject to the rule is a key
component in the assessment of
impacts. Ideally, we would not only
have an estimate of the number of
facilities in a source category for which
we are developing regulations, but we
would also have a list of those facilities.
During our information gathering
efforts, it was clear that the industry was
not well represented in the two national
emissions databases (TRI and NEI) that
we typically use to characterize an
industry and their emissions. We also
did not identify any other source of
information that would provide a list of
specific prepared feed manufacturing
facilities in the U.S. Therefore, we based
our estimate of 1,800 prepared feed
manufacturing facilities on the 2002
U.S. Economic Census of
Manufacturers. Prior to proposal, we
consulted with the commenter on this
topic, and the commenter agreed that
1,800 was a reasonable estimate.
However, we appreciate that the
commenter has now obtained other
information that they believe indicates
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that the number of facilities may be
higher than originally estimated. We
investigated the FDA inspections
database mentioned by the commenter
and found that this database includes
many more types of facilities than just
prepared feed mills. The FDA Web site
says the following: ‘‘Inspections of
renderers, feed mills, ruminant feeders,
protein blenders, pet feed
manufacturers, pet feed salvagers,
animal feed distributors and
transporters, ruminant feeders, and
others have been conducted to
determine compliance with the BSE/
Ruminant Feed regulations.’’ Clearly
this includes many types of facilities
that are not in the Prepared Feeds
Manufacturing area source category.
Facilities in the Prepared Feeds
Manufacturing Source Category are
classified under NAICS 311119, which
includes ‘‘establishments primarily
engaged in manufacturing animal food
(except dog and cat) from ingredients,
such as grains, oilseed mill products,
and meat products.’’ The proposed
applicability of the rule was taken
directly from this NAICS definition,
except that it limited applicability to
those animal feed manufacturers that
use chromium or manganese. The 2002
U.S. Economic Census of Manufacturers
reports 1,567 establishments under
NAICS 311119. The census reports
1,811 establishments under the broader
NAICS 31111. While NAICS 31111
likely includes establishments that
would not be included in the source
category, we chose to place our estimate
of the number of prepared feed facilities
at 1,800 to be conservative. As noted
above, we sought input on this estimate
and the commenter deemed it as a
‘‘reasonable estimate’’ (Docket No. EPA–
HQ–OAR–2008–0080–0010).
The commenter did not provide any
explanation why the Census data were
incorrect for these NAICS codes. The
commenter also did not provide
evidence that establishments counted
under other NAICS codes would be
subject to the rule. As discussed in
section V.B, we revised the applicability
provisions to ensure that it is clear that
the rule only applies to the types of
facilities that formed the basis for the
source category listing. Since this listing
was based on NAICS 311119, and no
evidence has been submitted that the
Census information for NAICS is
incorrect, we did not change our
estimate of the population of prepared
feed manufacturing facilities in the U.S.
Comment: One commenter pointed
out that data reported within the TRI,
which were used as a basis for EPA’s
baseline emission estimates, are not
solely an indication of emissions to the
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atmosphere. The commenter stated that,
by definition, the reported release may
result from spilling, leaking, pouring,
emptying, discharging, injecting,
escaping, leaching, dumping, or
disposing of the reported chemical into
the environment.
Response: The commenter is correct
that a variety of types of releases are
reported in the TRI. However, for our
analysis, we only used releases reported
as ‘‘Fugitive Air Emissions’’ and ‘‘Point
Source Air Emissions.’’ Therefore, we
disagree with the comment, as these
releases clearly represent an indication
of emissions to the atmosphere.
Comment: One commenter expressed
concerns about the methodology used to
estimate emission levels of chromium
compounds, manganese compounds,
and total PM. The commenter stated
their belief that this analysis lacked a
sound statistical basis, and that the
baseline emission estimates and
corresponding estimated potential
emission reductions used by EPA
within its proposed rule are erroneous
and do not support EPA’s proposed
management practices and equipment
controls.
In particular, the commenter believed
that it was inappropriate to extrapolate
the chromium compound and
manganese compound emissions for the
entire industry based on average
emission rates from only 22 facilities
represented in EPA’s 2006 TRI. The
commenter pointed out that this
problem was exacerbated by the fact
that only a fraction of these 22 facilities
reported emissions of chromium or
manganese compounds. Further, the
commenter also stated that facilities
reporting the majority of these
emissions produce trace mineral
premixes subsequently used by other
feed manufacturers, and that they do not
have pelleting operations, which EPA
identifies as the largest emission source
at prepared feed mills.
With regard to the estimated PM
emissions, the commenter indicated that
they believe that the average PM
emission level calculated from the NEI
was inaccurate. In particular, the
commenter believes that the 70 facilities
in the NEI with PM emissions represent
a number of the highest production
volume feed manufacturers in the
United States. Therefore, the commenter
states that using the average PM
emissions for these larger facilities
significantly overestimates the PM
emissions for the entire industry.
Response: The information
questioned by the commenter was
considered by EPA in the selection of
GACT. As discussed above in section
V.D, this information did not impact the
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decision to regulate chromium and
manganese from the prepared feeds
source category or the decision which
emission sources to regulate. Further,
the emission reductions estimated by
this analysis were only one of the
considerations that make up the GACT
decision.
With regard to the specific concerns
offered by the commenter, the technical
memorandum describing the estimation
of baseline emissions discussed the lack
of facility-specific emissions data for the
prepared feeds industry. Given this lack
of data, the approach selected was to
develop ‘‘model plants’’ to represent the
industry. The use of model plants with
‘‘average’’ parameters is a sound
technical approach that EPA has long
used when facility-specific information
is not available for the entire industry.
Therefore, we reject the argument by the
commenter that the use of average
emission levels is inappropriate.
However, we do recognize the
concerns of the commenters with regard
to the specific average emission levels
utilized and the manner in which they
were created. For instance, the average
chromium compound emission level
was based on a single facility’s
emissions in the 2006 TRI, and the
average manganese compound
emissions level was based on emissions
from eight facilities. The commenter did
not provide any suggestions on how to
improve the analysis using the existing
or other readily available information.
However, in light of the concerns, we
reexamined the available data and the
approaches used.
After this review, relatively
significant changes were made to five
specific areas of our impacts analysis.
Each of these is discussed below. There
is a technical memorandum in the
docket that discusses these changes
further and presents the detailed
updated results.
1. Changes to Analyses
Percentage of Industry in Small
Facility Subcategory. The proposal
analysis estimated the number of
prepared feed manufacturing facilities
with average daily feed production
values of 50 tpd or less based on
information submitted by the industry
in response to an EPA questionnaire.
Around 11 percent of the facilities
responding to this questionnaire had
daily production levels of 50 tpd or less.
Following the completion of the
baseline emissions and impacts
analyses, EPA conducted an economic
impact analysis. As part of this analysis,
EPA collected detailed data from the
2002 Economic Census of
Manufacturers that broke down the
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industry based on the number of
employees. This information suggested
that the profile of the industry based on
the industry questionnaire responses
may have been biased slightly toward
larger facilities (i.e., a larger percentage
of the industry would have average
daily feed production rates of 50 tpd or
less than originally estimated).
Therefore, this new information was
used, along with correlation between
production and revenues provided by a
commenter, to reassess this profile. The
revised analyses assume that 29 percent
of the facilities in the industry have
average daily feed production levels of
50 tpd or less.
Number of Facilities Emitting
Chromium. In the proposal analysis, it
was assumed that every facility in the
industry added chromium-containing
nutrients to their products. However, in
response to follow-up questions asked
by EPA on their public comments, the
industry trade organizations stated that:
‘‘The use of chromium compounds
among feed manufacturers is not as
prevalent as the use of manganese
compounds. Until a recent FDAapproval for use in dairy feeds earlier
this year, chromium compounds had
been approved for use only in swine
feeds. Only about 2 to 3 percent of feed
mills in the U.S. use a chromium
compound, and only two compounds,
chromium proprionate and chromium
tripicolinate, are approved by FDA for
use in swine feed.’’ Based on this
information, the revised impacts
analysis assumes that only 3 percent of
the prepared feed manufacturing
facilities in the United States use and
emit chromium.
Facility Average Chromium and
Manganese Emission Rates. Because the
national databases considered prior to
proposal contained data for such a
limited number of prepared feed
manufacturing facilities, a model plant
approach was used to estimate
nationwide emissions and impacts for
the source category. This model plant
approach used facility average emission
levels from the 2006 Toxics Release
Inventory (TRI) for chromium and
manganese. The commenter criticized
the development of average emission
rates from such a limited data set. To
broaden the data set, TRI data were
obtained for every facility reporting
NAICS code 311119 and/or SIC 3048 for
the years 1990 through 2007. There
were over 10,000 facilities reporting
these NAICS/SIC codes over these 18
years, averaging just over 570 facilities
per year. On average, there were 134
facilities reporting manganese emissions
each year and 2 reporting chromium.
These data were used to calculate new
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facility average manganese and
chromium emission rates, which were
used in the revised analyses.
Production Level To Calculate PM
Emission Factor. In the proposal
analyses, the facility average PM
emission rate from the 2002 NEI for
emission sources after the point in the
process when chromium or manganese
would be added was divided by the
average production rate from the
facilities that responded to the EPA
questionnaire to obtain an emission
factor in units of tons per year PM
emissions per tpd production level. The
commenter indicated that this average
production level used, 177 tpd, was not
representative of the facilities in the
NEI. They ‘‘conservatively estimated
that the average production that
occurred at those facilities listed in the
2002 NEI exceeded 500 tpd.’’ In the
revised analysis, the PM emissions
factor was calculated based on the
production level of 500 tpd provided by
the commenter.
Cyclone Efficiency for PM2.5. The
impacts analysis for the proposed rule
assumed that cyclones would achieve a
95 percent reduction efficiency for
PM2.5. An efficiency chart provided by
a commenter shows cyclone efficiencies
of approximately 30 percent for PM2.5.
This value was used in the revised
analysis.
2. Summary of Revised Results
The results of the revised impacts
analysis showed a decrease in the PM
emissions and increases in the
manganese, chromium, and PM2.5
emissions. The revised emissions levels
prior to the implementation of this
regulation are 8.2 tons per year of
chromium, 195 tons per year of
manganese, around 11,000 tons per year
of both PM and PM2.5.
The revised analysis also shows
higher levels of chromium and
manganese emission reductions and
lower levels of both PM and PM2.5
reductions. Since the costs were not
impacted by the changes to the analyses,
the cost effectiveness of the controls
were lower for the chromium and
manganese and higher for the PM and
PM2.5. Cost effectiveness values are
discussed further in the revised impacts
memo which is in the docket. Based on
the comments, we did change the
impacts, but none of these conclusions
affect our choice of GACT.
H. Title V Requirements
Comment: Several commenters agreed
with the proposed title V permit
exemption, noting such factors as the
adequacy of existing state programs to
ensure compliance, the additional
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539
economic and other burdens imposed
by title V permitting, and the lack of
technical resources to comply with
permitting requirements for facilities
that are mostly small businesses.
Response: We acknowledge the
commenters’ support for the exemption
from title V permitting requirements in
this rule.
Comment: One commenter argued
that the agency’s proposal to exempt the
area source category from title V
requirements is unlawful and arbitrary.
The commenter states that section
502(a) of the CAA authorizes EPA to
exempt area source categories from title
V permitting requirements if the
Administrator finds that compliance
with such requirements is
‘‘impracticable, infeasible or
unnecessarily burdensome.’’ 42 U.S.C.
7661a(a). The commenter notes that
EPA did not claim that title V
requirements are impracticable or
infeasible for the source category it
proposes to exempt, but that EPA
instead relied entirely on its claim that
title V would be ‘‘unnecessarily
burdensome.’’
Response: Section 502(a) of the CAA
states, in relevant part, that:
* * * [t]he Administrator may, in the
Administrator’s discretion and consistent
with the applicable provisions of this
chapter, promulgate regulations to exempt
one or more source categories (in whole or
in part) from the requirements of this
subsection if the Administrator finds that
compliance with such requirements is
impracticable, infeasible, or unnecessarily
burdensome on such categories, except that
the Administrator may not exempt any major
source from such regulations. See 42 U.S.C.
section 7661a(a).
The statute plainly vests the
Administrator with discretion to
determine when it is appropriate to
exempt non-major (i.e., area) sources of
air pollution from the requirements of
title V. The commenter correctly notes
that EPA based the proposed
exemptions solely on a determination
that title V is ‘‘unnecessarily
burdensome,’’ and did not rely on
whether the requirements of title V are
‘‘impracticable’’ or ‘‘infeasible’’, which
are alternative bases for exempting area
sources from title V.
To the extent the commenter is
asserting that EPA must determine that
all three criteria in CAA section 502 are
met before an area source category can
be exempted from title V, the
commenter misreads the statute. The
statute expressly provides that EPA may
exempt an area source category from
title V requirements if EPA determines
that the requirements are
‘‘impracticable, infeasible or
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unnecessarily burdensome.’’ See CAA
section 502 (emphasis added). If
Congress had wanted to require that all
three criteria be met before a category
could be exempted from title V, it
would have stated so by using the word
‘‘and,’’ in place of ‘‘or’’.
Comment: One commenter stated that,
in order to demonstrate that compliance
with title V would be ‘‘unnecessarily
burdensome,’’ EPA must show, among
other things, that the ‘‘burden’’ of
compliance is unnecessary. According
to the commenter, by promulgating title
V, Congress indicated that it viewed the
burden imposed by its requirements as
necessary as a general rule. The
commenter maintained that the title V
requirements provide many benefits that
Congress viewed as necessary. Thus, in
the commenter’s view, EPA must show
why, for any given category, special
circumstances make compliance
unnecessary. The commenter believed
that EPA has not made that showing for
the category it proposes to exempt.
Response: EPA does not agree with
the commenter’s characterization of the
demonstration required for determining
that title V is unnecessarily burdensome
for an area source category. As stated
above, the CAA provides the
Administrator discretion to exempt an
area source category from title V if he
determines that compliance with title V
requirements is ‘‘impracticable,
infeasible, or unnecessarily
burdensome’’ on an area source
category. See CAA section 502(a). In
December 2005, in a national
rulemaking, EPA interpreted the term
‘‘unnecessarily burdensome’’ in CAA
section 502 and developed a four-factor
balancing test for determining whether
title V is unnecessarily burdensome for
a particular area source category, such
that an exemption from title V is
appropriate. See 70 FR 75320, December
19, 2005 (‘‘Exemption Rule’’). In
addition to interpreting the term
‘‘unnecessarily burdensome’’ and
developing the four-factor balancing test
in the Exemption Rule, EPA applied the
test to certain area source categories.
The four factors that EPA identified in
the Exemption Rule for determining
whether title V is unnecessarily
burdensome on a particular area source
category include: (1) Whether title V
would result in significant
improvements to the compliance
requirements, including monitoring,
recordkeeping, and reporting, that are
proposed for an area source category (70
FR 75323); (2) whether title V
permitting would impose significant
burdens on the area source category and
whether the burdens would be
aggravated by any difficulty the sources
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may have in obtaining assistance from
permitting agencies (70 FR 75324); (3)
whether the costs of title V permitting
for the area source category would be
justified, taking into consideration any
potential gains in compliance likely to
occur for such sources (70 FR 75325);
and (4) whether there are
implementation and enforcement
programs in place that are sufficient to
assure compliance with the NESHAP for
the area source category, without relying
on title V permits (70 FR 75326).4
In discussing the above factors in the
Exemption Rule, we explained that we
considered on ‘‘a case-by-case basis the
extent to which one or more of the four
factors supported title V exemptions for
a given source category, and then we
assessed whether considered together
those factors demonstrated that
compliance with title V requirements
would be ‘unnecessarily burdensome’
on the category, consistent with section
502(a) of the Act.’’ See 70 FR 75323.
Thus, we concluded that not all of the
four factors must weigh in favor of
exemption for EPA to determine that
title V is unnecessarily burdensome for
a particular area source category.
Instead, the factors are to be considered
in combination and EPA determines
whether the factors, taken together,
support an exemption from title V for a
particular source category.
The commenter asserts that ‘‘EPA
must show * * * that the ‘‘burden’’ of
compliance is unnecessary.’’ This is not,
however, one of the four factors that we
developed in the Exemption Rule in
interpreting the term ‘‘unnecessarily
burdensome’’ in CAA section 502, but
rather a new test that the commenter
maintains EPA ‘‘must’’ meet in
determining what is ‘‘unnecessarily
burdensome’’ under CAA section 502.
EPA did not re-open its interpretation of
the term ‘‘unnecessarily burdensome’’
in CAA section 502 in the July 27, 2009
proposed rule for the category at issue
in this rule. Rather, we applied the fourfactor balancing test articulated in the
Exemption Rule to the source category
for which we proposed title V
4 In the Exemption Rule, in addition to
determining whether compliance with title V
requirements would be unnecessarily burdensome
on an area source category, we considered,
consistent with the guidance provided by the
legislative history of section 502(a), whether
exempting the area source category would adversely
affect public health, welfare or the environment.
See 72 FR 15254–15255, March 25, 2005. As
discussed in the proposed rule and below, after
conducting the four-factor balancing test and
determining that title V requirements would be
unnecessarily burdensome on the area source
categories at issue here, we examined whether the
exemption from title V would adversely affect
public health, welfare and the environment, and
found that it would not.
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exemption. Had we sought to re-open
our interpretation of the term
‘‘unnecessarily burdensome’’ in CAA
section 502 and modify it from what
was articulated in the Exemption Rule,
we would have stated so in the July 27,
2009 proposed rule and solicited
comments on a revised interpretation,
which we did not do. Accordingly, we
reject the commenter’s attempt to create
a new test for determining what
constitutes ‘‘unnecessarily burdensome’’
under CAA section 502, as that issue
falls outside the purview of this
rulemaking.5
Furthermore, we believe that the
commenter’s position that ‘‘EPA must
show * * * that the ‘burden’ of
compliance is unnecessary’’ is
unreasonable and contrary to
Congressional intent concerning the
applicability of title V to area sources.
Congress intended to treat area sources
differently under title V, as it expressly
authorized the EPA Administrator to
exempt such sources from the
requirements of title V at her discretion.
There are several instances throughout
the CAA where Congress chose to treat
major sources differently than nonmajor sources, as it did in CAA section
502. Moreover, although the commenter
espouses a new interpretation of the
term ‘unnecessarily burdensome’ in
CAA section 502 and attempts to create
a new test for determining whether the
requirements of title V are
’unnecessarily burdensome’ for an area
source category, the commenter does
not explain why EPA’s interpretation of
the term ‘unnecessarily burdensome’ is
arbitrary, capricious or otherwise not in
accordance with law. We maintain that
our interpretation of the term
‘unnecessarily burdensome’ in section
502, as set forth in the Exemption Rule,
is reasonable.
Comment: One commenter stated that
exempting a source category from title V
permitting requirements deprives both
the public generally and individual
members of the public who would
obtain and use permitting information
from the benefit of citizen oversight and
enforcement that Congress plainly
viewed as necessary. According to the
commenter, the text and legislative
history of the CAA provide that
Congress intended ordinary citizens to
be able to get emissions and compliance
information about air toxics sources and
5 If the commenter objected to our interpretation
of the term ‘‘unnecessarily burdensome’’ in the
Exemption Rule, it should have commented on, and
challenged, that rule. Any challenge to the
Exemption Rule is now time barred by CAA section
307(b). Although we received comments on the title
V Exemption Rule during the rulemaking process,
no one sought judicial review of that rule.
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to be able to use that information in
enforcement actions and in public
policy decisions on a state and local
level. The commenter stated that
Congress did not think that enforcement
by states or other government entities
was enough; if it had, Congress would
not have enacted the citizen suit
provisions, and the legislative history of
the CAA would not show that Congress
viewed citizens’ access to information
and ability to enforce CAA requirements
as highly important both as an
individual right and as a crucial means
to ensuring compliance. According to
the commenter, if a source does not
have a title V permit, it is difficult or
impossible—depending on the laws,
regulations and practices of the state in
which the source operates—for a
member of the public to obtain relevant
information about its emissions and
compliance status. The commenter
stated that, likewise, it is difficult or
impossible for citizens to bring
enforcement actions. The commenter
continued that EPA does not claim—far
less demonstrate with substantial
evidence—that citizens would have the
same ability to obtain compliance and
emissions information about sources in
the category it proposes to exempt
without title V permits. The commenter
also said that, likewise, EPA does not
claim—far less demonstrate with
substantial evidence—that citizens
would have the same enforcement
ability. Thus, according to the
commenter, the exemption EPA
proposes plainly eliminates benefits that
Congress thought necessary. The
commenter claimed that to, justify its
exemption, EPA would have to show
that the informational and enforcement
benefits that Congress intended title V
to confer—benefits which the
commenter argues are eliminated by the
exemptions—are for some reason
unnecessary with respect to the category
it proposes to exempt. The commenter
concluded that EPA does not even
acknowledge these benefits of title V, far
less explain why they are unnecessary,
and that for this reason alone, EPA’s
proposed exemptions are unlawful and
arbitrary.
Response: Once again, the commenter
attempts to create a new test for
determining whether the requirements
of title V are ‘‘unnecessarily
burdensome’’ on an area source
category. Specifically, the commenter
argues that EPA does not claim or
demonstrate with substantial evidence
that citizens would have the same
access to information and the same
ability to enforce under these NESHAP,
absent title V. The commenter’s position
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represents a significant revision of the
fourth factor that EPA developed in the
Exemption Rule in interpreting the term
‘‘unnecessarily burdensome’’ in CAA
section 502. For all of the reasons
explained above, the commenter’s
attempt to create a new test for EPA to
meet in determining whether title V is
‘‘unnecessarily burdensome’’ on an area
source category cannot be sustained.
Moreover, EPA’s interpretation of the
term ‘‘unnecessarily burdensome’’ in
CAA section 502 is reasonable.
EPA reasonably applied the four
factors to the facts of the category at
issue in this rule, and the commenter
has not identified any flaw in EPA’s
application of the four factor test to the
area source category at issue here.
Moreover, as explained in the proposal,
we considered implementation and
enforcement issues in the fourth factor
of the four-factor balancing test.
Specifically, the fourth factor of EPA’s
unnecessarily burdensome analysis
provides that EPA will consider
whether there are implementation and
enforcement programs in place that are
sufficient to assure compliance with the
NESHAP without relying on title V
permits. See 70 FR 75326.
In applying the fourth factor here,
EPA determined that there are adequate
enforcement programs in place to assure
compliance with the CAA. As stated in
the proposal, we believe that statedelegated programs are sufficient to
assure compliance with the NESHAP
and that States must have adequate
programs to enforce section 112
requirements and provide assurances
that they will enforce the NESHAP
before EPA will delegate the program. In
addition, EPA retains authority to
enforce this NESHAP under the CAA.
See 74 FR 36988. The commenter does
not challenge the conclusion that there
are adequate state and Federal programs
in place to ensure compliance with and
enforcement of the NESHAP. Instead,
the commenter provides an
unsubstantiated assertion that
information about compliance by the
area sources with this NESHAP will not
be as accessible to the public as
information provided to a State
pursuant to title V. The commenter does
not, however, provide any information
that States will treat information
submitted under these NESHAP
differently than information submitted
pursuant to a title V permit.
Even accepting the commenter’s
assertions that it is more difficult for
citizens to enforce the NESHAP absent
a title V permit, which we dispute, in
evaluating the fourth factor in EPA’s
balancing test, EPA concluded that there
are adequate implementation and
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541
enforcement programs in place to
enforce the NESHAP. The commenter
has provided no information to the
contrary or explained how the absence
of title V actually impairs the ability of
citizens to enforce the provisions of
these NESHAP.
Furthermore, the fourth factor is one
factor that we evaluated in determining
if the title V requirements were
unnecessarily burdensome. As
explained above, we considered that
factor together with the other factors
and determined that it was appropriate
to finalize the proposed exemption at
issue in this rule.
Comment: One commenter explained
that title V provides important
monitoring benefits, and, according to
the commenter, EPA assumes that title
V monitoring would not add any
monitoring requirements beyond those
required by the regulations for the
category. The commenter said that in its
proposal EPA proposed to require
‘‘continuous parameter monitoring and
periodic recording of the parameter for
the required control device to assure
compliance. 74 FR at 36987.’’ The
commenter further states that ‘‘EPA
argues that its proposed standard, by
including these requirements, provides
monitoring ‘sufficient to assure
compliance’ with the requirements of
the proposed rule. Id.’’ The commenter
maintains that EPA made conclusory
assertions and that the Agency failed to
provide any evidence to demonstrate
that the proposed monitoring
requirements will assure compliance
with the NESHAP for the exempt
sources. The commenter stated that, for
this reason as well, its claim that title V
requirements are ‘‘unnecessarily
burdensome’’ is arbitrary and
capricious, and its exemption is
unlawful and arbitrary and capricious.
Response: As noted in the earlier
comment, EPA used the four-factor test
to determine if title V requirements
were unnecessarily burdensome. In the
first factor, EPA considers whether
imposition of title V requirements
would result in significant
improvements to the compliance
requirements that are proposed for the
area source categories. See 74 FR 36987.
It is in the context of this first factor that
EPA evaluates the monitoring,
recordkeeping and reporting
requirements of the proposed NESHAP
to determine the extent to which those
requirements are consistent with the
requirements of title V. See 70 FR
75323.
The commenter asserts that ‘‘EPA
argues that its proposed standard, by
including these requirements, ‘provides
monitoring sufficient to assure
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compliance with the proposed rule.’ See
Fed Reg. 74 At 36987.’’ In the proposal,
we stated:
The proposed rule requires direct
monitoring of control device
parameters, recordkeeping that also may
serve as monitoring, and deviation and
other annual reporting to assure
compliance with the requirements.
The monitoring component of the first
factor favors title V exemption. For the
management practices, this proposed
standard provides monitoring in the
form of recordkeeping that would assure
compliance with the requirements of the
proposed rule. Monitoring by means
other than recordkeeping for the
management practices is not practical or
appropriate. Records are required to
ensure that the management practices
are followed. The rule requires
continuous parameter monitoring and
periodic recording of the parameter for
the required control device to assure
compliance. The proposed rule requires
the owner or operator to record the date
and results of periodic control device
inspections, as well as any actions taken
in response to findings of the
inspections. See 74 FR 36987.
As the above excerpt states, we
required continuous parameter
monitoring and periodic records of the
parameter for new and existing affected
sources when the rule requires the
installation of such controls. This
monitoring is in addition to the
recordkeeping that serves as monitoring
for the management practices. The
commenter does not provide any
evidence that contradicts the conclusion
that the proposed monitoring
requirements are sufficient to assure
compliance with the standards in the
rule.
Based on the foregoing, we considered
whether title V monitoring requirements
would lead to significant improvements
in the monitoring requirements in the
proposed NESHAP and determined that
they would not. We believe that the
monitoring, recordkeeping and
reporting requirements in this area
source rule can assure compliance.
For the reasons described above and
in the proposed rule, the first factor
supports exempting this area source
category from title V requirements.
Assuming, for arguments sake, that the
first factor alone cannot support the
exemption, the four-factor balancing test
requires EPA to examine the factors in
combination and determine whether the
factors, viewed together, weigh in favor
of exemption. See 74 FR 36987. As
explained above, we determined that
the factors, weighed together, support
exemption of the area source categories
from title V.
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Comment: One commenter believes
that EPA cannot justify exempting the
source from title V by asserting that
compliance with title V requirements
poses a ‘‘significant burden.’’ According
to the commenter, regardless of whether
EPA regards the burden as ‘‘significant,’’
the Agency may not exempt a category
from compliance with title V
requirements unless compliance is
‘‘unnecessarily burdensome.’’ Or in the
commenter’s words, that ‘‘the
compliance burden is especially great.’’
The commenter stated that in any event,
EPA’s claims about the alleged burden
of compliance are entirely conclusory
and could be applied equally to any
major or area source category; therefore,
the commenter claims that EPA has not
justified why this source category
should be exempt from title V
permitting as opposed to any other
category.
Response: The commenter appears to
take issue with the formulation of the
second factor of the four-factor
balancing test. Specifically, the
commenter states that EPA must
determine that title V compliance is
‘‘unnecessarily burdensome’’ and not a
‘‘significant burden,’’ as expressed in
the second factor of the four-factor
balancing test.
As we have stated before, we found
the burden placed on the prepared feed
manufacturing area source category in
complying with title V requirements is
unnecessarily burdensome when we
applied the four-factor balancing test.
We did not re-open EPA’s interpretation
of the term ‘‘unnecessarily burdensome’’
in this rule. As explained above, we
maintain that the Agency’s
interpretation of the term
‘‘unnecessarily burdensome,’’ as set
forth in the Exemption Rule and
reiterated in the proposal to this rule, is
reasonable.
In applying the four-factor test, we
properly analyzed the second factor, i.e.,
will title V permitting impose a
significant burden on the area source,
and will that burden be aggravated by
any difficulty that the source may have
in obtaining assistance from the
permitting agency. See 74 FR 36988.
EPA found that the sources would have
a significant burden because we
estimated that the average cost of
obtaining and complying with a title V
permit in general was $65,700 per
source for a 5-year permit period. 74 FR
36988. In addition, EPA found that most
of the sources affected by this rule are
small businesses. Small businesses often
lack the technical resources to comply
with the permitting requirements and
the financial resources needed to hire
the necessary staff or outside
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consultants. EPA found that not only is
the individual cost of permitting
significant for this source category (i.e.,
$65,700) but also that the cost to this
source category with approximately
1,800 sources as a whole is significant.
Furthermore, given the number of
affected sources in this source category
(i.e., approximately 1,800), it would
likely be difficult for them to obtain
assistance from the permitting
authorities. These specific factors for the
affected sources alone justify that EPA
has properly exempted the source
category from title V. However, as
discussed in the proposal and above,
EPA analyzed all of the four factors in
making its determination that these
sources should be exempt from title V
permitting requirements; and we found
that the totality of these factors weighs
heavily in favor of the exemption.
Comment: According to one
commenter, EPA argued that
compliance with title V would not yield
any gains in compliance with
underlying requirements in the relevant
NESHAP (74 FR 36988). The commenter
stated that EPA’s conclusory claim
could be made equally with respect to
any major or area source category.
According to the commenter, the
Agency provides no specific reasons to
believe that the additional
informational, monitoring, reporting,
certification, and enforcement
requirements that exist in title V, but
not in this NESHAP, would not provide
additional compliance benefits. The
commenter also stated that the only
basis for EPA’s claim is, apparently, its
beliefs that those additional
requirements never confer additional
compliance benefits. According to the
commenter, by advancing such
argument, EPA merely seeks to elevate
its own policy judgment over Congress’
decisions reflected in the CAA’s text
and legislative history.
Response: The commenter takes out of
context certain statements in the
proposed rule concerning the factors
used in the balancing test to determine
if imposition of title V permit
requirements is unnecessarily
burdensome for the prepared feeds
manufacturing area source category. The
commenter also mischaracterizes the
first of the four-factor balancing test
with regard to determining whether
imposition of title V would result in
significant improvements in
compliance. In addition, the commenter
mischaracterizes the analysis in the
third factor of the balancing test which
instructs EPA to take into account any
gains in compliance that would result
from the imposition of the title V
requirements.
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First, EPA nowhere states, nor does it
believe, that title V never confers
additional compliance benefits as the
commenter asserts. While EPA
recognizes that requiring a title V permit
offers additional compliance options,
the statute provides that EPA must
assess whether compliance with title V
would be unnecessarily burdensome to
the specific area sources at issue. For
the source category subject to this
rulemaking, EPA concluded that
requiring title V permits would be
unnecessarily burdensome.
Second, the commenter
mischaracterizes the first factor by
asserting that EPA must demonstrate
that title V will provide no additional
compliance benefits. The first factor
calls for a consideration of ‘‘whether
title V would result in significant
improvements to the compliance
requirements, including monitoring,
recordkeeping, and reporting, that are
proposed for an area source category.’’
Thus, contrary to the commenter’s
assertion, the inquiry under the first
factor is not whether title V will provide
any compliance benefit, but rather
whether it will provide significant
improvements in compliance
requirements.
The monitoring, recordkeeping and
reporting requirements in the rule are
sufficient to assure compliance with the
requirements of this rule, consistent
with the goal of title V permitting. For
example, in the Initial Notification, the
source must include information about
the facility and its operations. The
source must also certify how it is
complying and that it has complied
with the required management practices
and associated recordkeeping
requirements. The source must further
certify that it has installed controls, if
necessary to meet the final standards
and that it is monitoring the controls, as
required by the final rule and keeping
all necessary records regarding the
inspections of the controls and any
corrective actions taken as a result of
seeing changes in the operation of the
control equipment. See section 63.11624
in the final rule. The source must also
keep records and conduct inspections to
document that it is complying with the
management practices finalized in this
rule. See section 63.11624 in the final
rule. The source must monitor and
demonstrate cyclone performance
efficiency and, if applicable, must begin
corrective action and record the
specifics about the corrective action
upon seeing any deviation in the
pressure drop or fan amperage in the
control equipment. The source must
also submit deviation reports to the
permitting agency in the annual report
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if there has been a deviation in the
requirements of the rule. See section
63.11624 in the final rule. EPA believes
that these requirements in the rule itself
provide sufficient basis to assure
compliance with the final emission
standards, and does not believe that the
title V requirements, if applicable to
these sources, would offer significant
improvements in the compliance of the
sources with the rule.
Third, the commenter incorrectly
characterizes our statements in the
proposed rule concerning our
application of the third factor. Under
the third factor, EPA evaluates ‘‘whether
the costs of title V permitting for the
area source category would be justified,
taking into consideration any potential
gains in compliance likely to occur for
such sources.’’ Contrary to what the
commenter alleges, EPA did not state in
the proposed rule that compliance with
title V would not yield any gains in
compliance with the underlying
requirements in the relevant NESHAP,
nor does factor three require such a
determination. Instead, consistent with
the third factor, we considered whether
the costs of title V are justified in light
of any potential gains in compliance. In
other words, EPA must view the costs
of title V permitting requirements,
considering any improvement in
compliance above what the rule
requires. EPA reviewed the area source
category at issue and determined that
the vast majority of the approximately
1,800 sources that would be subject to
the rule currently do not have a title V
permit. As stated in the proposal, EPA
estimated that the average cost of
obtaining and complying with a title V
permit was $65,700 per source for a 5year permit period, including fees. See
Information Collection Request for Part
70 Operating Permit Regulations, 72 FR
32290, June 12, 2007, EPA ICR Number
1587.07. Based on this information, EPA
determined that there is a significant
cost burden to the industry to require
title V permitting for all the sources
subject to the rule. In addition, in
analyzing factor one, EPA found that
imposition of the title V requirements
offers no significant improvements in
compliance. In considering the third
factor, we stated in part that, ‘‘Because
the costs of compliance with title V are
so high, and the potential for gains in
compliance is low, title V permitting is
not justified for this source category.
Accordingly, the third factor supports
the proposed title V exemptions for this
area source category.’’ See 74 FR 36988.
Most importantly, EPA considered all
four factors in the balancing test in
determining whether title V was
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543
unnecessarily burdensome on the
prepared feeds manufacturing area
source category. EPA found it
reasonable after considering all four
factors to exempt this source category
from the permitting requirements in title
V. Because the commenter’s statements
do not demonstrate a flaw in EPA’s
application of the four-factor balancing
test to the specific facts of the source
category at issue here, the comments
provide no basis for the Agency to
reconsider its proposal to exempt this
area source category from title V.
Comment: According to one
commenter, ‘‘[t]he agency does not
identify any aspect of any of the
underlying NESHAP showing that with
respect to these specific NESHAP—
unlike all the other major and area
source NESHAP it has issued without
title V exemptions—title V compliance
is unnecessary.’’ Instead, according to
the commenter, EPA merely pointed to
existing State requirements and the
potential for actions by States and EPA
that are generally applicable to all
categories (along with some small
business and voluntary programs). The
commenter said that, absent a showing
by EPA that distinguishes the sources it
proposes to exempt from other sources,
however, the Agency’s argument boils
down to the claim that it generally
views title V requirements as
unnecessary. The commenter stated
that, while this may be EPA’s view, it
was not Congress’ view when Congress
enacted title V, and a general view that
title V is unnecessary does not suffice to
show that title V compliance is
unnecessarily burdensome.
Response: The commenter again takes
issue with the Agency’s test for
determining whether title V is
unnecessarily burdensome, as
developed in the Exemption Rule. Our
interpretation of the term
‘‘unnecessarily burdensome’’ is not the
subject of this rulemaking. In any event,
as explained above, we believe the
Agency’s interpretation of the term
‘‘unnecessarily burdensome’’ is a
reasonable one. To the extent the
commenter asserts that our application
of the fourth factor is flawed, we
disagree. The fourth factor involves a
determination as to whether there are
implementation and enforcement
programs in place that are sufficient to
assure compliance with the rule without
relying on the title V permits. In
discussing the fourth factor in the
proposal, EPA states that prior to
delegating implementation and
enforcement to a State, EPA must ensure
that the State has programs in place to
enforce the rule. EPA believes that these
programs will be sufficient to assure
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compliance with the rule. EPA also
retains authority to enforce this
NESHAP anytime under CAA sections
112, 113 and 114. EPA also noted other
factors in the proposal that together are
sufficient to assure compliance with this
area source.
The commenter argues that EPA
cannot exempt this area source category
from title V permitting requirements
because ‘‘[t]he agency does not identify
any aspect of any of the underlying
NESHAP showing that with respect to
these specific NESHAP—unlike all the
other major and area source NESHAP it
has issued without title V exemptions—
title V compliance is unnecessary’’
(emphasis added). As an initial matter,
EPA cannot exempt major sources from
title V permitting. 42 U.S.C. 502(a). As
for area sources, the standard that the
commenter proposes—that EPA must
show that ‘‘title V compliance is
unnecessary’’—is not consistent with
the standard the Agency established in
the Exemption Rule and applied in the
proposed rule in determining if title V
requirements are unnecessarily
burdensome for the source category at
issue.
Furthermore, we disagree that the
basis for excluding the area source
prepared feeds manufacturing category
from title V requirements is generally
applicable to any source category. As
explained in the proposal preamble and
above, we balanced the four factors
considering the facts and circumstances
of the source category at issue in this
rule. For example, in assessing whether
the costs of requiring the sources to
obtain a title V permit was burdensome,
we concluded that because the vast
majority of the sources did not have a
title V permit, the costs imposed on the
source category were significant
compared to the additional compliance
benefits offered by the title V permitting
process.
Comment: One commenter stated that
the legislative history of the CAA shows
that Congress did not intend EPA to
exempt source categories from
compliance with title V unless doing so
would not adversely affect public
health, welfare, or the environment. See
74 FR 36988. Nonetheless, according to
the commenter, EPA does not make any
showing that its exemption would not
have adverse impacts on health, welfare
and the environment. The commenter
stated that, instead, EPA offered only
the conclusory assertion that ‘‘the level
of control would remain the same’’
whether title V permits are required or
not 74 FR 36988–89. The commenter
continued by stating that EPA relied
entirely on the conclusory arguments
advanced elsewhere in its proposal that
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compliance with title V would not yield
additional compliance with the
underlying NESHAP. The commenter
stated that those arguments are wrong
for the reasons given above, and
therefore EPA’s claims about public
health, welfare and the environment are
wrong too. The commenter also stated
that Congress enacted title V for a
reason: To assure compliance with all
applicable requirements and to
empower citizens to get information and
enforce the CAA. The commenter said
that those benefits—of which EPA’s
proposed rule deprives the public—
would improve compliance with the
underlying standards and thus have
benefits for public health, welfare and
the environment. According to the
commenter, EPA has not demonstrated
that these benefits are unnecessary with
respect to any specific source category,
but again simply rests on its own
apparent belief that they are never
necessary. The commenter concluded
that, for the reasons given above, the
attempt to substitute EPA’s judgment for
Congress’ is unlawful and arbitrary.
Response: Congress gave the
Administrator the authority to exempt
area sources from compliance with title
V if, in his or her discretion, the
Administrator ‘‘finds that compliance
with [title V] is impracticable,
infeasible, or unnecessarily
burdensome.’’ See CAA section 502(a).
EPA has interpreted one of the three
justifications for exempting area
sources, ‘‘unnecessarily burdensome’’,
as requiring consideration of the four
factors discussed above. EPA applied
these four factors to the area source
category subject to this rule and
concluded that requiring title V for this
area source category would be
unnecessarily burdensome. In addition
to determining that title V would be
unnecessarily burdensome on the
prepared feed manufacturing area
source category, EPA also considered
whether exempting the area source
category would adversely affect public
health, welfare or the environment. As
explained in the proposal preamble, we
concluded that exempting the area
source category at issue in this rule
would not adversely affect public
health, welfare or the environment
because the level of control would be
the same even if title V applied. We
further explained in the proposal
preamble that the title V permit program
does not generally impose new
substantive air quality control
requirements on sources, but instead
requires that certain procedural
measures be followed, particularly with
respect to determining compliance with
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applicable requirements. The
commenter has not provided any
information that exemption of this area
source category from title V will
adversely affect public health, welfare
or the environment.
VI. Impacts of the Final Standards
We project that the baseline PM
emissions from the estimated 1,800
facilities in the prepared feeds source
category are approximately 11,000 tons/
yr, with approximatley 11,000 tons/yr of
PM2.5, 195 tons/yr of manganese and
just over 8 tons/yr of chromium. We
believe that management practices are
already being implemented throughout
the industry. Therefore, we do not
expect any additional reductions in
chromium compound, manganese
compound, or general PM emissions
from these measures. We estimate that
the requirement to install cyclones on
the pelleting processes at the facilities
with average daily feed production
levels exceeding 50 tpd will result in
emission reductions of around 1,100
tons/yr of PM, 100 tons/yr of PM2.5, and
approximately 20 tons/yr of manganese
and chromium emissions. While
cyclones do remove PM from the air
stream, these solids are typically
recycled back to the process. Therefore,
we do not anticipate any significant
indirect or secondary air impacts of this
rule as proposed. In addition, we do not
expect any non-air health,
environmental, or energy impacts.
As noted above, we believe all
prepared feed manufacturing facilities
already implement the proposed
management practices. Therefore, there
will be no additional costs for these
measures. We estimate that the
nationwide capital costs for the
installation of cyclones on the pelleting
cooling operations at the large facilities
will be around $2.5 million. The
associated annual costs are estimated to
be just over $3 million/year.
Many of the plants in this analysis
have fewer than 500 employees, which
is the threshold to be considered
‘‘small’’ by the Small Business
Administration. It is currently estimated
that under 2 percent of the facilities (26
facilities) in the category would
potentially need to install new cyclones
under the proposed regulatory
alternative. The potential impact on the
industry as a percentage of the value of
shipments is small. Under the proposed
regulatory alternative, the largest
potential impact is estimated as 0.96
percent of shipments for a subset of
firms with an overall impact of 0.94
percent of shipments for the industry as
a whole. As a result, this action is not
expected to have a significant impact on
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a substantial number of small entities or
the economy as a whole, regardless of
whether or not the firms in the industry
are able to pass along any increases in
their costs to the consumers.
VII. Statutory and Executive Order
Reviews
A. Executive Order 12866: Regulatory
Planning and Review
This action is a ‘‘significant regulatory
action’’ under the terms of Executive
Order 12866 (58 FR 51735, October 4,
1993) because it may raise novel legal or
policy issues and is, therefore, subject to
review under the Executive Order.
Accordingly, EPA submitted this action
to 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.
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B. Paperwork Reduction Act
The information collection
requirements in this final rule have been
submitted for approval to OMB under
the Paperwork Reduction Act, 44 U.S.C.
501 et seq. The Information Collection
Request (ICR) document prepared by
EPA has been assigned EPA ICR number
2354.02.
The recordkeeping and reporting
requirements in this final rule are based
on the requirements in EPA’s NESHAP
General Provisions (40 CFR part 63,
subpart A). The recordkeeping and
reporting requirements in the General
Provisions are mandatory pursuant to
section 114 of the CAA (42 U.S.C. 7414).
All information other than emissions
data submitted to EPA pursuant to the
information collection 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.
This NESHAP requires Prepared
Feeds Manufacturing area sources to
submit an Initial Notification and a
Notification of Compliance Status
according to the requirements in 40 CFR
63.9 of the General Provisions (subpart
A). The annual burden for this
information collection averaged over the
first three years of this ICR is estimated
to be a total of 27,000 labor hours per
year at a cost of $1.7 million or
approximately $980 per facility.
An agency may not conduct or
sponsor, and a person is not required to
respond to, a collection of information
unless it displays a currently valid OMB
control number. The OMB control
numbers for EPA regulations in 40 CFR
are listed in 40 CFR part 9.
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545
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act
The Regulatory Flexibility Act
generally requires an agency to prepare
a regulatory flexibility analysis of any
rule subject to notice and comment
rulemaking requirements under the
Administrative 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 this rule on small entities,
small entity is defined as: (1) A small
business that meets the Small Business
Administration size standards for small
businesses found at 13 CFR 121.201; (2)
a small governmental jurisdiction that is
a government of a city, county, town,
school district, or special district with a
population of less than 50,000; 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 this rule on small entities, I
certify that this action will not have a
significant economic impact on a
substantial number of small entities.
This rule is estimated to impact a total
of almost 1,800 area source prepared
feeds manufacturing facilities. We
estimate that all these facilities may be
small entities. We have determined that
small entity compliance costs, as
assessed by the facilities’ cost-to-sales
ratio, are expected to be less than 0.004
percent for the estimated 26 facilities
that would not initially be in
compliance. Although this final rule
contains requirements for new area
sources, we are not aware of any new
area sources being constructed now or
planned in the next three years, 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
such impact. The standards represent
practices and controls that are common
throughout the prepared feeds
manufacturing industry. The standards
also require only the essential
recordkeeping and reporting needed to
demonstrate and verify compliance.
These standards were developed in
consultation with small business
representatives on the State and
national level and the trade associations
that represent small businesses.
This final rule does not contain a
Federal mandate that may result in
expenditures of $100 million or more
for State, local, and Tribal governments,
in the aggregate, or to the private sector
in any one year. This rule is not
expected to impact State, local, or Tribal
governments. The nationwide
annualized cost of this rule for affected
industrial sources is around $3 million/
yr. Thus, this rule would not be subject
to the requirements of sections 202 and
205 of the Unfunded Mandates Reform
Act (UMRA).
This final rule would also not be
subject to the requirements of section
203 of UMRA because it contains no
regulatory requirements that might
significantly or uniquely affect small
governments. The rule would not apply
to such governments and would impose
no obligations upon them.
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E. Executive Order 13132: Federalism
This action does not have federalism
implications. It will not have substantial
direct effects on the States, on the
relationship between the national
government and the States, or on the
distribution of power and
responsibilities among the various
levels of government, as specified in
Executive Order 13132. This rule does
not impose any requirements on State
and local governments. Thus, Executive
Order 13132 does not apply to this final
rule.
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
This action does not have Tribal
implications, as specified in Executive
Order 13175 (65 FR 67249, November 9,
2000). This final rule imposes no
requirements on Tribal governments;
thus, Executive Order 13175 does not
apply to this action.
G. Executive Order 13045: Protection of
Children From Environmental Health
and Safety Risks
EPA interprets Executive Order 13045
(62 FR 19885, April 23, 1997) as
applying to those regulatory actions that
concern health or safety risks, such that
the analysis required under section 5–
501 of the Order has the potential to
influence the regulation. This action is
not subject to EO 13045 because it is
based solely on technology
performance.
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H. Executive Order 13211: Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use
This final rule is not a ‘‘significant
energy action’’ as defined in Executive
Order 13211 (66 FR 28355, May 22,
2001) because it is not likely to have a
significant adverse effect on the supply,
distribution, or use of energy. Further,
we have concluded that this rule is not
likely to have any adverse energy
effects. Existing energy requirements for
this industry would not be significantly
impacted by the additional controls or
other equipment that may be required
by this rule.
I. National Technology Transfer and
Advancement Act
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (‘‘NTTAA’’), Public Law
104–113, 12(d) (15 U.S.C. 272 note)
directs EPA to use voluntary consensus
standards in its regulatory activities
unless to do so would be inconsistent
with applicable law or otherwise
impractical. Voluntary consensus
standards are technical standards (e.g.,
materials specifications, test methods,
sampling procedures, and business
practices) that are developed or adopted
by voluntary consensus standards
bodies. NTTAA directs EPA to provide
Congress, through OMB, explanations
when the Agency decides not to use
available and applicable voluntary
consensus standards.
The rulemaking involves technical
standards. Therefore, the Agency
conducted a search to identify
potentially applicable voluntary
consensus standards. However, we
identified no such standards, and none
were brought to our attention in
comments. Therefore, EPA has decided
to use technical standard Method 5 of
40 CFR part 60, Appendix A in the
National Emissions Standards for
Hazardous Air Pollutants for Area
Sources: Prepared Feeds
Manufacturing—40 CFR part 63, subpart
DDDDDD.
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J. Executive Order 12898: Federal
Actions To Address Environmental
Justice in Minority Populations and
Low-Income Populations
17:12 Jan 04, 2010
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K. Congressional Review Act
The Congressional Review Act,
5 U.S.C. 801, et seq., as added by the
Small Business Regulatory Enforcement
Fairness Act of 1996, generally provides
that before a rule may take effect, the
agency promulgating the rule must
submit a rule report, which includes a
copy of the rule, to each House of
Congress and to the Comptroller General
of the United States. EPA will submit a
report containing this final rule and
other required information to the U.S.
Senate, the U.S. House of
Representatives, and the Comptroller
General of the United States prior to
publication of this final rule in the
Federal Register. A major rule cannot
take effect until 60 days after it is
published in the Federal Register. This
action is not a ‘‘major rule’’ as defined
by 5 U.S.C. 804(2). This final rule will
be effective on January 5, 2010.
List of Subjects in 40 CFR Part 63
Environmental protection, Air
pollution control, Hazardous
substances, Reporting and
recordkeeping requirements.
Dated: December 16, 2009.
Lisa P. Jackson,
Administrator.
For the reasons stated in the preamble,
title 40, chapter I, part 63 of the Code
of Federal Regulations is amended as
follows:
■
Executive Order 12898 (59 FR 7629,
February 16, 1994) establishes Federal
executive policy on environmental
justice. Its main provision directs
Federal agencies, to the greatest extent
practicable and permitted by law, to
make environmental justice part of their
mission by identifying and addressing,
as appropriate, disproportionately high
VerDate Nov<24>2008
and adverse human health or
environmental effects of their programs,
policies, and activities on minority
populations and low-income
populations in the United States.
EPA has determined that this final
rule would not have disproportionately
high and adverse human health or
environmental effects on minority or
low-income populations because it
increases the level of environmental
protection for all affected populations
without having any disproportionately
high and adverse human health or
environmental effects on any
population, including any minority or
low-income population. This rule
establishes national standards for the
Prepared Feeds Manufacturing area
source category; this will reduce HAP
emissions, therefore decreasing the
amount of emissions to which all
affected populations are exposed.
PART 63—[AMENDED]
1. The authority citation for part 63
continues to read as follows:
■
Authority: 42 U.S.C. 7401 et seq.
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Subpart A—[Amended]
2. Part 63 is amended by adding
subpart DDDDDDD to read as follows:
■
Subpart DDDDDDD—National Emission
Standards for Hazardous Air Pollutants for
Area Sources: Prepared Feeds
Manufacturing
Applicability and Compliance Dates
Sec.
63.11619 Am I subject to this subpart?
63.11620 What are my compliance dates?
Standards, Monitoring, and Compliance
Requirements
63.11621 What are the standards for new
and existing prepared feeds
manufacturing facilities?
63.11622 What are the monitoring
requirements for new and existing
sources?
63.11623 What are the testing
requirements?
63.11624 What are the notification,
reporting, and recordkeeping
requirements?
Other Requirements and Information
63.11625 What parts of the General
Provisions apply to my facility?
63.11626 Who implements and enforces
this subpart?
63.11627 What definitions apply to this
subpart?
63.11628—63.11638 [Reserved]
Tables to Subpart DDDDDDD of Part 63
Table 1 to Subpart DDDDDDD of Part 63—
Applicability of General Provisions to
Prepared Feeds Manufacturing Area
Sources
Subpart DDDDDDD—National
Emission Standards for Hazardous Air
Pollutants for Area Sources: Prepared
Feeds Manufacturing
Applicability and Compliance Dates
§ 63.11619
Am I subject to this subpart?
(a) You are subject to this subpart if
you own or operate a prepared feeds
manufacturing facility that uses a
material containing chromium or a
material containing manganese and is
an area source of emissions of
hazardous air pollutants (HAP).
(b) The provisions of this subpart
apply to each new and existing prepared
feeds manufacturing affected source. A
prepared feeds manufacturing affected
source is the collection of all equipment
and activities necessary to produce
animal feed from the point in the
process where a material containing
chromium or a material containing
manganese is added, to the point where
the finished animal feed product leaves
the facility. This includes, but is not
limited to, areas where materials
containing chromium and manganese
are stored, areas where materials
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containing chromium and manganese
are temporarily stored prior to addition
to the feed at the mixer, mixing and
grinding processes, pelleting and pellet
cooling processes, packing and bagging
processes, crumblers and screens, bulk
loading operations, and all conveyors
and other equipment that transfer the
feed materials throughout the
manufacturing facility.
(1) A prepared feeds manufacturing
affected source is existing if you
commenced construction or
reconstruction of the facility on or
before July 27, 2009.
(2) A prepared feeds manufacturing
affected source is new if you
commenced construction or
reconstruction of the facility after July
27, 2009.
(3) A collection of equipment and
activities necessary to produce animal
feed at a prepared feeds manufacturing
facility becomes an affected source
when you commence using a material
containing chromium or a material
containing manganese.
(c) An affected source is no longer
subject to this subpart if the facility
stops using materials containing
chromium or manganese.
(d) This subpart does not apply to the
facilities identified in paragraphs (d)(1)
and (2) of this section.
(1) Prepared feeds manufacturing
facilities that do not add any materials
containing chromium or manganese to
any product manufactured at the
facility.
(2) Research or laboratory facilities as
defined in section 112(c)(7) of the Clean
Air Act (CAA).
(e) 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. Notwithstanding the
previous sentence, you must continue to
comply with the provisions of this
subpart.
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§ 63.11620
dates?
What are my compliance
(a) If you own or operate an existing
affected source, you must achieve
compliance with the applicable
provisions of this subpart by no later
than January 5, 2012.
(b) If you own or operate a new
affected source, you must achieve
compliance with the applicable
provisions of this subpart by January 5,
2010, or upon startup of your affected
source, whichever is later.
(c) If you own or operate a facility that
becomes an affected source in
accordance with § 63.11619 after the
applicable compliance date in
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paragraphs (a) or (b) of this section, you
must achieve compliance with the
applicable provisions of this subpart by
the date that you commence using a
material containing manganese or a
material containing chromium.
(d) If the average daily feed
production level exceeds 50 tons per
day for a calendar year for a facility not
complying with the requirement in
§ 63.11621(e) to install and operate a
cyclone to control emissions from
pelleting operations, you must comply
with § 63.11621(e) and all associated
requirements by July 1 of the year
following the one-year period.
Standards, Monitoring, and
Compliance Requirements
§ 63.11621 What are the standards for new
and existing prepared feed manufacturing
facilities?
You must comply with the
management practices and standards in
paragraphs (a) through (f) of this section
at all times.
(a) In all areas of the affected source
where materials containing chromium
or manganese are stored, used, or
handled, you must comply with the
management practices in paragraphs
(a)(1) and (2) of this section.
(1) You must perform housekeeping
measures to minimize excess dust.
These measures must include, but not
be limited to, the practices specified in
paragraphs (a)(1)(i) through (iii) of this
section.
(i) You must use either an industrial
vacuum system or manual sweeping to
reduce the amount of dust;
(ii) At least once per month, you must
remove dust from walls, ledges, and
equipment using low pressure air or by
other means, and then sweep or vacuum
the area;
(iii) You must keep doors shut except
during normal ingress and egress.
(2) You must maintain and operate all
process equipment in accordance with
manufacturer’s specifications and in a
manner to minimize dust creation.
(b) You must store any raw materials
containing chromium or manganese in
closed containers.
(c) The mixer where materials
containing chromium or manganese are
added must be covered at all times
when mixing is occurring, except when
the materials are being added to the
mixer. Materials containing chromium
or manganese must be added to the
mixer in a manner that minimizes
emissions.
(d) For the bulk loading process
where prepared feed products
containing chromium or manganese are
loaded into trucks or railcars, you must
use a device at the loadout end of each
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bulk loader to lessen fugitive emissions
by reducing the distance between the
loading arm and the truck or railcar.
(e) For the pelleting operations at
prepared feeds manufacturing facilities
with an average daily feed production
level exceeding 50 tons per day, you
must capture emissions and route them
to a cyclone designed to reduce
emissions of particulate matter by 95
percent or greater. You must also
comply with the provisions in
paragraphs (e)(1) through (3) of this
section.
(1) You must demonstrate that the
cyclone is designed to reduce emissions
of particulate matter by 95 percent or
greater using one of the methods
specified in paragraphs (e)(1)(i) through
(iii) of this section.
(i) Manufacturer specifications;
(ii) Certification by a professional
engineer or responsible official; or
(iii) A performance test conducted in
accordance with § 63.11623 of this
section.
(2) You must establish an inlet flow
rate, inlet velocity, pressure drop, or fan
amperage range that represents proper
operation of the cyclone in accordance
with the applicable requirement in
paragraphs (e)(2)(i), (ii), or (iii) of this
section.
(i) If you demonstrate the cyclone
design efficiency using manufacturer
specifications in accordance with
paragraph (e)(1)(i) of this section, the
inlet flow rate, inlet velocity, pressure
drop, or fan amperage range that
represents proper operation of the
cyclone must be provided by the
manufacturer.
(ii) If you demonstrate the cyclone
design efficiency using certification by a
professional engineer or responsible
official in accordance with paragraph
(e)(1)(ii) of this section, this certification
must include calculations to establish
an inlet flow rate, inlet velocity,
pressure drop, or fan amperage range
that represents proper operation of the
cyclone.
(iii) If you demonstrate the cyclone
design efficiency using a performance
test in accordance with paragraph
(e)(1)(iii) of this section, you must
monitor the inlet flow rate, inlet
velocity, pressure drop, or fan amperage
during the test and establish a range that
represents proper operation of the
cyclone based on the data obtained
during the test.
(3) You must maintain and operate
the cyclone in accordance with
manufacturer’s specifications. If
manufacturer’s specifications are not
available, you must develop and follow
standard maintenance and operating
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procedures that ensure proper operation
of the cyclone.
§ 63.11622 What are the monitoring
requirements for new and existing sources?
(a) If you own or operate an affected
source required by § 63.11621(d) to use
a device at the loadout end of a bulk
loader that reduces fugitive emissions
from a bulk loading process, you must
perform monthly inspections of each
device to ensure it is in proper working
condition. You must record the results
of these inspections in accordance with
§ 63.11624(c)(4) of this subpart.
(b) If you own or operate an affected
source required by § 63.11621(e) to
install and operate a cyclone to control
emissions from pelleting operations,
you must comply with the inspection
and monitoring requirements in
paragraphs (b)(1) and (2) of this section.
(1) You must perform quarterly
inspections of the cyclone for corrosion,
erosion, or any other damage that could
result in air in-leakage, and record the
results in accordance with
§ 63.11624(c)(5)(ii).
(2) You must monitor inlet flow rate,
inlet velocity, pressure drop, or fan
amperage at least once per day when the
pelleting process is in operation. You
must also record the inlet flow rate,
inlet velocity, pressure drop, or fan
amperage in accordance with
§ 63.11624(c)(5)(iii).
§ 63.11623 What are the testing
requirements?
(a) If you are demonstrating that the
cyclone required by § 63.11621(e) is
⎛M
− M OUTLET ⎞
PM RED = ⎜ INLET
⎟ x 100
M INLET
⎝
⎠
Where:
PM RED = particulate matter reduction,
percent;
MINLET = Mass of particulate matter at the
inlet of the cyclone, dry basis, corrected
to standard conditions, g/min;
MOUTLET = Mass of particulate matter at the
outlet of the cyclone, dry basis, corrected
to standard conditions, g/min;
srobinson on DSKHWCL6B1PROD with RULES2
§ 63.11624 What are the notification,
reporting, and recordkeeping
requirements?
(a) Notifications. You must submit the
notifications identified in paragraphs
(a)(1) and (2) of this section.
(1) Initial Notification. If you are the
owner of an affected source you must
submit an Initial Notification no later
than May 5, 2010, or 120 days after you
become subject to this subpart,
whichever is later. The Initial
Notification must include the
information specified in paragraphs
(a)(1)(i) through (iv) of this section.
(i) The name, address, phone number
and e-mail address of the owner and
operator;
(ii) The address (physical location) of
the affected source;
(iii) An identification of the relevant
standard (i.e., this subpart); and
(iv) A brief description of the
operation.
(2) Notification of Compliance Status.
If you are the owner of an existing
affected source, you must submit a
Notification of Compliance Status in
accordance with § 63.9(h) of the General
Provisions on or before May 4, 2012. If
you are the owner or operator of a new
affected source, you must submit a
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Equation 1
Notification of Compliance Status
within 120 days of initial startup, or by
May 4, 2012, whichever is later. If you
own or operate an affected source that
becomes an affected source in
accordance with § 63.11619(b)(3) after
the applicable compliance date in
§ 63.11620 (a) or (b), you must submit a
Notification of Compliance Status
within 120 days of the date that you
commence using materials containing
manganese or chromium. This
Notification of Compliance Status must
include the information specified in
paragraphs (a)(2)(i) through (iv) of this
section.
(i) Your company’s name and address;
(ii) A statement by a responsible
official with that official’s name, title,
phone number, e-mail address and
signature, certifying the truth, accuracy,
and completeness of the notification
and a statement of whether the source
has complied with all the relevant
standards and other requirements of this
subpart;
(iii) If you own or operate an affected
source required by § 63.11621(e) to
install and operate a cyclone to control
emissions from pelleting operations, the
inlet flow rate, inlet velocity, pressure
drop, or fan amperage range that
constitutes proper operation of the
cyclone determined in accordance with
§ 63.11621(e)(2).
(iv) If you own or operate an affected
source that is not subject to the
requirement in § 63.11621(e) to install
and operate a cyclone to control
emissions from pelleting operations
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designed to reduce emissions of
particulate matter by 95 percent or
greater by the performance test option in
§ 63.11621(e)(1)(iii), you must conduct a
test in accordance with paragraph (b) of
this section and calculate the percent
reduction in accordance with paragraph
(c) of this section.
(b) You must use Method 5 in
Appendix A to part 60 to determine the
particulate matter mass rate at the inlet
and outlet of the cyclone. You must
conduct at least three runs at the
cyclone inlet and three runs at the
cyclone outlet. Each run must have a
sampling time of at least 60 minutes and
a sample volume of at least 0.85 dscm
(30 dscf).
(c) You must calculate the percent
particulate matter reduction using
Equation 1.
because your initial average daily feed
production level was 50 tpd or less,
documentation of your initial daily
pelleting production level
determination.
(b) Annual compliance certification
report. You must, by March 1 of each
year, prepare an annual compliance
certification report for the previous
calendar year containing the
information specified in paragraphs
(b)(1) through (b)(6) of this section.
(1) Your company’s name and
address.
(2) A statement by a responsible
official with that official’s name, title,
phone number, e-mail address and
signature, certifying the truth, accuracy,
and completeness of the notification
and a statement of whether the source
has complied with all the relevant
standards and other requirements of this
subpart.
(3) If the source is not in compliance,
include a description of deviations from
the applicable requirements, the time
periods during which the deviations
occurred, and the corrective actions
taken.
(4) Identification of all instances
when the daily inlet flow rate, inlet
velocity, pressure drop, or fan amperage
is outside range that constitutes proper
operation of the cyclone submitted as
part of your Notification of Compliance
Status. In these instances, include the
time periods when this occurred and the
corrective actions taken.
(5) If you own or operate an affected
source that is not subject to the
requirement in § 63.11621(e) to install
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and operate a cyclone to control
emissions from pelleting operations
because your average daily feed
production level was 50 tpd or less,
notification if your average daily feed
production level for the previous year
exceeded 50 tpd.
(6) If you own or operate an affected
source that was subject to the
requirement in § 63.11621(e) to install
and operate a cyclone to control
emissions from pelleting operations,
notification if your average daily feed
production level for the previous year
was 50 tpd or less and that you are no
longer complying with § 63.11621(e).
(c) Records. You must maintain the
records specified in paragraphs (c)(1)
through (5) of this section in accordance
with paragraphs (c)(6) through (8) of this
section.
(1) As required in § 63.10(b)(2)(xiv),
you must keep a copy of each
notification that you submitted to
comply with this subpart in accordance
with paragraph (a) of this section, and
all documentation supporting any Initial
Notification or Notification of
Compliance Status that you submitted.
(2) You must keep a copy of each
Annual Compliance Certification
prepared in accordance with paragraph
(b) of this section.
(3) For each device used to comply
with the requirements in § 63.11621(d),
you must keep the records of all
inspections including the information
identified in paragraphs (c)(3)(i) through
(iii) of this section.
(i) The date, place, and time of each
inspection;
(ii) Person performing the inspection;
(iii) Results of the inspection,
including the date, time, and duration of
the corrective action period from the
time the inspection indicated a problem
to the time of the indication that the
device was replaced or restored to
operation.
(4) For each cyclone used to comply
with the requirements in § 63.11621(e),
you must keep the records in paragraphs
(c)(4)(i) through (v) of this section.
(i) If you demonstrate that the cyclone
is designed to reduce emission of
particulate matter by 95 percent or
greater by manufacturer’s specifications
in accordance with § 63.11621(e)(1(i),
you must keep the records specified in
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paragraphs (c)(4)(i)(A) through (C) of
this section.
(A) Information from the
manufacturer regarding the design
efficiency of the cyclone,
(B) The inlet flow rate, inlet velocity,
pressure drop, or fan amperage range
that represents proper operation of the
cyclone,
(C) The operation and maintenance
procedures to ensure proper operation
of the cyclone.
(ii) If you demonstrate that the
cyclone is designed to reduce emissions
of particulate matter by 95 percent or
greater by certification by a professional
engineer in accordance with paragraph
§ 63.11621(e)(1)(ii), you must keep the
records specified in paragraphs
(c)(4)(ii)(A) through (C) of this section.
(A) Certification regarding the design
efficiency of the cyclone, along with
supporting information,
(B) The inlet flow rate, inlet velocity,
pressure drop, or fan amperage range
that represents proper operation of the
cyclone,
(C) The standard maintenance and
operating procedures that ensure proper
operation of the cyclone.
(iii) If you demonstrate that the
cyclone is designed to reduce emissions
of particulate matter by 95 percent or
greater by a performance in accordance
with paragraph § 63.11621(e)(1)(iii), you
must keep the records specified in
paragraphs (c)(4)(iii)(A) through (C) of
this section.
(A) Results of the testing conducted in
accordance with § 63.11623,
(B) The inlet flow rate, inlet velocity,
pressure drop, or fan amperage range
that represents proper operation of the
cyclone,
(C) The standard maintenance and
operating procedures that ensure proper
operation of the cyclone.
(iv) Records of all quarterly
inspections including the information
identified in paragraphs (c)(4)(iv)(A)
through (C) of this section.
(A) The date, place, and time of each
inspection;
(B) Person performing the inspection;
(C) Results of the inspection,
including the date, time, and duration of
the corrective action period from the
time the inspection indicated a problem
to the time of the indication that the
cyclone was restored to proper
operation.
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(v) Records of the daily inlet flow rate,
inlet velocity, pressure drop, or fan
amperage measurements, along with the
date, time, and duration of the
correction action period from the time
the monitoring indicated a problem to
the time of the indication that the
cyclone was restored to proper
operation.
(5) If you own or operate an affected
source that is not subject to the
requirement in § 63.11621(e) to install
and operate a cyclone to control
emissions from pelleting operations
because your average daily feed
production level is 50 tpd or less, feed
production records to enable the
determination of the average daily feed
production level.
(6) Your records must be in a form
suitable and readily available for
expeditious review, according to
§ 63.10(b)(1).
(7) As specified in § 63.10(b)(1), you
must keep each record for 5 years
following the date of each recorded
action.
(8) You must keep each record onsite
for at least 2 years after the date of each
recorded action according to
§ 63.10(b)(1). You may keep the records
offsite for the remaining 3 years.
(d) If you no longer use materials that
contain manganese or chromium after
January 5, 2010, you must submit a
Notification in accordance with
§ 63.11619(c) which includes the
information specified in paragraphs
(d)(1) and (2) of this section.
(1) Your company’s name and
address;
(2) A statement by a responsible
official indicating that the facility no
longer uses materials that contain
chromium or manganese. This statement
should also include an effective date for
the termination of use of materials that
contain chromium or manganese, and
the responsible official’s name, title,
phone number, e-mail address and
signature.
Other Requirements and Information
§ 63.11625 What parts of the General
Provisions apply to my facility?
Table 1 of this subpart shows which
parts of the General Provisions in
§§ 63.1 through 63.16 apply to you.
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§ 63.11626 Who implements and enforces
this subpart?
(a) This subpart can be implemented
and enforced by EPA or a delegated
authority such as your State, local, or
Tribal agency. If the EPA Administrator
has delegated authority to your State,
local, or Tribal agency, then that agency
has the authority to implement and
enforce this subpart. You should contact
your EPA Regional Office to find out if
implementation and enforcement of 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 paragraph (c) of this
section are retained by the EPA
Administrator and are not transferred to
the State, local, or Tribal agency.
(c) The authorities that cannot be
delegated to State, local, or Tribal
agencies are specified 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 and reporting under
§ 63.10(f). A ‘‘major change to
recordkeeping/reporting’’ is defined in
§ 63.90.
§ 63.11627
subpart?
What definitions apply to this
Terms used in this subpart are
defined in the CAA, in § 63.2, and in
this section.
Animal feed includes: Dehydrated
alfalfa meal; alfalfa prepared as feed for
animals; cubed alfalfa; prepared animal
feed; chopped, crushed, or ground
barley feed; prepared bird feed; blended
animal feed; bone meal prepared as feed
for animals and fowls; cattle feeds,
supplements, concentrates, and
premixes; prepared chicken feeds; cattle
feed citrus pulp; complete livestock
feed; custom milled animal feed; dairy
cattle feeds supplements, concentrates,
and premixes; earthworm food and
bedding; animal feed concentrates;
animal feed premixes; animal feed
supplements; prepared animal feeds;
specialty animal (e.g., guinea pig, mice,
mink) feeds; fish food for feeding fish;
custom ground grains for animal feed;
cubed hay; kelp meal and pellets animal
feed; laboratory animal feed; livestock
feeds, supplements, concentrates and
premixes; alfalfa meal; bone meal
prepared as feed for animals and fowls;
livestock micro and macro premixes;
mineral feed supplements; animal
mineral supplements; pet food; poultry
feeds, supplements, and concentrates;
rabbit food; shell crushed and ground
animal feed; swine feed; swine feed
supplements, concentrates, and
premixes; and prepared turkey feeds.
Feed products produced for dogs and
cats are not considered animal feed for
the purposes of this subpart.
Average daily feed production level
means the average amount of animal
feed products produced each day over
an annual period. The initial
determination of the average daily feed
production level is based on the oneyear period prior to the compliance date
for existing sources, or the design rate
for new sources. The subsequent
average daily feed production levels are
determined annually and are based on
the amount of animal feed products
produced in a calendar year divided by
Citation
63.1
63.2
63.3
63.4
63.5
srobinson on DSKHWCL6B1PROD with RULES2
63.6(a),(b)(1)–(b)(5), (b)(7), (c), (f)(2)–(3), (g),
(i), and (j).
63.6(e)(1), (e)(3), (f)(1), and (h) .........................
63.7 .....................................................................
63.8 .....................................................................
63.9(a), (b), (c), (d), (h), (i), and (j) ....................
63.9(e), (f), (g) ....................................................
63.10(a),(b)(1), (b)(2)(i)–(iii), (b)(2)(vi)–(xiv), (c),
(d)(1), (e), and (f).
63.10(b)(2)(iv)–(v), (b)(3), and (d)(2)–(5) ...........
63.11 ...................................................................
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§ 63.11628–63.11638
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[Reserved]
Tables to Subpart DDDDDDD of Part 63
Table 1 to Subpart DDDDDDD of Part
63—Applicability of General Provisions
to Prepared Feeds Manufacturing Area
Sources
As required in § 63.11619, you must
meet each requirement in the following
table that applies to you.
Subject
.....................................................................
.....................................................................
.....................................................................
.....................................................................
.....................................................................
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the number of days in which the
production processes were in operation.
Cyclone means a mechanically aided
collector that uses inertia to separate
particulate matter from the gas stream as
it spirals through the cyclone.
Material containing chromium means
a material that contains chromium (Cr,
atomic number 24) in amounts greater
than or equal to 0.1 percent by weight.
Material containing manganese
means a material that contains
manganese (Mn, atomic number 25) in
amounts greater than or equal to 1.0
percent by weight.
Pelleting operations means all
operations that make pelleted animal
feed, including but not limited to, steam
conditioning, die-casting, drying,
cooling, and crumbling, and
granulation.
Prepared feeds manufacturing facility
means a facility that is primarily
engaged in manufacturing animal feed.
A facility is primarily engaged in
manufacturing animal feed if the
production of animal feed comprises
greater than 50 percent of the total
production of the facility on an annual
basis. Facilities primarily engaged in
raising or feeding animals are not
prepared feed manufacturing facilities.
Facilities engaged in the growing of
agricultural crops that are used in the
manufacturing of feed are not
considered prepared feeds
manufacturing facilities.
Applies to Subpart DDDDDDD?
Applicability ......................................................
Definitions ........................................................
Units and Abbreviations ...................................
Prohibited Activities and Circumvention ..........
Preconstruction Review and Notification Requirements.
Compliance with Standards and Maintenance
Requirements.
Startup, shutdown, and malfunction requirements and opacity/visible emission standards.
Performance Testing Requirements ................
Monitoring Requirements .................................
Notification Requirements ................................
..........................................................................
Recordkeeping and Reporting Requirements
Yes.
Yes.
Yes.
Yes.
No.
Recordkeeping and Reporting Requirements
Control Device Requirements ..........................
No.
No.
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No. Standards apply at all times, including
during startup, shutdown, and malfunction
events.
Yes.
Yes.
Yes.
No.
Yes.
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Citation
Subject
Applies to Subpart DDDDDDD?
63.12 ...................................................................
63.13 ...................................................................
63.14 ...................................................................
63.15 ...................................................................
63.16 ...................................................................
63.1(a)(5), (a)(7)–(9), (b)(2), (c)(3)–(4), (d),
63.6(b)(6), (c)(3), (c)(4), (d), (e)(2), (e)(3)(ii),
(h)(3), (h)(5)(iv), 63.8(a)(3), 63.9(b)(3), (h)(4),
63.10(c)(2)–(4), (c)(9).
State Authorities and Delegations ...................
Addresses ........................................................
Incorporations by Reference ............................
Availability of Information and Confidentiality ..
Performance Track Provisions .........................
Reserved ..........................................................
Yes.
Yes.
Yes.
Yes.
Yes.
No.
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Agencies
[Federal Register Volume 75, Number 2 (Tuesday, January 5, 2010)]
[Rules and Regulations]
[Pages 522-551]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E9-30498]
[[Page 521]]
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Part II
Environmental Protection Agency
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40 CFR Part 63
National Emission Standards for Hazardous Air Pollutants: Area Source
Standards for Prepared Feeds Manufacturing; Final Rule
Federal Register / Vol. 75, No. 2 / Tuesday, January 5, 2010 / Rules
and Regulations
[[Page 522]]
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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 63
[EPA-HQ-OAR-2008-0080; FRL-9095-2]
RIN 2060-AO98
National Emission Standards for Hazardous Air Pollutants: Area
Source Standards for Prepared Feeds Manufacturing
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: EPA is issuing national emission standards for control of
hazardous air pollutants (HAP) for the Prepared Feeds Manufacturing
area source category. The emissions standards for new and existing
sources are based on EPA's determination as to what constitutes the
generally available control technology or management practices for the
area source category.
DATES: This final rule is effective on January 5, 2010.
ADDRESSES: EPA has established a docket for this action under Docket ID
No. EPA-HQ-OAR-2008-0080. All documents in the docket are listed in the
Federal Docket Management System index at https://www.regulations.gov.index. Although listed in the index, some
information is not publicly available, e.g., confidential business
information (CBI) or other information whose disclosure is restricted
by statute. Certain other material, such as copyrighted material, will
be publicly available only in hard copy form. Publicly available docket
materials are available either electronically in https://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. Jan King, Outreach and Information
Division, Office of Air Quality Planning and Standards (C404-05), U.S.
Environmental Protection Agency, Research Triangle Park, North Carolina
27711, telephone number: (919) 541-5665; fax number: (919) 541-7674; e-
mail address: king.jan@epa.gov.
SUPPLEMENTARY INFORMATION: The supplementary information in this
preamble is organized as follows:
I. General Information
A. Does This Action Apply to Me?
B. Where Can I Get a Copy of This Document?
C. Judicial Review
II. Background Information for This Final Rule
III. Summary of Changes Since Proposal
A. Applicability
B. Standards and Compliance Requirements
C. Reporting and Recordkeeping Requirements
D. Definitions
IV. Summary of Final Standards
A. What Are the Applicability Provisions and Compliance Dates?
B. What Are the Final Standards?
C. What Are the Compliance Requirements?
D. What Are the Notification, Recordkeeping, and Reporting
Requirements?
V. Summary of Comments and Responses
A. Rulemaking Process
B. Applicability
C. Emission Standards
D. Inspections and Compliance Provisions
E. Reporting and Recordkeeping Requirements
F. Definitions
G. Impacts Assessment
H. Title V Requirements
VI. Impacts of the Final Standards
VII. 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. Executive Order 12898: Federal Actions To Address
Environmental Justice in Minority Populations and Low-Income
Populations
K. Congressional Review Act
I. General Information
A. Does This Action Apply to Me?
The regulated categories and entities potentially affected by the
final standards are prepared feeds manufacturers who add chromium
compounds or manganese compounds to their product. In general, the
facilities potentially affected by the rule are covered under the North
American Industrial Classification System (NAICS) code listed in the
following table.
------------------------------------------------------------------------
Examples of regulated
Category NAICS code \1\ entities
------------------------------------------------------------------------
Industry:
Other Animal Foods 311119 Animal feeds, prepared
Manufacturing. (except dog and cat),
manufacturing.
------------------------------------------------------------------------
\1\ North American Industry Classification System.
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 would be regulated by this
action, you should examine the applicability criteria in 40 CFR
63.11619 of subpart DDDDDDD (NESHAP for Area Sources: Prepared Feeds
Manufacturing). 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 EPA's Technology Transfer Network (TTN). 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 this final rule is available only by filing a petition for review in
the United States Court of Appeals for the District of Columbia Circuit
by March 8, 2010. Under section 307(b)(2) of the CAA, the requirements
established by this final rule may not be challenged separately in any
civil or criminal proceedings
[[Page 523]]
brought by EPA to enforce these requirements.
Section 307(d)(7)(B) of the CAA further provides that ``[o]nly an
objection to a rule or procedure which was raised with reasonable
specificity during the period for public comment (including any public
hearing) may be raised during judicial review.'' This section also
provides a mechanism for EPA to convene a proceeding for
reconsideration, ``[i]f the person raising an objection can demonstrate
to EPA that it was impracticable to raise such objection within [the
period for public comment] or if the grounds for such objection arose
after the period for public comment (but within the time specified for
judicial review) and if such objection is of central relevance to the
outcome of the rule.'' Any person seeking to make such a demonstration
to us should submit a Petition for Reconsideration to the Office of the
Administrator, U.S. EPA, Room 3000, Ariel Rios Building, 1200
Pennsylvania Ave., NW., Washington, DC 20460, with a copy to both the
person(s) listed in the preceding FOR FURTHER INFORMATION CONTACT
section, and the Associate General Counsel for the Air and Radiation
Law Office, Office of General Counsel (Mail Code 2344A), U.S. EPA, 1200
Pennsylvania Ave., NW., Washington, DC 20460.
II. Background Information for This Final Rule
Section 112(d) of the CAA requires EPA to establish national
emission standards for hazardous air pollutants (NESHAP) for both major
and area sources of HAP that are listed for regulation under CAA
section 112(c). A major source emits or has the potential to emit 10
tons per year (tpy) or more of any single HAP or 25 tpy or more of any
combination of HAP. An area source is a stationary source that is not a
major source.
Section 112(k)(3)(B) of the CAA calls for EPA to identify at least
30 HAP which, as the result of emissions from area sources, pose the
greatest threat to public health in the largest number of urban areas.
EPA implemented this provision in 1999 in the Integrated Urban Air
Toxics Strategy, (64 FR 38715, July 19, 1999). Specifically, in the
Strategy, EPA identified 30 HAP that pose the greatest potential health
threat in urban areas, and these HAP are referred to as the ``30 urban
HAP.'' Section 112(c)(3) requires EPA to list sufficient categories or
subcategories of area sources to ensure that area sources representing
90 percent of the emissions of the 30 urban HAP are subject to
regulation. We implemented these requirements through the Integrated
Urban Air Toxics Strategy (64 FR 38715, July 19, 1999). A primary goal
of the Strategy is to achieve a 75 percent reduction in cancer
incidence attributable to HAP emitted from stationary sources.
Under CAA section 112(d)(5), we may elect to promulgate standards
or requirements for area sources ``which provide for the use of
generally available control technologies or management practices (GACT)
by such sources to reduce emissions of hazardous air pollutants.''
Additional information on GACT is found in the Senate report on the
legislation (Senate Report Number 101-228, December 20, 1989), which
describes GACT as:
* * * methods, practices and techniques which are commercially
available and appropriate for application by the sources in the
category considering economic impacts and the technical capabilities
of the firms to operate and maintain the emissions control systems.
Consistent with the legislative history, we can consider costs and
economic impacts in determining GACT. This is particularly important
when developing regulations for source categories, like this one, that
have many small businesses, as defined by the Small Business
Administration.
Determining what constitutes GACT involves considering the control
technologies and management practices that are generally available to
the area sources in the source category. We also consider the standards
applicable to major sources in the same industrial sector to determine
if the control technologies and management practices are transferable
and generally available to area sources. In appropriate circumstances,
we may also consider technologies and practices at area and major
sources in similar categories to determine whether such technologies
and practices could be considered generally available for the area
source category at issue. Finally, as noted above, in determining GACT
for a particular area source category, we consider the costs and
economic impacts of available control technologies and management
practices on that category.
We are promulgating these national emission standards in response
to a court-ordered deadline that requires EPA to sign final rules
establishing emission standards for two source categories listed
pursuant to section 112(c)(3) and (k) by December 16, 2009 (Sierra Club
v. Johnson, no. 01-1537, D.D.C., March 2006). We intend to publish a
separate rulemaking in the Federal Register for the other source
category due in December 2009.
III. Summary of Changes Since Proposal
This final rule contains several changes to the proposed rule as a
result of public comments. The following sections present a summary of
the changes to the proposed rule. We explain the reasons for these
changes in detail in the summary of comments and responses (section V
of this preamble).
A. Applicability
The final rule applies to any prepared feeds manufacturing facility
that produces animal feed products (not including cat and dog feed
products) and uses a material containing chromium or a material
containing manganese. In light of questions raised concerning the scope
of sources covered by this area source rule, we revised several
definitions in the rule and added other definitions. The prepared feeds
manufacturing area source category is identified by NAICS code 311119,
``Other Animal Food Manufacturing.'' This NAICS code includes
establishments primarily engaged in manufacturing animal feed (except
dog and cat) from ingredients, such as grains, oilseed mill products,
and meat products. The NAICS definition also contains a list of over 40
specific animal feed processes that are included in the NAICS code.
First, we added a definition of ``animal feed,'' and defined that term
to include all of the products in NAICS code 311119. This definition
also clarifies that dog and cat feed products are not considered animal
feed, consistent with the NAICS definition. The final rule, therefore,
applies not only to ``traditional'' feed products, but also to animal
feed ingredients, supplements, premixes, concentrates, and other
products included in the definition of NAICS code 311119. Second, we
revised the definition of a ``prepared feed manufacturing facility'' to
include the concept of ``primarily engaged.'' To meet the definition of
a prepared feeds manufacturing facility, a facility must be ``primarily
engaged'' in the production of animal feed. We identified that
primarily engaged in the production of animal feed means that the
animal feed makes up at least half of the facility's annual production
of all products. The definition of prepared feed manufacturing facility
explicitly states that facilities primarily engaged in feeding animals
are not prepared feed manufacturing facilities. We also added
definitions for ``a material containing chromium'' and ``a material
containing
[[Page 524]]
manganese.'' ``A material containing chromium'' is defined as any
material that contains chromium in an amount greater than 0.1 percent
by weight, and ``a material containing manganese'' is defined as any
material that contains manganese in an amount greater than 1 percent by
weight. We added a requirement to provide for the situation where a
facility starts using a material containing chromium or manganese after
the applicable compliance date. Specifically, facilities that are not
subject to the rule but start adding materials containing chromium or
manganese in the future become subject to the rule at the time they
begin adding these HAP. While the rule does not apply to prepared feeds
manufacturing facilities that do not use any materials containing
chromium or manganese, we added provisions that make it clear that
facilities that stop using all materials containing chromium and
manganese at a later date are no longer subject to the rule.
B. Standards and Compliance Requirements
The final rule retains the specific housekeeping management
practices discussed in the proposed rule. Those management practices
must reduce dust (use industrial vacuum, remove dust from walls and
ledges, keep doors shut). The only change we made to these provisions
was to require that doors be kept shut except during normal ingress and
egress, rather than the proposed requirement to keep doors shut ``as
practicable.''
The final rule requires that a device be installed and operated at
the loadout end of each bulk loader that loads products containing
chromium or manganese to lessen fugitive emissions by reducing the
distance between the loading arm and the truck or railcar. This is a
change from the proposed requirements, which specified that ``drop
filter socks'' be used on bulk loaders.
The final rule requires that emissions from the pelleting process
at facilities with an average daily feed production level exceeding 50
tons per day (tpd) be collected and routed to a cyclone designed to
achieve 95 percent or greater reduction in particulate matter (PM)
emissions. This is a change from the proposed rule, which required a
cyclone designed to achieve a 95 percent reduction in particulate
matter emissions less than 10 microns in diameter (PM10). To
demonstrate that your cyclone is designed to achieve a 95 percent
reduction in PM emissions, the final rule provides three different
options: (1) Manufacturer's specifications certifying that the cyclone
is designed to achieve 95 percent PM reduction, (2) certification by a
professional engineer or responsible official that the cyclone is
designed to achieve a 95 percent reduction in PM emissions, or (3) a
Method 5 performance test to demonstrate that the cyclone can achieve a
95 percent reduction in PM emissions.
The proposed rule required that the pressure drop across the
cyclone be monitored to demonstrate that the device was in good
condition and operating properly. The final rule expands the monitoring
options to include other measures that indicate proper flow through the
cyclone. Specifically, the final rule allows monitoring of inlet flow
rate, inlet velocity, pressure drop, or fan amperage.
C. Reporting and Recordkeeping Requirements
The final rule requires that all sources that have an average daily
feed production level of 50 tpd or less to keep production records.
These facilities must also submit their initial average daily feed
production level in the Notification of Compliance Status report.
We added recordkeeping and reporting requirements associated with
the new options on demonstrating cyclone performance efficiency
(certification by professional engineer or responsible official, or
testing). We also added provisions that require facilities that
discontinue the use of all materials containing chromium and manganese
to notify the Agency that they are no longer subject to the rule.
D. Definitions
As discussed above, definitions for animal feed, a material
containing chromium, a material containing manganese, and prepared
feeds manufacturing facility were added or modified. The definition of
filter drop sock was removed, as this term is no longer used in the
final rule.
IV. Summary of Final Standards
A. What Are the Applicability Provisions and Compliance Dates?
Subpart DDDDDDD standards apply to each new or existing prepared
feeds manufacturing facility that is an area source and uses a material
containing chromium or a material containing manganese. A prepared
feeds manufacturing facility is a facility where animal feed (as
defined in the rule) makes up at least half of the facility's annual
production of all products. A material containing chromium is any
material that contains chromium in an amount greater than 0.1 percent
by weight, and a material containing manganese is any material that
contains manganese in an amount greater than 1 percent by weight.
All existing area source facilities subject to this rule are
required to comply with the rule requirements no later than January 5,
2012. A new source is any affected source that commenced construction
or reconstruction after July 27, 2009. All new sources are required to
comply with the rule requirements by January 5, 2010 or upon startup,
whichever is later.
Prepared feeds manufacturing facilities that do not use any
materials containing chromium or manganese are not subject to this
rule. If a facility starts using a material containing chromium or
manganese after the applicable compliance date, they will be required
to comply at the time that they start using such materials. Also, if a
facility stops using all materials containing chromium and manganese,
they are no longer subject to the rule and should notify EPA or the
delegated authority of the change.
B. What Are the Final Standards?
The final requirements, which apply to all new and existing
sources, consist of equipment standards and management practices. There
are two general management practices that apply in all areas where
materials containing chromium or manganese are stored, used, or
handled. The first is to perform housekeeping measures to minimize
excess dust that could contain chromium or manganese. The specific
measures required by the rule are: (1) Use either an industrial vacuum
system or manual sweeping to reduce the amount of dust, (2) at least
once per month, remove dust from walls, ledges, and equipment using low
pressure air or by other means, and then sweep or vacuum the area, and
(3) keep doors shut except during normal ingress and egress.
The second general management practice is the requirement to
maintain and operate all process equipment that stores, processes, or
contains chromium or manganese in accordance with manufacturers'
specifications and in a manner to minimize dust creation.
There are also requirements that are specific to certain areas of
the plant or processes at all new and existing sources. These
requirements are:
For the storage area, all raw materials containing
chromium or manganese must be stored in closed containers.
[[Page 525]]
For mixing operations, materials containing chromium or
manganese must be added to the mixer in a manner to reduce emissions,
and the mixer must be covered at all times when mixing is occurring,
except when materials are being added.
For bulk loading processes where prepared feeds products
containing chromium or manganese are loaded into trucks or railcars,
you must use a device at the loadout end of each bulk loader to lessen
fugitive emissions by reducing the distance between the loading arm and
the truck or railcar.
In addition to the above requirements that apply to all facilities,
new and existing facilities with average daily feed production levels
exceeding 50 tpd are required to install and operate a cyclone to
reduce emissions from pelleting and pellet cooling operations. The
average daily feed production level means the average amount of
prepared feed product produced each operating day over an annual
period. The initial determination of the average daily feed production
level is based on the one-year period prior to the compliance date for
existing sources, or the design rate for new sources. Subsequent
average daily feed production levels are then determined annually and
are based on the amount of animal feed product produced in the calendar
year divided by the number of days in which the production processes
were in operation. Facilities with average daily feed production levels
of 50 tpd or less are required to submit production information in
their Notification of Compliance Status report and keep records
documenting their animal feed production levels.
For the pelleting operations at facilities with daily pelleting
production levels exceeding 50 tpd, the final rule requires that PM
emissions be collected and routed to a cyclone that is designed to
achieve 95 percent or greater reduction in PM. There are three ways you
can demonstrate that your cyclone is designed to achieve 95 percent
reduction in PM: (1) Manufacturer specifications that certifying the
cyclone is designed to achieve 95 percent reduction in PM emissions;
(2) certification by a professional engineer or responsible official
that the cyclone is designed to achieve a 95 or greater percent
reduction in PM emissions; or (3) a one-time Method 5 performance test
to demonstrate that the cyclone can achieve a 95 percent or greater
reduction in PM emissions.
In addition, the final rule requires that you establish an
operating parameter range that indicates proper operation of the
cyclone and then monitor this parameter at least once per day. The
specific parameters allowed to be monitored are inlet flow rate, inlet
velocity, pressure drop, or fan amperage. The range that represents
proper operation of the cyclone must be provided by the manufacturer,
determined as part of the engineering calculations demonstrating the
design efficiency, or determined based on monitoring conducted during
the performance test.
The final rule also requires that you maintain the cyclone in
accordance with manufacturer specifications. If manufacturer
specifications are not available, you must develop and follow standard
maintenance procedures.
C. What Are the Compliance Requirements?
For all new and existing sources, compliance with the final
regulation is demonstrated through installation of the required
equipment, adherence to the management practices specified in the rule,
and keeping the required records and submitting the required
notifications and reports described below.
To ensure that the cyclone for the pelleting and pellet cooling
process is operated properly at facilities with average daily feed
production levels exceeding 50 tpd, the final rule requires that the
cyclone be inspected quarterly for corrosion, erosion, or any other
damage that could result in air in-leakage, and that the inlet flow
rate, inlet velocity, pressure drop, or fan amperage be monitored and
recorded daily to ensure that it is being operated in accordance with
specified proper operating range.
The final rule also requires that the devices required at the
loadout end of a bulk loader to lessen fugitive emissions by containing
the unloaded product within the device be inspected monthly to ensure
that they are in good condition.
D. What Are the Notification, Recordkeeping, and Reporting
Requirements?
All new and existing sources are required to comply with some
requirements of the General Provisions (40 CFR part 63, subpart A),
which are identified in Table 1 of the final rule. The General
Provisions include specific requirements for notifications,
recordkeeping, and reporting. Each facility is required to submit an
Initial Notification and a one-time Notification of Compliance Status
according to the requirements in 40 CFR 63.9 in the General Provisions.
The Initial Notification, which is required to be submitted by affected
sources not later than May 5, 2010, or 120 days after you become
subject to the rule, whichever is later, must contain basic information
about the facility and its operations. The Notification of Compliance
Status, which is required to be submitted 120 days after the compliance
date, must contain a statement that the source has complied with all
relevant standards. The Notification of Compliance Status also must
include the inlet flow rate, inlet velocity, pressure drop, or fan
amperage range that constitutes proper operation of the cyclone used to
reduce emissions from the pelleting and pellet cooling operations.
Facilities not required to install and operate cyclones on their
pelleting operations are required to submit documentation of their
initial average daily feed production level.
The final rule requires that records be kept of all notifications
of compliance. The rule requires that records be kept documenting each
inspection of a cyclone and each inspection of a device at the loadout
end of a bulk loader. It also requires that the daily reading of
cyclone inlet flow rate, inlet velocity, pressure drop, or fan amperage
be recorded. In addition, records are required of any actions taken in
response to findings of the inspections or monitoring results outside
the proper operating range. Facilities with average daily feed
production levels of 50 tpd or less are required to keep records of the
annual production and the number of days of operation.
The final rule includes the requirement to prepare, by March 1 of
each year, and submit an annual compliance certification, a copy of
which will need to be maintained on site. This report must contain a
statement of whether the source has complied with all relevant
standards and other requirements of the final rule. If a deviation from
the standard occurred during the annual reporting period, or if an
instance occurred where the cyclone inlet flow rate, inlet velocity,
pressure drop, or fan amperage was outside of the proper operating
range submitted in the Notification of Compliance Status report, this
information is required to be included in the annual report and the
report needs to be submitted to the EPA Administrator or the designated
authority. All records are required to be maintained in a form suitable
and readily available for expeditious review, and kept for at least
five years, the first two of which must be onsite.
[[Page 526]]
V. Summary of Comments and Responses
EPA received 16 public comment letters on the proposed rule. Five
of these comment letters were requests for an extension to the comment
period,\1\ leaving 11 comment letters that provided comments on the
proposed rule. These comments were received from industry
representatives, trade associations, state agencies, and an
environmental organization. Sections V.A through V.G of this preamble
provide responses to the public comments received on the proposed
NESHAP.
---------------------------------------------------------------------------
\1\ We denied the requests for extension by letter, copies of
which are in the docket. These letters explain the reasons for the
denial. These reasons are also provided in section V.A.
---------------------------------------------------------------------------
A. Rulemaking Process
Comment: Several commenters requested that the comment period be
extended by 90 days. The commenters had concerns about the inputs to
the impacts analysis and requested additional time to collect and
provide factual information to the agency about the proposed rule's
provisions and their potential impact.
Response: Due to a court-ordered deadline for promulgation of this
rule (which at the time of proposal was November 16, 2009), we were
unable to extend the comment period in response to these requests.
Moreover, CAA section 307(d) requires that EPA provide a minimum of 30
days for public comment, and we provided that period for public
comment. Furthermore, consistent with section 307(d), the proposed rule
provided the public an opportunity to request a public hearing, and no
party requested such a hearing. See 307(d)(5) (record remains open 30
days after the date of the public hearing).
Comment: One commenter expressed their concerns about the process
that EPA used to develop its proposed national emission standard for
prepared feeds manufacturers. The commenter believes that EPA did not
provide ample due process in developing the proposed rule. The
commenter pointed out that they requested a 90-day extension to the
proposed rule's comment period so that accurate information could be
obtained to respond to the assumptions and estimates made by the
agency. In this request, the commenter indicated that they highlighted
five major areas of the proposed rule in which they believed EPA lacked
critical information that directly affects the provisions within the
proposed rule and its impact on prepared feeds manufacturers. Since EPA
denied their request for extension of the comment period, the commenter
indicated that they were left with what they believe was an
inappropriately short 30-day comment period to respond to a proposed
rule that, if promulgated as drafted, would have very significant
operational and economic impacts on prepared feeds manufacturers. While
cognizant of EPA's court-ordered mandate to issue this national
emission standard, the commenter believes that the agency's actions
related to gathering industry information, timing of the proposed rule
and its response to their request for extension of the comment period
are not indicative of a constructive or meaningful rulemaking process.
Response: EPA complied with the requirements of 307(d) during this
rulemaking process. We engaged industry prior to proposal by meeting
and by telephone to discuss our rulemaking process and the information
we intended to obtain through the 114 survey. EPA strongly disagrees
with the commenters' assertion that EPA did not provide ample due
process in developing the rule.
CAA 307(d) requires EPA to publish a notice of proposed rulemaking
and provide a minimum of 30 days for the public to comment on the
proposal, and EPA complied with this requirement. EPA also identified a
date for public hearing, if such hearing was requested by any member of
the public. No member of the public requested a hearing, and therefore,
a public hearing was not held.
In conclusion, we believe that lines of communication with the
industry were well established and open throughout the rulemaking
process, and that the commenters had ample opportunity to participate.
B. Applicability
Comment: Two commenters stated that the rule should clarify that a
prepared feeds manufacturing facility is a facility that produces
feeds, and not a facility that manufactures feed ingredients. One of
the commenters explained that although feed ingredient companies may
predominantly manufacture ingredients for animal feed and be classified
under the NAICS Code defining the Prepared Feeds Manufacturing source
category (NAICS 311119), they may also produce feed ingredients for
human and/or companion animal consumption.
Response: EPA would like to clarify that, in addition to facilities
that produce animal feed, facilities that manufacture feed ingredients
are part of the prepared feeds manufacturing area source category. The
category was identified in the original section 112(k) emissions
inventory through the use of the Standard Industrial Classification
(SIC) code 2048, Prepared Feeds Manufacturing, except cat and dog feed.
As noted by the commenter, the NAICS code that covers this area source
category is 311119, which is equivalent to the SIC code used in the
original source category definition. The SIC/NAICS code for the source
category includes many segments of the prepared feed industry,
including the production of feed ingredients. Specifically, in addition
to many other segments of the industry, NAICS code 311119, and thus the
prepared feeds manufacturing area source category, includes:
Feed concentrates, animal, manufacturing;
Feed premixes, animal, manufacturing;
Feed supplements, animal (except cat, dog), manufacturing;
Micro and macro premixes, livestock, manufacturing;
Mineral feed supplements (except cat, dog) manufacturing;
and
Mineral supplements, animal (except cat, dog),
manufacturing.
Therefore, since facilities that manufacture feed ingredients are
subject to the rule, we did not make the change suggested by the
commenter. We did, however, make changes to the applicability
provisions and definitions to clarify the various segments of the
prepared feeds industry that are included in the source category and,
therefore, subject to the rule (provided they use chromium or
manganese). These changes include adding a definition of ``animal
feed,'' which includes a list of all the products included under NAICS
code 311119. While we recognize that chromium and manganese are not
used in the production of many of the animal feed products in the
definition, we believe that a complete listing eliminates the confusion
of what types of processes are included in the source category. We
would point out, however, that, even if a facility produces a listed
animal feed product (e.g., earthworm feed and bedding), it is not
subject to the rule if no chromium or manganese is used.
One of the commenters raised the issue of a facility that produces
a product covered by the rule along with other similar products that
would not be covered by the rule. Specifically, the commenter mentions
a facility that produces animal feed ingredients along with feed
ingredients for humans and/or cats and dogs. First, the NAICS code only
includes establishments ``primarily engaged in'' manufacturing animal
feed.
[[Page 527]]
We have revised the definition of ``prepared feed manufacturing
facility'' to incorporate this concept. Specifically, the final rule
contains the following definition.
Prepared feeds manufacturing facility means a facility that is
primarily engaged in manufacturing animal feed. A facility is
primarily engaged in manufacturing animal feed if the production of
animal feed comprises greater than 50 percent of the total
production of the facility on an annual basis. Facilities primarily
engaged in raising or feeding animals are not considered prepared
feeds manufacturing facilities.
Thus, a facility would be a prepared feeds manufacturing facility
subject to the rule if the animal feed ingredients (not including
ingredients for dog, cat, or human feed) make up more than half of its
production. In addition, the final rule specifies that an affected
source at a prepared feeds manufacturing facility only includes the
collection of equipment and activities necessary to produce animal feed
containing chromium or manganese. Therefore, if the ingredients for
human and/or dog and cat feed at a facility primarily engaged in
manufacturing animal feed were produced in equipment that is never used
to produce ``animal feed,'' those production processes would not be
part of the affected source and would not be subject to the
requirements in the rule. While not specifically mentioned by the
commenters, consideration of these applicability issues, along with
comments related to the number of facilities in the source category,
caused us to clarify that prepared feeds manufacturing at farms and
animal feed lots is not part of this source category. Facilities
``primarily engaged'' in raising or feeding animals are listed under
different NAICS codes (e.g., 112210--Hog and Pig Farming, 112112--
Cattle Feedlots, 112111--Beef Cattle Ranching and Farming) and were not
part of the sources that formed the basis for the listing of the
prepared feed manufacturing area source category.
Comment: Five commenters stated that the rule should only apply to
prepared feeds manufacturing facilities that use or emit chromium
compounds or manganese compounds above a specified threshold. The
commenters claimed that such an approach would focus attention on
facilities that are more significant emitters of chromium and manganese
and will avoid requiring extremely small facilities to comply with the
rule with little environmental benefit. The commenters suggested
several different threshold levels. One commenter recommended a
threshold based on established Superfund Amendments and Reauthorization
Act of 1986 (SARA) Tier II threshold quantities (10,000 pounds per
year), while another suggested 2,000 pounds per year based on levels
determined to be insignificant under the title V program. Another
commenter noted that Toxics Release Inventory (TRI) regulations require
a covered facility to report only if it manufactures or processes non-
exempt chromium and/or manganese compounds in quantities exceeding
25,000 pounds per year, and suggested that a threshold be established
at this 25,000 pounds per year level. Still another commenter suggested
a level of 1,000 pounds per day. One of the commenters recommended
that, if such a threshold is established, compounds having a
concentration of less than 1 percent of the chromium compounds or
manganese compounds need not be counted by a facility when determining
whether it has used a sufficient quantity to reach the threshold use
level that establishes whether a facility is subject to the rule's
provisions.
Response: Although several commenters advocated for a usage
threshold for chromium compounds and manganese compounds, below which a
facility would be exempt, we are not adopting any exemptions. Prepared
Feeds Manufacturing is one of the area source categories needed to meet
the section 112(c)(3) requirement that we subject to regulation, (i.e.,
area source categories representing 90 percent of the emissions of
chromium and manganese). We reviewed the listing decision for this area
source category and did not identify any information suggesting that
small sources were not included in the listing decision. As such, we do
not believe we can satisfy our requirement to regulate sources
representing 90 percent of the emissions of Prepared Feeds
Manufacturing urban HAP unless we subject all sources that emit those
HAP to the rule.
We recognize that the Prepared Feeds Manufacturing source category
is comprised of a large number of relatively small facilities. Although
area sources individually may be considered low-emitting sources,
collectively, they are not. The commenter's suggestion fails to address
the requirement of section 112(c)(3), and, as discussed above, we
previously determined that we need to subject the Prepared Feeds
Manufacturing area source category to regulations in order to meet the
requirement that EPA regulate area sources accounting for 90 percent of
the emissions of the 30 urban HAP.
Comment: One commenter suggested that the applicability be changed
to only include facilities that utilize pelletizing operations. The
commenter noted that this would more adequately match the original
group of prepared feeds manufacturers who were surveyed and those in
the same class. The commenter also pointed out that the pelleting and
pellet cooling process is the most significant source of pollutants, as
it is estimated to emit 90 percent or more of the total chromium and
manganese.
Response: The basis for the listing of the area source category was
not limited to emissions from pelleting. Thus, we conclude that the
applicability should remain as proposed.
C. Emission Standards
1. General
Comment: One commenter stated that EPA based the proposed standard
on erroneous and misguided assumptions and estimates of emissions of
chromium compounds and manganese compounds. This commenter had numerous
objections to the impacts analyses (see section V.G) and how these
analyses impacted EPA's decision to regulate this category and specific
emission points.
Response: In section 112(c)(3) of the CAA, EPA is required to list
``sufficient categories or subcategories of area sources to ensure that
area source representing 90 percent of the emissions of the 30 urban
HAP are subject to regulation.'' An area source emissions inventory was
compiled for each of the 30 urban HAP and the area source categories
identified that comprised 90 percent of the emissions of each of these
HAP. For the prepared feeds manufacturing source category, this
inventory was based on data from the 1990 TRI. The TRI is an EPA
inventory of annual emissions self-reported by industry. Based on this
information, EPA determined that chromium compounds emissions and
manganese compounds emissions from prepared feeds manufacturing area
sources needed to be regulated to achieve the 90 percent requirement in
CAA section 112(c)(3). Therefore, the decision to regulate emissions of
chromium compounds and manganese compounds from the prepared feeds
manufacturing industry was based on emissions data submitted directly
by the industry. The information and analyses referred to by the
commenter were prepared to evaluate potential impacts of regulatory
options. This information had no bearing on the basic decision to
develop regulations for the prepared feeds manufacturing area source
category.
The commenter is also incorrect with respect to how emission points
were identified for regulation. They assume that the information
compiled for the
[[Page 528]]
impacts analyses was used as the basis to identify emission points for
regulation. Rather, chromium and manganese emission points were
identified primarily based on information submitted directly by the
industry. Specifically, we conducted a survey of the industry, and
responses were received for over 100 prepared feeds manufacturing
facilities. In the responses to this survey, prepared feeds
manufacturing facilities identified potential emission sources and
reported controls and management practices that were being used. This
information formed the basis for the decisions regarding the emission
points and process areas for which standards were proposed.
In conclusion, the commenter raised several issues on the impacts
analyses (see section V.G below). However, the issues associated with
these analyses did not influence the basic decision to regulate this
source category or the decisions on the specific emission sources that
would be regulated.
Comment: One commenter asserted that, ``* * * The legislative
history of Sec. 112 explains that Congress intended GACT standards to
reflect `methods, practices and techniques which are commercially
available and appropriate for application by sources in the category
considering economic impacts and technical capabilities of the firms to
operate and maintain emission control systems'.''
The commenter also asserted that, although EPA used its discretion
to issue GACT standards and that Sec. 112(d)(5) authorizes EPA to do
so, that decision is subject to administrative law requirements. The
commenter asserted that EPA's decision is arbitrary and capricious
because that decision was not supported with a rational explanation.
Response: As the commenter recognizes, in CAA section 112(d)(5),
Congress gave EPA explicit authority to issue alternative emission
standards for area sources. Specifically, CAA section 112(d)(5), which
is entitled ``Alternative standard for area sources,'' provides:
With respect only to categories and subcategories of area
sources listed pursuant to subsection (c) of this section, the
Administrator may, in lieu of the authorities provided in paragraph
(2) and subsection (f) of this section, elect to promulgate
standards or requirements applicable to sources in such categories
or subcategories which provide for the use of generally available
control technologies or management practices by such sources to
reduce emissions of hazardous air pollutants.
See CAA section 112(d)(5) (Emphasis added).
There are two critical aspects to CAA section 112(d)(5). First, CAA
section 112(d)(5) applies only to those categories and subcategories of
area sources listed pursuant to CAA section 112(c). The commenter does
not dispute that EPA listed the area source category noted above
pursuant to CAA section 112(c)(3). Second, CAA section 112(d)(5)
provides that, for area sources listed pursuant to CAA section 112(c),
EPA ``may, in lieu of'' the authorities provided in CAA section
112(d)(2) and 112(f), elect to promulgate standards pursuant to CAA
section 112(d)(5). CAA Section 112(d)(2) provides that emission
standards established under that provision ``require the maximum degree
of reduction in emissions'' of HAP (also known as maximum achievable
control technology or MACT). CAA section 112(d)(3), in turn, defines
what constitutes the ``maximum degree of reduction in emissions'' for
new and existing sources. See CAA section 112(d)(3).\2\ Webster's
dictionary defines the phrase ``in lieu of'' to mean ``in the place
of'' or ``instead of.'' See Webster's II New Riverside University
(1994). Thus, CAA section 112(d)(5) authorizes EPA to promulgate
standards under CAA section 112(d)(5) that provide for the use of GACT,
instead of issuing MACT standards pursuant to CAA section 112(d)(2) and
(d)(3). The statute does not set any condition precedent for issuing
standards under CAA section 112(d)(5) other than that the area source
category or subcategory at issue must be one that EPA listed pursuant
to CAA section 112(c), which is the case here.\3\
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\2\ Specifically, CAA section 112(d)(3) sets the minimum degree
of emission reduction that MACT standards must achieve, which is
known as the MACT floor. For new sources, the degree of emission
reduction shall not be less stringent than the emission control that
is achieved in practice by the best controlled similar source, and
for existing sources, the degree of emission reduction shall not be
less stringent than the average emission limitation achieved by the
best performing 12 percent of the existing sources for which the
Administrator has emissions information. CAA Section 112(d)(2)
directs EPA to consider whether more stringent emission reductions
(so called beyond-the-floor limits) are technologically achievable
considering, among other things, the cost of achieving the emission
reduction.
\3\ CAA Section 112(d)(5) also references CAA section 112(f).
See CAA section 112(f)(5) (entitled ``Area Sources'' and providing
that EPA is not required to conduct a review or promulgate standards
under CAA section 112(f) for any area source category or subcategory
listed pursuant to CAA section 112(c)(3), and for which an emission
standard is issued pursuant to CAA section 112(d)(5)).
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We disagree with the commenter's assertion that we must provide a
rationale for issuing GACT standards under section 112(d)(5), instead
of MACT standards. Had Congress intended that EPA first conduct a MACT
analysis for each area source category, Congress would have stated so
expressly in section 112(d)(5). Congress did not require EPA to conduct
any MACT analysis, floor analysis or beyond-the-floor analysis before
the Agency could issue a section 112(d)(5) standard. Rather, Congress
authorized EPA to issue GACT standards for area source categories
listed under section 112(c), and that is precisely what EPA has done in
this rulemaking.
Although EPA has no obligation to justify why it is issuing a GACT
standard for an area source category as opposed to a MACT standard, we
did explain at proposal that being able to consider costs and economic
impacts is important when establishing standards for a category like
this with many small sources. Furthermore, EPA must set a GACT standard
that is consistent with the requirements of CAA section 112(d)(5) and
have a reasoned basis for its GACT determination. As explained in the
proposed rule and below. The legislative history supporting section
112(d)(5) provides that GACT is to encompass:
``* * * methods, practices and techniques which are commercially
available and appropriate for application by the sources in the
category considering economic impacts and the technical capabilities
of the firms to operate and maintain the emissions control
systems.''
The discussion in the Senate report clearly provides that EPA may
consider costs in determining what constitutes GACT for the area source
category. Congress plainly recognized that area sources differ from
major sources, which is why Congress allowed EPA to consider costs in
setting GACT standards for area sources under section 112(d)(5), but
did not allow that consideration in setting MACT floors for major
sources pursuant to section 112(d)(3). This important dichotomy between
section 112(d)(3) and section 112(d)(5) provides further evidence that
Congress sought to do precisely what the title of section 112(d)(5)
states, i.e., provide EPA the authority to issue ``alternative
standards for area sources.''
Notwithstanding the commenter's claim, EPA properly issued
standards for the area source categories at issue here under section
112(d)(5), and in doing so provided a reasoned basis for its selection
of GACT for these area source categories. As explained in the proposed
rule, EPA evaluated the control technologies and management practices
that reduce HAP emissions at Prepared Feeds Manufacturing area source
facilities. In its evaluation, EPA used information on pollution
[[Page 529]]
prevention from industry trade associations, and reviewed operating
permits to identify the emission controls and management practices that
are currently used to control volatile and particulate HAP emissions.
We also considered technologies and practices at major and area sources
in similar categories.
Finally, even though not required, EPA did provide a rationale for
why it set a GACT standard in the proposed rule. In the proposal, we
explained that the facilities in the source categories at issue are
already well controlled for the urban HAP for which the source category
was listed pursuant to section 112(c)(3). Consideration of costs and
economic impacts proves especially important for the well-controlled
area sources at issue in this final action. Given the current, well
controlled emission levels, a MACT floor determination, where costs
cannot be considered, could result in only marginal reductions in
emissions at very high costs for modest incremental improvement in
control for the area source category.
Comment: One commenter questioned why EPA was not considering
regulation for all HAP emissions. The commenter explained that, as
documented in the record for this rulemaking, that Prepared Feed
Manufacturing facilities often generate emissions other than manganese,
such as arsenic and arsenic compounds, benzene, beryllium and beryllium
compounds, cadmium and cadmium compounds, chlorine, cobalt and cobalt
compounds, formaldehyde, hexane, hydrochloric acid, hydrogen fluoride,
lead and lead compounds, mercury and mercury compounds, naphthalene,
nickel and nickel compounds, polycyclic organic matter, selenium and
selenium compounds, and toluene. The commenter acknowledged that
management practices and PM controls required by the rule will likely
reduce other metal HAP emissions to some degree; however they indicated
that the Agency failed to quantify this benefit. The commenter also
indicated that EPA should consider controls for other HAPs that will
not be co-controlled with the manganese and chromium.
Response: Section 112(k)(3)(B) of the CAA requires EPA to identify
at least 30 HAP emitted from area sources that pose the greatest threat
to public health in the largest number of urban areas (the ``Urban
HAP'') and identify the area source categories emitting such pollutants
that are or will be listed pursuant to section 112(c)(3). Section
112(c)(3), in relevant part, provides:
The Administrator shall * * *, pursuant to subsection (k)(3)(B)
of this section, list, based on actual or estimated aggregate
emissions of a listed pollutant or pollutants, sufficient categories
or subcategories of area sources to ensure that area sources
representing 90 percent of the area source emissions of the 30
hazardous air pollutants that present the greatest threat to public
health in the largest number of urban areas are subject to
regulation under this section.
Thus, section 112(c)(3) requires EPA to list sufficient categories or
subcategories of area sources to ensure that area sources representing
90 percent of the area source emissions of the 30 urban HAP are subject
to regulation. Section 112(d)(1) requires the Administrator to
promulgate regulations establishing emissions standards for each area
source category of HAP listed for regulation pursuant to section
112(c).
EPA identified the 30 Urban HAP that posed the greatest threat to
public health in the Integrated Urban Air Toxics Strategy (Strategy).
In the Strategy and subsequent Federal Register notices, EPA listed the
area source categories necessary to meet the 90 percent requirement in
section 112(c)(3) and (k)(3)(B), and one of those categories was the
Prepared Feeds Manufacturing area source category.
We have interpreted sections 112(c)(3) and 112(k)(3)(B) together to
require EPA to regulate only those Urban HAP emissions for which an
area source category is listed pursuant to section 112(c)(3), not all
urban HAP or all section 112(b) HAP emitted from a listed area source
category. As stated above, section 112(k)(3)(B) addresses the strategy
to control HAP from area sources in urban areas and the focus of the
strategy as it relates to control of area sources is on the 30 HAP that
pose the greatest threat to public health in the largest number of
urban areas. Section 112(c)(3) specifically references section
112(k)(3)(B) as the basis for selecting area sources for listing to
satisfy the Agency's responsibility for regulating urban HAP emissions
from area sources. Under these provisions, area sources categories are
listed because they emit one or more of the 30 listed Urban HAP and the
Agency has identified the category as one that is necessary to satisfy
the requirement to subject area sources representing 90 percent of the
area source emissions of the 30 urban HAP to regulation.
EPA listed the Prepared Feeds Manufacturing area source category
pursuant to sections 112(c)(3) and 112(k)(3)(B). We must regulate only
the chromium and manganese emissions from the Prepared Feeds
Manufacturing area source category, as these are the urban HAP
emissions for which the category was listed to meet the 90 percent
requirement in sections 112(c)(3) and (k)(3)(B). See 112(c)(3) (EPA
must ``ensure that area sources representing 90 percent of the area
source emissions of the 30 hazardous air pollutants * * * are subject
to regulation.''). We recognize that the source category emits other
section 112(b) HAP, including other urban HAP; however, as stated
above, sections 112(c)(3) and 112(k)(3)(B) do not require the Agency to
regulate the area source category for any HAP other than those for
which the category was listed. As to the other urban HAP emitted from
this category, we have identified other area source categories that
emit these urban HAP and subjecting those area source categories to
regulation will satisfy the requirement to subject to regulation area
sources that account for 90 percent of the area source emissions of
those urban HAP.
While the Agency is not required to regulate all section 112(b) HAP
from area sources listed pursuant to section 112(c)(3) and
112(k)(3)(B), section 112 of the CAA does not preclude EPA from
regulating other HAP from these area sources at our discretion and in
appropriate circumstances. Section 112(d)(5) states that, for area
sources listed pursuant to section 112(c), the Administrator may, in
lieu of section 112(d)(2) ``MACT'' standards, promulgate standards or
requirements ``applicable to sources'' which provide for the use of
GACT or management practices ``to reduce emissions of hazardous air
pollutants.'' This provision does not limit EPA's authority to regulate
only those urban HAP emissions for which the category is needed to
achieve the 90 percent requirement in sections 112(k)(3)(B) and
112(c)(3). In fact, in two other area source rules, in addition to
regulating the urban HAP that were necessary to satisfy the 90 percent
requirement in sections 112(k)(3)(B) and 112(c)(3), we regulated
additional section 112(b) HAP. Specifically, in the chemical
manufacturing area source rule and the paint and allied products area
source rule, although not required, we exercised our discretion to
regulate other section 112(b) HAP beyond the urban HAP for which the
categories were listed under section 112(c)(3) and (k)(3)(B), including
non-urban section 112(b) HAP. The chemical manufacturing area source
rule and the paints and allied products area source rule both involve
specific circumstances which EPA believes justify regulating organic
and metal section 112(b) HAP in
[[Page 530]]
addition to the specific urban HAP needed to meet the 90 percent
requirement in section 112(c)(3) and (k)(3)(B), which served as the
basis for the listing of the categories. In the chemical manufacturing
area source rule, which establishes standards for 9 area source
categories, we regulated such HAP because the emission standards
designed to control the urban HAP for which the categories were listed
were equally effective at removing other urban and non-urban metal and
organic HAP, and demonstrating compliance for total HAP was less
burdensome than demonstrating compliance for speciated HAP for those
sources required to install add-on controls. In the paint and allied
products area source rule, we included emission standards for HAP
beyond the urban HAP for which the category was listed because the
emission standards designed to control those urban HAP would also
control other urban and non-urban metal and organic HAP.
In conclusion, we believe that we have appropriately exercised our
discretion in regulating only the chromium and manganese emissions from
the prepared feeds manufacturing area source category. Therefore, we
did not make any changes in the final rule based on this comment.
2. Housekeeping Management Practices
Comment: One commenter claimed that the Agency's proposed
housekeeping practices are ``overreaching,'' ``unfounded,'' and
``unnecessary.'' The commenter believed that EPA had no basis for
correlating housekeeping practices with ambient air concentrations of
chromium compounds or manganese compounds.
The commenter also had concerns with regard to two of the specific
plant-wide housekeeping requirements proposed. The commenter argued
that the requirement that dust be removed from walls, ledges and
equipment at least once per month is not performance-orientated and
fails to consider individual facility operations or existing management
practices. The commenter also disagreed with the Agency's assertion
that air flow through open doors `stirs-up' dust and causes chromium
compounds and manganese compounds to be emitted into the atmosphere.
Therefore, the commenter opposed the proposed requirement that affected
facilities keep doors shut, as practicable. In addition, the commenter
also expressed concern over the facilities ability to comply with this
requirement as they questioned what would be the parameters set/used to
determine that having a door shut is not practicable.
The commenter noted that prepared feeds manufacturing facilities
already comply with Occupational Safety and Health Administration's
(OSHA) Grain Handling Standard (29 CFR 1910.272) and the Food and Drug
Administration's (FDA's) Current Good Manufacturing Practices (CGMPs)
for Medicated Feeds (21 CFR part 225), and that they are regularly
inspected by Federal and State authorities. Because of this, the
commenter believed that EPA's proposed housekeeping practices are
unnecessary. The commenter provided more detailed descriptions of these
two programs.
Occupational Safety and Health Administration's (OSHA) Grain
Handling Standard (29 CFR 1910.272): This standard requires
facilities to ``develop and implement a written housekeeping program
that establishes the frequency and method(s) determined best to
reduce accumulations of fugitive grain dust on ledges, floors,
equipment and other exposed surfaces'' throughout the entire
facility. OSHA's housekeeping requirements are performance-oriented,
allowing facilities the flexibility to design housekeeping programs
to achieve compliance through methods that are most effective for
individual facilities and operations.
FDA's Current Good Manufacturing Practices (CGMPs) for Medicated
Feeds (21 CFR 225): The vast majority of prepared feed manufacturers
are mandated to comply with CGMPs that require buildings and
equipment be maintained and kept in a reasonably clean and orderly
manner to avoid the potential adulteration of feed products.
Regarding this provision, FDA's compliance program guidance states,
``Accumulated dust or residue will be considered objectionable when
there is a likelihood that the material could contribute to
significant contamination of animal feed.'' Similar to the OSHA
requirement, FDA's housekeeping standard also is performance-
orientated. The CGMP regulations allow facilities to implement those
housekeeping practices that are effective for their individual
operations and achieve compliance with the standard.
Another commenter recommended that instead of the specific
requirements,