National Emission Standards for Hazardous Air Pollutants for Iron and Steel Foundries, 19150-19164 [E7-7203]
Download as PDF
19150
Federal Register / Vol. 72, No. 73 / Tuesday, April 17, 2007 / Proposed Rules
cprice-sewell on PRODPC61 with PROPOSALS
179 and 40 CFR 52.31 because the State
of Nevada has an approved stationary
source permitting program in the
applicable SIP and is not required under
the Clean Air Act to submit its updated
stationary source permitting program to
EPA for approval.6
III. Statutory and Executive Order
Reviews
Under Executive Order 12866 (58 FR
51735, October 4, 1993), this proposed
action is not a ‘‘significant regulatory
action’’ and therefore is not subject to
review by the Office of Management and
Budget. For this reason, this action is
also not subject to Executive Order
13211, ‘‘Actions Concerning Regulations
That Significantly Affect Energy Supply,
Distribution, or Use’’ (66 FR 28355, May
22, 2001). This action merely proposes
to approve or disapprove new or
amended state rules, or to approve or
disapprove requests for rescission of
previously-approved state rules, as
meeting Federal requirements and
imposes no additional requirements
beyond those imposed by state law.
Accordingly, the Administrator certifies
that this proposed rule will not have a
significant economic impact on a
substantial number of small entities
under the Regulatory Flexibility Act (5
U.S.C. 601 et seq.). Because this rule
proposes to approve or disapprove preexisting requirements under state law
and does not impose any additional
enforceable duty beyond that required
by state law, it does not contain any
unfunded mandate or significantly or
uniquely affect small governments, as
described in the Unfunded Mandates
Reform Act of 1995 (Pub. L. 104–4).
This proposed rule also does not have
tribal implications because it will not
have a substantial direct effect on one or
more Indian tribes, on the relationship
between the Federal Government and
Indian tribes, or on the distribution of
power and responsibilities between the
Federal Government and Indian tribes,
as specified by Executive Order 13175
(65 FR 67249, November 9, 2000). This
action also does not have Federalism
implications because it does 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 (64 FR 43255,
6 In
this context, we are referring to NDEP’s
program for issuing pre-construction permits for all
new sources and modifications other than those for
which part C (i.e., PSD) or part D (i.e.,
Nonattainment NSR) of title I of the CAA apply and
for issuing operating permits under title I of the
CAA (not title V).
VerDate Aug<31>2005
14:58 Apr 16, 2007
Jkt 211001
August 10, 1999). This action merely
proposes to approve or disapprove new
or amended state rules, or to approve or
disapprove requests for rescission of
previously-approved state rules,
implementing a Federal standard, and
does not alter the relationship or the
distribution of power and
responsibilities established in the Clean
Air Act. This proposed rule also is not
subject to Executive Order 13045
‘‘Protection of Children from
Environmental Health Risks and Safety
Risks’’ (62 FR 19885, April 23, 1997),
because it is not economically
significant.
In reviewing SIP submissions, EPA’s
role is to approve state choices,
provided that they meet the criteria of
the Clean Air Act. In this context, in the
absence of a prior existing requirement
for the State to use voluntary consensus
standards (VCS), EPA has no authority
to disapprove a SIP submission for
failure to use VCS. It would thus be
inconsistent with applicable law for
EPA, when it reviews a SIP submission,
to use VCS in place of a SIP submission
that otherwise satisfies the provisions of
the Clean Air Act. Thus, the
requirements of section 12(d) of the
National Technology Transfer and
Advancement Act of 1995 (15 U.S.C.
272 note) do not apply. This proposed
rule does not impose an information
collection burden under the provisions
of the Paperwork Reduction Act of 1995
(44 U.S.C. 3501 et seq.).
List of Subjects in 40 CFR Part 52
Environmental protection, Air
pollution control, Intergovernmental
relations, Lead, Particulate matter,
Reporting and recordkeeping
requirements, Sulfur oxides.
Authority: 42 U.S.C. 7401 et seq.
Dated: April 4, 2007.
Jane Diamond,
Acting Regional Administrator, Region IX.
[FR Doc. E7–7285 Filed 4–16–07; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 63
[EPA–HQ–OAR–2002–0034; FRL–8299–8]
RIN 2060–AM85
National Emission Standards for
Hazardous Air Pollutants for Iron and
Steel Foundries
Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
AGENCY:
PO 00000
Frm 00025
Fmt 4702
Sfmt 4702
SUMMARY: EPA is proposing
amendments to the national emission
standards for hazardous air pollutants
for iron and steel foundries. The
proposed amendments add alternative
compliance options for cupolas at
existing foundries and clarify several
provisions to increase operational
flexibility and improve understanding
of the final rule requirements.
DATES: Comments must be received on
or before May 17, 2007, unless a public
hearing is requested by April 27, 2007.
If a hearing is requested on the proposed
rule, written comments must be
received by June 1, 2007.
ADDRESSES: Submit your comments,
identified by Docket ID No. EPA–HQ–
OAR–2002–0034, by one of the
following methods:
• www.regulations.gov: Follow the
on-line instructions for submitting
comments.
• E-mail: a-and-r-docket@epa.gov.
• Fax: (202) 566–1741.
• Mail: National Emission Standards
for Hazardous Air Pollutants for Iron
and Steel Foundries Docket,
Environmental Protection Agency,
Mailcode: 6102T, 1200 Pennsylvania
Ave., NW., Washington, DC 20460.
Please include a total of two copies.
• Hand Delivery: EPA Docket Center,
Public Reading Room, EPA West, Room
3334, 1301 Constitution Ave., NW.,
Washington, DC 20460. Such deliveries
are only accepted during the Docket’s
normal hours of operation, and special
arrangements should be made for
deliveries of boxed information.
Instructions: Direct your comments to
Docket ID No. EPA–HQ–OAR–2002–
0034. EPA’s policy is that all comments
received will be included in the public
docket without change and may be
made available online at https://
www.regulations.gov, including any
personal information provided, unless
the comment includes information
claimed to be confidential business
information (CBI) or other information
whose disclosure is restricted by statute.
Do not submit information that you
consider to be CBI or otherwise
protected through www.regulations.gov
or e-mail. The www.regulations.gov Web
site is an ‘‘anonymous access’’ system,
which means EPA will not know your
identity or contact information unless
you provide it in the body of your
comment. If you send an e-mail
comment directly to EPA without going
through www.regulations.gov, your email address will be automatically
captured and included as part of the
comment that is placed in the public
docket and made available on the
Internet. If you submit an electronic
E:\FR\FM\17APP1.SGM
17APP1
Federal Register / Vol. 72, No. 73 / Tuesday, April 17, 2007 / Proposed Rules
comment, EPA recommends that you
include your name and other contact
information in the body of your
comment and with any disk or CD–ROM
you submit. If EPA cannot read your
comment due to technical difficulties
and cannot contact you for clarification,
EPA may not be able to consider your
comment. Electronic files should avoid
the use of special characters, any form
of encryption, and be free of any defects
or viruses.
Docket: All documents in the docket
are listed in the www.regulations.gov
index. Although listed in the index,
some information is not publicly
available, e.g., CBI or other information
whose disclosure is restricted by statute.
Certain other material, such as
copyrighted material, is not placed on
the Internet and will be publicly
available only in hard copy form.
Publicly available docket materials are
available either electronically through
www.regulations.gov or in hard copy at
the National Emission Standards for
Hazardous Air Pollutants for Iron and
Steel Foundries Docket, EPA/DC, 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.
NAICS code 1
Category
Industry .....................................................
331511
Federal government ..................................
State/local/tribal government ....................
331512
331513
........................
........................
1 North
Mr.
Phil Mulrine, Sector Policies and
Programs Division, Office of Air Quality
Planning and Standards (D243–02),
Environmental Protection Agency,
Research Triangle Park, North Carolina
27711, telephone number: (919) 541–
5289; fax number: (919) 541–3207; email address: mulrine.phil@epa.gov.
FOR FURTHER INFORMATION CONTACT:
SUPPLEMENTARY INFORMATION:
I. General Information
A. Does this action apply to me?
The regulated categories and entities
potentially affected by this proposed
action include:
Examples of regulated entities
Iron foundries. Iron and steel plants. Automotive and large equipment manufacturers.
Steel investment foundries.
Steel foundries (except investment).
Not affected.
Not affected.
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 63.7682 of subpart EEEEE
(NESHAP for Iron and Steel Foundries).
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. What should I consider as I prepare
my comments to EPA?
cprice-sewell on PRODPC61 with PROPOSALS
19151
Do not submit information containing
confidential business information (CBI)
to EPA through www.regulations.gov or
e-mail. Send or deliver information
identified as CBI only to the following
address: Roberto Morales, OAQPS
Document Control Officer (C404–02),
Environmental Protection Agency,
Office of Air Quality Planning and
Standards, Research Triangle Park,
North Carolina 27711, Attention Docket
ID EPA-HQ-OAR–2002–0034. Clearly
mark the part or all of the information
that you claim to be CBI. For CBI
information in a disk or CD ROM that
you mail to EPA, mark the outside of the
disk or CD ROM as CBI and then
identify electronically within the disk or
CD ROM the specific information that is
VerDate Aug<31>2005
14:58 Apr 16, 2007
Jkt 211001
claimed as CBI. In addition to one
complete version of the comment that
includes information claimed as CBI, a
copy of the comment that does not
contain the information claimed as CBI
must be submitted for inclusion in the
public docket. Information so marked
will not be disclosed except in
accordance with procedures set forth in
40 CFR part 2.
C. Where can I get a copy of this
document?
In addition to being available in the
docket, an electronic copy of this
proposed action will also be available
on the Worldwide Web (WWW) through
the Technology Transfer Network
(TTN). Following signature, a copy of
this proposed 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.
D. When would a public hearing occur?
If anyone contacts EPA requesting to
speak at a public hearing concerning the
proposed amendments by April 27,
2007, we will hold a public hearing on
May 2, 2007. If you are interested in
attending the public hearing, contact
Ms. Pamela Garrett at (919) 541–7966 to
verify that a hearing will be held.
PO 00000
Frm 00026
Fmt 4702
Sfmt 4702
E. How is this document organized?
The supplementary information in
this preamble is organized as follows:
I. General Information
A. Does this action apply to me?
B. What should I consider as I prepare my
comments to EPA?
C. Where can I get a copy of this
document?
D. When would a public hearing occur?
E. How is this document organized?
II. Background Information
III. Summary of Proposed Amendments
A. Emissions Limitations
B. Work Practice Standards
C. Operation and Maintenance
Requirements
D. Compliance With Alternative Emissions
Limits
E. Monitoring Requirements
F. Recordkeeping and Reporting
Requirements
G. Definitions
H. Applicability
I. Editorial Corrections
IV. 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
E:\FR\FM\17APP1.SGM
17APP1
19152
Federal Register / Vol. 72, No. 73 / Tuesday, April 17, 2007 / Proposed Rules
I. National Technology Transfer
Advancement Act
J. Executive Order 12898: Federal Actions
to Address Environmental Justice in
Minority Populations and Low-Income
Populations
cprice-sewell on PRODPC61 with PROPOSALS
II. Background Information
The national emission standards for
hazardous air pollutants (NESHAP) for
iron and steel foundries (40 CFR part 63,
subpart EEEEE) establish emissions
limitations and work practice
requirements for the control of
hazardous air pollutants (HAP) from
foundry operations. The NESHAP
implement section 112(d) of the Clean
Air Act (CAA) by requiring all iron and
steel foundries that are major sources of
HAP to meet standards reflecting
application of the maximum achievable
control technology (MACT). The
compliance date for most of the subpart
EEEEE requirements is April 23, 2007.
After publication of the NESHAP (69
FR 21906, April 22, 2004), the American
Foundry Society, the Alliance of
Automobile Manufacturers, and the
Steel Founders’ Society of America filed
petitions for reconsideration of the final
rule. The American Foundry Society
and the Steel Founders’ Society of
America also filed petitions for review
of the final rule (Steel Founders’ Society
of America v. U.S. EPA, No. 04–1190,
DC Cir.) and American Foundry Society
v. U.S. EPA, No. 04–1191, DC Cir.). The
concerns raised by the petitioners
regarding the work practice standards
for scrap management have been
resolved by rule amendments issued on
May 20, 2005 (97 FR 29400). The Steel
Founders’ Society of America petitioned
the court for voluntary dismissal of their
petition for review on March 23, 2006,
and the court granted that petition on
May 2, 2006. Thus, the only challenge
to the NESHAP remaining before the
court is the American Foundry Society
petition for review, No. 04–1191. This
proposed rule addresses the need for
alternative emissions limits for cupolas
at existing foundries and clarification of
other rule requirements. EPA anticipates
that these proposed amendments will
resolve the remaining issues raised by
the petitioners.
These amendments are set out in
Attachment A to a settlement agreement
between EPA and the petitioners that
became final on March 9, 2007. In
accordance with section 113(g) of the
CAA, EPA published a notice of the
proposed settlement agreement (72 FR
1986, January 17, 2007) and provided a
30-day comment period which ended on
February 16, 2007. The settlement
agreement requires that the EPA
VerDate Aug<31>2005
14:58 Apr 16, 2007
Jkt 211001
Administrator sign proposed
amendments no later than April 9, 2007.
In addition, since publication of the
final rule, we have identified a few
minor editorial errors requiring
correction. Rather than publish a
separate notice of corrections, we are
including those changes along with the
proposed amendments.
III. Summary of Proposed Amendments
A. Emissions Limitations
1. New Compliance Options for Cupola
Metal Melting Furnaces
Section 63.7690(a)(2) of the NESHAP
establishes HAP emissions limits for
cupola metal melting furnaces at
existing iron and steel foundries. The
owner or operator may elect to comply
with a limit of 0.006 grains per dry
standard cubic foot (gr/dscf) of
particulate matter (PM) or 0.0005 gr/dscf
of total metal HAP. The PM emissions
limits for cupolas were based on an
evaluation of the average performance
achieved by the top 12 percent of the
cupola emissions sources (i.e., the
‘‘MACT floor’’). Because baghouses (the
technology on which the MACT floor
performance was based) are generally
designed to meet a specified outlet
concentration limit and because EPA
Method 5 (40 CFR part 60, appendix A)
directly determines concentration, a
concentration-based emissions limit was
selected for inclusion in the rule. The
alternative concentration-based
emissions limit expressed as total metal
HAP provided equivalent metal HAP
emissions reductions as the MACT floor
PM emissions limit. We documented the
determination of these emissions limits
in a memorandum titled,
‘‘Determination of the MACT Floor
Metal HAP Emission Limits for Iron and
Steel Foundries’’, which is included in
the docket for the final rule (Docket Item
No. EPA–HQ–OAR– 2002–0034–0239).
As part of our discussions with the
petitioners on technical issues, we
recognized the need for an equivalent
mass-based emissions limit for cupola
melting furnaces to allow the use of
control technologies that are designed
on a mass removal basis rather than an
outlet concentration basis. We reviewed
the data previously identified for the top
12 percent of cupola emissions sources
as well as the 6th percentile unit on
which the promulgated emissions limit
was based. These data indicate that the
equivalent mass PM emissions rate for
a baghouse operating at the MACT floor
emissions limit for cupolas at existing
sources (0.006 gr/dscf) is 0.10 pound per
ton (lb/ton) of metal charged. In terms
of total metal HAP, the MACTequivalent mass emissions rate for
PO 00000
Frm 00027
Fmt 4702
Sfmt 4702
cupolas at existing sources is 0.008 lb/
ton. We documented the determination
of these mass-based emissions limits in
a memorandum titled, ‘‘Determination
of a MACT Floor Equivalent Emission
Limit for Cupola Melting Furnaces,’’
which is included in the docket for this
rulemaking (Docket Item EPA–HQ–
OAR–2002–0034–0223). Therefore, we
are proposing to amend the emissions
limits in 40 CFR 63.7690(a)(2) for
cupolas at existing sources to add
alternative limits of 0.10 lb/ton of PM or
0.008 lb/ton of total metal HAP.
2. Fugitive Emissions Opacity Limit
Some of the petitioners requested that
we revise the opacity limit for fugitive
emissions in 40 CFR 63.7690(a)(7) to
clarify that the limit does not apply to
fugitive emissions that are unrelated to
emissions sources subject to the
NESHAP. According to the petitioners,
the rule could be interpreted to apply to
fugitive emissions from foundry-related
operations not subject to the rule or
operations in other source categories
that may be co-located in foundries.
Some foundries are co-located with
other manufacturing processes that are
housed in separate buildings. We did
not intend to set emissions limitations
for these co-located operations.
Therefore, we are clarifying that the
opacity emissions limitations apply
only to buildings that house iron and
steel foundry emissions sources. If
nonfoundry operations are housed in
the same building as the foundry
operations, the foundry must comply
with the opacity limits for that building.
3. Triethylamine Emissions Limit
In response to the petitioners’
suggestion, we are proposing to clarify
the language of the emissions limit for
triethylamine (TEA) in § 63.7690(a)(11)
by replacing the reference to test
conditions (‘‘as determined when
scrubbing with fresh acid solution’’)
with the phrase ‘‘according to the
performance test procedures in
§ 63.7732(g)’’ since § 63.7732(g) contains
the requirement to conduct the test
when scrubbing with fresh acid
solution.
Although the existing NESHAP
primarily address the control of HAP
metals, there are potential opportunities
for foundries to reduce emissions of
other HAP such as TEA through the use
of low-HAP binders and other pollution
prevention (P2) techniques. Current
information indicates that these P2
methods show promise, but they are not
appropriate for all foundries or casting
methods. And, in some cases, it can be
quite costly for the foundry to
incorporate P2 methods into their
E:\FR\FM\17APP1.SGM
17APP1
Federal Register / Vol. 72, No. 73 / Tuesday, April 17, 2007 / Proposed Rules
overall process. EPA encourages
foundries to explore the various P2
options available and use them when
appropriate and cost-effective to further
reduce their HAP footprint.
B. Work Practice Standards
1. Capture and Collection Systems
Section 63.7690(b)(1) of the NESHAP
requires the owner or operator of an iron
or steel foundry to install, operate, and
maintain a capture and collection
system for all emissions sources subject
to a limit or standard for volatile organic
hazardous air pollutants (VOHAP) or
TEA in 40 CFR 63.7690(a)(8) through
(11). One petitioner was concerned that
this provision could be construed to
require capture and collection systems
for electric arc furnaces and electric
induction furnaces, even though these
furnaces are not directly subject to a
VOHAP limit. According to the
petitioner, the scrap certification and
inspection/selection requirements in 40
CFR 63.7700 could be understood as
work practice standards to limit
organics from entering electric arc
furnaces and electric induction
furnaces. It could be inferred that a
‘‘standard’’ limiting VOHAP does exist
for these furnaces and therefore, a
capture and collection system is
required. A similar concern exists for
foundries that decide to meet the work
practice requirement in 40 CFR
63.7700(e) instead of the VOHAP
emissions limit in 40 CFR 7690(a)(9).
The petitioner requests that EPA
confirm that the scrap certification and
inspection/selection requirements are
not considered VOHAP work practice
standards which would necessitate a
capture and collection system.
It is our intent that the requirements
for capture and collection systems apply
to emissions sources subject to an
emissions limit but not to an emissions
source subject to work practice
standards. A capture and control system
that routes emissions to an add-on
control device is not needed because the
work practice acts to reduce or prevent
the release of emissions. In response to
the petitioner’s concerns, we are
proposing to clarify the requirement in
§ 63.7690(b)(1) by deleting the reference
to ‘‘standard’’.
cprice-sewell on PRODPC61 with PROPOSALS
2. Scrap Management
Section 63.7700(a) of the NESHAP
establishes work practice standards to
minimize the organics and HAP metals
in charge materials. The owner or
operator must comply with certification
requirements in § 63.7700(b) or operate
according to a scrap selection and
inspection plan required in § 63.7700(c).
VerDate Aug<31>2005
14:58 Apr 16, 2007
Jkt 211001
One commenter requested that the work
practice standards specify that the
requirements for the certification and
the written plan specify ‘‘chlorinated’’
plastics. Plastics were included in the
list of undesirable scrap material
primarily because certain types of
plastics, such as polyvinyl chloride,
could lead to the formation of dioxins.
We did not intend to make certain metal
components, such as Quiet Steel(),
that contain some plastics that cannot
be removed from the scrap unrecyclable.
Recycling these materials in foundries is
environmentally preferable to
landfilling these materials. Therefore, to
clarify our intent, we now specify that
it is ‘‘chlorinated’’ plastics that are to be
removed from the scrap material.
The petitioner also objected to the
requirement in 40 CFR 63.7700(c)(2) for
the owner or operator to obtain and
maintain onsite a copy of the
procedures used by the scrap supplier
for either removing accessible mercury
switches or for purchasing automobile
bodies that have had the switches
removed. According to the petitioner, it
is difficult for some plants to obtain
such written procedures from scrap
suppliers. In this case, the plant should
be able to document their attempts to
obtain a copy of the procedures. The
proposed amendments include an
alternative procedure that allows the
plant to document their attempts to
obtain a copy of the procedures from the
scrap suppliers servicing their area. We
note, however, that under 40 CFR
63.7700(c)(2) the materials acquisition
program must specify that the scrap
supplier remove accessible mercury
switches from the trunks and hoods of
any automotive bodies contained in the
scrap in addition to accessible lead
components such as batteries and wheel
weights. It is incumbent on the foundry
owner or operator to communicate these
specifications to their scrap suppliers.
3. Scrap Preheaters
Section 63.7700(e) of the rule
establishes requirements for scrap
preheaters at an existing iron and steel
foundry. The owner or operator must
install, operate, and maintain a gas-fired
preheater according to 40 CFR
63.7700(e)(1) or charge only certain
materials according to 40 CFR
63.7700(e)(2). One petitioner was
concerned that the language in 40 CFR
63.7700(e)(1) could be interpreted to
require foundries to install gas-fired
preheaters, even when not necessary for
foundry operations. It was not our intent
to mandate installation of preheaters,
but rather to establish requirements for
those existing facilities that use scrap
preheaters in lieu of selecting the option
PO 00000
Frm 00028
Fmt 4702
Sfmt 4702
19153
in 40 CFR 63.7700(e)(2). Therefore, we
are proposing to clarify § 63.7700(e)(1)
by deleting the word ‘‘install’’. Instead,
the owner or operator would be required
to operate and maintain a gas-fired
preheater where the flame directly
contacts the scrap charged.
C. Operation and Maintenance
Requirements
One petitioner suggested that the
requirement in 40 CFR 63.7710(b) for an
operation and maintenance plan would
be better understood if it clarified the
emissions sources subject to the plan
requirements. The proposed
amendments clarify that the
requirement applies to each capture and
collection system and control device for
an emissions source subject to a PM,
metal HAP, TEA, or VOHAP emissions
limit in 40 CFR 63.7690(a).
D. Compliance With Alternative
Emissions Limits
The existing NESHAP establishes PM
emissions limits and alternative
emissions limits expressed in total
metal HAP for cupolas and other
foundry processes. In response to
requests by the petitioners, we are
proposing amendments to 40 CFR
63.7732, 40 CFR 63.7690, and 40 CFR
63.7734 to clarify our original intent to
allow foundries to demonstrate
compliance with any of the applicable
alternative emissions limitations that
are provided for a specific emissions
source. When multiple alternative
emissions limitations are provided for a
specific emissions source, iron and steel
foundries can demonstrate initial
compliance with any of the alternative
limits; they are not required to comply
with all of the alternative emissions
limits at any one time. We are also
clarifying a facility’s ability to change
their selected compliance alternative
and the procedures needed to effect that
change. However, regarding continuous
compliance, the facility is expected to
continuously comply with the
alternative emissions limit that was
selected as their compliance option as
demonstrated in their most recent
performance test. The facility may
choose to alter their selected alternative
but must continue to comply with the
previously selected alternative until
they successfully demonstrate
compliance with the new alternative
emissions limitation.
We are also proposing requirements
for determining initial compliance for
cupola melting furnaces at existing iron
and steel foundries that are subject to
the new mass rate emissions limit.
Revisions to 40 CFR 63.7732(b) and (c)
would include new equations for
E:\FR\FM\17APP1.SGM
17APP1
19154
Federal Register / Vol. 72, No. 73 / Tuesday, April 17, 2007 / Proposed Rules
determining PM or total metal HAP
emissions from cupolas in the lb/ton
format. Other amendments to 40 CFR
63.7732(b) and (c) would clarify test
method and emissions source sampling
requirements.
cprice-sewell on PRODPC61 with PROPOSALS
1. Single Performance Test for Control
Devices Serving Multiple Units
Section 63.7734 of the NESHAP
requires iron and steel foundries to
demonstrate initial compliance with PM
emissions limits by conducting a
performance test for each process unit
according to the procedures in 40 CFR
63.7732. One petitioner pointed out that
a common emissions control system
may serve two similar or identical
cupolas or serve multiple furnaces or
process units. According to the
petitioner, a requirement for separate
tests of the control device while the
emissions sources are operating is
redundant and imposes unnecessary
costs because the control device should
perform the same on each identical
furnace.
We acknowledge that there are certain
control device configurations that we
cannot fully address within the rule
requirements. These situations are best
evaluated on a case-by-case basis.
Therefore, we are proposing to resolve
the petitioner’s concern by adding a
new provision to the performance test
requirements. The proposed amendment
requires foundries to submit a sitespecific test plan for the situation
described by the petitioner or other
situations not expressly considered in
40 CFR 63.7734. The site-specific test
plan, which is subject to approval by the
Administrator, would explain the
procedures that would be followed
during the test, such as operation of the
unit or units at the maximum operating
condition of the control system. The
Administrator or delegated authority
would determine on a case-by-case basis
if one representative furnace/control
device configuration may be tested.
2. Sampling Procedure for Electric Arc
Furnaces, Electric Induction Furnaces,
and Scrap Preheaters
One petitioner objected to the
sampling instructions in 40 CFR
63.7732(c)(4) and (5) for electric arc and
electric induction metal melting
furnaces (when metal is being melted)
and scrap preheaters (when scrap is
being preheated) as inappropriate
restrictions on performance testing.
Many operations that occur during the
furnace melting process are considered
part of typical operation. Scrap
preheaters operate on a batch basis and
do not heat scrap for extended periods
of time. It is not practical to start and
VerDate Aug<31>2005
14:58 Apr 16, 2007
Jkt 211001
stop tests for these emissions sources
over the course of a heat until the
required sampling time is accumulated.
According to the petitioner, testing
during all phases of operations is
consistent with the requirement in
§ 63.6(f)(2)(iii)(A) of the NESHAP
General Provisions (40 CFR part 63,
subpart A), which state that a
performance test must be conducted
under representative operating
conditions of the source.
In response to these concerns, we are
proposing to clarify that the initial
compliance demonstrations for electric
arc metal melting furnaces, electric
induction metal melting furnaces, and
scrap preheaters should be conducted
under normal production conditions.
The emissions limitations derived for
these sources used data for various
production cycles, including charging,
melting, back-charging, and tapping. As
the MACT floor emissions limitation
was based on various production cycles
and because significant PM and metal
HAP emissions can occur from these
other production cycles, the
promulgated requirement to test only
during melting is being amended to
more accurately align the testing
requirements to the testing procedures
used as the basis of the MACT
emissions limitation. The proposed
amendments require sampling during
normal operating conditions, which
may include charging, melting, alloying,
refining, slagging, and tapping (for a
furnace) or charging, heating, and
discharging (for a scrap preheater).
3. Minimum Sampling Volume for Total
Metal HAP
One petitioner pointed out that it was
unnecessary to specify the minimum
sample volume for test runs by EPA
Method 29 (40 CFR part 60, appendix A)
because the method already includes a
requirement. The proposed amendments
remove this requirement from 40 CFR
63.7732(c)(2).
4. Opacity Test
Section 63.7732(d) of the existing rule
establishes the requirements for opacity
tests. The proposed amendments
instruct the certified observer how to
take opacity readings by Method 9 (40
CFR part 60, appendix A) for a building
that has many openings. This issue was
not addressed in the NESHAP. Under
the proposed amendments, the observer
would be allowed to take readings from
a limited number of openings or vents
that appear to have the highest opacities
instead of making observations for each
opening or vent from the building or
structure. Alternatively, a single
observation for the entire building
PO 00000
Frm 00029
Fmt 4702
Sfmt 4702
would be allowed if the fugitive release
points afford such an observation.
Section 63.7732(d)(2) requires that
opacity observations to demonstrate
compliance with the fugitive emissions
opacity standards in 40 CFR
63.7690(a)(7) overlap with the PM
performance tests. One petitioner stated
that it is not feasible for opacity
observations to overlap with PM
performance tests in all cases because
subsequent tests are required every 6
months for opacity and every 5 years for
PM emissions. The petitioner raised the
concern that the rule could have been
read to require a PM performance test
during each opacity test; however, this
was not our intent. In response to the
petitioner’s concern, we are proposing
amendments to 40 CFR 63.7732(d)(2) to
clarify that opacity tests are to be
conducted during PM performance tests,
but that PM performance tests are not
required to occur during the semiannual
opacity tests.
5. Alternative Test Method
Section 63.7732(g)(v) of the NESHAP
requires the use of EPA Method 18 (40
CFR part 60, appendix A) to determine
the triethylamine (TEA) concentration
of gases from the TEA cold box mold or
core making line. One petitioner
requested EPA to allow an alternative to
Method 18 because the detection limit
of Method 18, which is approximately 1
part per million by volume (ppmv), is
not significantly less than the emissions
limit. The petitioner believed this could
make compliance determinations
problematic. According to the
petitioner, operators will need to use the
alternative silica gel adsorption tube
sampling technique in section 8.2.4 of
Method 18 to achieve lower detection
limits, but that not all facilities will
know to specify the alternative sampling
techniques to their testing contractors.
The commenter stated that the
alternative methodology is equivalent to
National Institute of Occupational
Safety and Health (NIOSH) Method
2010 and requested that the rule allow
the NIOSH method as an acceptable
alternative. If the rule specifies the
NIOSH method as an alternative,
facilities can ensure that proper
sampling techniques are used to achieve
the low detection limits.
We agree that NIOSH Method 2010 is
an acceptable and equivalent sampling
alternative to EPA Method 18. However,
the NIOSH method does not include
quality assurance performance
requirements. Therefore, we are
proposing NIOSH Method 2010,
‘‘Amines, Aliphatic’’ (incorporated by
reference-see § 63.14) as an acceptable
alternative to EPA Method 18 (40 CFR
E:\FR\FM\17APP1.SGM
17APP1
Federal Register / Vol. 72, No. 73 / Tuesday, April 17, 2007 / Proposed Rules
part 60, appendix A) provided the
performance requirements outlined in
section 13.1 of EPA Method 18 are
satisfied. Method 2010 is included in
the NIOSH Manual of Analytical
Methods (4th edition, NIOSH
Publication 94–113, August 1994). The
manual is available from the
Government Printing Office and the
National Technical Information Service
(NTIS), NTIS publication no.
PB95154191. The NIOSH method may
also be found on the NIOSH Web site at
the following address: www.cdc.gov/
niosh/nmam/method-4000.html.
E. Monitoring Requirements
7. Repeat Performance Tests
1. Baghouse Monitoring Requirements
Section 63.7740(b) of the existing
NESHAP requires a bag leak detection
system for each negative pressure
baghouse and for each positive pressure
baghouse equipped with a stack where
the baghouse is applied to meet any PM
or total metal HAP emissions limitation
in subpart EEEEE. This provision also
requires inspection of each baghouse
according to the requirements in 40 CFR
63.7740(b) (1) through (8). One
petitioner states that the final rule
appears to omit any monitoring
requirements for positive pressure
baghouses not equipped with a stack.
Although these units are not required to
install a bag leak detection system, we
intended to require the visual
inspection of these positive pressure
baghouses to ensure their proper
performance. Therefore, we are
proposing amendments to clarify our
original intent to require monitoring
inspections of positive baghouses that
are not equipped with a stack. The
proposed amendments to 40 CFR
63.7740(b) clarify the text to ensure that
the requirements in this paragraph for
installing and using a bag leak detection
system apply only to negative pressure
baghouses and positive pressure
baghouses equipped with a stack. The
inspection requirements would be
separated and placed in a new
paragraph (c) and clarified to state that
the inspection requirements apply to
each baghouse regardless of type. The
proposed amendments to 40 CFR
63.7740 also renumber the paragraphs
which follow new paragraph (c). Similar
clarifications would be made to the
requirements for demonstrating
continuous compliance in 40 CFR
63.7743(c).
One petitioner requested EPA to
clarify that demonstrating compliance
by one method does not preclude a
demonstration of compliance using an
alternative method at a later date. EPA
agrees that a plant may elect to
demonstrate compliance with an
alternative emissions limit during the
repeat performance tests conducted at
least every 5 years. Furthermore, the
plant may elect to conduct a
performance test earlier than 5 years in
order to change an operating limit or to
demonstrate compliance with a different
alternative emissions limit. The
proposed amendments clarify these
testing options in amendments to 40
CFR 63.7731(a). A test conducted for the
purpose of changing operating limits is
subject to notification requirements in
40 CFR 63.7750(d).
2. Demonstration of Initial Compliance
With Bag Leak Detection System
Operation and Maintenance
Requirements
Section 63.7736(c) of the existing
NESHAP instructs the owner or operator
how to demonstrate initial compliance
with the requirements for bag leak
detection systems. Under 40 CFR
63.7736(c)(1), the owner or operator
must submit the bag leak detection
system monitoring plan to the
Administrator for approval according to
the requirements in 40 CFR 63.7710(b).
One petitioner requested EPA to clarify
this provision because the requirement
could be interpreted to necessitate
submission of the monitoring plan
independent of the operation and
maintenance plan. Our intent in the
existing rule was to include the bag leak
6. Procedures for Establishing Operating
Limits
cprice-sewell on PRODPC61 with PROPOSALS
One petitioner pointed out that the
procedures for establishing control
device operating limits in 40 CFR
63.7733(b) through (d) should not
instruct operators to compute and
record the 3-hour average parameter
value because some sampling durations
are based on sampling volumes which
do not correspond to a 3-hour period.
This requirement could be
misinterpreted to require performance
testing over a period of at least 3 hours.
We originally intended that the
performance test consist of three 1-hour
tests runs, and that the control device
parameter operating limit would be
based on the average of these data.
However, there are instances where the
duration of the sampling runs may be
greater than 1 hour. The proposed
amendments delete the reference to the
3-hour average from the test procedures
and clarify that the operator is to
compute and record the average
operating parameter value for each valid
sampling run in which the applicable
limit is met.
VerDate Aug<31>2005
14:58 Apr 16, 2007
Jkt 211001
PO 00000
Frm 00030
Fmt 4702
Sfmt 4702
19155
detection system information in the
operation and maintenance plan to
streamline the approval process and
avoid the administrative costs
associated with a separate submission.
In addition, having one integrated plan
provides a centralized reference tool for
control device operation and
maintenance requirements. The
proposed amendments to 40 CFR
63.7736(c)(1) clarify the requirement to
submit the bag leak system monitoring
information to the Administrator within
the written operation and maintenance
plan for approval according to the
requirements in § 63.7710(b).
3. Installation, Operation, and
Maintenance Requirements for Monitors
One petitioner requested that EPA
revise the requirements for operation
and maintenance of continuous
parameter monitoring systems (CPMS)
to more clearly describe the inspection
requirements. Under the operation and
maintenance requirements for flow
measurement devices in 40 CFR
63.7741(a)(1)(iv), the owner or operator
must perform monthly inspections of all
flow sensor components for integrity, all
electrical connections for continuity,
and all mechanical connections for
leakage. The proposed amendments
change this provision to require a
monthly visual inspection of all
components, including all electrical and
mechanical connections for proper
functioning. The same changes would
be made to the monthly inspection
requirements for other types of
monitoring devices in
§§ 63.7741(a)(2)(vi), (c)(1)(vi), (c)(2)(iv),
(d)(8), and (e)(2)(iv).
We are proposing these changes in
response to the concerns expressed by
one petitioner who explained that the
changes are needed to ensure the ability
of a facility to comply on a monthly
basis. According to the petitioner, the
ability of a facility to specifically
inspect for ‘‘integrity’’, ‘‘continuity’’ and
‘‘leakage’’ depends on where the
components are located, but a facility
would be able to readily determine
proper functioning. One the facility
determines that a connection is not
working properly, additional steps can
be taken to address the problem, which
may include removing a barrier to allow
access to the connection. In addition,
testing of the electrical connections for
continuity is not necessary when
indicators are routinely used to show
whether the current is flowing. A visual
inspection is sufficient to ensure that
current is flowing to each electrical
connection.
The proposed amendments also revise
the requirement for pressure
E:\FR\FM\17APP1.SGM
17APP1
19156
Federal Register / Vol. 72, No. 73 / Tuesday, April 17, 2007 / Proposed Rules
measurement devices in 40 CFR
63.7741(a)(2)(iii) and 40 CFR
63.7741(c)(1)(iv) for a ‘‘daily check of
the pressure tap for pluggage.’’ We are
proposing to require a daily check for
pluggage when using a regular pressure
tap and a monthly check when using a
non-clogging pressure tap. Less frequent
checks for non-clogging pressure taps
would encourage use of newer
technology and provide an inspection
frequency commensurate with the
operation of a non-clogging pressure
tap. The proposed amendments also
clarify the requirements for pressure
measurement devices in 40 CFR
63.7741(a)(2)(iv) and 40 CFR
63.7741(c)(1)(iv) to allow the use of a
manometer or equivalent device for
calibrations.
cprice-sewell on PRODPC61 with PROPOSALS
F. Recordkeeping and Reporting
Requirements
The proposed amendments clarify
two of the recordkeeping requirements
in 40 CFR 63.7752(a)(4). The
requirement for the annual quantity of
chemical binder or coating materials
used to make molds and cores would be
revised to require the annual quantity of
chemical binder or coating materials
used to coat or make molds and cores.
We inadvertently omitted the word
‘‘coat’’ from the original rule language.
The requirement for records of the
annual quantity of HAP used would
state that records are required of the
annual quantity of HAP used in these
chemical binder or coating materials at
the foundry, as calculated from the
recorded quantities and chemical
compositions (from Material Data Safety
Sheet or other documentation). This
proposed amendment clarifies that the
HAP records requirement is specific to
the chemicals used in the mold and
core-making and coating operations and
not to other HAP materials used at the
foundry such as solvents used to clean
or degrease equipment.
Proposed amendments to the
reporting requirements allow foundries
to report the results of the semiannual
opacity tests within the semiannual
reports rather than having to submit
these semiannual documents separately.
This change would reduce the
administrative costs associated with
submission of separate reports. Other
proposed amendments to the reporting
requirements clarify the requirements
for an immediate startup, shutdown,
and malfunction report by adding the
same language used in 40 CFR
63.10(d)(5)(ii). The proposed
amendments require an immediate
report if you had a startup, shutdown,
or malfunction and the source exceeded
VerDate Aug<31>2005
14:58 Apr 16, 2007
Jkt 211001
any applicable emissions limitation in
40 CFR 63.7690.
G. Definitions
We are proposing to add definitions of
the terms ‘‘off blast’’ and ‘‘on blast’’ to
40 CFR 63.7765. These definitions
would clarify that blast conditions used
to bring the cupola up to operating
temperature during start-up are not
covered by the VOHAP parameter
operating limit in 40 CFR 63.7690(b)(3).
The existing parameter operating limit
requires the foundry to operate each
combustion device applied to emissions
from a cupola that is subject to the
VOHAP emissions limit so that the 15minute average combustion zone
temperature does not fall below a
certain level. The operating limit states
that periods when the cupola is off-blast
and for 15 minutes after going on-blast
from an off-blast condition are not
included in the 15-minute average
combustion zone temperature. The term
‘‘off blast’’ would be defined as those
periods of cupola operation when the
cupola is not actively being used to
produce molten metal. Off-blast
conditions include cupola startup
procedures as defined in the startup,
shutdown, and malfunction plan. Offblast conditions also include idling
conditions when the blast air is turned
off or down to the point that the cupola
does not produce additional molten
metal. The term ‘‘on blast’’ would mean
those periods of cupola operation when
combustion (blast) air is introduced to
the cupola furnace and the furnace is
capable of producing molten metal. On
blast conditions are characterized by
both blast air introduction and molten
metal production.
The petitioners also raised the
concern that only a limited number of
metal constituents were evaluated when
assessing the total metal HAP emissions
limits. They noted that not all
constituents for which EPA Method 29
(40 CFR part 60, appendix A) is
applicable are HAP. They also sought
clarification on how to calculate the
total metal HAP if certain constituents
were below the analytical detection
limit.
The evaluation of the total metal HAP
emissions limits actually included most
Method 29 HAP constituents, although
it did not include phosphorus. The
evaluation did not include detection
limits or other non-zero values for metal
constituents measured below detection
limit. To address the petitioners’
concerns, we are proposing to revise the
definition of ‘‘total metal HAP’’ to
specify the analytes to be included and
how non-detect values are to be used in
calculating the total metal HAP
PO 00000
Frm 00031
Fmt 4702
Sfmt 4702
quantity. The proposed definition is
based on the analytes and methods used
to derive the total metal HAP
alternative. The definition of ‘‘total
metal HAP’’ would be the sum of the
concentrations of antimony, arsenic,
beryllium, cadmium, chromium, cobalt,
lead, manganese, mercury, nickel, and
selenium as measured by EPA Method
29 (40 CFR part 60, appendix A). Only
the measured concentration of the listed
analytes that are present at
concentrations exceeding one-half of the
quantification limit of the analytical
method are used in the sum. If any of
the analytes are not detected or are
detected at concentrations less than onehalf the quantification limit of the
analytical method, the concentration of
those analytes is assumed to be zero for
the purposes of calculating the total
metal HAP for this subpart.
We are also proposing to clarify the
definition of ‘‘scrap preheater’’ to
differentiate scrap dryers that are used
solely to remove moisture from the
scrap metal from scrap preheaters. Scrap
preheaters are used to preheat the metal
scrap and reduce the energy required to
effect melting. Most scrap preheaters
heat the scrap metal to 400 degrees
Fahrenheit or higher while scrap dryers
operate at lower temperatures and are
used solely to remove moisture from the
scrap metal as a safety consideration
when operating an electric induction
furnace. Because of the lower operating
temperatures, we do not believe that
scrap dryers are a significant potential
source for VOHAP emissions. We are
proposing to amend the definition of
‘‘scrap preheater’’ to state that scrap
dryers, which are used solely to remove
water from metal scrap that does not
contain any volatile impurities or other
tramp materials, are not considered to
be scrap preheaters for purposes of this
subpart.
H. Applicability
One of the petitioners asked EPA to
reference the CAA or NESHAP General
Provisions definition of ‘‘major source’’
in 40 CFR 63.7681 (Am I subject to this
subpart?). We are proposing to add a
reference to 40 CFR 63.2 as requested by
the commenter. This addition would
clarify that when we refer to a ‘‘major
source’’ of hazardous air pollutants in
40 CFR 63.7681, we are referring to the
definition of major source in 40 CFR
63.2, and not, for example, to the
definition of major source in 40 CFR
51.166.
I. Editorial Corrections
We are proposing to correct a
grammatical error in 40 CFR 63.7710(b),
which should refer to an emissions
E:\FR\FM\17APP1.SGM
17APP1
Federal Register / Vol. 72, No. 73 / Tuesday, April 17, 2007 / Proposed Rules
source subject to a (rather than ‘‘an’’)
PM, metal HAP, TEA, or VOHAP
emissions limit in 40 CFR 63.7690(a). A
comma would be added to 40 CFR
63.7734(a)(11). The words ‘‘as possible’’
were inadvertently omitted from 40 CFR
63.7741(a)(2)(i) and would be added.
The proposed amendments also correct
a misspelling of the word ‘‘calendar’’ in
40 CFR 63.7700(c)(3)(iii).
IV. Statutory and Executive Order
Reviews
A. Executive Order 12866: Regulatory
Planning and Review
Under Executive Order 12866 (58 FR
51735, October 4, 1993), this action is a
‘‘significant regulatory action’’ because
it may ‘‘raise novel legal or policy
issues.’’ Accordingly, EPA submitted
this action to the Office of Management
and Budget (OMB) for review under
Executive Order 12866 and any changes
made in response to OMB
recommendations have been
documented in the docket for this
action.
cprice-sewell on PRODPC61 with PROPOSALS
B. Paperwork Reduction Act
This action does not impose any new
information collection burden. The
proposed amendments add a new
compliance alternative, allow a new
alternative test method, and clarify
requirements in the existing rule. One
proposed amendment to the baghouse
monitoring requirements clarifies our
original intent to require inspections of
positive pressure baghouses not
equipped with a stack. No new burden
is associated with this proposed
requirement because the burden was
included in the approved information
collection request (ICR) for the existing
rule. The OMB has previously approved
the information collection requirements
contained in the existing regulation (40
CFR part 63, subpart EEEEE) under the
provisions of the Paperwork Reduction
Act, 44 U.S.C. 3501 et seq. and has
assigned OMB control number 2060–
0543, EPA ICR number 2096.02. A copy
of the OMB-approved ICR may be
obtained from Susan Auby, Collection
Strategies Division, U.S. EPA (2822T),
1200 Pennsylvania Ave., NW.,
Washington, DC 20460, by e-mail at
auby.susan@epa.gov, or by calling (202)
566–1672.
Burden means the total time, effort, or
financial resources expended by persons
to generate, maintain, retain, disclose, or
provide information to or for a Federal
agency. This includes the time needed
to review instructions; develop, acquire,
install, and utilize technology and
systems for the purposes of collecting,
validating, and verifying information,
VerDate Aug<31>2005
14:58 Apr 16, 2007
Jkt 211001
processing and maintaining
information, and disclosing and
providing information; adjust the
existing ways to comply with any
previously applicable instructions and
requirements; train personnel to be able
to respond to a collection of
information; search data sources;
complete and review the collection of
information; and transmit or otherwise
disclose the information.
An agency may not conduct or
sponsor, and a person is not required to
respond to, a collection of information
unless it displays a currently valid OMB
control number. The OMB control
numbers for EPA’s regulations in 40
CFR part 63 are listed in 40 CFR part 9.
C. Regulatory Flexibility Act
The Regulatory Flexibility Act (RFA)
generally requires an agency to prepare
a regulatory flexibility analysis of any
rule subject to notice and comment
rulemaking requirements under the
Administrative Procedure Act or any
other statute unless the agency certifies
that the rule would not have a
significant economic impact on a
substantial number of small entities.
Small entities include small businesses,
small not-for-profit enterprises, and
small governmental jurisdictions.
For the purposes of assessing the
impacts of the proposed amendments 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 (less than 500
employees for NAICS codes 331511,
331512, and 331513); (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 the proposed amendments on
small entities, I certify that this action
will not have a significant economic
impact on a substantial number of small
entities. In determining whether a rule
has a significant economic impact on a
substantial number of small entities, the
impact of concern is any significant
adverse economic impact on small
entities, since the primary purpose of
the regulatory flexibility analyses is to
identify and address regulatory
alternatives ‘‘which minimize any
significant economic impact of the rule
on small entities.’’ 5 U.S.C 603 and 604.
Thus, an agency may certify that a rule
will not have a significant economic
impact on a substantial number of small
PO 00000
Frm 00032
Fmt 4702
Sfmt 4702
19157
entities if the rule relieves regulatory
burden, or otherwise has a positive
economic effect on all of the small
entities subject to the rule.
There would not be any adverse
impacts on any source (including any
small entity) as a result of the proposed
amendments because the proposed
amendments provide an overall
economic benefit to entities subject to
the rule. The proposed amendments do
not create any new requirements or
burdens that were not already included
in the economic impact assessment for
the existing rule. The proposed
amendments relieve regulatory burden
for all entities as a result of the
operational flexibility afforded by the
alternative compliance option,
alternative test method, and provisions
allowing plants to combine multiple
reports into a single submission. We
have therefore concluded that these
proposed amendments will relieve
regulatory burden for all affected small
entities. We continue to be interested in
the potential impacts of the proposed
action on small entities and welcome
comments on issues related to such
impacts.
D. Unfunded Mandates Reform Act
Title II of the Unfunded Mandates
Reform Act of 1995 (UMRA), Pub. L.
104–4, establishes requirements for
Federal agencies to assess the effects of
their regulatory actions on State, local,
and tribal governments and the private
sector. Under section 202 of the UMRA,
EPA generally must prepare a written
statement, including a cost-benefit
analysis, for proposed and final rules
with ‘‘Federal mandates’’ that may
result in expenditures by State, local,
and tribal governments, in the aggregate,
or by the private sector, of $100 million
or more in any 1 year. Before
promulgating an EPA rule for which a
written statement is needed, section 205
of the UMRA generally requires EPA to
identify and consider a reasonable
number of regulatory alternatives and
adopt the least costly, most costeffective, or least burdensome
alternative that achieves the objectives
of the rule. The provisions of section
205 do not apply when they are
inconsistent with applicable law.
Moreover, section 205 allows EPA to
adopt an alternative other than the least
costly, most cost-effective, or least
burdensome alternative if the
Administrator publishes with the final
rule an explanation why that alternative
was not adopted. Before EPA establishes
any regulatory requirements that may
significantly or uniquely affect small
governments, including tribal
governments, it must have developed
E:\FR\FM\17APP1.SGM
17APP1
19158
Federal Register / Vol. 72, No. 73 / Tuesday, April 17, 2007 / Proposed Rules
cprice-sewell on PRODPC61 with PROPOSALS
under section 203 of the UMRA a small
government agency plan. The plan must
provide for notifying potentially
affected small governments, enabling
officials of affected small governments
to have meaningful and timely input in
the development of EPA regulatory
proposals with significant Federal
intergovernmental mandates, and
informing, educating, and advising
small governments on compliance with
the regulatory requirements.
EPA has determined that the
proposed amendments do 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 the private sector in
any one year. The proposed
amendments are expected to result in an
overall reduction in expenditures for the
private sector and are not expected to
impact State, local, or tribal
governments. Thus, the proposed
amendments are not subject to the
requirements of sections 202 and 205 of
the UMRA. In addition, the proposed
amendments do not significantly or
uniquely affect small governments. The
proposed amendments contain no
requirements that apply to such
governments, and impose no obligations
upon them.
E. Executive Order 13132: Federalism
Executive Order 13132 (64 FR 43255,
August 10, 1999) requires EPA to
develop an accountable process to
ensure ‘‘meaningful and timely input by
State and local officials in the
development of regulatory policies that
have federalism implications.’’ ‘‘Policies
that have federalism implications’’ are
defined in the Executive Order to
include regulations that have
‘‘substantial direct effects on the States,
on the relationship between the national
government and the States, or on the
distribution of power and
responsibilities among the various
levels of government.’’
The proposed amendments do not
have federalism implications. They
would 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. The
proposed amendments do not impose
any requirements on State and local
governments. Thus, Executive Order
13132 does not apply to the proposed
amendments.
In the spirit of Executive Order 13132,
and consistent with EPA policy to
promote communications between EPA
and State and local government, EPA
VerDate Aug<31>2005
14:58 Apr 16, 2007
Jkt 211001
specifically solicits comments on this
proposed rule from State and local
officials.
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
Executive Order 13175 (65 FR 67249,
November 6, 2000), requires EPA to
develop an accountable process to
ensure ‘‘meaningful and timely input by
tribal officials in the development of
regulatory policies that have tribal
implications.’’ The proposed rule
amendments do not have tribal
implications, as specified in Executive
Order 13175. They would not have
substantial direct effects on tribal
governments, on the relationship
between the Federal government and
Indian tribes, or on the distribution of
power and responsibilities between the
Federal government and Indian tribes,
as specified in Executive Order 13175.
The proposed amendments impose no
requirements on tribal governments.
Thus, Executive Order 13175 does not
apply to the proposed amendments.
G. Executive Order 13045: Protection of
Children From Environmental Health
and Safety Risks
Executive Order 13045, ‘‘Protection of
Children from Environmental Health
Risks and Safety Risks’’ (62 FR 19885,
April 23, 1997) applies to any rule that:
(1) Is determined to be ‘‘economically
significant’’ as defined under Executive
Order 12866, and (2) concerns an
environmental health or safety risk that
EPA has reason to believe may have a
disproportionate effect on children. If
the regulatory action meets both criteria,
EPA must evaluate the environmental
health or safety effects of the planned
rule on children, and explain why the
planned regulation is preferable to other
potentially effective and reasonably
feasible alternatives considered by the
Agency.
EPA interprets Executive Order 13045
as applying only to those regulatory
actions that are based on health or safety
risks, such that the analysis required
under section 5–501 of the Executive
Order has the potential to influence the
regulation. These proposed amendments
are not subject to the Executive Order
because they are based solely on
technology performance.
H. Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution, or Use
These proposed amendments are not
a ‘‘significant energy action’’ as defined
in Executive Order 13211, ‘‘Actions
Concerning Regulations That
Significantly Affect Energy Supply,
PO 00000
Frm 00033
Fmt 4702
Sfmt 4702
Distribution, or Use’’ (66 FR 28355, May
22, 2001) because they are not likely to
have a significant adverse effect on the
supply, distribution, or use of energy.
Further, we have concluded that these
proposed amendments are not likely to
have any adverse energy effects because
energy requirements would remain at
the existing level. No additional
pollution controls or other equipment
that would consume energy are required
by the proposed amendments.
I. National Technology Transfer
Advancement Act
Section 12(d) of the National
Technology Transfer and Advancement
Act (NTTAA) of 1995 (Pub. L. No. 104–
113, Section 12(d), 15 U.S.C. 272 note)
directs EPA to use voluntary consensus
standards (VCS) in its regulatory
activities, unless to do so would be
inconsistent with applicable law or
otherwise impractical. The VCS are
technical standards (e.g., materials
specifications, test methods, sampling
procedures, and business practices) that
are developed or adopted by VCS
bodies. The NTTAA directs EPA to
provide Congress, through OMB,
explanations when the Agency does not
use available and applicable VCS.
The proposed amendments involve
technical standards. These proposed
amendments include an alternative
methodology, the NIOSH Method 2010,
‘‘Amines, Aliphatic’’ (incorporated by
reference in § 63.14) for EPA Method 18
(40 CFR part 60, appendix A) to
determine the triethylamine (TEA)
concentration of gases from the TEA
cold box mold or core making line
provided the performance requirements
outlined in section 13.1 of EPA Method
18 are satisfied.
Consistent with the NTTAA, EPA
conducted searches to identify
voluntary consensus standards in
addition to these EPA and alternative
methods. No applicable voluntary
consensus standards were identified.
For the methods required or
referenced by this proposed rule, a
source may apply to EPA for permission
to use alternative test methods or
alternative monitoring requirements in
place of any required testing methods,
performance specifications, or
procedures under §§ 63.7(f) and 63.8(f)
of Subpart A of the General Provisions.
EPA welcomes comments on this
aspect of the proposed rulemaking and,
specifically, invites the public to
identify potentially-applicable
voluntary consensus standards and to
explain why such standards should be
used in this regulation.
E:\FR\FM\17APP1.SGM
17APP1
Federal Register / Vol. 72, No. 73 / Tuesday, April 17, 2007 / Proposed Rules
J. Executive Order 12898: Federal
Actions To Address Environmental
Justice in Minority Populations and
Low-Income Populations
Executive Order 12898 (59 FR 7629,
February 16, 1994) establishes Federal
executive policy on environmental
justice. Its main provision directs
Federal agencies, to the greatest extent
practicable and permitted by law, to
make environmental justice part of their
mission by identifying and addressing,
as appropriate, disproportionately high
and adverse human health or
environmental effects of their programs,
policies, and activities on minority
populations and low-income
populations in the United States.
EPA has determined that these
proposed amendments will not have
disproportionately high and adverse
human health or environmental effects
on minority or low-income populations
because it does not affect the level of
protection provided to human health or
the environment. These proposed
amendments do not relax the control
measures on sources regulated by the
rule and therefore will not cause
emissions increases from these sources.
List of Subjects in 40 CFR Part 63
Environmental protection, Air
pollution control, Hazardous
substances, Incorporation by reference,
Reporting and recordkeeping
requirements.
Dated: April 9, 2007.
Stephen L. Johnson,
Administrator.
For the reasons stated in the
preamble, part 63, title 40, chapter I, of
the Code of Federal Regulations is
proposed to be amended as follows:
PART 63—[AMENDED]
1. The authority citation for part 63
continues to read as follows:
Authority: 42 U.S.C. 7401, et seq.
Subpart A—[AMENDED]
2. Section 63.14 is amended by
adding paragraph (k)(2) to read as
follows:
§ 63.14
Incorporations by reference.
cprice-sewell on PRODPC61 with PROPOSALS
*
*
*
*
*
(k) * * *
(2) The following method as
published in the National Institute of
Occupational Safety and Health
(NIOSH) test method compendium,
‘‘NIOSH Manual of Analytical
Methods’’, NIOSH publication no. 94–
113, Fourth Edition.
(i) NIOSH Method 2010, ‘‘Amines,
Aliphatic,’’ Issue 2 (and subsequent
VerDate Aug<31>2005
14:58 Apr 16, 2007
Jkt 211001
revisions), August 15, 1994, IBR
approved for § 63.7732(g)(1)(v) of
Subpart EEEEE of this part.
(ii) [Reserved]
Subpart EEEEE—[Amended]
3. Section 63.7681 is amended by
revising the second sentence to read as
follows:
§ 63.7681
Am I subject to this subpart?
* * * Your iron and steel foundry is
a major source of HAP for purposes of
this subpart if it emits or has the
potential to emit any single HAP at a
rate of 10 tons or more per year or any
combination of HAP at a rate of 25 tons
or more per year or if it is located at a
facility that emits or has the potential to
emit any single HAP at a rate of 10 tons
or more per year or any combination of
HAP at a rate of 25 tons or more per year
as defined in § 63.2.
4. Section 63.7690 is amended by:
a. Revising paragraphs (a)
introductory text;
b. Revising paragraph (a)(2);
c. Revising paragraph (a)(7);
d. Revising paragraphs (a)(11)(i) and
(ii); and
e. Revising paragraph (b)(1)
introductory text to read as follows:
§ 63.7690
I meet?
What emissions limitations must
(a) You must meet the emissions
limits or standards in paragraphs (a)(1)
through (11) of this section that apply to
you. When alternative emissions
limitations are provided for a given
emissions source, you are not restricted
in the selection of which applicable
alternative emissions limitation is used
to demonstrate compliance.
*
*
*
*
*
(2) For each cupola metal melting
furnace at an existing iron and steel
foundry, you must not discharge
emissions through a conveyance to the
atmosphere that exceed either the limit
for PM in paragraph (a)(2)(i) or (ii) of
this section or, alternatively the limit for
total metal HAP in paragraph (a)(2)(iii)
or (iv) of this section:
(i) 0.006 gr/dscf of PM; or
(ii) 0.10 pound of PM per ton (lb/ton)
of metal charged, or
(iii) 0.0005 gr/dscf of total metal HAP;
or
(iv) 0.008 lb/ton of total metal HAP.
*
*
*
*
*
(7) For each building or structure
housing any iron and steel foundry
emissions source at the iron and steel
foundry, you must not discharge any
fugitive emissions to the atmosphere
from foundry operations that exhibit
opacity greater than 20 percent (6-
PO 00000
Frm 00034
Fmt 4702
Sfmt 4702
19159
minute average), except for one 6minute average per hour that does not
exceed 27 percent opacity.
*
*
*
*
*
(11) * * *
(i) You must not discharge emissions
of TEA through a conveyance to the
atmosphere that exceed 1 ppmv, as
determined according to the
performance test procedures in
§ 63.7732(g); or
(ii) You must reduce emissions of
TEA from each TEA cold box mold or
core making line by at least 99 percent,
as determined according to the
performance test procedures in
§ 63.7732(g).
(b) * * *
(1) You must install, operate, and
maintain a capture and collection
system for all emissions sources subject
to an emissions limit for VOHAP or TEA
in paragraphs (a)(8) through (11) of this
section.
*
*
*
*
*
5. Section 63.7700 is amended by:
a. Revising the last sentence in
paragraph (b);
b. Revising paragraphs (c)(1)(i) and
(ii);
c. Revising the last sentence in
paragraph (c)(2);
d. Revising paragraph (c)(3)(iii); and
e. Revising paragraph (e)(1) to read as
follows:
§ 63.7700 What work practice standards
must I meet?
*
*
*
*
*
(b) * * * Any post-consumer engine
blocks, post-consumer oil filters, or oily
turnings that are processed and/or
cleaned to the extent practicable such
that the materials do not include lead
components, mercury switches,
chlorinated plastics, or free organic
liquids can be included in this
certification.
(c) * * *
(1) * * *
(i) For scrap charged to a scrap
preheater, electric arc metal melting
furnace, or electric induction metal
melting furnace, specifications for scrap
materials to be depleted (to the extent
practicable) of the presence of used oil
filters, chlorinated plastic parts, organic
liquids, and a program to ensure the
scrap materials are drained of free
liquids; or
(ii) For scrap charged to a cupola
metal melting furnace, specifications for
scrap materials to be depleted (to the
extent practicable) of the presence of
chlorinated plastic, and a program to
ensure the scrap materials are drained of
free liquids.
(2) * * * You must either obtain and
maintain onsite a copy of the
E:\FR\FM\17APP1.SGM
17APP1
Federal Register / Vol. 72, No. 73 / Tuesday, April 17, 2007 / Proposed Rules
procedures used by the scrap supplier
for either removing accessible mercury
switches or for purchasing automobile
bodies that have had mercury switches
removed, as applicable, or document
your attempts to obtain a copy of these
procedures from the scrap suppliers
servicing your area.
(3) * * *
(iii) The inspection procedures must
include provisions for rejecting or
returning entire or partial scrap
shipments that do not meet
specifications and limiting purchases
from vendors whose shipments fail to
meet specifications for more than three
inspections in one calendar year.
*
*
*
*
*
(e) * * *
(1) You must operate and maintain a
gas-fired preheater where the flame
directly contacts the scrap charged; or
*
*
*
*
*
6. Section 63.7710 is amended by
revising the first sentence in paragraph
(b) introductory text to read as follows:
§ 63.7710 What are my operation and
maintenance requirements?
*
*
*
*
*
(b) You must prepare and operate at
all times according to a written
operation and maintenance plan for
each capture and collection system and
control device for an emissions source
subject to a PM, metal HAP, TEA, or
VOHAP emissions limit in § 63.7690(a).
* * *
*
*
*
*
*
7. Section 63.7731 is amended by
revising the first sentence in paragraph
(a) to read as follows:
§ 63.7732 What test methods and other
procedures must I use to demonstrate
initial compliance with the emissions
limitations?
§ 63.7731 When must I conduct
subsequent performance tests?
(a) You must conduct each
performance test that applies to your
iron and steel foundry based on your
selected compliance alternative, if
applicable, according to the
requirements in § 63.7(e)(1) and the
conditions specified in paragraphs (b)
through (i) of this section.
(b) To determine compliance with the
applicable emissions limit for PM in
§ 63.7690(a)(1) through (6) for a metal
melting furnace, scrap preheater,
pouring station, or pouring area, follow
the test methods and procedures in
paragraphs (b)(1) through (6) of this
section.
*
*
*
*
*
(4) For electric arc and electric
induction metal melting furnaces,
sample only during normal production
conditions, which may include, but are
not limited to the following cycles:
Charging, melting, alloying, refining,
slagging, and tapping.
(5) For scrap preheaters, sample only
during normal production conditions,
which may include, but are not limited
to the following cycles: Charging,
heating, and discharging.
(6) Determine the total mass of metal
charged to the furnace or scrap
preheater For a cupola metal melting
furnace at an existing iron and steel
foundry that is subject to the PM
emissions limit in § 63.7690(a)(ii),
calculate the PM emissions rate in lb/
ton using Equation 1 of this section:
(a) You must conduct subsequent
performance tests to demonstrate
compliance with all applicable PM or
total metal HAP, VOHAP, and TEA
emissions limitations in § 63.7690 for
your iron and steel foundry no less
frequently than every 5 years and each
time you elect to change an operating
limit or to comply with a different
alternative emissions limit, if
applicable. * * *
*
*
*
*
*
8. Section 63.7732 is amended by:
a. Revising paragraph (a);
b. Revising paragraphs (b)
introductory text, (b)(4), and (b)(5) and
adding paragraph (b)(6);
c. Revising paragraphs (c)
introductory text, (c)(2), (c)(4), and (c)(5)
and adding paragraph (c)(6);
d. Revising paragraph (d) introductory
text, adding two sentences to the end of
paragraph (d)(1), and revising paragraph
(d)(2);
e. Revising paragraph (e)(3);
f. Revising paragraphs (f)(2)(ix) and
(f)(3);
g. Revising paragraphs (g)(1)(v), (g)(2),
and (g)(4);
h. Revising paragraphs (h)(2)(ii),
(h)(3)(ii), and (h)(3)(iii); and
i. Adding paragraph (i) to read as
follows:
Q
EFPM = CPM ×
M
charge
cprice-sewell on PRODPC61 with PROPOSALS
Where:
EFPM = Mass emissions rate of PM, lb/ton;
CPM = Concentration of PM measured during
performance test run, gr/dscf;
Q = Volumetric flow rate of exhaust gas, dry
standard cubic feet per minute (dscfm);
Mcharge = Mass of metal charged during
performance test run, tons;
ttest = Duration of performance test run,
minutes; and
7,000 = Unit conversion factor, grains per
pound (gr/lb).
(c) To determine compliance with the
applicable emissions limit for total
metal HAP in § 63.7690(a)(1) through (6)
t test
×
7, 000
for a metal melting furnace, scrap
preheater, pouring station, or pouring
area, follow the test methods and
procedures in paragraphs (c)(1) through
(6) of this section.
*
*
*
*
*
(2) A minimum of three valid test
runs are needed to comprise a
performance test.
*
*
*
*
*
(4) For electric arc and electric
induction metal melting furnaces,
sample only during normal production
conditions, which may include, but are
Q
EFTMHAP = CTMHAP ×
M
charge
VerDate Aug<31>2005
14:58 Apr 16, 2007
Jkt 211001
(Eq. 1)
PO 00000
Frm 00035
Fmt 4702
t test
×
7, 000
Sfmt 4725
not limited to the following cycles:
Charging, melting, alloying, refining,
slagging, and tapping.
(5) For scrap preheaters, sample only
during normal production conditions,
which may include, but are not limited
to the following cycles: Charging,
heating, and discharging.
(6) Determine the total mass of metal
charged to the furnace or scrap
preheater during each performance test
run and calculate the total metal HAP
emissions rate using Equation 2 of this
section:
(Eq. 2)
E:\FR\FM\17APP1.SGM
17APP1
EP17AP07.000 EP17AP07.001
19160
Federal Register / Vol. 72, No. 73 / Tuesday, April 17, 2007 / Proposed Rules
10.9%
CVOHAP , 10% O2 = CVOHAP
20.9% − %O 2
*
*
*
*
*
(f) * * *
(2) * * *
(ix) Calculate the site-specific VOC
emissions limit using Equation 4 of this
section:
VOC
limit
= 20 ×
CVOHAP , avg
CCEM
(Eq. 4)
cprice-sewell on PRODPC61 with PROPOSALS
Where:
CVOHAP,avg = Average concentration of
VOHAP for the source test in ppmv as
measured by Method 18 in 40 CFR part
60, appendix A or the average
concentration of TGNMO for the source
test in ppmv as hexane as measured by
Method 25 in 40 CFR part 60, appendix
A; and
CCEM = Average concentration of total
hydrocarbons in ppmv as hexane as
measured using the CEMS during the
source test.
(3) For two or more exhaust streams
from one or more automated conveyor
and pallet cooling lines or automated
shakeout lines, compute the flowweighted average concentration of
VOHAP emissions for each combination
of exhaust streams using Equation 5 of
this section:
VerDate Aug<31>2005
14:58 Apr 16, 2007
Jkt 211001
(Eq. 3)
n
∑C Q
i
CW =
i =1
n
∑Q
i
(Eq. 5)
(4) If you are subject to the 99 percent
reduction standard, calculate the mass
emissions reduction using Equation 6 of
this section:
i
i =1
% reduction =
Ei − Eo
× 100%
E1
(Eq. 6)
Where:
Cw = Flow-weighted concentration of VOHAP
or VOC, ppmv (as hexane);
Ci = Concentration of VOHAP or VOC from
exhaust stream ‘‘i’’, ppmv (as hexane);
n = Number of exhaust streams sampled; and
Qi = Volumetric flow rate of effluent gas from
exhaust stream ‘‘i,’’, dscfm.
(g) * * *
(1) * * *
(v) Method 18 to determine the TEA
concentration. Alternatively, you may
use NIOSH Method 2010 (incorporated
by reference-see § 63.14) to determine
the TEA concentration provided the
performance requirements outlined in
section 13.1 of EPA Method 18 are
satisfied. The sampling option and time
must be sufficiently long such that
either the TEA concentration in the field
sample is at least 5 times the limit of
detection for the analytical method or
the test results calculated using the
laboratory’s reported analytical
detection limit for the specific field
samples are less than 1⁄5 of the
applicable emissions limit. When using
Method 18, the adsorbent tube
approach, as described in section 8.2.4
of Method 18, may be required to
achieve the necessary analytical
detection limits. The sampling time
must be at least 1 hour in all cases.
(2) If you use a wet acid scrubber,
conduct the test as soon as practicable
after adding fresh acid solution and the
system has reached normal operating
conditions.
*
*
*
*
*
Where:
Ei = Mass emissions rate of TEA at control
device inlet, kilograms per hour (kg/hr);
and
Eo = Mass emissions rate of TEA at control
device outlet, kg/hr.
(h) * * *
(2) * * *
(ii) Calculate the flow-weighted
average emissions limit, considering
only the regulated streams, using
Equation 5 of this section, except Cw is
the flow-weighted average emissions
limit for PM or total metal HAP in the
exhaust stream, gr/dscf; and Ci is the
concentration of PM or total metal HAP
in exhaust stream ‘‘i’’, gr/dscf.
*
*
*
*
*
(3) * * *
(ii) Measure the flow rate and PM or
total metal HAP concentration of the
combined exhaust stream both before
and after the control device and
calculate the mass removal efficiency of
the control device using Equation 6 of
this section, except Ei is the mass
emissions rate of PM or total metal HAP
at the control device inlet, lb/hr and Eo
is the mass emissions rate of PM or total
metal HAP at the control device outlet,
lb/hr.
(iii) Meet the applicable emissions
limit based on the calculated PM or total
metal HAP concentration for the
regulated emissions sources using
Equation 7 of this section:
PO 00000
Frm 00036
Fmt 4702
Sfmt 4702
E:\FR\FM\17APP1.SGM
17APP1
EP17AP07.005
Where:
CVOHAP = Concentration of VOHAP in ppmv
as measured by Method 18 in 40 CFR
part 60, appendix A or the concentration
of TGNMO or TOC in ppmv as hexane
as measured by Method 25 or 25A in 40
CFR part 60, appendix A; and
%O2 = Oxygen concentration in gas stream,
percent by volume (dry basis).
structure may be performed, if the
fugitive release points afford such an
observation.
(2) During testing intervals when PM
performance tests, if applicable, are
being conducted, conduct the opacity
test such the opacity observations are
recorded during the PM performance
tests.
(e) * * *
(3) For a cupola metal melting
furnace, correct the measured
concentration of VOHAP, TGNMO, or
TOC for oxygen content in the gas
stream using Equation 3 of this section:
EP17AP07.004
(d) To determine compliance with the
opacity limit in § 63.7690(a)(7) for
fugitive emissions from buildings or
structures housing any iron and steel
foundry emissions source at the iron
and steel foundry, follow the procedures
in paragraphs (d)(1) and (2) of this
section.
(1) * * * The certified observer may
identify a limited number of openings or
vents that appear to have the highest
opacities and perform opacity
observations on the identified openings
or vents in lieu of performing
observations for each opening or vent
from the building or structure.
Alternatively, a single opacity
observation for the entire building or
EP17AP07.002 EP17AP07.003
Where:
EFTMHAP = Emissions rate of total metal HAP,
lb/ton;
CTMHAP = Concentration of total metal HAP
measured during performance test run,
gr/dscf;
Q = Volumetric flow rate of exhaust gas,
dscfm;
Mcharge = Mass of metal charged during
performance test run, tons;
ttest = Duration of performance test run,
minutes; and
7,000 = Unit conversion factor, gr/lb.
19161
Federal Register / Vol. 72, No. 73 / Tuesday, April 17, 2007 / Proposed Rules
% reduction
Creleased = Ci × 1 −
100
Where:
Creleased = Calculated concentration of PM (or
total metal HAP) predicted to be released
to the atmosphere from the regulated
emissions source, gr/dscf; and
Ci = Concentration of PM (or total metal
HAP) in the uncontrolled regulated
exhaust stream, gr/dscf.
(i) To determine compliance with an
emissions limit for situations when
multiple sources are controlled by a
single control device, but only one
source operates at a time, or other
situations that are not expressly
considered in paragraphs (b) through (h)
of this section, a site-specific test plan
should be submitted to the
Administrator for approval according to
the requirements in § 63.7(c)(2) and (3).
9. Section 63.7733 is amended by
revising paragraphs (b)(2), (c)(2), and
(d)(2) to read as follows:
§ 63.7733 What procedures must I use to
establish operating limits?
*
*
*
*
*
(b) * * *
(2) Compute and record the average
pressure drop and average scrubber
water flow rate for each valid sampling
run in which the applicable emissions
limit is met.
(c) * * *
(2) Compute and record the average
combustion zone temperature for each
valid sampling run in which the
applicable emissions limit is met.
(d) * * *
(2) Compute and record the average
scrubbing liquid flow rate for each valid
sampling run in which the applicable
emissions limit is met.
*
*
*
*
*
10. Section 63.7734 is amended by:
a. Revising paragraph (a) introductory
text;
b. Revising paragraph (a)(2)(ii);
c. Adding paragraphs (a)(2)(iii) and
(iv);
d. Revising paragraphs (a)(7) and
(a)(11) to read as follows:
cprice-sewell on PRODPC61 with PROPOSALS
§ 63.7734 How do I demonstrate initial
compliance with the emissions limitations
that apply to me?
(a) You have demonstrated initial
compliance with the emissions limits in
§ 63.7690(a) by meeting the applicable
conditions in paragraphs (a)(1) through
(11) of this section. When alternative
emissions limitations are provided for a
given emissions source, you are not
restricted in the selection of which
applicable alternative emissions
VerDate Aug<31>2005
14:58 Apr 16, 2007
Jkt 211001
(Eq. 7)
limitation is used to demonstrate
compliance.
*
*
*
*
*
(2) * * *
(ii) The average total metal HAP
concentration in the exhaust stream,
determined according to the
performance test procedures in
§ 63.7732(c), did not exceed 0.0005 gr/
dscf; or
(iii) The average PM mass emissions
rate, determined according to the
performance test procedures in
§ 63.7732(b), did not exceed 0.10 lb/ton;
or
(iv) The average total metal HAP mass
emissions rate, determined according to
the performance test procedures in
§ 63.7732(c), did not exceed 0.008 lb/
ton.
*
*
*
*
*
(7) For each building or structure
housing any iron and steel foundry
emissions source at the iron and steel
foundry, the opacity of fugitive
emissions from foundry operations
discharged to the atmosphere,
determined according to the
performance test procedures in
§ 63.7732(d), did not exceed 20 percent
(6-minute average), except for one 6minute average per hour that did not
exceed 27 percent opacity.
*
*
*
*
*
(11) For each TEA cold box mold or
core making line in a new or existing
iron and steel foundry, the average TEA
concentration, determined according to
the performance test procedures in
§ 63.7732(g), did not exceed 1 ppmv or
was reduced by 99 percent.
*
*
*
*
*
11. Section 63.7736 is amended by
revising paragraph (c)(1) to read as
follows:
§ 63.7736 How do I demonstrate initial
compliance with the operation and
maintenance requirements that apply to
me?
*
*
*
*
*
(c) * * *
(1) You have submitted the bag leak
detection system monitoring
information to the Administrator within
the written O&M plan for approval
according to the requirements of
§ 63.7710(b);
*
*
*
*
*
12. Section 63.7740 is amended by:
a. Revising paragraph (b);
b. Redesignating paragraphs (c)
through (g) as (d) through (h); and
PO 00000
Frm 00037
Fmt 4702
Sfmt 4702
c. Adding paragraph (c) to read as
follows:
§ 63.7740 What are my monitoring
requirements?
*
*
*
*
*
(b) For each negative pressure
baghouse or positive pressure baghouse
equipped with a stack that is applied to
meet any PM or total metal HAP
emissions limitation in this subpart, you
must at all times monitor the relative
change in PM loadings using a bag leak
detection system according to the
requirements in § 63.7741(b).
(c) For each baghouse, regardless of
type, that is applied to meet any PM or
total metal HAP emissions limitation in
this subpart, you must conduct
inspections at their specified
frequencies according to the
requirements specified in paragraphs
(c)(1) through (8) of this section.
(1) Monitor the pressure drop across
each baghouse cell each day to ensure
pressure drop is within the normal
operating range identified in the
manual.
(2) Confirm that dust is being
removed from hoppers through weekly
visual inspections or other means of
ensuring the proper functioning of
removal mechanisms.
(3) Check the compressed air supply
for pulse-jet baghouses each day.
(4) Monitor cleaning cycles to ensure
proper operation using an appropriate
methodology.
(5) Check bag cleaning mechanisms
for proper functioning through monthly
visual inspections or equivalent means.
(6) Make monthly visual checks of bag
tension on reverse air and shaker-type
baghouses to ensure that bags are not
kinked (kneed or bent) or lying on their
sides. You do not have to make this
check for shaker-type baghouses using
self-tensioning (spring-loaded) devices.
(7) Confirm the physical integrity of
the baghouse through quarterly visual
inspections of the baghouse interior for
air leaks.
(8) Inspect fans for wear, material
buildup, and corrosion through
quarterly visual inspections, vibration
detectors, or equivalent means.
*
*
*
*
*
13. Section 63.7741 is amended by:
a. Revising paragraphs (a)(1)(iv),
(a)(2)(i), (a)(2)(iii), (a)(2)(iv), and
(a)(2)(vi);
b. Revising paragraph (b) introductory
text;
c. Revising paragraphs (c)(1)(iii),
(c)(1)(iv), (c)(1)(vi), and (c)(2)(iv);
E:\FR\FM\17APP1.SGM
17APP1
EP17AP07.006
19162
Federal Register / Vol. 72, No. 73 / Tuesday, April 17, 2007 / Proposed Rules
d. Revising paragraph (d)(8); and
e. Revising paragraph (e)(2)(iv) to read
as follows:
cprice-sewell on PRODPC61 with PROPOSALS
§ 63.7741 What are the installation,
operation, and maintenance requirements
for my monitors?
(a) * * *
(1) * * *
(iv) At least monthly, visually inspect
all components, including all electrical
and mechanical connections, for proper
functioning.
(2) * * *
(i) Locate the pressure sensor(s) in or
as close as possible to a position that
provides a representative measurement
of the pressure and that minimizes or
eliminates pulsating pressure, vibration,
and internal and external corrosion.
*
*
*
*
*
(iii) Check the pressure tap for
pluggage daily. If a ‘‘non-clogging’’
pressure tap is used, check for pluggage
monthly.
(iv) Using a manometer or equivalent
device such as a magnahelic or other
pressure indicating transmitter, check
gauge and transducer calibration
quarterly.
*
*
*
*
*
(vi) At least monthly, visually inspect
all components, including all electrical
and mechanical connections, for proper
functioning.
*
*
*
*
*
(b) For each negative pressure
baghouse or positive pressure baghouse
equipped with a stack that is applied to
meet any PM or total metal HAP
emissions limitation in this subpart, you
must install, operate, and maintain a bag
leak detection system according to the
requirements in paragraphs (b)(1)
through (7) of this section.
*
*
*
*
*
(c) * * *
(1) * * *
(iii) Check the pressure tap for
pluggage daily. If a ‘‘non-clogging’’
pressure tap is used, check for pluggage
monthly.
(iv) Using a manometer or equivalent
device such as a magnahelic or other
pressure indicating transmitter, check
gauge and transducer calibration
quarterly.
*
*
*
*
*
(vi) At least monthly, visually inspect
all components, including all electrical
and mechanical connections, for proper
functioning.
(2) * * *
(iv) At least monthly, visually inspect
all components, including all electrical
and mechanical connections, for proper
functioning.
(d) * * *
VerDate Aug<31>2005
14:58 Apr 16, 2007
Jkt 211001
(8) At least monthly, visually inspect
all components, including all electrical
and mechanical connections, for proper
functioning.
(e) * * *
(2) * * *
(iv) At least monthly, visually inspect
all components, including all electrical
and mechanical connections, for proper
functioning.
*
*
*
*
*
14. Section 63.7743 is amended by:
a. Adding a second sentence to the
end of paragraph (a) introductory text
and removing the colon after the first
sentence in paragraph (a) in text and
adding period in its place;
b. Revising paragraph (a)(2)(ii) and
adding paragraphs (a)(2)(iii) and (iv);
c. Revising paragraph (a)(7); and
d. Revising paragraph (c) introductory
text and paragraphs (c)(1) and (2) to read
as follows:
§ 63.7743 How do I demonstrate
continuous compliance with the emissions
limitations that apply to me?
(a) * * * When alternative emissions
limitations are provided for a given
emissions source, you must comply
with the alternative emissions limitation
most recently selected as your
compliance alternative.
*
*
*
*
*
(2) * * *
(ii) Maintaining the average total
metal HAP concentration in the exhaust
stream at or below 0.0005 gr/dscf; or
(iii) Maintaining the average PM mass
emissions rate at or below 0.10 lb/ton;
or
(iv) Maintaining the average total
metal HAP mass emissions rate at or
below 0.008 lb/ton.
*
*
*
*
*
(7) For each building or structure
housing any iron and steel foundry
emissions source at the iron and steel
foundry, maintaining the opacity of any
fugitive emissions from foundry
operations discharged to the atmosphere
at or below 20 percent opacity (6-minute
average), except for one 6-minute
average per hour that does not exceed
27 percent opacity.
*
*
*
*
*
(c) For each baghouse,
(1) Inspecting and maintaining each
baghouse according to the requirements
of § 63.7740(c)(1) through (8) and
recording all information needed to
document conformance with these
requirements; and
(2) If the baghouse is equipped with
a bag leak detection system, maintaining
records of the times the bag leak
detection system sounded, and for each
valid alarm, the time you initiated
PO 00000
Frm 00038
Fmt 4702
Sfmt 4702
19163
corrective action, the corrective action
taken, and the date on which corrective
action was completed.
*
*
*
*
*
15. Section 63.7750 is amended by
adding a sentence to the end of
paragraph (e) introductory text to read
as follows:
§ 63.7750 What notifications must I submit
and when?
*
*
*
*
*
(e) * * * For opacity performance
tests, the notification of compliance
status may be submitted with the
semiannual compliance report in
§ 63.7751(a) and (b) or the semiannual
part 70 monitoring report in
§ 63.7551(d).
*
*
*
*
*
16. Section 63.7751 is amended by
revising paragraph (c) to read as follows:
§ 63.7751
when?
What reports must I submit and
*
*
*
*
*
(c) Immediate startup, shutdown, and
malfunction report. If you had a startup,
shutdown, or malfunction during the
semiannual reporting period that was
not consistent with your startup,
shutdown, and malfunction plan and
the source exceeds any applicable
emissions limitation in § 63.7690, you
must submit an immediate startup,
shutdown, and malfunction report
according to the requirements of
§ 63.10(d)(5)(ii).
*
*
*
*
*
17. Section 63.7752 is amended by
revising paragraph (a)(4) to read as
follows:
§ 63.7752
What records must I keep?
(a) * * *
(4) Records of the annual quantity of
each chemical binder or coating
material used to coat or make molds and
cores, the Material Data Safety Sheet or
other documentation that provides the
chemical composition of each
component, and the annual quantity of
HAP used in these chemical binder or
coating materials at the foundry as
calculated from the recorded quantities
and chemical compositions (from
Material Data Safety Sheets or other
documentation).
*
*
*
*
*
18. Section 63.7765 is amended by:
a. Revising the definition for
‘‘Deviation’’;
b. Adding, in alphabetical order,
definitions for ‘‘Offblast’’ and ‘‘On
blast’’; and
c. Revising the definitions ‘‘Scrap
preheater’’ and adding ‘‘Total metal
HAP’’ to read as follows:
E:\FR\FM\17APP1.SGM
17APP1
19164
Federal Register / Vol. 72, No. 73 / Tuesday, April 17, 2007 / Proposed Rules
§ 63.7765
subpart?
What definitions apply to this
Total metal HAP means, for the
purposes of this subpart, the sum of the
concentrations of antimony, arsenic,
beryllium, cadmium, chromium, cobalt,
lead, manganese, mercury, nickel, and
selenium as measured by EPA Method
29 (40 CFR part 60, appendix A). Only
the measured concentration of the listed
analytes that are present at
concentrations exceeding one-half the
quantitation limit of the analytical
method are to be used in the sum. If any
of the analytes are not detected or are
detected at concentrations less than onehalf the quantitation limit of the
analytical method, the concentration of
those analytes will be assumed to be
zero for the purposes of calculating the
total metal HAP for this subpart.
*
*
*
*
*
19. Table 1 to subpart EEEEE is
amended by revising the entry for § 63.9
to read as follows:
point that the cupola does not produce
additional molten metal.
On blast means those periods of
cupola operation when combustion
(blast) air is introduced to the cupola
furnace and the furnace is capable of
producing molten metal. On blast
conditions are characterized by both
blast air introduction and molten metal
production.
*
*
*
*
*
Scrap preheater means a vessel or
other piece of equipment in which
metal scrap that is to be used as melting
furnace feed is heated to a temperature
high enough to eliminate volatile
impurities or other tramp materials by
direct flame heating or similar means of
heating. Scrap dryers, which solely
remove moisture from metal scrap, are
not considered to be scrap preheaters for
purposes of this subpart.
*
*
*
*
*
*
*
*
*
*
Deviation means any instance in
which an affected source or an owner or
operator of such an affected source. A
deviation is not always a violation. The
determination of whether a deviation
constitutes a violation of the standard is
up to the discretion of the entity
responsible for enforcement of the
standards.
*
*
*
*
*
Off blast means those periods of
cupola operation when the cupola is not
actively being used to produce molten
metal. Off blast conditions include
cupola startup when air is introduced to
the cupola to preheat the sand bed and
other cupola startup procedures as
defined in the startup, shutdown, and
malfunction plan. Off blast conditions
also include idling conditions when the
blast air is turned off or down to the
TABLE 1 TO SUBPART EEEEE OF PART 63.—APPLICABILITY OF GENERAL PROVISIONS TO SUBPART EEEEE
*
Citation
*
*
Notification requirements
*
*
*
*
Applies to subpart
EEEEE?
Subject
*
63.9 ....................
*
*
*
Yes
*
Explanation
*
*
*
Except: For opacity performance tests, Subpart EEEEE allows the
notification of compliance status to be submitted with the semiannual compliance report or the semiannual part 70 monitoring
report.
*
*
*
[FR Doc. E7–7203 Filed 4–16–07; 8:45 am]
cprice-sewell on PRODPC61 with PROPOSALS
BILLING CODE 6560–50–P
VerDate Aug<31>2005
14:58 Apr 16, 2007
Jkt 211001
PO 00000
Frm 00039
Fmt 4702
Sfmt 4702
E:\FR\FM\17APP1.SGM
17APP1
*
Agencies
[Federal Register Volume 72, Number 73 (Tuesday, April 17, 2007)]
[Proposed Rules]
[Pages 19150-19164]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E7-7203]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 63
[EPA-HQ-OAR-2002-0034; FRL-8299-8]
RIN 2060-AM85
National Emission Standards for Hazardous Air Pollutants for Iron
and Steel Foundries
AGENCY: Environmental Protection Agency (EPA).
ACTION: Proposed rule.
-----------------------------------------------------------------------
SUMMARY: EPA is proposing amendments to the national emission standards
for hazardous air pollutants for iron and steel foundries. The proposed
amendments add alternative compliance options for cupolas at existing
foundries and clarify several provisions to increase operational
flexibility and improve understanding of the final rule requirements.
DATES: Comments must be received on or before May 17, 2007, unless a
public hearing is requested by April 27, 2007. If a hearing is
requested on the proposed rule, written comments must be received by
June 1, 2007.
ADDRESSES: Submit your comments, identified by Docket ID No. EPA-HQ-
OAR-2002-0034, by one of the following methods:
www.regulations.gov: Follow the on-line instructions for
submitting comments.
E-mail: a-and-r-docket@epa.gov.
Fax: (202) 566-1741.
Mail: National Emission Standards for Hazardous Air
Pollutants for Iron and Steel Foundries Docket, Environmental
Protection Agency, Mailcode: 6102T, 1200 Pennsylvania Ave., NW.,
Washington, DC 20460. Please include a total of two copies.
Hand Delivery: EPA Docket Center, Public Reading Room, EPA
West, Room 3334, 1301 Constitution Ave., NW., Washington, DC 20460.
Such deliveries are only accepted during the Docket's normal hours of
operation, and special arrangements should be made for deliveries of
boxed information.
Instructions: Direct your comments to Docket ID No. EPA-HQ-OAR-
2002-0034. EPA's policy is that all comments received will be included
in the public docket without change and may be made available online at
https://www.regulations.gov, including any personal information
provided, unless the comment includes information claimed to be
confidential business information (CBI) or other information whose
disclosure is restricted by statute. Do not submit information that you
consider to be CBI or otherwise protected through www.regulations.gov
or e-mail. The www.regulations.gov Web site is an ``anonymous access''
system, which means EPA will not know your identity or contact
information unless you provide it in the body of your comment. If you
send an e-mail comment directly to EPA without going through
www.regulations.gov, your e-mail address will be automatically captured
and included as part of the comment that is placed in the public docket
and made available on the Internet. If you submit an electronic
[[Page 19151]]
comment, EPA recommends that you include your name and other contact
information in the body of your comment and with any disk or CD-ROM you
submit. If EPA cannot read your comment due to technical difficulties
and cannot contact you for clarification, EPA may not be able to
consider your comment. Electronic files should avoid the use of special
characters, any form of encryption, and be free of any defects or
viruses.
Docket: All documents in the docket are listed in the
www.regulations.gov index. Although listed in the index, some
information is not publicly available, e.g., CBI or other information
whose disclosure is restricted by statute. Certain other material, such
as copyrighted material, is not placed on the Internet and will be
publicly available only in hard copy form. Publicly available docket
materials are available either electronically through
www.regulations.gov or in hard copy at the National Emission Standards
for Hazardous Air Pollutants for Iron and Steel Foundries Docket, EPA/
DC, 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: Mr. Phil Mulrine, Sector Policies and
Programs Division, Office of Air Quality Planning and Standards (D243-
02), Environmental Protection Agency, Research Triangle Park, North
Carolina 27711, telephone number: (919) 541-5289; fax number: (919)
541-3207; e-mail address: mulrine.phil@epa.gov.
SUPPLEMENTARY INFORMATION:
I. General Information
A. Does this action apply to me?
The regulated categories and entities potentially affected by this
proposed action include:
------------------------------------------------------------------------
Examples of regulated
Category NAICS code \1\ entities
------------------------------------------------------------------------
Industry....................... 331511 Iron foundries. Iron
and steel plants.
Automotive and large
equipment
manufacturers.
331512 Steel investment
foundries.
331513 Steel foundries (except
investment).
Federal government............. .............. Not affected.
State/local/tribal government.. .............. Not affected.
------------------------------------------------------------------------
\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 63.7682
of subpart EEEEE (NESHAP for Iron and Steel Foundries). 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. What should I consider as I prepare my comments to EPA?
Do not submit information containing confidential business
information (CBI) to EPA through www.regulations.gov or e-mail. Send or
deliver information identified as CBI only to the following address:
Roberto Morales, OAQPS Document Control Officer (C404-02),
Environmental Protection Agency, Office of Air Quality Planning and
Standards, Research Triangle Park, North Carolina 27711, Attention
Docket ID EPA-HQ-OAR-2002-0034. Clearly mark the part or all of the
information that you claim to be CBI. For CBI information in a disk or
CD ROM that you mail to EPA, mark the outside of the disk or CD ROM as
CBI and then identify electronically within the disk or CD ROM the
specific information that is claimed as CBI. In addition to one
complete version of the comment that includes information claimed as
CBI, a copy of the comment that does not contain the information
claimed as CBI must be submitted for inclusion in the public docket.
Information so marked will not be disclosed except in accordance with
procedures set forth in 40 CFR part 2.
C. Where can I get a copy of this document?
In addition to being available in the docket, an electronic copy of
this proposed action will also be available on the Worldwide Web (WWW)
through the Technology Transfer Network (TTN). Following signature, a
copy of this proposed 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.
D. When would a public hearing occur?
If anyone contacts EPA requesting to speak at a public hearing
concerning the proposed amendments by April 27, 2007, we will hold a
public hearing on May 2, 2007. If you are interested in attending the
public hearing, contact Ms. Pamela Garrett at (919) 541-7966 to verify
that a hearing will be held.
E. How is this document organized?
The supplementary information in this preamble is organized as
follows:
I. General Information
A. Does this action apply to me?
B. What should I consider as I prepare my comments to EPA?
C. Where can I get a copy of this document?
D. When would a public hearing occur?
E. How is this document organized?
II. Background Information
III. Summary of Proposed Amendments
A. Emissions Limitations
B. Work Practice Standards
C. Operation and Maintenance Requirements
D. Compliance With Alternative Emissions Limits
E. Monitoring Requirements
F. Recordkeeping and Reporting Requirements
G. Definitions
H. Applicability
I. Editorial Corrections
IV. 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
[[Page 19152]]
I. National Technology Transfer Advancement Act
J. Executive Order 12898: Federal Actions to Address
Environmental Justice in Minority Populations and Low-Income
Populations
II. Background Information
The national emission standards for hazardous air pollutants
(NESHAP) for iron and steel foundries (40 CFR part 63, subpart EEEEE)
establish emissions limitations and work practice requirements for the
control of hazardous air pollutants (HAP) from foundry operations. The
NESHAP implement section 112(d) of the Clean Air Act (CAA) by requiring
all iron and steel foundries that are major sources of HAP to meet
standards reflecting application of the maximum achievable control
technology (MACT). The compliance date for most of the subpart EEEEE
requirements is April 23, 2007.
After publication of the NESHAP (69 FR 21906, April 22, 2004), the
American Foundry Society, the Alliance of Automobile Manufacturers, and
the Steel Founders' Society of America filed petitions for
reconsideration of the final rule. The American Foundry Society and the
Steel Founders' Society of America also filed petitions for review of
the final rule (Steel Founders' Society of America v. U.S. EPA, No. 04-
1190, DC Cir.) and American Foundry Society v. U.S. EPA, No. 04-1191,
DC Cir.). The concerns raised by the petitioners regarding the work
practice standards for scrap management have been resolved by rule
amendments issued on May 20, 2005 (97 FR 29400). The Steel Founders'
Society of America petitioned the court for voluntary dismissal of
their petition for review on March 23, 2006, and the court granted that
petition on May 2, 2006. Thus, the only challenge to the NESHAP
remaining before the court is the American Foundry Society petition for
review, No. 04-1191. This proposed rule addresses the need for
alternative emissions limits for cupolas at existing foundries and
clarification of other rule requirements. EPA anticipates that these
proposed amendments will resolve the remaining issues raised by the
petitioners.
These amendments are set out in Attachment A to a settlement
agreement between EPA and the petitioners that became final on March 9,
2007. In accordance with section 113(g) of the CAA, EPA published a
notice of the proposed settlement agreement (72 FR 1986, January 17,
2007) and provided a 30-day comment period which ended on February 16,
2007. The settlement agreement requires that the EPA Administrator sign
proposed amendments no later than April 9, 2007.
In addition, since publication of the final rule, we have
identified a few minor editorial errors requiring correction. Rather
than publish a separate notice of corrections, we are including those
changes along with the proposed amendments.
III. Summary of Proposed Amendments
A. Emissions Limitations
1. New Compliance Options for Cupola Metal Melting Furnaces
Section 63.7690(a)(2) of the NESHAP establishes HAP emissions
limits for cupola metal melting furnaces at existing iron and steel
foundries. The owner or operator may elect to comply with a limit of
0.006 grains per dry standard cubic foot (gr/dscf) of particulate
matter (PM) or 0.0005 gr/dscf of total metal HAP. The PM emissions
limits for cupolas were based on an evaluation of the average
performance achieved by the top 12 percent of the cupola emissions
sources (i.e., the ``MACT floor''). Because baghouses (the technology
on which the MACT floor performance was based) are generally designed
to meet a specified outlet concentration limit and because EPA Method 5
(40 CFR part 60, appendix A) directly determines concentration, a
concentration-based emissions limit was selected for inclusion in the
rule. The alternative concentration-based emissions limit expressed as
total metal HAP provided equivalent metal HAP emissions reductions as
the MACT floor PM emissions limit. We documented the determination of
these emissions limits in a memorandum titled, ``Determination of the
MACT Floor Metal HAP Emission Limits for Iron and Steel Foundries'',
which is included in the docket for the final rule (Docket Item No.
EPA-HQ-OAR- 2002-0034-0239).
As part of our discussions with the petitioners on technical
issues, we recognized the need for an equivalent mass-based emissions
limit for cupola melting furnaces to allow the use of control
technologies that are designed on a mass removal basis rather than an
outlet concentration basis. We reviewed the data previously identified
for the top 12 percent of cupola emissions sources as well as the 6th
percentile unit on which the promulgated emissions limit was based.
These data indicate that the equivalent mass PM emissions rate for a
baghouse operating at the MACT floor emissions limit for cupolas at
existing sources (0.006 gr/dscf) is 0.10 pound per ton (lb/ton) of
metal charged. In terms of total metal HAP, the MACT-equivalent mass
emissions rate for cupolas at existing sources is 0.008 lb/ton. We
documented the determination of these mass-based emissions limits in a
memorandum titled, ``Determination of a MACT Floor Equivalent Emission
Limit for Cupola Melting Furnaces,'' which is included in the docket
for this rulemaking (Docket Item EPA-HQ-OAR-2002-0034-0223). Therefore,
we are proposing to amend the emissions limits in 40 CFR 63.7690(a)(2)
for cupolas at existing sources to add alternative limits of 0.10 lb/
ton of PM or 0.008 lb/ton of total metal HAP.
2. Fugitive Emissions Opacity Limit
Some of the petitioners requested that we revise the opacity limit
for fugitive emissions in 40 CFR 63.7690(a)(7) to clarify that the
limit does not apply to fugitive emissions that are unrelated to
emissions sources subject to the NESHAP. According to the petitioners,
the rule could be interpreted to apply to fugitive emissions from
foundry-related operations not subject to the rule or operations in
other source categories that may be co-located in foundries.
Some foundries are co-located with other manufacturing processes
that are housed in separate buildings. We did not intend to set
emissions limitations for these co-located operations. Therefore, we
are clarifying that the opacity emissions limitations apply only to
buildings that house iron and steel foundry emissions sources. If
nonfoundry operations are housed in the same building as the foundry
operations, the foundry must comply with the opacity limits for that
building.
3. Triethylamine Emissions Limit
In response to the petitioners' suggestion, we are proposing to
clarify the language of the emissions limit for triethylamine (TEA) in
Sec. 63.7690(a)(11) by replacing the reference to test conditions
(``as determined when scrubbing with fresh acid solution'') with the
phrase ``according to the performance test procedures in Sec.
63.7732(g)'' since Sec. 63.7732(g) contains the requirement to conduct
the test when scrubbing with fresh acid solution.
Although the existing NESHAP primarily address the control of HAP
metals, there are potential opportunities for foundries to reduce
emissions of other HAP such as TEA through the use of low-HAP binders
and other pollution prevention (P2) techniques. Current information
indicates that these P2 methods show promise, but they are not
appropriate for all foundries or casting methods. And, in some cases,
it can be quite costly for the foundry to incorporate P2 methods into
their
[[Page 19153]]
overall process. EPA encourages foundries to explore the various P2
options available and use them when appropriate and cost-effective to
further reduce their HAP footprint.
B. Work Practice Standards
1. Capture and Collection Systems
Section 63.7690(b)(1) of the NESHAP requires the owner or operator
of an iron or steel foundry to install, operate, and maintain a capture
and collection system for all emissions sources subject to a limit or
standard for volatile organic hazardous air pollutants (VOHAP) or TEA
in 40 CFR 63.7690(a)(8) through (11). One petitioner was concerned that
this provision could be construed to require capture and collection
systems for electric arc furnaces and electric induction furnaces, even
though these furnaces are not directly subject to a VOHAP limit.
According to the petitioner, the scrap certification and inspection/
selection requirements in 40 CFR 63.7700 could be understood as work
practice standards to limit organics from entering electric arc
furnaces and electric induction furnaces. It could be inferred that a
``standard'' limiting VOHAP does exist for these furnaces and
therefore, a capture and collection system is required. A similar
concern exists for foundries that decide to meet the work practice
requirement in 40 CFR 63.7700(e) instead of the VOHAP emissions limit
in 40 CFR 7690(a)(9). The petitioner requests that EPA confirm that the
scrap certification and inspection/selection requirements are not
considered VOHAP work practice standards which would necessitate a
capture and collection system.
It is our intent that the requirements for capture and collection
systems apply to emissions sources subject to an emissions limit but
not to an emissions source subject to work practice standards. A
capture and control system that routes emissions to an add-on control
device is not needed because the work practice acts to reduce or
prevent the release of emissions. In response to the petitioner's
concerns, we are proposing to clarify the requirement in Sec.
63.7690(b)(1) by deleting the reference to ``standard''.
2. Scrap Management
Section 63.7700(a) of the NESHAP establishes work practice
standards to minimize the organics and HAP metals in charge materials.
The owner or operator must comply with certification requirements in
Sec. 63.7700(b) or operate according to a scrap selection and
inspection plan required in Sec. 63.7700(c). One commenter requested
that the work practice standards specify that the requirements for the
certification and the written plan specify ``chlorinated'' plastics.
Plastics were included in the list of undesirable scrap material
primarily because certain types of plastics, such as polyvinyl
chloride, could lead to the formation of dioxins. We did not intend to
make certain metal components, such as Quiet Steel([reg]), that contain
some plastics that cannot be removed from the scrap unrecyclable.
Recycling these materials in foundries is environmentally preferable to
landfilling these materials. Therefore, to clarify our intent, we now
specify that it is ``chlorinated'' plastics that are to be removed from
the scrap material.
The petitioner also objected to the requirement in 40 CFR
63.7700(c)(2) for the owner or operator to obtain and maintain onsite a
copy of the procedures used by the scrap supplier for either removing
accessible mercury switches or for purchasing automobile bodies that
have had the switches removed. According to the petitioner, it is
difficult for some plants to obtain such written procedures from scrap
suppliers. In this case, the plant should be able to document their
attempts to obtain a copy of the procedures. The proposed amendments
include an alternative procedure that allows the plant to document
their attempts to obtain a copy of the procedures from the scrap
suppliers servicing their area. We note, however, that under 40 CFR
63.7700(c)(2) the materials acquisition program must specify that the
scrap supplier remove accessible mercury switches from the trunks and
hoods of any automotive bodies contained in the scrap in addition to
accessible lead components such as batteries and wheel weights. It is
incumbent on the foundry owner or operator to communicate these
specifications to their scrap suppliers.
3. Scrap Preheaters
Section 63.7700(e) of the rule establishes requirements for scrap
preheaters at an existing iron and steel foundry. The owner or operator
must install, operate, and maintain a gas-fired preheater according to
40 CFR 63.7700(e)(1) or charge only certain materials according to 40
CFR 63.7700(e)(2). One petitioner was concerned that the language in 40
CFR 63.7700(e)(1) could be interpreted to require foundries to install
gas-fired preheaters, even when not necessary for foundry operations.
It was not our intent to mandate installation of preheaters, but rather
to establish requirements for those existing facilities that use scrap
preheaters in lieu of selecting the option in 40 CFR 63.7700(e)(2).
Therefore, we are proposing to clarify Sec. 63.7700(e)(1) by deleting
the word ``install''. Instead, the owner or operator would be required
to operate and maintain a gas-fired preheater where the flame directly
contacts the scrap charged.
C. Operation and Maintenance Requirements
One petitioner suggested that the requirement in 40 CFR 63.7710(b)
for an operation and maintenance plan would be better understood if it
clarified the emissions sources subject to the plan requirements. The
proposed amendments clarify that the requirement applies to each
capture and collection system and control device for an emissions
source subject to a PM, metal HAP, TEA, or VOHAP emissions limit in 40
CFR 63.7690(a).
D. Compliance With Alternative Emissions Limits
The existing NESHAP establishes PM emissions limits and alternative
emissions limits expressed in total metal HAP for cupolas and other
foundry processes. In response to requests by the petitioners, we are
proposing amendments to 40 CFR 63.7732, 40 CFR 63.7690, and 40 CFR
63.7734 to clarify our original intent to allow foundries to
demonstrate compliance with any of the applicable alternative emissions
limitations that are provided for a specific emissions source. When
multiple alternative emissions limitations are provided for a specific
emissions source, iron and steel foundries can demonstrate initial
compliance with any of the alternative limits; they are not required to
comply with all of the alternative emissions limits at any one time. We
are also clarifying a facility's ability to change their selected
compliance alternative and the procedures needed to effect that change.
However, regarding continuous compliance, the facility is expected to
continuously comply with the alternative emissions limit that was
selected as their compliance option as demonstrated in their most
recent performance test. The facility may choose to alter their
selected alternative but must continue to comply with the previously
selected alternative until they successfully demonstrate compliance
with the new alternative emissions limitation.
We are also proposing requirements for determining initial
compliance for cupola melting furnaces at existing iron and steel
foundries that are subject to the new mass rate emissions limit.
Revisions to 40 CFR 63.7732(b) and (c) would include new equations for
[[Page 19154]]
determining PM or total metal HAP emissions from cupolas in the lb/ton
format. Other amendments to 40 CFR 63.7732(b) and (c) would clarify
test method and emissions source sampling requirements.
1. Single Performance Test for Control Devices Serving Multiple Units
Section 63.7734 of the NESHAP requires iron and steel foundries to
demonstrate initial compliance with PM emissions limits by conducting a
performance test for each process unit according to the procedures in
40 CFR 63.7732. One petitioner pointed out that a common emissions
control system may serve two similar or identical cupolas or serve
multiple furnaces or process units. According to the petitioner, a
requirement for separate tests of the control device while the
emissions sources are operating is redundant and imposes unnecessary
costs because the control device should perform the same on each
identical furnace.
We acknowledge that there are certain control device configurations
that we cannot fully address within the rule requirements. These
situations are best evaluated on a case-by-case basis. Therefore, we
are proposing to resolve the petitioner's concern by adding a new
provision to the performance test requirements. The proposed amendment
requires foundries to submit a site-specific test plan for the
situation described by the petitioner or other situations not expressly
considered in 40 CFR 63.7734. The site-specific test plan, which is
subject to approval by the Administrator, would explain the procedures
that would be followed during the test, such as operation of the unit
or units at the maximum operating condition of the control system. The
Administrator or delegated authority would determine on a case-by-case
basis if one representative furnace/control device configuration may be
tested.
2. Sampling Procedure for Electric Arc Furnaces, Electric Induction
Furnaces, and Scrap Preheaters
One petitioner objected to the sampling instructions in 40 CFR
63.7732(c)(4) and (5) for electric arc and electric induction metal
melting furnaces (when metal is being melted) and scrap preheaters
(when scrap is being preheated) as inappropriate restrictions on
performance testing. Many operations that occur during the furnace
melting process are considered part of typical operation. Scrap
preheaters operate on a batch basis and do not heat scrap for extended
periods of time. It is not practical to start and stop tests for these
emissions sources over the course of a heat until the required sampling
time is accumulated. According to the petitioner, testing during all
phases of operations is consistent with the requirement in Sec.
63.6(f)(2)(iii)(A) of the NESHAP General Provisions (40 CFR part 63,
subpart A), which state that a performance test must be conducted under
representative operating conditions of the source.
In response to these concerns, we are proposing to clarify that the
initial compliance demonstrations for electric arc metal melting
furnaces, electric induction metal melting furnaces, and scrap
preheaters should be conducted under normal production conditions. The
emissions limitations derived for these sources used data for various
production cycles, including charging, melting, back-charging, and
tapping. As the MACT floor emissions limitation was based on various
production cycles and because significant PM and metal HAP emissions
can occur from these other production cycles, the promulgated
requirement to test only during melting is being amended to more
accurately align the testing requirements to the testing procedures
used as the basis of the MACT emissions limitation. The proposed
amendments require sampling during normal operating conditions, which
may include charging, melting, alloying, refining, slagging, and
tapping (for a furnace) or charging, heating, and discharging (for a
scrap preheater).
3. Minimum Sampling Volume for Total Metal HAP
One petitioner pointed out that it was unnecessary to specify the
minimum sample volume for test runs by EPA Method 29 (40 CFR part 60,
appendix A) because the method already includes a requirement. The
proposed amendments remove this requirement from 40 CFR 63.7732(c)(2).
4. Opacity Test
Section 63.7732(d) of the existing rule establishes the
requirements for opacity tests. The proposed amendments instruct the
certified observer how to take opacity readings by Method 9 (40 CFR
part 60, appendix A) for a building that has many openings. This issue
was not addressed in the NESHAP. Under the proposed amendments, the
observer would be allowed to take readings from a limited number of
openings or vents that appear to have the highest opacities instead of
making observations for each opening or vent from the building or
structure. Alternatively, a single observation for the entire building
would be allowed if the fugitive release points afford such an
observation.
Section 63.7732(d)(2) requires that opacity observations to
demonstrate compliance with the fugitive emissions opacity standards in
40 CFR 63.7690(a)(7) overlap with the PM performance tests. One
petitioner stated that it is not feasible for opacity observations to
overlap with PM performance tests in all cases because subsequent tests
are required every 6 months for opacity and every 5 years for PM
emissions. The petitioner raised the concern that the rule could have
been read to require a PM performance test during each opacity test;
however, this was not our intent. In response to the petitioner's
concern, we are proposing amendments to 40 CFR 63.7732(d)(2) to clarify
that opacity tests are to be conducted during PM performance tests, but
that PM performance tests are not required to occur during the
semiannual opacity tests.
5. Alternative Test Method
Section 63.7732(g)(v) of the NESHAP requires the use of EPA Method
18 (40 CFR part 60, appendix A) to determine the triethylamine (TEA)
concentration of gases from the TEA cold box mold or core making line.
One petitioner requested EPA to allow an alternative to Method 18
because the detection limit of Method 18, which is approximately 1 part
per million by volume (ppmv), is not significantly less than the
emissions limit. The petitioner believed this could make compliance
determinations problematic. According to the petitioner, operators will
need to use the alternative silica gel adsorption tube sampling
technique in section 8.2.4 of Method 18 to achieve lower detection
limits, but that not all facilities will know to specify the
alternative sampling techniques to their testing contractors. The
commenter stated that the alternative methodology is equivalent to
National Institute of Occupational Safety and Health (NIOSH) Method
2010 and requested that the rule allow the NIOSH method as an
acceptable alternative. If the rule specifies the NIOSH method as an
alternative, facilities can ensure that proper sampling techniques are
used to achieve the low detection limits.
We agree that NIOSH Method 2010 is an acceptable and equivalent
sampling alternative to EPA Method 18. However, the NIOSH method does
not include quality assurance performance requirements. Therefore, we
are proposing NIOSH Method 2010, ``Amines, Aliphatic'' (incorporated by
reference-see Sec. 63.14) as an acceptable alternative to EPA Method
18 (40 CFR
[[Page 19155]]
part 60, appendix A) provided the performance requirements outlined in
section 13.1 of EPA Method 18 are satisfied. Method 2010 is included in
the NIOSH Manual of Analytical Methods (4th edition, NIOSH Publication
94-113, August 1994). The manual is available from the Government
Printing Office and the National Technical Information Service (NTIS),
NTIS publication no. PB95154191. The NIOSH method may also be found on
the NIOSH Web site at the following address: www.cdc.gov/niosh/nmam/
method-4000.html.
6. Procedures for Establishing Operating Limits
One petitioner pointed out that the procedures for establishing
control device operating limits in 40 CFR 63.7733(b) through (d) should
not instruct operators to compute and record the 3-hour average
parameter value because some sampling durations are based on sampling
volumes which do not correspond to a 3-hour period. This requirement
could be misinterpreted to require performance testing over a period of
at least 3 hours.
We originally intended that the performance test consist of three
1-hour tests runs, and that the control device parameter operating
limit would be based on the average of these data. However, there are
instances where the duration of the sampling runs may be greater than 1
hour. The proposed amendments delete the reference to the 3-hour
average from the test procedures and clarify that the operator is to
compute and record the average operating parameter value for each valid
sampling run in which the applicable limit is met.
7. Repeat Performance Tests
One petitioner requested EPA to clarify that demonstrating
compliance by one method does not preclude a demonstration of
compliance using an alternative method at a later date. EPA agrees that
a plant may elect to demonstrate compliance with an alternative
emissions limit during the repeat performance tests conducted at least
every 5 years. Furthermore, the plant may elect to conduct a
performance test earlier than 5 years in order to change an operating
limit or to demonstrate compliance with a different alternative
emissions limit. The proposed amendments clarify these testing options
in amendments to 40 CFR 63.7731(a). A test conducted for the purpose of
changing operating limits is subject to notification requirements in 40
CFR 63.7750(d).
E. Monitoring Requirements
1. Baghouse Monitoring Requirements
Section 63.7740(b) of the existing NESHAP requires a bag leak
detection system for each negative pressure baghouse and for each
positive pressure baghouse equipped with a stack where the baghouse is
applied to meet any PM or total metal HAP emissions limitation in
subpart EEEEE. This provision also requires inspection of each baghouse
according to the requirements in 40 CFR 63.7740(b) (1) through (8). One
petitioner states that the final rule appears to omit any monitoring
requirements for positive pressure baghouses not equipped with a stack.
Although these units are not required to install a bag leak detection
system, we intended to require the visual inspection of these positive
pressure baghouses to ensure their proper performance. Therefore, we
are proposing amendments to clarify our original intent to require
monitoring inspections of positive baghouses that are not equipped with
a stack. The proposed amendments to 40 CFR 63.7740(b) clarify the text
to ensure that the requirements in this paragraph for installing and
using a bag leak detection system apply only to negative pressure
baghouses and positive pressure baghouses equipped with a stack. The
inspection requirements would be separated and placed in a new
paragraph (c) and clarified to state that the inspection requirements
apply to each baghouse regardless of type. The proposed amendments to
40 CFR 63.7740 also renumber the paragraphs which follow new paragraph
(c). Similar clarifications would be made to the requirements for
demonstrating continuous compliance in 40 CFR 63.7743(c).
2. Demonstration of Initial Compliance With Bag Leak Detection System
Operation and Maintenance Requirements
Section 63.7736(c) of the existing NESHAP instructs the owner or
operator how to demonstrate initial compliance with the requirements
for bag leak detection systems. Under 40 CFR 63.7736(c)(1), the owner
or operator must submit the bag leak detection system monitoring plan
to the Administrator for approval according to the requirements in 40
CFR 63.7710(b). One petitioner requested EPA to clarify this provision
because the requirement could be interpreted to necessitate submission
of the monitoring plan independent of the operation and maintenance
plan. Our intent in the existing rule was to include the bag leak
detection system information in the operation and maintenance plan to
streamline the approval process and avoid the administrative costs
associated with a separate submission. In addition, having one
integrated plan provides a centralized reference tool for control
device operation and maintenance requirements. The proposed amendments
to 40 CFR 63.7736(c)(1) clarify the requirement to submit the bag leak
system monitoring information to the Administrator within the written
operation and maintenance plan for approval according to the
requirements in Sec. 63.7710(b).
3. Installation, Operation, and Maintenance Requirements for Monitors
One petitioner requested that EPA revise the requirements for
operation and maintenance of continuous parameter monitoring systems
(CPMS) to more clearly describe the inspection requirements. Under the
operation and maintenance requirements for flow measurement devices in
40 CFR 63.7741(a)(1)(iv), the owner or operator must perform monthly
inspections of all flow sensor components for integrity, all electrical
connections for continuity, and all mechanical connections for leakage.
The proposed amendments change this provision to require a monthly
visual inspection of all components, including all electrical and
mechanical connections for proper functioning. The same changes would
be made to the monthly inspection requirements for other types of
monitoring devices in Sec. Sec. 63.7741(a)(2)(vi), (c)(1)(vi),
(c)(2)(iv), (d)(8), and (e)(2)(iv).
We are proposing these changes in response to the concerns
expressed by one petitioner who explained that the changes are needed
to ensure the ability of a facility to comply on a monthly basis.
According to the petitioner, the ability of a facility to specifically
inspect for ``integrity'', ``continuity'' and ``leakage'' depends on
where the components are located, but a facility would be able to
readily determine proper functioning. One the facility determines that
a connection is not working properly, additional steps can be taken to
address the problem, which may include removing a barrier to allow
access to the connection. In addition, testing of the electrical
connections for continuity is not necessary when indicators are
routinely used to show whether the current is flowing. A visual
inspection is sufficient to ensure that current is flowing to each
electrical connection.
The proposed amendments also revise the requirement for pressure
[[Page 19156]]
measurement devices in 40 CFR 63.7741(a)(2)(iii) and 40 CFR
63.7741(c)(1)(iv) for a ``daily check of the pressure tap for
pluggage.'' We are proposing to require a daily check for pluggage when
using a regular pressure tap and a monthly check when using a non-
clogging pressure tap. Less frequent checks for non-clogging pressure
taps would encourage use of newer technology and provide an inspection
frequency commensurate with the operation of a non-clogging pressure
tap. The proposed amendments also clarify the requirements for pressure
measurement devices in 40 CFR 63.7741(a)(2)(iv) and 40 CFR
63.7741(c)(1)(iv) to allow the use of a manometer or equivalent device
for calibrations.
F. Recordkeeping and Reporting Requirements
The proposed amendments clarify two of the recordkeeping
requirements in 40 CFR 63.7752(a)(4). The requirement for the annual
quantity of chemical binder or coating materials used to make molds and
cores would be revised to require the annual quantity of chemical
binder or coating materials used to coat or make molds and cores. We
inadvertently omitted the word ``coat'' from the original rule
language. The requirement for records of the annual quantity of HAP
used would state that records are required of the annual quantity of
HAP used in these chemical binder or coating materials at the foundry,
as calculated from the recorded quantities and chemical compositions
(from Material Data Safety Sheet or other documentation). This proposed
amendment clarifies that the HAP records requirement is specific to the
chemicals used in the mold and core-making and coating operations and
not to other HAP materials used at the foundry such as solvents used to
clean or degrease equipment.
Proposed amendments to the reporting requirements allow foundries
to report the results of the semiannual opacity tests within the
semiannual reports rather than having to submit these semiannual
documents separately. This change would reduce the administrative costs
associated with submission of separate reports. Other proposed
amendments to the reporting requirements clarify the requirements for
an immediate startup, shutdown, and malfunction report by adding the
same language used in 40 CFR 63.10(d)(5)(ii). The proposed amendments
require an immediate report if you had a startup, shutdown, or
malfunction and the source exceeded any applicable emissions limitation
in 40 CFR 63.7690.
G. Definitions
We are proposing to add definitions of the terms ``off blast'' and
``on blast'' to 40 CFR 63.7765. These definitions would clarify that
blast conditions used to bring the cupola up to operating temperature
during start-up are not covered by the VOHAP parameter operating limit
in 40 CFR 63.7690(b)(3). The existing parameter operating limit
requires the foundry to operate each combustion device applied to
emissions from a cupola that is subject to the VOHAP emissions limit so
that the 15-minute average combustion zone temperature does not fall
below a certain level. The operating limit states that periods when the
cupola is off-blast and for 15 minutes after going on-blast from an
off-blast condition are not included in the 15-minute average
combustion zone temperature. The term ``off blast'' would be defined as
those periods of cupola operation when the cupola is not actively being
used to produce molten metal. Off-blast conditions include cupola
startup procedures as defined in the startup, shutdown, and malfunction
plan. Off-blast conditions also include idling conditions when the
blast air is turned off or down to the point that the cupola does not
produce additional molten metal. The term ``on blast'' would mean those
periods of cupola operation when combustion (blast) air is introduced
to the cupola furnace and the furnace is capable of producing molten
metal. On blast conditions are characterized by both blast air
introduction and molten metal production.
The petitioners also raised the concern that only a limited number
of metal constituents were evaluated when assessing the total metal HAP
emissions limits. They noted that not all constituents for which EPA
Method 29 (40 CFR part 60, appendix A) is applicable are HAP. They also
sought clarification on how to calculate the total metal HAP if certain
constituents were below the analytical detection limit.
The evaluation of the total metal HAP emissions limits actually
included most Method 29 HAP constituents, although it did not include
phosphorus. The evaluation did not include detection limits or other
non-zero values for metal constituents measured below detection limit.
To address the petitioners' concerns, we are proposing to revise the
definition of ``total metal HAP'' to specify the analytes to be
included and how non-detect values are to be used in calculating the
total metal HAP quantity. The proposed definition is based on the
analytes and methods used to derive the total metal HAP alternative.
The definition of ``total metal HAP'' would be the sum of the
concentrations of antimony, arsenic, beryllium, cadmium, chromium,
cobalt, lead, manganese, mercury, nickel, and selenium as measured by
EPA Method 29 (40 CFR part 60, appendix A). Only the measured
concentration of the listed analytes that are present at concentrations
exceeding one-half of the quantification limit of the analytical method
are used in the sum. If any of the analytes are not detected or are
detected at concentrations less than one-half the quantification limit
of the analytical method, the concentration of those analytes is
assumed to be zero for the purposes of calculating the total metal HAP
for this subpart.
We are also proposing to clarify the definition of ``scrap
preheater'' to differentiate scrap dryers that are used solely to
remove moisture from the scrap metal from scrap preheaters. Scrap
preheaters are used to preheat the metal scrap and reduce the energy
required to effect melting. Most scrap preheaters heat the scrap metal
to 400 degrees Fahrenheit or higher while scrap dryers operate at lower
temperatures and are used solely to remove moisture from the scrap
metal as a safety consideration when operating an electric induction
furnace. Because of the lower operating temperatures, we do not believe
that scrap dryers are a significant potential source for VOHAP
emissions. We are proposing to amend the definition of ``scrap
preheater'' to state that scrap dryers, which are used solely to remove
water from metal scrap that does not contain any volatile impurities or
other tramp materials, are not considered to be scrap preheaters for
purposes of this subpart.
H. Applicability
One of the petitioners asked EPA to reference the CAA or NESHAP
General Provisions definition of ``major source'' in 40 CFR 63.7681 (Am
I subject to this subpart?). We are proposing to add a reference to 40
CFR 63.2 as requested by the commenter. This addition would clarify
that when we refer to a ``major source'' of hazardous air pollutants in
40 CFR 63.7681, we are referring to the definition of major source in
40 CFR 63.2, and not, for example, to the definition of major source in
40 CFR 51.166.
I. Editorial Corrections
We are proposing to correct a grammatical error in 40 CFR
63.7710(b), which should refer to an emissions
[[Page 19157]]
source subject to a (rather than ``an'') PM, metal HAP, TEA, or VOHAP
emissions limit in 40 CFR 63.7690(a). A comma would be added to 40 CFR
63.7734(a)(11). The words ``as possible'' were inadvertently omitted
from 40 CFR 63.7741(a)(2)(i) and would be added. The proposed
amendments also correct a misspelling of the word ``calendar'' in 40
CFR 63.7700(c)(3)(iii).
IV. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory Planning and Review
Under Executive Order 12866 (58 FR 51735, October 4, 1993), this
action is a ``significant regulatory action'' because it may ``raise
novel legal or policy issues.'' Accordingly, EPA submitted this action
to the Office of Management and Budget (OMB) for review under Executive
Order 12866 and any changes made in response to OMB recommendations
have been documented in the docket for this action.
B. Paperwork Reduction Act
This action does not impose any new information collection burden.
The proposed amendments add a new compliance alternative, allow a new
alternative test method, and clarify requirements in the existing rule.
One proposed amendment to the baghouse monitoring requirements
clarifies our original intent to require inspections of positive
pressure baghouses not equipped with a stack. No new burden is
associated with this proposed requirement because the burden was
included in the approved information collection request (ICR) for the
existing rule. The OMB has previously approved the information
collection requirements contained in the existing regulation (40 CFR
part 63, subpart EEEEE) under the provisions of the Paperwork Reduction
Act, 44 U.S.C. 3501 et seq. and has assigned OMB control number 2060-
0543, EPA ICR number 2096.02. A copy of the OMB-approved ICR may be
obtained from Susan Auby, Collection Strategies Division, U.S. EPA
(2822T), 1200 Pennsylvania Ave., NW., Washington, DC 20460, by e-mail
at auby.susan@epa.gov, or by calling (202) 566-1672.
Burden means the total time, effort, or financial resources
expended by persons to generate, maintain, retain, disclose, or provide
information to or for a Federal agency. This includes the time needed
to review instructions; develop, acquire, install, and utilize
technology and systems for the purposes of collecting, validating, and
verifying information, processing and maintaining information, and
disclosing and providing information; adjust the existing ways to
comply with any previously applicable instructions and requirements;
train personnel to be able to respond to a collection of information;
search data sources; complete and review the collection of information;
and transmit or otherwise disclose the information.
An agency may not conduct or sponsor, and a person is not required
to respond to, a collection of information unless it displays a
currently valid OMB control number. The OMB control numbers for EPA's
regulations in 40 CFR part 63 are listed in 40 CFR part 9.
C. Regulatory Flexibility Act
The Regulatory Flexibility Act (RFA) generally requires an agency
to prepare a regulatory flexibility analysis of any rule subject to
notice and comment rulemaking requirements under the Administrative
Procedure Act or any other statute unless the agency certifies that the
rule would not have a significant economic impact on a substantial
number of small entities. Small entities include small businesses,
small not-for-profit enterprises, and small governmental jurisdictions.
For the purposes of assessing the impacts of the proposed
amendments 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 (less than 500 employees
for NAICS codes 331511, 331512, and 331513); (2) a small governmental
jurisdiction that is a government of a city, county, town, school
district, or special district with a population of less than 50,000;
and (3) a small organization that is any not-for-profit enterprise
which is independently owned and operated and is not dominant in its
field.
After considering the economic impacts of the proposed amendments
on small entities, I certify that this action will not have a
significant economic impact on a substantial number of small entities.
In determining whether a rule has a significant economic impact on a
substantial number of small entities, the impact of concern is any
significant adverse economic impact on small entities, since the
primary purpose of the regulatory flexibility analyses is to identify
and address regulatory alternatives ``which minimize any significant
economic impact of the rule on small entities.'' 5 U.S.C 603 and 604.
Thus, an agency may certify that a rule will not have a significant
economic impact on a substantial number of small entities if the rule
relieves regulatory burden, or otherwise has a positive economic effect
on all of the small entities subject to the rule.
There would not be any adverse impacts on any source (including any
small entity) as a result of the proposed amendments because the
proposed amendments provide an overall economic benefit to entities
subject to the rule. The proposed amendments do not create any new
requirements or burdens that were not already included in the economic
impact assessment for the existing rule. The proposed amendments
relieve regulatory burden for all entities as a result of the
operational flexibility afforded by the alternative compliance option,
alternative test method, and provisions allowing plants to combine
multiple reports into a single submission. We have therefore concluded
that these proposed amendments will relieve regulatory burden for all
affected small entities. We continue to be interested in the potential
impacts of the proposed action on small entities and welcome comments
on issues related to such impacts.
D. Unfunded Mandates Reform Act
Title II of the Unfunded Mandates Reform Act of 1995 (UMRA), Pub.
L. 104-4, establishes requirements for Federal agencies to assess the
effects of their regulatory actions on State, local, and tribal
governments and the private sector. Under section 202 of the UMRA, EPA
generally must prepare a written statement, including a cost-benefit
analysis, for proposed and final rules with ``Federal mandates'' that
may result in expenditures by State, local, and tribal governments, in
the aggregate, or by the private sector, of $100 million or more in any
1 year. Before promulgating an EPA rule for which a written statement
is needed, section 205 of the UMRA generally requires EPA to identify
and consider a reasonable number of regulatory alternatives and adopt
the least costly, most cost-effective, or least burdensome alternative
that achieves the objectives of the rule. The provisions of section 205
do not apply when they are inconsistent with applicable law. Moreover,
section 205 allows EPA to adopt an alternative other than the least
costly, most cost-effective, or least burdensome alternative if the
Administrator publishes with the final rule an explanation why that
alternative was not adopted. Before EPA establishes any regulatory
requirements that may significantly or uniquely affect small
governments, including tribal governments, it must have developed
[[Page 19158]]
under section 203 of the UMRA a small government agency plan. The plan
must provide for notifying potentially affected small governments,
enabling officials of affected small governments to have meaningful and
timely input in the development of EPA regulatory proposals with
significant Federal intergovernmental mandates, and informing,
educating, and advising small governments on compliance with the
regulatory requirements.
EPA has determined that the proposed amendments do 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 the
private sector in any one year. The proposed amendments are expected to
result in an overall reduction in expenditures for the private sector
and are not expected to impact State, local, or tribal governments.
Thus, the proposed amendments are not subject to the requirements of
sections 202 and 205 of the UMRA. In addition, the proposed amendments
do not significantly or uniquely affect small governments. The proposed
amendments contain no requirements that apply to such governments, and
impose no obligations upon them.
E. Executive Order 13132: Federalism
Executive Order 13132 (64 FR 43255, August 10, 1999) requires EPA
to develop an accountable process to ensure ``meaningful and timely
input by State and local officials in the development of regulatory
policies that have federalism implications.'' ``Policies that have
federalism implications'' are defined in the Executive Order to include
regulations that have ``substantial direct effects on the States, on
the relationship between the national government and the States, or on
the distribution of power and responsibilities among the various levels
of government.''
The proposed amendments do not have federalism implications. They
would 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. The proposed
amendments do not impose any requirements on State and local
governments. Thus, Executive Order 13132 does not apply to the proposed
amendments.
In the spirit of Executive Order 13132, and consistent with EPA
policy to promote communications between EPA and State and local
government, EPA specifically solicits comments on this proposed rule
from State and local officials.
F. Executive Order 13175: Consultation and Coordination With Indian
Tribal Governments
Executive Order 13175 (65 FR 67249, November 6, 2000), requires EPA
to develop an accountable process to ensure ``meaningful and timely
input by tribal officials in the development of regulatory policies
that have tribal implications.'' The proposed rule amendments do not
have tribal implications, as specified in Executive Order 13175. They
would not have substantial direct effects on tribal governments, on the
relationship between the Federal government and Indian tribes, or on
the distribution of power and responsibilities between the Federal
government and Indian tribes, as specified in Executive Order 13175.
The proposed amendments impose no requirements on tribal governments.
Thus, Executive Order 13175 does not apply to the proposed amendments.
G. Executive Order 13045: Protection of Children From Environmental
Health and Safety Risks
Executive Order 13045, ``Protection of Children from Environmental
Health Risks and Safety Risks'' (62 FR 19885, April 23, 1997) applies
to any rule that: (1) Is determined to be ``economically significant''
as defined under Executive Order 12866, and (2) concerns an
environmental health or safety risk that EPA has reason to believe may
have a disproportionate effect on children. If the regulatory action
meets both criteria, EPA must evaluate the environmental health or
safety effects of the planned rule on children, and explain why the
planned regulation is preferable to other potentially effective and
reasonably feasible alternatives considered by the Agency.
EPA interprets Executive Order 13045 as applying only to those
regulatory actions that are based on health or safety risks, such that
the analysis required under section 5-501 of the Executive Order has
the potential to influence the regulation. These proposed amendments
are not subject to the Executive Order because they are based solely on
technology performance.
H. Executive Order 13211: Actions That Significantly Affect Energy
Supply, Distribution, or Use
These proposed amendments are not a ``significant energy action''
as defined in Executive Order 13211, ``Actions Concerning Regulations
That Significantly Affect Energy Supply, Distribution, or Use'' (66 FR
28355, May 22, 2001) because they are not likely to have a significant
adverse effect on the supply, distribution, or use of energy. Further,
we have concluded that these proposed amendments are not likely to have
any adverse energy effects because energy requirements would remain at
the existing level. No additional pollution controls or other equipment
that would consume energy are required by the proposed amendments.
I. National Technology Transfer Advancement Act
Section 12(d) of the National Technology Transfer and Advancement
Act (NTTAA) of 1995 (Pub. L. No. 104-113, Section 12(d), 15 U.S.C. 272
note) directs EPA to use voluntary consensus standards (VCS) in its
regulatory activities, unless to do so would be inconsistent with
applicable law or otherwise impractical. The VCS are technical
standards (e.g., materials specifications, test methods, sampling
procedures, and business practices) that are developed or adopted by
VCS bodies. The NTTAA directs EPA to provide Congress, through OMB,
explanations when the Agency does not use available and applicable VCS.
The proposed amendments involve technical standards. These proposed
amendments include an alternative methodology, the NIOSH Method 2010,
``Amines, Aliphatic'' (incorporated by reference in Sec. 63.14) for
EPA Method 18 (40 CFR part 60, appendix A) to determine the
triethylamine (TEA) concentration of gases from the TEA cold box mold
or core making line provided the performance requirements outlined in
section 13.1 of EPA Method 18 are satisfied.
Consistent with the NTTAA, EPA conducted searches to identify
voluntary consensus standards in addition to these EPA and alternative
methods. No applicable voluntary consensus standards were identified.
For the methods required or referenced by this proposed rule, a
source may apply to EPA for permission to use alternative test methods
or alternative monitoring requirements in place of any required testing
methods, performance specifications, or procedures under Sec. Sec.
63.7(f) and 63.8(f) of Subpart A of the General Provisions.
EPA welcomes comments on this aspect of the proposed rulemaking
and, specifically, invites the public to identify potentially-
applicable voluntary consensus standards and to explain why such
standards should be used in this regulation.
[[Page 19159]]
J. Executive Order 12898: Federal Actions To Address Environmental
Justice in Minority Populations and Low-Income Populations
Executive Order 12898 (59 FR 7629, February 16, 1994) establishes
Federal executive policy on environmental justice. Its main provision
directs Federal agencies, to the greatest extent practicable and
permitted by law, to make environmental justice part of their mission
by identifying and addressing, as appropriate, disproportionately high
and adverse human health or environmental effects of their programs,
policies, and activities on minority populations and low-income
populations in the United States.
EPA has determined that these proposed amendments will not have
disproportionately high and adverse human health or environmental
effects on minority or low-income populations because it does not
affect the level of protection provided to human health or the
environment. These proposed amendments do not relax the control
measures on sources regulated by the rule and therefore will not cause
emissions increases from these sources.
List of Subjects in 40 CFR Part 63
Environmental protection, Air pollution control, Hazardous
substances, Incorporation by reference, Reporting and recordkeeping
requirements.
Dated: April 9, 2007.
Stephen L. Johnson,
Administrator.
For the reasons stated in the preamble, part 63, title 40, chapter
I, of the Code of Federal Regulations is proposed to be amended as
follows:
PART 63--[AMENDED]
1. The authority citation for part 63 continues to read as follows:
Authority: 42 U.S.C. 7401, et seq.
Subpart A--[AMENDED]
2. Section 63.14 is amended by adding paragraph (k)(2) to read as
follows:
Sec. 63.14 Incorporations by reference.
* * * * *
(k) * * *
(2) The following method as published in the National Institute of
Occupational Safety and Health (NIOSH) test method compendium, ``NIOSH
Manual of Analytical Methods'', NIOSH publication no. 94-113, Fourth
Edition.
(i) NIOSH Method 2010, ``Amines, Aliphatic,'' Issue 2 (and
subsequent revisions), August 15, 1994, IBR approved for Sec.
63.7732(g)(1)(v) of Subpart EEEEE of this part.
(ii) [Reserved]
Subpart EEEEE--[Amended]
3. Section 63.7681 is amended by revising the second sentence to
read as follows:
Sec. 63.7681 Am I subject to this subpart?
* * * Your iron and steel foundry is a major source of HAP for
purposes of this subpart if it emits or has the potential to emit any
single HAP at a rate of 10 tons or more per year or any combination of
HAP at a rate of 25 tons or more per year or if it is located at a
facility that emits or has the potential to emit any single HAP at a
rate of 10 tons or more per year or any combination of HAP at a rate of
25 tons or more per year as defined in Sec. 63.2.
4. Section 63.7690 is amended by:
a. Revising paragraphs (a) introductory text;
b. Revising paragraph (a)(2);
c. Revising paragraph (a)(7);
d. Revising paragraphs (a)(11