National Emission Standards for Hazardous Air Pollutants From Petroleum Refineries, 66694-66712 [E8-26403]
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Federal Register / Vol. 73, No. 218 / Monday, November 10, 2008 / Proposed Rules
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 63
[EPA–HQ–OAR–2003–0146; FRL–8737–8]
RIN 2060–AO55
National Emission Standards for
Hazardous Air Pollutants From
Petroleum Refineries
Environmental Protection
Agency (EPA).
ACTION: Supplemental notice to
proposed rulemaking.
AGENCY:
SUMMARY: This action supplements the
proposed amendments to the national
emission standards for petroleum
refineries (Refinery MACT 1) published
on September 4, 2007. The 2007
proposal, in part, sets forth proposed
maximum achievable control
technology and residual risk
requirements for cooling towers and
proposed residual risk and technology
review requirements for storage tanks.
This supplemental proposal contains
new proposed requirements for cooling
towers, a new option for storage vessels,
and clarifications and corrections to
definitions, tables, and regulatory
citations.
DATES: Comments must be received on
or before December 10, 2008, unless a
public hearing is requested by
November 20, 2008. If a hearing is
requested on the proposed rule, written
comments must be received by
December 26, 2008. Under the
Paperwork Reduction Act, comments on
the information collection provisions
must be received by the Office of
Management and Budget (OMB) on or
before December 10, 2008.
ADDRESSES: Submit your comments,
identified by Docket ID No. EPA–HQ–
OAR–2003–0146, by one of the
following methods:
• www.regulations.gov. Follow the
on-line instructions for submitting
comments.
• E-mail: Comments may be sent by
electronic mail (e-mail) to a-and-rDocket@epa.gov, Attention Docket ID
No. EPA–HQ–OAR–2003–0146.
Category
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Industry .................................
1 North
• Fax: Fax your comments to: (202)
566–9744, Attention Docket ID No.
EPA–HQ–OAR–2003–0146.
• Mail: Send your comments to: Air
and Radiation Docket and Information
Center, Environmental Protection
Agency, Mailcode: 2822T, 1200
Pennsylvania Ave., NW., Washington,
DC 20460, Attention Docket ID No.
EPA–HQ–OAR–2003–0146. Please
include a total of two copies. We request
that a separate copy also be sent to the
contact person identified below (see FOR
FURTHER INFORMATION CONTACT). In
addition, please mail a copy of your
comments on the information collection
provisions to the Office of Information
and Regulatory Affairs, Office of
Management and Budget (OMB), Attn:
Desk Office for EPA, 725 17th St., NW.,
Washington, DC 20503.
• Hand Delivery or Courier: Deliver
your comments to: EPA Docket Center,
Room 3334, 1301 Constitution Avenue,
NW., Washington, DC 20004. Such
deliveries are accepted only 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–2003–
0146. EPA’s policy is that all comments
received will be included in the public
docket without change and may be
made available online at
www.regulations.gov, including any
personal information provided, unless
the comment includes information
claimed to be confidential business
information (CBI) or other information
whose disclosure is restricted by statute.
Do not submit information that you
consider to be CBI or otherwise
protected through www.regulations.gov
or 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
NAICS 1 code
32411
Internet. If you submit an electronic
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, will be publicly
available only in hard copy. Publicly
available docket materials are available
either electronically in
www.regulations.gov or in hard copy at
the EPA Docket Center, Public Reading
Room, EPA West Building, Room 3334,
1301 Constitution Ave., NW.,
Washington, DC. The Public Reading
Room is open from 8:30 a.m. to 4:30
p.m. Eastern Standard Time (EST),
Monday through Friday, excluding legal
holidays. The telephone number for the
Public Reading Room is (202) 566–1744,
and the telephone number for the Air
and Radiation Docket is (202) 566–1742.
Mr.
Robert Lucas, Office of Air Quality
Planning and Standards, Sector Policies
and Programs Division, Coatings and
Chemicals Group (E143–01),
Environmental Protection Agency,
Research Triangle Park, North Carolina
27711, telephone number (919) 541–
0884; fax number (919) 541–0246; email address: lucas.bob@epa.gov.
FOR FURTHER INFORMATION CONTACT:
SUPPLEMENTARY INFORMATION:
I. General Information
A. Does this action apply to me?
The regulated category and entities
affected by this proposed action
include:
Examples of regulated entities
Petroleum refineries located at a major source that are subject to 40 CFR part 63, subpart CC.
American Industry Classification System.
This table is not intended to be
exhaustive, but rather provides a guide
for readers regarding entities likely to be
regulated by the proposed rule. To
determine whether your facility would
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be regulated by the proposed
amendments, you should carefully
examine the applicability criteria in 40
CFR 63.100 of subpart CC (National
Emission Standards for Hazardous Air
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Pollutants From Petroleum Refineries).
If you have any questions regarding the
applicability of this action to a
particular entity, contact either the air
permit authority for the entity or your
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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 for EPA?
Do not submit information containing
CBI to EPA through
www.regulations.gov or e-mail. Send or
deliver information as CBI only to the
following address: Roberto Morales,
OAQPS Document Control Officer
(C404–02), Office of Air Quality
Planning and Standards, Environmental
Protection Agency, Research Triangle
Park, NC 27711, Attention Docket ID
No. EPA–HQ–OAR–2003–0146 (for
petroleum refineries). 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.
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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 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
supplemental proposal by November 20,
2008, we will hold a public hearing on
November 25, 2008. If you are interested
in attending the public hearing, contact
Janet Eck at (919) 541–7946 to verify
that a hearing will be held. If a public
hearing is held, it will be held at 10 a.m.
at the EPA’s Environmental Research
Center Auditorium, Research Triangle
Park, NC, or an alternate site nearby.
E. How is this document organized?
I. General Information
A. Does this action apply to me?
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B. What should I consider as I prepare my
comments for EPA?
C. Where can I get a copy of this
document?
D. When would a public hearing occur?
II. Background Information
III. Summary of Supplemental Proposal
A. What are the proposed requirements to
meet CAA sections 112(f)(2) and (d)(6)
for Group 1 storage vessels?
B. What are the proposed requirements for
cooling towers under CAA sections
112(d)(2) and (f)(2)?
C. What other revisions and clarifications
are we proposing?
IV. Rationale for Supplemental Proposed
Amendments
A. Storage Vessels
B. Cooling Towers
V. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory
Planning and Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation
and Coordination with Indian Tribal
Governments
G. Executive Order 13045: Protection of
Children from Environmental Health
Risks and Safety Risks
H. Executive Order 13211: Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use
I. National Technology Transfer and
Advancement Act
J. Executive Order 12898: Federal Actions
to Address Environmental Justice in
Minority Populations and Low-Income
Populations
II. Background Information
On September 4, 2007 (72 FR 50716),
EPA proposed several actions under
section 112 of the Clean Air Act (CAA)
with respect to petroleum refineries
subject to the 1995 Refinery MACT 1
Rule (40 CFR part 63, subpart CC).
Please refer to the 2007 proposal for
additional background material. See 72
FR 50717–18. In response to comments
received on the 2007 proposed rule,
EPA further evaluated that proposal and
is now supplementing its proposal with
respect to cooling towers and storage
vessels. In addition, as part of this
notice, we are providing proposed
revisions to the regulatory text to clarify
and correct definitions, tables, and
regulatory citations.
III. Summary of Supplemental Proposal
A. What are the proposed requirements
to meet CAA sections 112(f)(2) and
(d)(6) for Group 1 storage vessels?
In the September 2007 proposed rule,
EPA initially proposed two regulatory
options for storage vessels under CAA
sections 112(f)(2) and (d)(6): Option 1
would require no revisions to the
Refinery MACT 1 rule and Option 2
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would add the requirements in 40 CFR
63.119(c)(2)(ix) and (x) for slotted guide
poles on existing external floating roof
(EFR) storage vessels (Refinery MACT 1
currently provides an exemption from
these requirements for existing storage
vessels). For more detail on the
proposed options, please see 72 FR
50726–27.
Many commenters agreed that, of
EPA’s proposed options, Option 2,
controls for slotted guide poles, is an
appropriate and cost-effective level of
control. However, several commenters
supporting Option 2 requested that EPA
revise the regulatory text associated
with Option 2 to use clear terminology
consistent with the most recent rules
and technologies for storage vessels, i.e.,
the rules at 40 CFR part 63, subpart WW
and the Storage Tank Emission
Reduction Partnership Program
(STERPP) (described at 65 FR 19891).
Specifically, commenters noted that
subpart WW and STERPP include
clearer descriptions and definitions of
control options and provide clear and
specific criteria for requirements such as
the required height of a pole float and
the position of a gasket.
Based on our review of public
comments and subsequent analysis, we
are proposing an additional option
under CAA sections 112(f)(2) and (d)(6)
for storage vessels. Specifically, we are
proposing to remove the exemptions for
existing EFR storage vessels and amend
the requirements for all Group 1 storage
vessels to be consistent with, and refer
directly to, the requirements of 40 CFR
part 63, subpart WW. The subpart WW
requirements include the requirements
for fitting controls on slotted guide
poles, which were originally proposed
under Option 2, as well as additional
requirements for fittings for unslotted
guide poles and other openings on EFR
storage vessels. The proposed
amendments also include the
inspection, recordkeeping, and
reporting requirements in subpart WW
to account for the additional
requirements for fitting controls for EFR
storage vessels. It should be noted that,
while subpart WW was preferred by the
commenters and its stringency is
equivalent to the HON, the existing 40
CFR part 63, subpart CC does not
require all the specific tank fitting
control requirements in the HON. While
proposed Option 2 in the September
2007 proposal included some tank
fitting control requirements not
currently included in subpart CC,
Option 2 did not include all of the tank
fitting control requirements in the HON
and subpart WW. Consequently, by
proposing to require compliance with
subpart WW, we are proposing full tank
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fitting controls for Group 1 storage
vessels, and, therefore, today’s proposed
amendments are more stringent than the
existing subpart CC rules and the
subpart CC amendments proposed in
September 2007.
The subpart WW requirements are
being proposed because, in addition to
providing clearer language for fitting
controls, they provide an ample margin
of safety to protect public health. This
option reduces hazardous air pollutants
(HAP) emissions and risks beyond the
current maximum achievable control
technology (MACT) standard using
controls that are technically and
economically feasible and that pose no
adverse environmental impacts. We
estimate that these changes would
reduce the number of people at cancer
risk greater than 1-in-1 million by
20,000 individuals and the cancer
incidence by 0.002—0.003 cases per
year (i.e., prevent one cancer case every
400 years). This option would reduce
emissions of volatile organic
compounds (VOC) by 14,800 tons per
year (tpy). Reducing VOC provides the
added benefit of reducing ambient
concentrations of ozone and may reduce
fine particulate matter. The annualized
cost impacts of this option are estimated
to be a cost savings of $6.8 million. Our
economic analysis (summarized later in
this preamble) indicates that this cost
will have little impact on the price and
output of petroleum products.
Under this option, we are proposing
that the owner or operator of an existing
Group 1 storage vessel comply with the
requirements in subpart WW of this part
no later than 90 days after promulgation
of these amendments. As provided in 40
CFR part 63, subpart WW, and for the
reasons provided in Section IV, we are
proposing that retrofitting floating roof
tanks with the guide pole controls and
certain other requirements is not
required until the next time the vessel
is emptied and degassed, or 10 years
from the promulgation date of the final
standards, whichever is sooner.
B. What are the proposed requirements
for cooling towers under CAA sections
112(d)(2) and (f)(2)?
Under CAA sections 112(d)(2) and
(d)(3), we proposed work practice
standards for cooling towers that would
require the owner or operator of a new
or existing source to monitor for leaks
in the cooling tower return lines from
heat exchangers in organic HAP service
(i.e., lines that contain or contact fluids
with 5 weight percent or greater of total
organic HAP listed in Table 1 of the
rule) and, where leaks are detected, to
repair such leaks within a specified
period of time. We proposed two
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options for new and existing sources,
one based on the MACT floor analysis
that accompanied the proposal, i.e., the
average emissions limitations achieved
by the top 12 percent of the affected
sources, and the other based on an
analysis of beyond-the-floor techniques.
For more detail on those options, please
see 72 FR 50722–24.
In response to public comments that
the terms used in the proposed cooling
tower requirements needed to be
defined and should focus on heat
exchange systems, we are proposing to
add several definitions to clarify the
cooling tower monitoring requirements.
We are proposing that the cooling tower
requirements would apply to each ‘‘heat
exchange system.’’ A ‘‘heat exchange
system’’ means a device or series of
devices used to transfer heat from
process fluids to water without
intentional direct contact of the process
fluid with the water (i.e., non-contact
heat exchangers) and to transport and/
or cool the water in a closed loop
recirculation system (cooling tower
system) or a once through system (e.g.,
river or pond water). A ‘‘heat exchange
system’’ can include one or more heat
exchangers, all water lines to and from
the heat exchanger(s), and, for
recirculating systems, the cooling tower
or towers that receive water from the
heat exchanger(s).
In response to public comments that
our floor analysis did not include
existing State standards, we collected
new information on existing State and
local cooling towers provisions and
revised our MACT floor analysis. More
detail regarding the development of the
revised MACT floor for existing and
new sources based on review of these
existing State requirements is provided
in Section IV.B. of this preamble and in
the docket memorandum entitled
‘‘Cooling Towers: Control Alternatives
and Impact Estimates’’ (EPA–HQ–OAR–
2003–0146). The revised proposed
requirements are described below and
are based on the revised MACT floor
determination. Control techniques
considered as beyond-the-floor options
are described in Section IV.B of this
preamble; we are not proposing any of
these options because they were
determined not to be cost-effective.
We are proposing that owners and
operators of heat exchange systems that
are in organic HAP service at new and
existing sources would be required to
conduct monthly sampling and analyses
using the Texas Commission on
Environmental Quality’s (TCEQ)
Modified El Paso method, Revision
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Number One, dated January 2003.1 For
existing sources, monthly cooling tower
monitoring would begin within 18
months of promulgation of the final
amendments. For new sources, monthly
cooling tower monitoring would begin
upon start-up or on the date of
promulgation of these amendments,
whichever is later. For existing sources,
a leak would be defined as 6.2 parts per
million by volume (ppmv) total
strippable VOC in the stripping gas
collected via the Modified El Paso
method. For new sources, a leak would
be defined as 3.1 ppmv total strippable
VOC collected via the Modified El Paso
method. The proposed amendments
would require the repair of leaks in heat
exchangers in organic HAP service
within 45 days of the sampling event in
which the leak was detected, unless a
delay in repair is allowed. Delay in
repair of the leak would be allowed
until the next shutdown if the repair of
the leak would require the process unit
served by the leaking heat exchanger to
be shut down and the total strippable
VOC concentration is less than 62
ppmv. Delay in repair of the leak would
also be allowed for up to 120 days if the
total strippable VOC concentration is
less than 62 ppmv and if critical parts
or personnel are not available. The
owner or operator would be required to
continue monthly monitoring and repair
the heat exchanger within 45 days if
sampling results show that the leak
exceeds 62 ppmv total strippable VOC.
Within the first 3 years after
promulgation of these amendments,
delay in repair of a leak would also be
allowed if the leak exceeds 62 ppmv
total strippable VOC and the repair of
the leak would require the process unit
served by the leaking heat exchanger to
be shut down and a shutdown is
planned within 60 days or if critical
parts or personnel are not available.
Starting 3 years after promulgation of
these amendments, delay of repair
beyond 45 days would not be allowed
if the leak exceeds 62 ppmv total
strippable VOC.
Sampling for leaks would be
conducted either at individual heat
exchanger return lines (i.e., water lines
returning the water from the heat
exchanger to the cooling tower) or the
combined cooling tower inlet water
location. That is, if the cooling tower
services multiple heat exchangers, the
1 ‘‘Air Stripping Method (Modified El Paso
Method) for Determination of Volatile Organic
Compound Emissions from Water Sources,’’
Revision Number One, dated January 2003,
Sampling Procedures Manual, Appendix P: Cooling
Tower Monitoring, prepared by Texas Commission
on Environmental Quality, January 31, 2003
(incorporated by reference-see § 63.14).
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owner or operator may elect to monitor
only the heat exchangers ‘‘in organic
HAP service’’ or monitor at the
combined cooling tower inlet. If a leak
is detected at the combined cooling
tower inlet, the owner or operator may
elect to fix the leak regardless of its
location or begin monitoring at each
heat exchanger ‘‘in organic HAP
service’’ to document that the leak is not
originating from a heat exchanger ‘‘in
organic HAP service.’’
All new or existing refineries with a
heat exchange system ‘‘in organic HAP
service’’ would be required to maintain
records of the heat exchangers in
organic HAP service, the cooling towers
associated with heat exchangers in
organic HAP service, monthly
monitoring results, and information for
any delays in repair of a leak.
requirement cross-references in Tables 4
and 5 of subpart CC to part 63. We are
also proposing to clarify applicability
sections by specifying the promulgation
date of the original subpart CC. Finally,
we are proposing amendments to clarify
how owners and operators should
comply with overlapping standards for
equipment leaks. These proposed
amendments are included to clarify the
requirements of subpart CC.
IV. Rationale for Supplemental
Proposed Amendments
A. Storage Vessels
In response to public comments on
the original proposal, we revised and
updated the analysis of the options we
proposed in September 2007. We also
evaluated a wider range of control
options, such as the requirements
included in the Generic Storage Vessel
C. What other revisions and
MACT (40 CFR part 63, subpart WW)
clarifications are we proposing?
and STERPP, as well as other specific
In the September 2007 proposal, we
controls suggested by the commenters.
proposed to amend Table 6 to 40 CFR
A detailed explanation of our impacts
part 63, subpart CC (General Provisions
analysis for each of the options
Applicability to Subpart CC) to bring the described in this section is provided in
table up-to-date with current
‘‘Storage Vessels: Revised Control
requirements of the General Provisions
Options and Impact Estimates’’ in
and clarify certain requirements. In
Docket ID No. EPA–HQ–OAR–2003–
conjunction with the publication of
0146.
Table 6 in the proposal, we erroneously
The storage vessel controls in 40 CFR
included a Table 11. We are clarifying
part 63, subpart WW and for STERPP
that we are not proposing to include
include several compliance options for
Table 11 and, thus, do not plan to
controlling slotted guide poles as well
include it as part of the final rule.
as requirements for additional fitting
We received public comments that
controls on other EFR deck openings.
methyl ethyl ketone (also known as 2We determined that, based on emission
butanone) has been delisted as a HAP.
modeling runs using a model gasoline
We are, therefore, proposing to revise
storage vessel, the STERPP and subpart
Table 1 to delete methyl ethyl ketone
WW requirements for slotted guide
from the HAP listed in Table 1.
poles achieve the same or better
emission reduction efficiencies as the
We also received several public
originally proposed Option 2 for Group
comments noting that cross-references
1 storage vessels. And, while additional
to other subparts should be updated.
deck fitting controls on EFR storage
Therefore, we are also proposing
vessels contained in the STERPP and
amendments to correct cross-references
to subparts R and Y of part 63 in the rule subpart WW provide only a tenth of the
emission reductions as the guide pole
text, as well as to correct the
controls, these controls (primarily use of
recordkeeping and reporting
gaskets) are inexpensive. As seen in
Table 1 of this preamble, our cost
analysis indicates that these fitting
controls are cost-effective. Therefore, we
are proposing an additional option that
would require these additional fitting
controls for existing Group 1 storage
vessels covered by Refinery MACT 1.
Based on our evaluation of the
STERPP and 40 CFR part 63, subpart
WW control requirements, we
determined that those standards require
solid, or unslotted, guide poles to be
gasketed and have a wiper system, and
we evaluated the impacts of also adding
these requirements to Refinery MACT 1.
We determined that, provided the
retrofits could be performed without
additional emissions and cost associated
with an unplanned emptying and
degassing of the storage vessel (i.e.,
during a turnaround or when the vessel
is taken out of service for maintenance/
repair), the control requirements for
solid guide poles were cost-effective.
That is, over a 10-year cycle using a 7percent annual interest rate, these
controls yield a net cost savings (from
reduced product losses). The
combination of additional deck fitting
controls and full guide pole controls is
presented in Table 1 as ‘‘full deck and
guide pole controls.’’ Consequently, we
are proposing as an additional option to
amend Refinery MACT 1 to refer
directly to the storage vessel control
requirements in subpart WW. As the
cost-effectiveness of the control retrofits
are predicated on a lack of additional
emissions and cost associated with
emptying and degassing the storage
vessel, we are providing up to 10 years
for compliance with these requirements
as provided for in 40 CFR 63.1063(a)(ix)
of subpart WW. Because these controls
are cost-effective and incrementally
reduce public exposure, we believe this
option, in addition to the two options
proposed earlier, would provide an
ample margin of safety and meet the
requirements of the technology review.
TABLE 1—NATIONWIDE IMPACTS OF VARIOUS STORAGE VESSEL REGULATORY OPTIONS
Total capital investment
($ million)
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Control option
Total
annualized
cost without recovery
($ million)
Product
recovery
credit
($ million)
Total
annualized
costs
($ million/
yr)
HAP
emissions
(tons per
year) a
HAP
emission
reductions
(tons per
year)
0
0
0
0
2,970
0
(b)
5.3
10
0.76
1.5
¥3.3
¥8.3
¥2.6
¥6.8
2,300
1,300
660
1,640
¥3,900
¥4,100
Option 1: Baseline (proposed at 72 FR 50726–27) a ........
Option 2: Slotted guide pole sleeves (proposed at 72 FR
50726–27) b ....................................................................
Option 3: Full deck and guide pole controls .....................
Cost-effectiveness
($/ton
HAP)
a Costs and emission reductions have been revised since September 2007 proposal; see memorandum entitled ‘‘Storage Vessels: Revised
Control Options and Impact Estimates’’ in Docket ID No. EPA–HQ–OAR–2003–0146 for details on these revisions.
b Not applicable.
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Table 2 of this preamble presents the
risk reduction associated with the
control option for storage vessels.
TABLE 2—INHALATION RISK IMPACTS OF REGULATORY ALTERNATIVE FOR STORAGE VESSELS
Parameter
Control
option 2
Baseline option 1
Risk to Most Exposed Individual:
Cancer (in 1 million) ..................................................
Noncancer (HI) ..........................................................
Size of Population at Cancer Risk:
> 100-in-1 million .......................................................
> 10-in-1 million .........................................................
> 1-in-1 million ...........................................................
Number of Plants at Cancer Risk Level:
> 100-in-1 million .......................................................
> 10-in-1 million .........................................................
> 1-in-1 million ...........................................................
Population with HI > 1 1 .................................................
No of Plants with HI > 1 ...................................................
Annual Cancer Incidence 2 ................................................
Cancer Incidence Reduction (Percent) .............................
HAP Emission Reduction (Percent) ..................................
Control
option 3
30 .....................................................................................
0.3 ....................................................................................
30
0.3
30
0.3
0 .......................................................................................
4,000 ................................................................................
460,000 ............................................................................
0
3,900
450,000
0
3,800
440,000
0 .......................................................................................
23 .....................................................................................
88 .....................................................................................
0 .......................................................................................
0 .......................................................................................
0.032–0.049 .....................................................................
(3) ......................................................................................
(3) ......................................................................................
0
23
88
0
0
0.031–0.048
2
4
22
87
0
0
0.030–0.046
5
10
dwashington3 on PRODPC61 with PROPOSALS2
1 If the Hazard Index (HI) is calculated to be less than or equal to 1, then no adverse non-cancer chronic health effects are expected as a result of the exposure. However, an HI exceeding 1 does not translate to a probability that adverse effects occur. Rather, it suggests the possibility
that adverse health effects may occur. Acute non-cancer effects not estimated in this analysis.
2 The range of cancer incidence reflects the cancer potency range of benzene, either end of which is considered equally plausible.
3 Not applicable.
B. Cooling Towers
To respond to public comments that
our floor analysis did not include
existing State standards, we collected
additional information on cooling tower
requirements for multiple petroleum
refineries in several States. Using these
data, we reanalyzed the MACT floor for
new and existing sources and identified
39 petroleum refineries in California,
Illinois, Indiana, Louisiana, Minnesota,
and Texas with permit requirements for
HAP and/or VOC in cooling tower
return water along with cooling tower
monitoring requirements. We note that
the permit requirements are based on
calculated emission estimates using the
water recirculation rates and monitored
concentrations in the cooling waters.
Consequently, the permit requirements
effectively define a maximum allowable
concentration limit of strippable
organics in the cooling water so that the
effective leak definition could be
determined for each cooling tower. We
further note that no refineries directly
measure cooling tower emissions, and
we reaffirm our conclusion that cooling
tower work practice standards are
appropriate because the emissions are
not emitted through a stack or other
conveyance and are, therefore, not
practically measurable.
We ranked cooling tower
requirements based on the projected
emissions that would occur given the
specific cooling tower monitoring
provision. Based on preliminary
calculations performed using the
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cooling tower impacts model (see
‘‘Cooling Towers: Control Alternatives
and Impact Estimates’’ memorandum in
Docket ID No. EPA–HQ–OAR–2003–
0146), the leak definition was the
primary factor influencing the emissions
limitations achieved by a cooling tower
monitoring program; the second most
important factor was the specification of
time frames for completing repairs and
provisions or limitations for delay of
repair. Monitoring frequency, while a
contributing factor to overall cooling
tower emissions performance, was not
as important as the leak definition and
specified repair deadlines. We selected
the 6th percentile cooling tower as
indicative of the average emission
limitation achieved by the best
performing 12 percent of cooling towers.
Based on this, we determined that the
MACT floor for cooling towers at
existing sources is cooling water
sampling on a monthly basis for total
strippable VOC compounds, where a
leak is defined as 6.2 ppmv of total
strippable VOC compounds in the
stripping air of the TCEQ Modified El
Paso method. We note that this leak
definition is equivalent to the controlled
emission factor in AP–42,2 and that
many refineries use this controlled
2 U.S. EPA (Environmental Protection Agency).
1995. Compilation of Air Pollutant Emission
Factors. Sections 5.1. AP–42. Office of Air Quality
Planning and Standards, Research Triangle Park,
NC.
PO 00000
Frm 00006
Fmt 4701
Sfmt 4702
emission factor when estimating and
reporting their cooling tower emissions.
Additionally, based on this MACT
floor analysis, we determined that the
existing source MACT floor repair
requirements include identifying the
source of the leak and repairing within
45 days of originally finding the leak.
Delay of repair is allowed under certain
conditions if the total strippable VOC is
less than 62 ppmv, but is not allowed
if the total strippable VOC concentration
is equal to or greater than 62 ppmv.
When total strippable VOC is less than
62 ppmv, delay of repair is allowed for
up to 120 days if the necessary
equipment, parts, or personnel are not
available, and delay of repair is allowed
until the next shutdown if a shutdown
is required to effect the repair. For delay
of repair, the refinery must document
the basis for the delay, including the
reason for delaying repair, provide a
schedule for completing the repair, and
determine the emissions of HAP during
the time duration of the delay.
While these delay of repair provisions
are based on our MACT floor
assessment, we note that some of the
permits for facilities in the top 12
percent provide time to implement the
monitoring requirements before the ban
on delay of repairs for leaks exceeding
62 ppmv becomes effective. We
recognize that when facilities first start
to monitor their cooling towers, the
likelihood of finding large leaks is much
greater than after a monthly monitoring
program has been implemented. As
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Federal Register / Vol. 73, No. 218 / Monday, November 10, 2008 / Proposed Rules
such, when first implementing the
monthly monitoring, they may identify
heat exchange systems that have leaks
exceeding 62 ppmv, but may not have
the spare parts or adequate time to plan
for the repair of the heat exchange
system that would typically be available
after the monthly monitoring program
has been in place for some time. As
such, we propose to phase-in the
cooling tower requirements for existing
sources. The monitoring and leak repair
provisions for existing sources would
become effective no later than 18
months after promulgation of the final
rule; however, the delay of repair is
allowed regardless of the leak size for
the first 18 months of the monitoring
program. No later than 3 years from the
promulgation date of these
amendments, no delay of repair is
allowed for leaks exceeding 62 ppmv
total strippable VOC.
The new source MACT for cooling
towers must be no less stringent than
the best-performing refinery cooling
towers. In our ranking of the
information collected on monitoring
requirements, the best-performing
cooling tower has a leak definition of
3.1 ppmv of strippable total organics as
methane in the stripping air using
monthly Modified El Paso method
sampling and analysis. As such, the
MACT floor for cooling towers at new
sources is monthly cooling water
sampling for total strippable VOC,
where a leak is defined as 3.1 ppmv of
total strippable VOC in the stripping air
using the Modified El Paso method. The
repair requirements for the topperforming cooling towers include
identifying the source of the leak and
repairing within 45 days of originally
finding the leak. Delay of repair for the
top-performing cooling towers is
allowed if strippable total VOC
concentration is less than 62 ppmv, but
not allowed if strippable total VOC
concentration is equal to or greater than
62 ppmv. That is, the delay of repair
provisions for the new source MACT
floor cooling towers are the same as
those for an existing source MACT floor
cooling towers.
We revised our cooling tower
emissions estimates since the 2007
proposal based on reanalysis of the
emissions inventory information
obtained from TCEQ for the 2004
reporting year, as well as other
information collected regarding cooling
tower monitoring provisions and flow
data from the Industrial Cooling Tower
National Emission Standards for
Hazardous Air Pollutants (NESHAP).
Model cooling tower emissions for each
refinery facility in the nation were
estimated based on crude throughput
data which were used to estimate total
cooling water flow rates and generic
refinery stream VOC and HAP
compositions. These data were used
with controlled and uncontrolled AP–42
emission factors for VOC emissions
from cooling towers and the fraction of
cooling towers with specific monitoring
requirements to estimate cooling tower
baseline HAP emissions. The
nationwide baseline HAP emissions
were estimated at 770 tpy as compared
to a baseline estimate of greater than
3,000 tpy in the 2007 proposal. These
emissions compare reasonably well with
the organic HAP emissions estimate
based on the TCEQ data, as revised, to
correct a reporting error identified by a
public commenter. From the updated
TCEQ 2004 database, we estimated the
organic HAP emissions from cooling
towers to be 95 tpy for Texas refineries
alone. Extrapolation of the Texas data
based on direct crude distillation
capacity provides a nationwide
emissions estimate for cooling towers of
352 tpy of organic HAP. However,
refineries in Texas had the most
stringent cooling tower monitoring
provisions of any of the State
requirements, and the Texas refineries
used the controlled AP–42 emission
factor for their cooling tower emission
estimates. If the non-Texas refineries
operate nearer the uncontrolled AP–42
emission factor, nationwide cooling
tower emissions are projected to be
2,300 tpy of organic HAP. While there
is significant uncertainty in the actual
cooling tower emission estimate, the
projected baseline emissions fall easily
within the range expected based on
reanalysis of the Texas dataset.
Following reanalysis of the MACT
floor for cooling towers, we also
conducted a revised cost analysis for the
MACT floor level of control. We
included costs for a strippable total VOC
monitoring system, increased the time
needed for sampling and analysis for
each cooling tower, and added costs for
sampling and analysis for specific heat
exchangers for triggered monitoring
following identification of a cooling
tower leak. We also increased the cost
associated with repairing a leaking heat
exchanger. The cost-effectiveness of the
MACT floor control for cooling towers
at both new and existing sources was
approximately $4,700 per ton of HAP
reduced when considering product
recovery credits and approximately
$8,200 per ton when product recovery
credits were not included. See Table 3
of this preamble.
We also evaluated the costs of
applying the new source leak definition
to existing sources and implementing
this option with continuous strippable
total VOC monitoring systems as a
beyond-the-MACT floor control options.
The first alternative reduces an
additional 40 tpy of HAP emissions at
an incremental cost-effectiveness of
almost $6,000 per ton on HAP emission
reduction and the second option with
continuous monitoring reduces HAP
emissions by an additional 10 tpy and
has an incremental cost-effectiveness of
almost $600,000 per ton of HAP
reduced.
Based on this analysis, we conclude
that the beyond-the-MACT floor control
options are not cost-effective and we are
proposing standards for cooling towers
commensurate with the MACT floor
determinations under CAA sections
112(d)(2) and (3). Further, we are
proposing that the MACT floor level of
control also provides an ample margin
of safety and satisfies the risk review
requirements under CAA section
112(f)(2). For more information on the
costing methodology, see Table 3 of this
preamble and the ‘‘Cooling Towers:
Control Alternatives and Impact
Estimates’’ memorandum in the docket
(Docket ID No. EPA–HQ–OAR–2003–
0146).
dwashington3 on PRODPC61 with PROPOSALS2
TABLE 3—NATIONWIDE IMPACTS FOR COOLING TOWER OPTIONS
Total
capital
investment
($ million)
Control option
Total
annualized
cost
without
recovery
($ million)
Product
recovery
credit
($ million)
Total
annualized
costs
($ million)
HAP
emissions
(tpy)
16
16
72
5.2
5.5
11
¥2.2
¥2.3
¥2.2
3.0
3.2
8.8
140
100
90
MACT Floor ...................................................
Beyond-the-floor Alternative 1 ......................
Beyond-the-floor Alternative 2 ......................
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E:\FR\FM\10NOP2.SGM
HAP
emission
reductions
(tpy)
10NOP2
630
670
680
Costeffectiveness
($/ton HAP)
Overall
4,700
4,700
13,000
Incremental
4,700
5,700
580,000
66700
Federal Register / Vol. 73, No. 218 / Monday, November 10, 2008 / Proposed Rules
Table 4 of this preamble provides
information relevant to our proposed
ample margin of safety determination
under CAA section 112(f)(2).
Specifically, the table presents the pre-
MACT risk, the risk associated with the
proposed MACT floor which is the
baseline for our residual risk analysis,
and the risk reduction for the first
beyond the MACT floor alternative for
cooling towers. Reductions in risk for
the second alternative are not shown
because this alternative is clearly not
cost-effective.
TABLE 4—INHALATION RISK IMPACTS FOR COOLING TOWERS
Baseline preMACT
Parameter
Risk to Most Exposed Individual:
Cancer (in 1 million) ...........................................................................................
Noncancer (HI) ...................................................................................................
Size of Population at Cancer Risk:
> 100-in-1 million ................................................................................................
> 10-in-1 million ..................................................................................................
> 1-in-1 million ....................................................................................................
Number of Plants at Cancer Risk Level:
> 100-in-1 million ................................................................................................
> 10-in-1 million ..................................................................................................
> 1-in-1 million ....................................................................................................
Population with HI > 1 a .............................................................................................
No of Plants with HI > 1 ............................................................................................
Annual Cancer Incidence b ........................................................................................
Cancer Incidence Reduction (Percent) .....................................................................
HAP Emission Reduction (Percent) ..........................................................................
MACT floor
(risk baseline)
Beyond the MACT
floor
alternative 1
30
0.3
30
0.3
30
0.3
0
4,000
460,000
0
3,900
450,000
0
3,800
440,000
0
23
88
0
0
0.032–0.049
NA
NA
0
22
88
0
0
0.031–0.047
3
4
0
22
87
0
0
0.030–0.047
4
6
a If the Hazard Index (HI) is calculated to be less than or equal to 1, then no adverse non-cancer chronic health effects are expected as a result of the exposure. However, an HI exceeding 1 does not translate to a probability that adverse effects occur. Rather, it suggests the possibility
that adverse health effects may occur. Acute non-cancer effects not estimated in this analysis.
b The range of cancer incidence reflects the cancer potency range of benzene, either end of which is considered equally plausible.
V. Statutory and Executive Order
Reviews
A. Executive Order 12866: Regulatory
Planning and Review
Under Executive Order 12866 (58 FR
51735, October 4, 1993), this action is a
‘‘significant regulatory action’’ because
it may raise novel legal or policy issues.
Accordingly, EPA submitted this action
to 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.
dwashington3 on PRODPC61 with PROPOSALS2
B. Paperwork Reduction Act
The information collection
requirements in this proposed rule have
been submitted for approval to the OMB
under the Paperwork Reduction Act, 44
U.S.C. 3501, et seq. The Information
Collection Request (ICR) document
prepared by EPA has been assigned ICR
number 2334.01.
The information requirements in the
proposed amendments include
monitoring, recordkeeping, and
reporting provisions for storage vessels
and cooling towers. Owners or operators
of storage vessels must comply with the
inspection, recordkeeping, and
reporting requirements in 40 CFR part
63, subpart WW. Owners or operators of
cooling towers must conduct monthly
monitoring of each heat exchanger to
identify and repair leaks. Records of
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monitoring and repair data also must be
kept. All respondents must submit onetime notifications and semiannual
compliance reports.
The information collection
requirements in the proposed
amendments are needed by EPA and
delegated authorities to determine that
compliance has been achieved. The
recordkeeping and reporting
requirements in this proposed rule are
based on the information collection
requirements in the part 63 General
Provisions (40 CFR part 63, subpart A).
The recordkeeping and reporting
requirements in the General Provisions
are mandatory pursuant to section 114
of the CAA (42 U.S.C. 7414). All
information submitted to EPA pursuant
to the information collection
requirements for which a claim of
confidentiality is made is safeguarded
according to CAA section 114(c) and the
Agency’s implementing regulations at
40 CFR part 2, subpart B.
The annual burden for this
information collection averaged over the
first 3 years of this ICR is estimated to
total 13,714 labor hours per year at a
cost of $1,056,081 for one new refinery
and 153 existing refineries. The average
annual reporting burden is 353.9 labor
hours for 205.9 total annual responses;
the average annual burden per response
is 1.72 hours. Responses include
notifications of compliance status for
cooling towers and storage vessels at
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Sfmt 4702
new and existing refineries, notification
of initial startup for storage vessels at
one new refinery, and semiannual
compliance reports containing
information on cooling towers and
storage vessels at new and existing
refineries. Capital/startup costs are
estimated at $16,306,000. The operation
and maintenance costs associated with
the proposed rule amendments are
estimated at $61,711. Burden is defined
at 5 CFR 1320.3(b).
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 are listed in 40 CFR part 9.
To comment on the EPA’s need for
this information, the accuracy of the
provided burden estimates, and any
suggested methods for minimizing
respondent burden, including the use of
automated collection techniques, EPA
has established a public docket for this
action, which includes this ICR, under
Docket ID No. EPA–HQ–OAR–2003–
0146. Submit any comments related to
the ICR for the proposed rule to EPA
and OMB. See the ADDRESSES section at
the beginning of this preamble for where
to submit comments to EPA. Send
comments to OMB at the Office of
Information and Regulatory Affairs,
Office of Management and Budget, 725
17th Street, NW., Washington, DC
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dwashington3 on PRODPC61 with PROPOSALS2
20503, Attention: Desk Office for EPA.
Because OMB is required to make a
decision concerning the ICR between 30
and 60 days after November 10, 2008, a
comment to OMB is best assured of
having its full effect if OMB receives it
by December 10, 2008. The final rule
will respond to any OMB or public
comments on the information collection
requirements contained in this proposal.
C. Regulatory Flexibility Act
The Regulatory Flexibility Act
generally requires an agency to prepare
a regulatory flexibility analysis of any
rule subject to notice and comment
rulemaking requirements under the
Administrative Procedure Act or any
other statute unless the agency certifies
that the rule will not have a significant
economic impact on a substantial
number of small entities. Small entities
include small businesses, small
organizations, and small governmental
jurisdictions.
For the purposes of assessing the
impacts of this proposed rule on small
entities, small entity is defined as: (1) A
small business that meets the Small
Business Administration size standards
for small businesses at 13 CFR 121.201
(a firm having no more than 1,500
employees; (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 this proposed rule on small
entities, I certify that this action will not
have a significant economic impact on
a substantial number of small entities.
Based on our economic impact analysis,
the proposed amendments will result in
a nationwide net annualized cost
savings of about $3.8 million due to a
return of about $10.5 million per year
from reductions in product losses. Only
one oil refining entity would incur net
annualized costs as a result of the
proposed amendments; all other
refinery entities would have net savings.
This refinery entity is a small parent
entity. Net annualized costs for this
affected small entity are well below 0.01
percent of their revenue; therefore, no
‘‘significant’’ adverse economic impacts
are expected for any small entity. Thus,
the costs associated with the proposed
amendments will not result in any
‘‘significant’’ adverse economic impact
for any small entity. For more
information, please refer to the
economic impact analysis that is in the
docket for this rulemaking.
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Although the proposed rule will not
have a significant economic impact on
a substantial number of small entities,
we nonetheless tried to reduce the
impact of the proposed rule on small
entities. We held meetings with
industry trade associations and
company representatives to discuss the
proposed rule and have included
provisions for small facilities that
address their concerns. 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
This action contains no Federal
mandates under the provisions of Title
II of the Unfunded Mandates Reform
Act of 1995 (UMRA), 2 U.S.C. 1531–
1538 for State, local, or tribal
governments or the private sector.
The proposed rule does not contain a
Federal mandate that may result in
expenditures of $100 million or more
for State, local, and tribal governments,
in the aggregate, or to the private sector
in any one year. As discussed earlier in
this preamble, these amendments result
in nationwide net savings to the private
sector. Therefore, the proposed rule is
not subject to the requirements of
sections 202 or 205 of the UMRA.
This proposed rule is also not subject
to the requirements of section 203 of
UMRA because it contains no regulatory
requirements that might significantly or
uniquely affect small governments. 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, entitled
Federalism (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’’ is 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
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Fmt 4701
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66701
specified in Executive Order 13132. The
proposed amendments add control and
monitoring requirements. They do not
modify existing responsibilities or
create new responsibilities among EPA
Regional offices, States, or local
enforcement agencies. 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 governments, EPA
specifically solicits comment on this
proposed rule from State and local
officials.
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
This action does not have tribal
implications, as specified in Executive
Order 13175 (65 FR 67249, November 9,
2000). The proposed amendments will
not have substantial direct effects on
tribal governments, on the relationship
between the Federal Government and
Indian tribes, or on the distribution of
power and responsibilities between the
Federal government and Indian tribes,
as specified in Executive Order 13175.
The proposed amendments impose no
requirements on tribal governments.
Thus, Executive Order 13175 does not
apply to this action.
EPA specifically solicits additional
comment on this proposed action From
tribal officials.
G. Executive Order 13045: Protection of
Children From Environmental Health
Risks and Safety Risks
This action is not subject to Executive
Order 13045 (62 FR 19885, April 23,
1997) because it is not economically
significant as defined in Executive
Order 12866, and because the Agency
does not believe the environmental
health or safety risks addressed by this
action present a disproportionate risk to
children. This action’s health and risk
assessments are contained in the revised
Residual Risk Assessment for MACT 1
Petroleum Refining Sources, which is
available in the docket.
H. Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution, or Use
The proposed amendments are not a
‘‘significant energy action’’ as defined in
Executive Order 13211 (66 FR 28355,
May 22, 2001) because they are not
likely to have a significant adverse effect
on the supply, distribution, or use of
energy. Further, we have concluded that
the proposed amendments are not likely
to have any adverse energy effects
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Federal Register / Vol. 73, No. 218 / Monday, November 10, 2008 / Proposed Rules
dwashington3 on PRODPC61 with PROPOSALS2
because they result in overall savings
due to product recovery.
I. National Technology Transfer and
Advancement Act
Section 12(d) of the National
Technology Transfer and Advancement
Act (NTTAA) of 1995 (Pub. L. No. 104–
113, 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.
VCS are technical standards (e.g.,
materials specifications, test methods,
sampling procedures, and business
practices) that are developed or adopted
by VCS bodies. NTTAA directs EPA to
provide Congress, through OMB,
explanations when the Agency does not
use available and applicable VCS.
This proposed rule involves technical
standards. EPA proposes to use ‘‘Air
Stripping Method (Modified El Paso
Method) for Determination of Volatile
Organic Compound Emissions from
Water Sources,’’ Revision Number One,
dated January 2003, and will
incorporate the method by reference
(see 40 CFR 63.14). This method is
available at https://www.tceq.state.tx.us/
assets/public/implementation/air/sip/
sipdocs/2002–12–HGB/
02046sipapp_ado.pdf , or from the
Texas Commission on Environmental
Quality (TCEQ) Library, Post Office Box
13087, Austin, Texas, 78711–3087,
telephone number (512) 239–0028. This
method was chosen based on public
comments regarding the sampling and
analysis of air emissions from cooling
towers, and is required in these
proposed amendments instead of the
originally proposed requirements in 40
CFR 61.355(c) for water sample
collection, and EPA Method 8260B for
analysis of water samples taken from
cooling tower return lines.
This TCEQ method utilizes a dynamic
or flow-through system for air stripping
a sample of the water and analyzing the
resultant off-gases for VOC using a
common flame ionization detector (FID)
analyzer. While direct water analyses,
such as purge and trap analyses of water
samples utilizing gas chromatography
and/or mass spectrometry techniques,
have been shown to be effective for
cooling tower measurements of heavier
molecular weight organic compounds
with relatively high boiling points, it
has been determined that this approach
may be ineffective for capture and
measurement of VOC with lower boiling
points, such as ethylene, propylene, 1,3butadiene, and butenes. The VOC with
a low molecular weight and boiling
point are generally lost in the sample
collection step of purge/trap type
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analyses. Consequently, this TCEQ air
stripping method is used for cooling
tower and other applicable water matrix
emission measurements when VOC with
boiling points below 140o F need to be
evaluated.
Under 40 CFR 63.7(f) and 40 CFR
63.8(f) of subpart A of the General
Provisions, 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 in the
proposed amendments.
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 the
regulations.
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 they increase the level of
environmental protection for all affected
populations without having any
disproportionately high and adverse
human health or environmental effects
on any population, including any
minority or low-income population.
The proposed amendments add new
control requirements to established
national standards for petroleum
refineries to address risk remaining after
implementation of the 1995 standards
and, thus, decrease the amount of toxic
emissions to which all affected
populations are exposed.
List of Subjects in 40 CFR Part 63
Environmental protection, Air
pollution control, Hazardous
substances, Incorporation by reference,
Reporting and recordkeeping
requirements.
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Dated: October 30, 2008.
Stephen L. Johnson,
Administrator.
For the reasons stated in the
preamble, title 40, chapter I, part 63 of
the Code of Federal Regulations is
proposed to be amended as follows:
PART 63—[AMENDED]
1. The authority citation for part 63
continues to read as follows:
Authority: 42 U.S.C. 7401, et seq.
Subpart A—[Amended]
2. Section 63.14 is amended by
adding paragraph (n) to read as follows:
§ 63.14
Incorporations by reference.
*
*
*
*
*
(n) The following material is available
from the Texas Commission on
Environmental Quality (TCEQ) Library,
Post Office Box 13087, Austin, Texas
78711–3087, telephone number (512)
239–0028 or at https://
www.tceq.state.tx.us/assets/public/
implementation/air/sip/sipdocs/2002–
12–HGB/02046sipapp_ado.pdf :
(1) ‘‘Air Stripping Method (Modified
El Paso Method) for Determination of
Volatile Organic Compound Emissions
from Water Sources’’, Revision Number
One, dated January 2003, Sampling
Procedures Manual, Appendix P:
Cooling Tower Monitoring, prepared by
Texas Commission on Environmental
Quality, January 31, 2003, IBR approved
for § 63.654(c)(1) and (g)(4)(i) of Subpart
CC of this part.
(2) [Reserved]
Subpart CC—[Amended]
3. Section 63.640 is amended by:
a. Revising paragraph (a) introductory
text;
b. Revising paragraph (b)(2);
c. Revising paragraph (c) introductory
text;
d. Revising paragraphs (c)(6) and (7);
e. Adding paragraph (c)(8);
f. Revising paragraph (e) introductory
text, and paragraph (e)(2)(iii);
g. Revising paragraph (f) introductory
text, and paragraph (f)(5);
h. Revising paragraph (h) introductory
text;
i. Revising paragraphs (h)(1) and (2);
j. Revising paragraph (h)(4);
k. Adding paragraph (h)(6);
l. Revising paragraphs (k)(1), (k)(2)(i),
(k)(2)(ii), (k)(2)(iii), and the first
sentence in paragraph (k)(2)(vi);
m. Revising paragraph (l) introductory
text, paragraph (l)(2)(i), the first
sentence in paragraph (l)(2)(ii), the first
sentence in paragraph (l)(3) introductory
text, paragraph (l)(3)(i), paragraph
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(l)(3)(ii), the first sentence in paragraph
(l)(3)(vi), and the first sentence in
paragraph (l)(3)(vii);
n. Revising paragraph (n) introductory
text and paragraphs (n)(1), (n)(2),
(n)(8)(ii), and (n)(9)(i);
o. Removing and reserving paragraph
(n)(5); and
p. Revising paragraph (p).
dwashington3 on PRODPC61 with PROPOSALS2
§ 63.640 Applicability and designation of
affected source.
(a) This subpart applies to petroleum
refining process units and to related
emissions points that are specified in
paragraphs (c)(5) through (8) of this
section that are located at a plant site
and that meet the criteria in paragraphs
(a)(1) and (2) of this section:
*
*
*
*
*
(b) * * *
(2) The determination of applicability
of this subpart to petroleum refining
process units that are designed and
operated as flexible operation units
shall be reported as specified in
§ 63.655(h)(6)(i).
(c) For the purposes of this subpart,
the affected source shall comprise all
emissions points, in combination, listed
in paragraphs (c)(1) through (8) of this
section that are located at a single
refinery plant site.
*
*
*
*
*
(6) All marine vessel loading
operations located at a petroleum
refinery meeting the criteria in
paragraph (a) of this section and the
applicability criteria of subpart Y,
§ 63.560;
(7) All storage vessels and equipment
leaks associated with a bulk gasoline
terminal or pipeline classified under
Standard Industrial Classification code
2911 located within a contiguous area
and under common control with a
refinery meeting the criteria in
paragraph (a) of this section; and
(8) All heat exchange systems
associated with petroleum refining
process units meeting the criteria in
paragraph (a) of this section and which
are in organic hazardous air pollutants
(HAP) service as defined in this subpart.
*
*
*
*
*
(e) The owner or operator of a storage
vessel constructed on or before August
18, 1994, shall follow the procedures
specified in paragraphs (e)(1) and (e)(2)
of this section to determine whether a
storage vessel is part of a source to
which this subpart applies. The owner
or operator of a storage vessel
constructed after August 18, 1994, shall
follow the procedures specified in
paragraphs (e)(1), (e)(2)(i), and (e)(2)(ii)
of this section to determine whether a
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storage vessel is part of a source to
which this subpart applies.
*
*
*
*
*
(2) * * *
(iii) If the predominant use of a
storage vessel varies from year to year,
then the applicability of this subpart
shall be determined based on the
utilization of that storage vessel during
the year preceding August 18, 1995.
This determination shall be reported as
specified in § 63.655(h)(6)(ii).
(f) The owner or operator of a
distillation unit constructed on or before
August 18, 1994, shall follow the
procedures specified in paragraphs (f)(1)
through (f)(4) of this section to
determine whether a miscellaneous
process vent from a distillation unit is
part of a source to which this subpart
applies. The owner or operator of a
distillation unit constructed after
August 18, 1994, shall follow the
procedures specified in paragraphs (f)(1)
through (f)(5) of this section to
determine whether a miscellaneous
process vent from a distillation unit is
part of a source to which this subpart
applies.
*
*
*
*
*
(5) If the predominant use of a
distillation unit varies from year to year,
then the applicability of this subpart
shall be determined based on the
utilization of that distillation unit
during the year preceding August 18,
1995. This determination shall be
reported as specified in
§ 63.655(h)(6)(iii).
*
*
*
*
*
(h) Except as provided in paragraphs
(k), (l), or (m) of this section, sources
subject to this subpart are required to
achieve compliance on or before the
dates specified in paragraphs (h)(1)
through (6) of this section.
(1) Except as provided in paragraphs
(h)(1)(i) and (ii) of this section, new
sources that commence construction or
reconstruction after July 14, 1994, shall
be in compliance with this subpart upon
initial startup or August 18, 1995,
whichever is later.
(i) Heat exchange systems that
commence construction or
reconstruction after September 4, 2007,
shall be in compliance with new source
standards in § 63.654 upon initial
startup or by [the date of publication of
the final amendments in the Federal
Register], whichever is later.
(ii) New sources shall be in
compliance with § 63.646 upon initial
startup or [90 days after the date of
publication of the final amendments in
the Federal Register], whichever is
later.
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(2) Except as provided in paragraphs
(h)(3) through (h)(6) of this section,
existing sources shall be in compliance
with this subpart no later than August
18, 1998, except as provided in
§ 63.6(c)(5) of subpart A of this part, or
unless an extension has been granted by
the Administrator as provided in
§ 63.6(i) of subpart A of this part.
*
*
*
*
*
(4) All Group 1 storage vessels that are
part of an existing source shall be in
compliance with § 63.646 of this subpart
no later than [90 days after publication
of the final amendments in the Federal
Register].
*
*
*
*
*
(6) Heat exchange systems that
commence construction or
reconstruction on or before September
4, 2007, shall be in compliance with the
existing source standards in § 63.654 no
later than [18 months after publication
of the final amendments in the Federal
Register].
*
*
*
*
*
(k) * * *
(1) The reconstructed source,
addition, or change shall be in
compliance with the new source
requirements upon initial startup of the
reconstructed source or by August 18,
1995, whichever is later; and
(2) * * *
(i) The application for approval of
construction or reconstruction shall be
submitted as soon as practical before the
construction or reconstruction is
planned to commence (but it need not
be sooner than November 16, 1995);
(ii) The Notification of Compliance
Status report as required by § 63.655(f)
for a new source, addition, or change;
(iii) Periodic Reports and other
reports as required by § 63.655(g) and
(h);
*
*
*
*
*
(vi) Reports and notifications required
by § 63.428(b), (c), (g)(1), (h)(1) through
(h)(3), and (k) of subpart R. * * *
*
*
*
*
*
(l) If an additional petroleum refining
process unit is added to a plant site or
if a miscellaneous process vent, storage
vessel, gasoline loading rack, marine
tank vessel loading operation, or heat
exchange system that meets the criteria
in paragraphs (c)(1) through (8) of this
section is added to an existing
petroleum refinery or if another
deliberate operational process change
creating an additional Group 1
emissions point(s) (as defined in
§ 63.641) is made to an existing
petroleum refining process unit, and if
the addition or process change is not
subject to the new source requirements
as determined according to paragraphs
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(i) or (j) of this section, the requirements
in paragraphs (l)(1) through (3) of this
section shall apply. Examples of process
changes include, but are not limited to,
changes in production capacity, or feed
or raw material where the change
requires construction or physical
alteration of the existing equipment or
catalyst type, or whenever there is
replacement, removal, or addition of
recovery equipment. For purposes of
this paragraph and paragraph (m) of this
section, process changes do not include:
Process upsets, unintentional temporary
process changes, and changes that are
within the equipment configuration and
operating conditions documented in the
Notification of Compliance Status report
required by § 63.655(f).
*
*
*
*
*
(2) * * *
(i) If a petroleum refining process unit
is added to a plant site or an emission
point(s) is added to any existing
petroleum refining process unit, the
added emission point(s) shall be in
compliance upon initial startup of any
added petroleum refining process unit
or emission point(s) or by August 18,
1998, whichever is later.
(ii) If a deliberate operational process
change to an existing petroleum refining
process unit causes a Group 2 emission
point to become a Group 1 emission
point (as defined in § 63.641), the owner
or operator shall be in compliance upon
initial startup or by August 18, 1998,
whichever is later, unless the owner or
operator demonstrates to the
Administrator that achieving
compliance will take longer than
making the change. * * *
(3) The owner or operator of a
petroleum refining process unit or of a
storage vessel, miscellaneous process
vent, wastewater stream, gasoline
loading rack, marine tank vessel loading
operation, or heat exchange system
meeting the criteria in paragraphs (c)(1)
through (8) of this section that is added
to a plant site and is subject to the
requirements for existing sources shall
comply with the reporting and
recordkeeping requirements that are
applicable to existing sources including,
but not limited to, the reports listed in
paragraphs (l)(3)(i) through (vii) of this
section. * * *
(i) The Notification of Compliance
Status report as required by § 63.655(f)
for the emission points that were added
or changed;
(ii) Periodic Reports and other reports
as required by § 63.655(g) and (h);
*
*
*
*
*
(vi) Reports and notifications required
by § 63.428(b), (c), (g)(1), (h)(1) through
(h)(3), and (k) of subpart R. * * *
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(vii) Reports and notifications
required by §§ 63.565 and 63.567 of
subpart Y. * * *
*
*
*
*
*
(n) Overlap of subpart CC with other
regulations for storage vessels. As
applicable, paragraphs (n)(1), (n)(3),
(n)(4), (n)(6), and (n)(7) of this section
apply for Group 2 storage vessels.
Beginning [90 days after publication of
the final amendments in the Federal
Register], paragraph (n)(2) of this
section applies for Group 1 storage
vessels.
(1) After the compliance dates
specified in paragraph (h) of this
section, a Group 2 storage vessel that is
part of an existing source and is also
subject to the provisions of 40 CFR part
60, subpart Kb, is required to comply
only with the requirements of 40 CFR
part 60, subpart Kb, except as provided
in paragraph (n)(8) of this section.
(2) After the compliance dates
specified in paragraph (h) of this
section, a Group 1 storage vessel that is
subject to 40 CFR part 60, subparts K,
Ka, or Kb is required to comply only
with this subpart.
*
*
*
*
*
(5) [Reserved]
*
*
*
*
*
(8) * * *
(ii) If the owner or operator
determines that it is unsafe to perform
the seal gap measurements required in
40 CFR 60.113b(b) or to inspect the
vessel to determine compliance with 40
CFR 60.113b(a) because the roof appears
to be structurally unsound and poses an
imminent danger to inspecting
personnel, the owner or operator shall
comply with the requirements in either
§ 63.1063(c)(2)(iv)(A) or
§ 63.1063(c)(2)(iv)(B) of subpart WW.
*
*
*
*
*
(9) * * *
(i) If the owner or operator determines
that it is unsafe to perform the seal gap
measurements required in 40 CFR
60.113a(a)(1) because the floating roof
appears to be structurally unsound and
poses an imminent danger to inspecting
personnel, the owner or operator shall
comply with the requirements in either
§ 63.1063(c)(2)(iv)(A) or
§ 63.1063(c)(2)(iv)(B) of subpart WW.
*
*
*
*
*
(p) Overlap of subpart CC with other
regulations for equipment leaks.
(1) After the compliance dates
specified in paragraph (h) of this
section, equipment leaks that are also
subject to the provisions of 40 CFR parts
60 and 61 standards promulgated before
September 4, 2007, are required to
comply only with the provisions
specified in this subpart.
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(2) Equipment leaks that are also
subject to the provisions of 40 CFR part
60, subpart GGGa, are required to
comply only with the provisions
specified in 40 CFR part 60, subpart
GGGa.
*
*
*
*
*
4. Section 63.641 is amended by:
a. Adding, in alphabetical order,
definitions for ‘‘Cooling tower,’’
‘‘Cooling tower return line,’’ ‘‘Heat
exchange system,’’ and ‘‘Heat exchanger
exit line’’; and
b. Revising the definitions of
‘‘Continuous record’’ and ‘‘Reference
control technology for storage vessels’’
to read as follows:
§ 63.641
Definitions.
*
*
*
*
*
Continuous record means
documentation, either in hard copy or
computer readable form, of data values
measured at least once every hour and
recorded at the frequency specified in
§ 63.655(i).
*
*
*
*
*
Cooling tower means a heat removal
device used to remove the heat absorbed
in circulating cooling water systems by
transferring the heat to the atmosphere
using natural or mechanical draft.
Cooling tower return line means the
main water trunk lines at the inlet to the
cooling tower before exposure to the
atmosphere.
*
*
*
*
*
Heat exchange system means a device
or series of devices used to transfer heat
from process fluids to water without
intentional direct contact of the process
fluid with the water (i.e., non-contact
heat exchanger) and to transport and/or
cool the water in a closed loop
recirculation system (cooling tower
system) or a once through system (e.g.,
river or pond water). A heat exchange
system can include one or more heat
exchangers, all water lines to and from
the heat exchanger(s), and, for
recirculating systems, the cooling tower
or towers that receive water from the
heat exchanger(s).
Heat exchanger exit line means the
cooling water line at the exit of the heat
exchanger, where cooling water leaves
the heat exchanger and is routed to the
cooling tower return line.
*
*
*
*
*
Reference control technology for
storage vessels means either:
(1) An internal floating roof meeting
the specifications of §§ 63.1063(a)(1)(i),
(a)(2), and (b) of subpart WW;
(2) An external floating roof meeting
the specifications of §§ 63.1063(a)(1)(ii),
(a)(2), and (b) of subpart WW;
(3) An external floating roof converted
to an internal floating roof meeting the
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specifications of §§ 63.1063(a)(1)(ii),
(a)(2), and (b); or
(4) A closed-vent system to a control
device that reduces organic HAP
emissions by 95 percent, or to an outlet
concentration of 20 parts per million by
volume (ppmv).
(5) For purposes of emissions
averaging, these four technologies are
considered equivalent.
*
*
*
*
*
5. Section 63.642 is amended by:
a. Revising paragraph (k)(1); and
b. Revising paragraph (l)(2) to read as
follows:
§ 63.642
General standards.
*
*
*
*
*
(k) * * *
(1) The owner or operator using this
compliance approach shall also comply
with the requirements of § 63.655 as
applicable.
*
*
*
*
*
(l) * * *
(2) Comply with the requirements of
§§ 63.652, 63.653, and 63.655, as
applicable.
*
*
*
*
*
6. Section 63.644 is amended by:
a. Revising paragraph (b) introductory
text;
b. Revising paragraph (c)(1);
c. Revising paragraph (d); and
d. Revising paragraph (e) to read as
follows:
§ 63.644 Monitoring provisions for
miscellaneous process vents.
dwashington3 on PRODPC61 with PROPOSALS2
*
*
*
*
*
(b) An owner or operator of a Group
1 miscellaneous process vent may
request approval to monitor parameters
other than those listed in paragraph (a)
of this section. The request shall be
submitted according to the procedures
specified in § 63.655(h). Approval shall
be requested if the owner or operator:
*
*
*
*
*
(c) * * *
(1) Install, calibrate, maintain, and
operate a flow indicator that determines
whether a vent stream flow is present at
least once every hour. Records shall be
generated as specified in § 63.655(h) and
(i). The flow indicator shall be installed
at the entrance to any bypass line that
could divert the vent stream away from
the control device to the atmosphere; or
*
*
*
*
*
(d) The owner or operator shall
establish a range that ensures
compliance with the emissions standard
for each parameter monitored under
paragraphs (a) and (b) of this section. In
order to establish the range, the
information required in § 63.655(f)(3)
shall be submitted in the Notification of
Compliance Status report.
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(e) Each owner or operator of a control
device subject to the monitoring
provisions of this section shall operate
the control device in a manner
consistent with the minimum and/or
maximum operating parameter value or
procedure required to be monitored
under paragraphs (a) and (b) of this
section. Operation of the control device
in a manner that constitutes a period of
excess emissions, as defined in
§ 63.655(g)(6), or failure to perform
procedures required by this section
shall constitute a violation of the
applicable emission standard of this
subpart.
7. Section 63.645 is amended by
revising paragraph (h)(2) to read as
follows:
§ 63.645 Test methods and procedures for
miscellaneous process vents.
*
*
*
*
*
(h) * * *
(2) Where the recalculated TOC
emission rate is greater than 33
kilograms per day for an existing source
or greater than 6.8 kilograms per day for
a new source, the owner or operator
shall submit a report as specified in
§ 63.655(f), (g), or (h) and shall comply
with the appropriate provisions in
§ 63.643 by the dates specified in
§ 63.640.
*
*
*
*
*
8. Section 63.646 is amended by:
a. Revising paragraph (a);
b. Revising paragraphs (b)
introductory text and (b)(1);
c. Revising paragraph (c);
d. Revising paragraph (d);
e. Revising paragraph (e);
f. Revising paragraph (f);
g. Revising paragraph (g); and
h. Removing paragraphs (h) through
(l) to read as follows:
§ 63.646
Storage vessel provisions.
(a) On and after the applicable
compliance date for a Group 1 storage
vessel located at a new or existing
source as specified in § 63.640(h)(1)(ii)
and (h)(4), the owner or operator of a
Group 1 storage vessel that is part of a
new or existing source shall comply
with the requirements of subpart WW
according to the requirements in
paragraphs (b) through (g) of this
section.
(b) As used in this section, all terms
not defined in § 63.641 shall have the
meaning given them in 40 CFR part 63,
subpart A or WW. The definitions of
‘‘Group 1 storage vessel’’ and ‘‘storage
vessel’’ in § 63.641 shall apply in lieu of
the definition of ‘‘storage vessel’’ in
§ 63.1061 of subpart WW.
(1) An owner or operator may use
good engineering judgment or test
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results to determine the stored liquid
weight percent total organic HAP for
purposes of group determination. Data,
assumptions, and procedures used in
the determination shall be documented.
*
*
*
*
*
(c) For the purposes of this subpart,
all references to ‘‘the proposal date for
a referencing subpart’’ and ‘‘the
proposal date of the referencing
subpart’’ in subpart WW mean
September 4, 2007.
(d) For the purposes of this subpart,
all references to ‘‘10 years after
promulgation of the referencing
subpart’’ and ‘‘10 years after the
promulgation date of the referencing
subpart’’ in subpart WW mean the date
10 years after publication of the final
amendments in the Federal Register.
(e) Failure to perform inspections and
monitoring required by this section
shall constitute a violation of the
applicable standard of this subpart.
(f) References in § 63.1066(a) to initial
startup notification requirements do not
apply.
(g) References to the Periodic Reports
in § 63.1066(b) mean the Periodic
Report required by § 63.655(g).
9. Section 63.650 is amended by
revising paragraph (a) to read as follows.
§ 63.650
Gasoline loading rack provisions.
(a) Except as provided in paragraphs
(b) through (c) of this section, each
owner or operator of a Group 1 gasoline
loading rack classified under Standard
Industrial Classification code 2911
located within a contiguous area and
under common control with a
petroleum refinery shall comply with
subpart R, §§ 63.421, 63.422(a) through
(c) and (e), 63.425(a) through (c) and (i),
63.425(e) through (h), 63.427(a) and (b),
and 63.428(b), (c), (g)(1), (h)(1) through
(3), and (k).
*
*
*
*
*
10. Section 63.651 is amended by
revising paragraphs (a) and (c) to read as
follows:
§ 63.651 Marine tank vessel loading
operation provisions.
(a) Except as provided in paragraphs
(b) through (d) of this section, each
owner or operator of a marine tank
vessel loading operation located at a
petroleum refinery shall comply with
the requirements of §§ 63.560 through
63.568.
*
*
*
*
*
(c) The notification reports under
§ 63.567(b) are not required.
*
*
*
*
*
11. Section 63.652 is amended by:
a. Revising paragraph (a);
b. Revising paragraph (d)(2);
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c. Revising paragraph (e)(5);
d. Revising the first sentence of
paragraph (f)(3) introductory text;
e. Revising the first sentence in
paragraph (g)(5)(ii)(B)(1); and
f. Revising paragraph (l)(1) to read as
follows:
dwashington3 on PRODPC61 with PROPOSALS2
§ 63.652
Emissions averaging provisions.
(a) This section applies to owners or
operators of existing sources who seek
to comply with the emission standard in
§ 63.642(g) by using emissions averaging
according to § 63.642(l) rather than
following the provisions of §§ 63.643
through 63.647, and §§ 63.650 and
63.651. Existing marine tank vessel
loading operations located at the Valdez
Marine Terminal source may not
comply with the standard by using
emissions averaging.
*
*
*
*
*
(d) * * *
(2) Group 1 emission points that are
controlled by a reference control
technology unless the reference control
technology has been approved for use in
a different manner and a higher nominal
efficiency has been assigned according
to the procedures in paragraph (i) of this
section;
*
*
*
*
*
(e) * * *
(5) Record and report quarterly and
annual credits and debits in the Periodic
Reports as specified in § 63.655(g)(8).
Every fourth Periodic Report shall
include a certification of compliance
with the emissions averaging provisions
as required by § 63.655(g)(8)(iii).
(f) * * *
(3) For emission points for which
continuous monitors are used, periods
of excess emissions as defined in
§ 63.655(g)(6)(i). * * *
*
*
*
*
*
(g) * * *
(5) * * *
(ii) * * *
(B) * * *
(1) The percent reduction for a control
device shall be measured according to
the procedures and test methods
specified in § 63.565(d) of subpart Y.
* * *
*
*
*
*
*
(l) * * *
(1) The owner or operator shall notify
the Administrator of excess emissions in
the Periodic Reports as required in
§ 63.655(g)(6).
*
*
*
*
*
12. Section 63.653 is amended by:
a. Revising paragraphs (a)(3)(i) and
(a)(7);
b. Revising paragraph (b);
c. Revising paragraph (c); and
d. Revising paragraph (d) introductory
text, paragraph (d)(2)(vii) introductory
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text, and paragraph (d)(2)(viii)(G) to
read as follows:
§ 63.653 Monitoring, recordkeeping, and
implementation plan for emissions
averaging.
(a) * * *
(3) * * *
(i) Perform the monitoring or
inspection procedures in § 63.646 and
§ 63.1063 of subpart WW; and
*
*
*
*
*
(7) If an emission point in an
emissions average is controlled using a
pollution prevention measure or a
device or technique for which no
monitoring parameters or inspection
procedures are specified in §§ 63.643
through 63.647 and §§ 63.650 and
63.651, the owner or operator shall
establish a site-specific monitoring
parameter and shall submit the
information specified in § 63.655(h)(4)
in the Implementation Plan.
(b) Records of all information required
to calculate emission debits and credits
and records required by § 63.655 shall
be retained for 5 years.
(c) Notifications of Compliance Status
report, Periodic Reports, and other
reports shall be submitted as required
by § 63.655.
(d) Each owner or operator of an
existing source who elects to comply
with § 63.655(g) and (h) by using
emissions averaging for any emission
points shall submit an Implementation
Plan.
*
*
*
*
*
(2) * * *
(vii) The information specified in
§ 63.655(h)(4) for:
*
*
*
*
*
(viii) * * *
(G) For each pollution prevention
measure, treatment process, or control
device used to reduce air emissions of
organic HAP from wastewater and for
which no monitoring parameters or
inspection procedures are specified in
§ 63.647, the information specified in
§ 63.655(h)(4) shall be included in the
Implementation Plan.
*
*
*
*
*
13. Sections 63.654 and 63.655 are
redesignated as §§ 63.655 and 63.656.
14. A new § 63.654 is added to read
as follows:
§ 63.654
Heat exchange systems.
(a) Except as specified in paragraph
(b) of this section, the owner or operator
of a heat exchange system that meets the
criteria in § 63.640(c)(8) must comply
with the requirements of paragraphs (c)
through (g) of this section.
(b) A heat exchange system is exempt
from the requirements in paragraphs (c)
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through (g) of this section if it meets any
one of the criteria in paragraphs (b)(1)
through (3) of this section.
(1) The heat exchange system operates
with the minimum pressure on the
cooling water side at least 35 kilopascals
greater than the maximum pressure on
the process side.
(2) The heat exchange system contains
an intervening cooling fluid, containing
less than 5 percent by weight of total
HAP listed in Table 1 to this subpart,
between the process and the cooling
water. This intervening fluid must serve
to isolate the cooling water from the
process fluid and must not be sent
through a cooling tower or discharged.
For purposes of this section, discharge
does not include emptying for
maintenance purposes.
(3) The heat exchange system cools
process fluids that contain less than 5
percent by weight of total HAP listed in
Table 1 to this subpart (i.e., the heat
exchange system is not in organic HAP
service as defined in this subpart).
(c) You must perform monthly
monitoring to identify leaks of total
strippable volatile organic compound
(VOC) from each heat exchange system
subject to the requirements of this
subpart according to the procedures in
paragraphs (c)(1) and (2) of this section.
(1) Collect and analyze a sample from
each cooling tower return line prior to
exposure to air for each heat exchanger
system in organic HAP service or from
each heat exchanger exit line for each
heat exchanger in organic HAP service
within that heat exchange system to
determine the total strippable VOC
concentration (as methane) from the air
stripping testing system using ‘‘Air
Stripping Method (Modified El Paso
Method) for Determination of Volatile
Organic Compound Emissions from
Water Sources’’ Revision Number One,
dated January 2003, Sampling
Procedures Manual, Appendix P:
Cooling Tower Monitoring, prepared by
Texas Commission on Environmental
Quality, January 31, 2003 (incorporated
by reference-see § 63.14).
(2) For a heat exchange system at an
existing source, a leak is a total
strippable VOC concentration (as
methane) in the stripping gas of 6.2
ppmv or greater. For a heat exchange
system at a new source, a leak is a total
strippable VOC concentration (as
methane) in the stripping gas of 3.1
ppmv or greater.
(d) If a leak is detected, you must
repair the leak to reduce the measured
concentration to below the applicable
action level as soon as practicable, but
no later than 45 days after identifying
the leak, except as specified in
paragraphs (e) and (f). Actions that can
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be taken to achieve repair include but
are not limited to:
(1) Physical modifications to the
leaking heat exchanger, such as welding
the leak or replacing a tube;
(2) Blocking the leaking tube within
the heat exchanger;
(3) Changing the pressure so that
water flows into the process fluid;
(4) Replacing the heat exchanger or
heat exchanger bundle; or
(5) Isolating, bypassing, or otherwise
removing the leaking heat exchanger
from service until it is otherwise
repaired.
(e) If you detect a leak when
monitoring a cooling tower return line
under paragraph (c)(1), you may
conduct additional monitoring to
identify leaks of total strippable VOC
emissions using Modified El Paso
method from each heat exchanger in
organic HAP service associated with the
heat exchange system for which the leak
was detected. If the additional
monitoring shows that the total
strippable VOC concentration in the
stripped air at the heat exchanger exit
line for each heat exchanger in organic
HAP service is less than 6.2 ppmv for
existing sources or less than 3.1 ppmv
for new sources, the heat exchange
system is excluded from repair
requirements in paragraph (d).
(f) You may delay the repair of a
leaking heat exchanger when you meet
one of the conditions in paragraphs
(f)(1) through (3) of this section. You
must determine if a delay of repair is
necessary as soon as practicable, but no
later than 45 days after first identifying
the leak.
(1) If the repair is technically
infeasible without a shutdown and the
total strippable VOC concentration (as
methane) is initially and remains less
than 62 ppmv for all monthly
monitoring periods during the delay of
repair, you may delay repair until the
next scheduled shutdown of the heat
exchange system. If, during subsequent
monthly monitoring, the total strippable
VOC concentration (as methane) is 62
ppmv or greater, you must repair the
leak within 30 days of the monitoring
event in which the leak was equal to or
exceeded 62 ppmv total strippable VOC
(as methane), except as provided in
paragraph (f)(3) of this section.
(2) If the necessary equipment, parts,
or personnel are not available and the
total strippable VOC concentration (as
methane) is initially and remains less
than 62 ppmv for all monthly
monitoring periods during the delay of
repair, you may delay the repair for a
maximum of 120 calendar days. You
must demonstrate that the necessary
equipment, parts, or personnel were not
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available. If, during subsequent monthly
monitoring, the total strippable VOC
concentration (as methane) is 62 ppmv
or greater, you must repair the leak
within 30 days of the monitoring event
in which the leak was equal to or
exceeded 62 ppmv total strippable VOC
(as methane), except as provided in
paragraph (f)(3) of this section, or the
original 120 day delay of repair
deadline, whichever occurs first.
(3) Prior to [3 years after the date of
publication of the final amendments in
the Federal Register], you may delay the
repair of a heat exchanger for which the
total strippable VOC concentration (as
methane) is 62 ppmv or greater as
provided in paragraphs (f)(3)(i) through
(f)(3)(iii) of this section. On and after the
date [3 years after publication of the
final amendments in the Federal
Register], you are not allowed to delay
the repair of a heat exchanger for which
the total strippable VOC concentration
(as methane) is 62 ppmv or greater.
(i) If the repair is technically
infeasible without a shutdown and a
shutdown of the unit is scheduled
within 60 days of determining a delay
of repair is necessary.
(ii) If the necessary equipment, parts,
or personnel are not available, may
delay the repair for a maximum of 120
calendar days.
(iii) If the repair is technically
infeasible without a shutdown and a
shutdown of the unit will cause more
emissions than the delay of repair.
(g) To delay the repair under
paragraph (f), you must record the
information in paragraphs (g)(1) through
(g)(4) of this section.
(1) The reason(s) for delaying repair.
(2) A schedule for completing the
repair as soon as practical.
(3) The date and concentration of the
leak as first identified and the results of
all subsequent monthly monitoring
events during the delay of repair.
(4) An estimate of the potential
emissions from the leaking heat
exchange system or heat exchanger
following the procedures in paragraphs
(g)(4)(i) and (g)(4)(ii) of this section.
(i) Determine the total strippable VOC
concentration in the cooling water, in
parts per million by weight (ppmw),
using equation 7–1 from Modified El
Paso method (incorporated by reference
in § 63.14), based on the total strippable
concentration in the stripped air, ppmv,
from monitoring.
(ii) Calculate the VOC emissions for
the leaking heat exchange system or
heat exchanger by multiplying the VOC
concentration in the cooling water,
ppmw, by the flow rate of the cooling
water from the leaking tower or heat
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66707
exchanger and by the expected duration
of the delay.
15. Newly redesignated § 63.655 is
amended by:
a. Revising the first sentence of
paragraph (b);
b. Revising the first sentence of
paragraph (c);
c. Revising paragraph (f)(1)
introductory text and adding paragraph
(f)(1)(vi);
d. Revising paragraph (g) introductory
text, and paragraphs (g)(1), (g)(2), (g)(3),
(g)(5), and (g)(8)(ii)(C);
e. Adding paragraph (g)(9);
f. Revising the first sentence in
paragraph (h)(2)(i)(B) and revising
paragraph (h)(2)(ii);
g. Revising paragraph (i)(1);
h. Redesignating existing paragraph
(i)(4) as (i)(5); and
i. Adding paragraph (i)(4) to read as
follows:
§ 63.655 Reporting and recordkeeping
requirements.
*
*
*
*
*
(b) Each owner or operator subject to
the gasoline loading rack provisions in
§ 63.650 shall comply with the
recordkeeping and reporting provisions
in § 63.428(b) and (c), (g)(1), (h)(1)
through (h)(3), and (k) of subpart R.
* * *
(c) Each owner or operator subject to
the marine tank vessel loading operation
standards in § 63.651 shall comply with
the recordkeeping and reporting
provisions in § 63.567(a) and § 63.567(c)
through (k) of subpart Y. * * *
*
*
*
*
*
(f) * * *
(1) The Notification of Compliance
Status report shall include the
information specified in paragraphs
(f)(1)(i) through (f)(1)(vi) of this section.
*
*
*
*
*
(vi) For each heat exchange system,
identification of the heat exchange
systems that are subject to the
requirements of this subpart.
*
*
*
*
*
(g) The owner or operator of a source
subject to this subpart shall submit
Periodic Reports no later than 60 days
after the end of each 6-month period
when any of the compliance exceptions
specified in paragraphs (g)(1) through
(6) of this section or paragraph (g)(9) of
this section occur. The first 6-month
period shall begin on the date the
Notification of Compliance Status report
is required to be submitted. A Periodic
Report is not required if none of the
compliance exceptions identified in
paragraph (g)(1) through (6) of this
section or paragraph (g)(9) of this
section occurred during the 6-month
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period unless emissions averaging is
utilized. Quarterly reports must be
submitted for emission points included
in emission averages, as provided in
paragraph (g)(8) of this section. An
owner or operator may submit reports
required by other regulations in place of
or as part of the Periodic Report
required by this paragraph if the reports
contain the information required by
paragraphs (g)(1) through (9) of this
section.
(1) For storage vessels, Periodic
Reports shall include the information
specified for Periodic Reports in
paragraph (g)(2) through (g)(5) of this
section.
(2) An owner or operator who elects
to comply with § 63.646 by using a fixed
roof and an internal floating roof or by
using an external floating roof converted
to an internal floating roof shall submit
the results of each inspection conducted
in accordance with § 63.1063(c)(1),
(d)(1), and (d)(2) of subpart WW in
which a failure is detected in the control
equipment. For vessels for which
inspections are required under
§ 63.1063(c) and (d), the specifications
and requirements listed in paragraphs
(g)(2)(i) through (g)(2)(iii) of this section
apply.
(i) A failure is defined in
§ 63.1063(d)(1) of subpart WW.
(ii) Each Periodic Report shall include
a copy of the inspection record required
by § 63.1065(b) of subpart WW when a
failure occurs.
(iii) An owner or operator who elects
to use an extension in accordance with
§ 63.1063(e)(2) of subpart WW shall, in
the next Periodic Report, submit the
documentation required by
§ 63.1063(e)(2).
(3) An owner or operator who elects
to comply with § 63.646(a) through (l)
by using an external floating roof shall
meet the periodic reporting
requirements specified in paragraphs
(g)(3)(i) and (g)(3)(ii) of this section.
(i) For vessels for which inspections
are required under § 63.1063(c)(2),
(d)(1), and (d)(3) of subpart WW, the
owner or operator shall submit, as part
of the Periodic Report, a copy of the
inspection record required by
§ 63.1065(b) of subpart WW when a
failure occurs. A failure is defined in
§ 63.1063(d)(1).
(ii) An owner or operator who elects
to use an extension in accordance with
§ 63.1063(e)(2) or § 63.1063(c)(2)(iv)(B)
of subpart WW shall, in the next
Periodic Report, submit the
documentation required by those
paragraphs.
*
*
*
*
*
(5) An owner or operator who elects
to comply with § 63.646 by installing a
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closed vent system and other alternate
control device as described in § 63.1064
of subpart WW shall submit, as part of
the next Periodic Report, a written
application as described in
§ 63.1066(b)(3) of subpart WW.
*
*
*
*
*
(8) * * *
(ii) * * *
(C) The information required to be
reported by §§ 63.567(e)(4) and
63.567(j)(3) of subpart Y for each marine
tank vessel loading operation included
in an emissions average, unless the
information has already been submitted
in a separate report;
*
*
*
*
*
(9) For heat exchange systems,
Periodic Reports must include the
following information:
(i) The number of heat exchange
systems in HAP service.
(ii) The number of heat exchange
systems in HAP service found to be
leaking.
(iii) A summary of the monitoring
data that indicate a leak, including the
number of leaks determined to be equal
to or greater than the leak definitions
specified in § 63.654(c)(2);
(iv) If applicable, the date a leak was
identified, the date the source of the
leak was identified, and the date of
repair;
(v) If applicable, a summary of the
reason for delayed repair of any leak
and the date of repair; and
(vi) Estimate of VOC emissions for
delay of repair.
*
*
*
*
*
(h) * * *
(2) * * *
(i) * * *
(B) Except as provided in paragraph
(h)(2)(i)(C) of this section, if the internal
inspection required by § 63.1063(d)(1) of
subpart WW is not planned and the
owner or operator could not have
known about the inspection 30 calendar
days in advance of refilling the vessel
with organic HAP, the owner or
operator shall notify the Administrator
at least 7 calendar days prior to refilling
of the storage vessel. * * *
*
*
*
*
*
(ii) In order to afford the
Administrator the opportunity to have
an observer present, the owner or
operator of a storage vessel equipped
with an external floating roof shall
notify the Administrator of any seal gap
measurements. The notification shall be
made in writing at least 30 calendar
days in advance of any gap
measurements required by
§ 63.1062(d)(3) of subpart WW. The
State or local permitting authority can
waive this notification requirement for
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all or some storage vessels subject to the
rule or can allow less than 30 calendar
days’ notice.
*
*
*
*
*
(i) * * *
(1) Each owner or operator subject to
the storage vessel provisions in § 63.646
shall keep records as specified in
paragraphs (i)(1)(i) and (i)(1)(ii) of this
section.
(i) Each owner or operator of a Group
1 storage vessel subject to the provisions
in § 63.646 shall keep the records
specified in § 63.1065 of subpart WW.
(ii) Each owner or operator of a Group
2 storage vessel shall keep the records
specified in § 63.1065(a) of subpart WW.
If a storage vessel is determined to be
Group 2 because the weight percent
total organic HAP of the stored liquid is
less than or equal to 4 percent for
existing sources or 2 percent for new
sources, a record of any data,
assumptions, and procedures used to
make this determination shall be
retained.
*
*
*
*
*
(4) The owner or operator of a heat
exchange system subject to the
monitoring requirements in § 63.654
shall comply with the recordkeeping
requirements in paragraphs (i)(4)(i)
through (v) of this section.
(i) Identification of all heat
exchangers at the facility and the
average annual HAP concentration and
the range of HAP concentrations of
process fluid or intervening cooling
fluid described in § 63.654(c).
(ii) Identification of all heat exchange
systems that are in organic HAP service.
For each heat exchange system that is
subject to this subpart, this must
include identification of all heat
exchangers within each heat exchange
system, identification of the individual
heat exchangers in organic HAP service
within each heat exchange system, and
the cooling tower included in each heat
exchange system.
(iii) Results of the following
monitoring data for each monthly
monitoring event:
(A) Date/time of event.
(B) Barometric pressure.
(C) El Paso air stripping apparatus
water flow (ml/min) and air flow, ml/
min, and air temperature, C.
(D) FID reading (ppmv).
(E) Heat exchange exit line flow or
cooling tower return line flow, gal/min.
(F) Calibration information identified
in Section 5.4.2 of the Modified El Paso
Method, incorporated by reference in
§ 63.14(n).
(iv) The date when a leak was
identified and the date when the heat
exchanger was repaired or taken out of
service.
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(v) If a repair is delayed, the reason
for the delay, the schedule for
completing the repair, and the estimate
of potential emissions for the delay of
repair.
*
*
*
*
*
16. Newly redesignated § 63.656 is
amended by revising the first sentence
of paragraph (c)(1) to read as follows:
§ 63.656
Implementation and enforcement.
*
*
*
*
*
(c) * * *
(1) Approval of alternatives to the
requirements in §§ 63.640, 63.642(g)
through (l), 63.643, 63.646 through
63.652, and 63.654. * * *
*
*
*
*
*
Appendix to Subpart CC of Part 63–
Tables [Amended]
17. Table 1 of the appendix to subpart
CC is revised to read as follows:
TABLE 1 TO SUBPART CC OF PART
63—HAZARDOUS AIR POLLUTANTS
CAS No.a
Chemical name
Benzene ......................................
Biphenyl ......................................
Butadiene (1,3) ...........................
Carbon disulfide ..........................
Carbonyl sulfide ..........................
Cresol (mixed isomers b) ............
Cresol (m-) ..................................
Cresol (o-) ...................................
Cresol (p-) ...................................
Cumene ......................................
Dibromoethane (1,2) (ethylene
dibromide) ...............................
Dichloroethane (1,2) ...................
Diethanolamine ...........................
Ethylbenzene ..............................
Ethylene glycol ...........................
Hexane .......................................
Methanol .....................................
Methyl isobutyl ketone (hexone)
Methyl tert butyl ether .................
71432
92524
10990
75150
463581
1319773
108394
95487
106445
98828
106934
107062
111422
100414
107211
110543
67561
108101
1634044
66709
TABLE 1 TO SUBPART CC OF PART
63—HAZARDOUS AIR POLLUTANTS—
Continued
Chemical name
Naphthalene ...............................
Phenol .........................................
Toluene .......................................
Trimethylpentane (2,2,4) ............
Xylene (mixed isomers b) ............
xylene (m-) ..................................
xylene (o-) ...................................
xylene (p-) ...................................
CAS No.a
91203
108952
108883
540841
1330207
108383
95476
106423
a CAS number = Chemical Abstract Service
registry number assigned to specific compounds, isomers, or mixtures of compounds.
b Isomer means all structural arrangements
for the same number of atoms of each element and does not mean salts, esters, or
derivatives.
18. Table 4 of the appendix to subpart
CC is revised to read as follows:
TABLE 4 TO SUBPART CC OF PART 63—GASOLINE DISTRIBUTION EMISSION POINT RECORDKEEPING AND REPORTING
REQUIREMENTSa
Reference (section of subpart Y)
Description
63.428(b) or (k) ....................
63.428(g)(1) .........................
Records of test results for each gasoline cargo tank
loaded at the facility.
Continuous monitoring data recordkeeping requirements.
Semiannual report loading rack information ...................
63.428 (h)(1) through (h)(3)
Excess emissions report loading rack information .........
63.428(c) ..............................
a This
Comment
Required to be submitted with the Periodic Report required under 40 CFR part 63, subpart CC.
Required to be submitted with the Periodic Report required under 40 CFR part 63, subpart CC.
table does not include all the requirements delineated under the referenced sections. See referenced sections for specific requirements.
19. Table 5 of the appendix to subpart
CC is revised to read as follows:
TABLE 5 TO SUBPART CC OF PART 63—MARINE VESSEL LOADING AND UNLOADING OPERATIONS RECORDKEEPING AND
REPORTING REQUIREMENTSa
Reference (section of subpart Y)
Description
63.562(e)(2) .........................
Operation and maintenance plan for control equipment
and monitoring equipment.
Performance test/site test plan .......................................
63.565(a) ..............................
dwashington3 on PRODPC61 with PROPOSALS2
63.565(b)
63.567(a)
63.567(c)
63.567(d)
63.567(e)
Comment
..............................
..............................
..............................
..............................
..............................
Performance test data requirements.
General Provisions (subpart A) applicability.
Request for extension of compliance.
Flare recordkeeping requirements.
Summary report and excess emissions and monitoring
system performance report requirements.
63.567(f) ...............................
63.567(g) ..............................
63.567(h) ..............................
63.567(i) ...............................
63.567(j) ...............................
The information required under this paragraph is to be
submitted with the Notification of Compliance Status
report required under 40 CFR part 63, subpart CC.
Vapor collection system engineering report.
Vent system valve bypass recordkeeping requirements.
Marine vessel vapor-tightness documentation.
Documentation file maintenance.
Emission estimation reporting and recordkeeping procedures.
a This
The information required under this paragraph is to be
submitted with the Periodic Report required under 40
CFR part 63, subpart CC.
table does not include all the requirements delineated under the referenced sections. See referenced sections for specific requirements.
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20. Table 6 of the appendix to subpart
CC is revised to read as follows:
TABLE 6 TO SUBPART CC OF PART 63—GENERAL PROVISIONS APPLICABILITY TO SUBPART CCa
Applies to
subpart CC
63.1(a)(1) ........................
63.1(a)(2) ........................
63.1(a)(3) ........................
63.1(a)(4) ........................
63.1(a)(5) ........................
63.1(a)(6) ........................
63.1(a)(7)–63.1(a)(9) ......
63.1(a)(10) ......................
63.1(a)(11) ......................
63.1(a)(12) ......................
63.1(b)(1) ........................
63.1(b)(2) ........................
63.1(b)(3) ........................
63.1(c)(1) ........................
63.1(c)(2) ........................
Yes .......................
Yes .......................
Yes .......................
Yes .......................
No .........................
Yes .......................
No .........................
Yes .......................
Yes .......................
Yes .......................
Yes .......................
No .........................
Yes .......................
Yes .......................
Yes .......................
63.1(c)(3)–63.1(c)(4) ......
63.1(c)(5) ........................
63.1(d) ............................
63.1(e) ............................
63.2 ................................
No .........................
Yes .......................
No .........................
No .........................
Yes .......................
63.3 ................................
63.4(a)(1)–63.4(a)(2) ......
63.4(a)(3)–63.4(a)(5) ......
63.4(b) ............................
63.4(c) ............................
63.5(a) ............................
63.5(b)(1) ........................
63.5(b)(2) ........................
63.5(b)(3) ........................
63.5(b)(4) ........................
Yes .......................
Yes .......................
No .........................
Yes .......................
Yes .......................
Yes .......................
Yes .......................
No .........................
Yes .......................
Yes .......................
63.5(b)(5) ........................
63.5(b)(6) ........................
63.5(c) ............................
63.5(d) ............................
No .........................
Yes .......................
No .........................
Yes .......................
63.5(e) ............................
63.5(f) .............................
63.6(a) ............................
63.6(b)(1)–63.6(b)(5) ......
63.6(b)(6) ........................
63.6(b)(7) ........................
63.6(c)(1)–63.6(c)(2) ......
63.6(c)(3)–63.6(c)(4) ......
63.6(c)(5) ........................
63.6(d) ............................
63.6(e)(1) ........................
Yes .......................
Yes .......................
Yes .......................
No .........................
No .........................
Yes .......................
No .........................
No .........................
Yes .......................
No .........................
Yes .......................
63.6(e)(2) ........................
63.6(e)(3)(i) ....................
No .........................
Yes .......................
63.6(e)(3)(ii) ....................
63.6(e)(3)(iii)–
63.6(e)(3)(ix).
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No .........................
Yes .......................
63.6(f) .............................
Yes .......................
63.6(g) ............................
63.6(h)(1) and 63.6(h)(2)
63.6(h)(3) ........................
63.6(h)(4) ........................
63.6(h)(5) ........................
63.6(h)(6) ........................
63.6(h)(7) ........................
Yes .......................
Yes .......................
No .........................
No .........................
No .........................
Yes .......................
No .........................
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Comment
Reserved.
Except the correct mail drop (MD) number is C404–04.
Reserved.
Except subpart CC specifies pollutants subject to the rule are listed in Table 1.
Reserved.
Except area sources are not subject to subpart CC and are not required to obtain a title V permit solely for subpart CC.
Reserved.
Except that sources are not required to submit notifications overridden by this table.
Reserved.
No CAA section 112(j) standard applies to the affected sources under subpart CC.
§ 63.641 of subpart CC specifies that if the same term is defined in subparts A and CC, it shall
have the meaning given in subpart CC.
Reserved.
Reserved.
Except the cross-reference to § 63.9(b) is changed to § 63.9(b)(4) and (5). Subpart CC overrides § 63.9(b)(2).
Reserved.
Reserved.
Except that the application in § 63.5(d)(1)(i) shall be submitted as soon as practicable before
startup, but no later than 90 days after the promulgation date of subpart CC if the construction or reconstruction had commenced and initial startup had not occurred before the promulgation of subpart CC.
Subpart CC specifies compliance dates and notifications for sources subject to subpart CC.
Reserved.
§ 63.640 of subpart CC specifies the compliance date.
Reserved.
Reserved.
Except the startup, shutdown, or malfunction plan does not apply to Group 2 emission points
that are not part of an emissions averaging group.b
Reserved.
Except the startup, shutdown, or malfunction plan does not apply to Group 2 emission points
that are not part of an emissions averaging group.b
Reserved.
Except the reports specified in § 63.6(e)(3)(iv) do not need to be reported within 2 and 7 days
of commencing and completing the action, respectively, but must be included in the next periodic report.
Except the phrase ‘‘as specified in § 63.7(c)’’ in § 63.6(f)(2)(iii)(D) does not apply because subpart CC does not require a site-specific test plan.
Except subparagraph § 63.6(h)(2)(ii), which is reserved.
Reserved.
Notification of visible emission test not required in subpart CC.
Visible emission requirements and timing is specified in § 63.645(i) of subpart CC.
Subpart CC does not require opacity standards.
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Federal Register / Vol. 73, No. 218 / Monday, November 10, 2008 / Proposed Rules
66711
TABLE 6 TO SUBPART CC OF PART 63—GENERAL PROVISIONS APPLICABILITY TO SUBPART CCa—Continued
Applies to
subpart CC
63.6(h)(8) ........................
63.6(h)(9) ........................
63.6(i) .............................
63.6(j) .............................
63.7(a)(1) ........................
63.7(a)(2) ........................
Yes .......................
No .........................
Yes .......................
Yes .......................
Yes .......................
Yes .......................
63.7(a)(3) ........................
63.7(a)(4) ........................
63.7(b) ............................
Yes .......................
Yes .......................
No .........................
63.7(c) ............................
63.7(d) ............................
63.7(e)(1) ........................
No .........................
Yes .......................
Yes .......................
63.7(e)(2)–63.7(e)(4) ......
63.7(f) .............................
Yes .......................
No .........................
63.7(g) ............................
63.7(h)(1) ........................
63.7(h)(2) ........................
63.7(h)(3) ........................
No .........................
Yes .......................
Yes .......................
Yes .......................
63.7(h)(4)(i) ....................
63.7(h)(4)(ii) ....................
63.7(h)(4)(iii) and (iv) .....
63.7(h)(5) ........................
63.8(a) ............................
63.8(b) ............................
63.8(c)(1) ........................
63.8(c)(2) ........................
63.8(c)(3) ........................
Yes .......................
No .........................
Yes .......................
Yes .......................
Yes .......................
Yes .......................
Yes .......................
Yes .......................
Yes .......................
63.8(c)(4) ........................
63.8(c)(5)–63.8(c)(8) ......
63.8(d) ............................
63.8(e) ............................
No
No
No
No
63.8(f)(1) .........................
63.8(f)(2) .........................
63.8(f)(3) .........................
63.8(f)(4)(i) .....................
63.8(f)(4)(ii) .....................
63.8(f)(4)(iii) ....................
63.8(f)(5) .........................
63.8(f)(6) .........................
63.8(g) ............................
63.9(a) ............................
Yes .......................
Yes .......................
Yes .......................
No .........................
Yes .......................
No .........................
Yes .......................
No .........................
No .........................
Yes .......................
63.9(b)(1) ........................
Yes .......................
63.9(b)(2) ........................
63.9(b)(3) ........................
63.9(b)(4) ........................
63.9(b)(5) ........................
63.9(c) ............................
63.9(d) ............................
63.9(e) ............................
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No .........................
No .........................
Yes .......................
Yes .......................
Yes .......................
Yes .......................
No .........................
63.9(f) .............................
63.9(g) ............................
63.9(h) ............................
63.9(i) .............................
63.9(j) .............................
63.10(a) ..........................
63.10(b)(1) ......................
63.10(b)(2)(i) ..................
No .........................
No .........................
No .........................
Yes .......................
No .........................
Yes .......................
No .........................
Yes .......................
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Comment
.........................
.........................
.........................
.........................
Jkt 217001
Subpart CC does not require opacity standards.
Except for § 63.6(i)(15), which is reserved.
Except test results must be submitted in the Notification of Compliance Status report due 150
days after compliance date, as specified in § 63.655(f) of subpart CC.
Subpart CC requires notification of performance test at least 30 days (rather than 60 days) prior
to the performance test.
Subpart CC does not require a site-specific test plan.
Except the performance test must be conducted at the maximum representative capacity as
specified in § 63.642(d)(3) of subpart CC.
Subpart CC specifies applicable methods and provides alternatives without additional notification or approval.
Performance test reporting specified in § 63.655(f).
Yes, except site-specific test plans shall not be required, and where § 63.7(g)(3) specifies submittal by the date the site-specific test plan is due, the date shall be 90 days prior to the Notification of Compliance Status report in § 63.655(f).
Site-specific test plans are not required in subpart CC.
Except § 63.8(a)(3), which is reserved.
Except that verification of operational status shall, at a minimum, include completion of the
manufacturer’s written specifications or recommendations for installation, operation, and calibration of the system or other written procedures that provide adequate assurance that the
equipment would monitor accurately.
Subpart CC specifies monitoring frequency in § 63.655(i)(3) of subpart CC.
Subpart CC does not require performance evaluations; however, this shall not abrogate the Administrator’s authority to require performance evaluation under section 114 of the Clean Air
Act.
Timeframe for submitting request is specified in § 63.655(h)(5)(i) of subpart CC.
Timeframe for submitting request is specified in § 63.655(h)(5)(i) of subpart CC.
Subpart CC does not require continuous emission monitors.
Subpart CC specifies data reduction procedures in § 63.655(i)(3).
Except that the owner or operator does not need to send a copy of each notification submitted
to the Regional Office of the EPA as stated in § 63.9(a)(4)(ii).
Except the notification of compliance status report specified in § 63.655(f) of subpart CC may
also serve as the initial compliance notification required in § 63.9(b)(1)(iii).
A separate Initial Notification report is not required under subpart CC.
Reserved.
Except for subparagraphs § 63.9(b)(4)(ii) through (iv), which are reserved.
Subpart CC requires notification of performance test at least 30 days (rather than 60 days) prior
to the performance test and does not require a site-specific test plan.
Subpart CC does not require advanced notification of visible emissions test.
Subpart CC § 63.655(f) specifies Notification of Compliance Status report requirements.
§ 63.644(d) of subpart CC specifies record retention requirements.
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Federal Register / Vol. 73, No. 218 / Monday, November 10, 2008 / Proposed Rules
TABLE 6 TO SUBPART CC OF PART 63—GENERAL PROVISIONS APPLICABILITY TO SUBPART CCa—Continued
Reference
Applies to
subpart CC
63.10(b)(2)(ii) ..................
63.10(b)(2)(iii) .................
63.10(b)(2)(iv) .................
63.10(b)(2)(v) .................
63.10(b)(2)(vi) .................
63.10(b)(2)(vii) ................
63.10(b)(2)(viii) ...............
63.10(b)(2)(ix) .................
63.10(b)(2)(x) .................
63.10(b)(2)(xi) .................
63.10(b)(2)(xii) ................
63.10(b)(2)(xiii) ...............
63.10(b)(2)(xiv) ...............
63.10(b)(3) ......................
63.10(c)(1)–63.10(c)(6) ..
63.10(c)(7) and
63.10(c)(8).
63.10(c)(9)–63.10(c)(15)
63.10(d)(1) ......................
63.10(d)(2) ......................
63.10(d)(3) ......................
Yes .......................
No .........................
Yes .......................
Yes .......................
Yes .......................
No .........................
Yes .......................
Yes .......................
Yes .......................
No .........................
Yes .......................
No .........................
Yes .......................
Yes .......................
No .........................
Yes .......................
63.10(d)(4) ......................
63.10(d)(5)(i) ..................
Yes .......................
Yesb ......................
63.10(d)(5)(ii) ..................
Yes .......................
63.10(e) ..........................
63.10(f) ...........................
63.11–63.16 ...................
No .........................
Yes .......................
Yes .......................
Comment
No .........................
Yes .......................
No .........................
No .........................
§ 63.655(f) of subpart CC specifies performance test reporting.
Results of visible emissions test are included in Compliance Status Report as specified in
§ 63.655(f).
Except that reports required by § 63.10(d)(5)(i) may be submitted at the same time as periodic
reports specified in § 63.655(g) of subpart CC.
Except that actions taken during a startup, shutdown, or malfunction that are not consistent with
the startup, shutdown, and malfunction plan and that cause the source to exceed any applicable emission limitation do not need to be reported within 2 and 7 days of commencing and
completing the action, respectively, but must be included in the next periodic report.
a Wherever subpart A specifies ‘‘postmark’’ dates, submittals may be sent by methods other than the U.S. Mail (e.g., by fax or courier). Submittals shall be sent by the specified dates, but a postmark is not required.
b The plan, and any records or reports of startup, shutdown, and malfunction do not apply to Group 2 emission points that are not part of an
emissions averaging group.
21. Table 10 of the appendix to
subpart CC is amended by revising
footnotes d, f, and g to read as follows:
Table 10 to Subpart CC of Part 63—
Miscellaneous Process Vents—
Monitoring, Recordkeeping, and
Reporting Requirements for Complying
With 98 Weight-Percent Reduction of
Total Organic HAP Emissions or a
Limit of 20 Parts Per Million by Volume
*
*
*
*
*
= Notification of Compliance
Status Report described in § 63.655.
*
*
*
*
*
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f When a period of excess emission is
caused by insufficient monitoring data,
as described in § 63.655(g)(6)(i)(C) or
(D), the duration of the period when
monitoring data were not collected shall
be included in the Periodic Report.
g PR = Periodic Reports described in
§ 63.655(g).
*
*
*
*
*
[FR Doc. E8–26403 Filed 11–7–08; 8:45 am]
BILLING CODE 6560–50–P
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Agencies
[Federal Register Volume 73, Number 218 (Monday, November 10, 2008)]
[Proposed Rules]
[Pages 66694-66712]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E8-26403]
[[Page 66693]]
-----------------------------------------------------------------------
Part II
Environmental Protection Agency
-----------------------------------------------------------------------
40 CFR Part 63
National Emission Standards for Hazardous Air Pollutants From Petroleum
Refineries; Proposed Rule
Federal Register / Vol. 73 , No. 218 / Monday, November 10, 2008 /
Proposed Rules
[[Page 66694]]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 63
[EPA-HQ-OAR-2003-0146; FRL-8737-8]
RIN 2060-AO55
National Emission Standards for Hazardous Air Pollutants From
Petroleum Refineries
AGENCY: Environmental Protection Agency (EPA).
ACTION: Supplemental notice to proposed rulemaking.
-----------------------------------------------------------------------
SUMMARY: This action supplements the proposed amendments to the
national emission standards for petroleum refineries (Refinery MACT 1)
published on September 4, 2007. The 2007 proposal, in part, sets forth
proposed maximum achievable control technology and residual risk
requirements for cooling towers and proposed residual risk and
technology review requirements for storage tanks. This supplemental
proposal contains new proposed requirements for cooling towers, a new
option for storage vessels, and clarifications and corrections to
definitions, tables, and regulatory citations.
DATES: Comments must be received on or before December 10, 2008, unless
a public hearing is requested by November 20, 2008. If a hearing is
requested on the proposed rule, written comments must be received by
December 26, 2008. Under the Paperwork Reduction Act, comments on the
information collection provisions must be received by the Office of
Management and Budget (OMB) on or before December 10, 2008.
ADDRESSES: Submit your comments, identified by Docket ID No. EPA-HQ-
OAR-2003-0146, by one of the following methods:
www.regulations.gov. Follow the on-line instructions for
submitting comments.
E-mail: Comments may be sent by electronic mail (e-mail)
to a-and-r-Docket@epa.gov, Attention Docket ID No. EPA-HQ-OAR-2003-
0146.
Fax: Fax your comments to: (202) 566-9744, Attention
Docket ID No. EPA-HQ-OAR-2003-0146.
Mail: Send your comments to: Air and Radiation Docket and
Information Center, Environmental Protection Agency, Mailcode: 2822T,
1200 Pennsylvania Ave., NW., Washington, DC 20460, Attention Docket ID
No. EPA-HQ-OAR-2003-0146. Please include a total of two copies. We
request that a separate copy also be sent to the contact person
identified below (see FOR FURTHER INFORMATION CONTACT). In addition,
please mail a copy of your comments on the information collection
provisions to the Office of Information and Regulatory Affairs, Office
of Management and Budget (OMB), Attn: Desk Office for EPA, 725 17th
St., NW., Washington, DC 20503.
Hand Delivery or Courier: Deliver your comments to: EPA
Docket Center, Room 3334, 1301 Constitution Avenue, NW., Washington, DC
20004. Such deliveries are accepted only 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-
2003-0146. EPA's policy is that all comments received will be included
in the public docket without change and may be made available online at
www.regulations.gov, including any personal information provided,
unless the comment includes information claimed to be confidential
business information (CBI) or other information whose disclosure is
restricted by statute. Do not submit information that you consider to
be CBI or otherwise protected through www.regulations.gov or 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 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, will be publicly available only in hard copy.
Publicly available docket materials are available either electronically
in www.regulations.gov or in hard copy at the EPA Docket Center, Public
Reading Room, EPA West Building, Room 3334, 1301 Constitution Ave.,
NW., Washington, DC. The Public Reading Room is open from 8:30 a.m. to
4:30 p.m. Eastern Standard Time (EST), Monday through Friday, excluding
legal holidays. The telephone number for the Public Reading Room is
(202) 566-1744, and the telephone number for the Air and Radiation
Docket is (202) 566-1742.
FOR FURTHER INFORMATION CONTACT: Mr. Robert Lucas, Office of Air
Quality Planning and Standards, Sector Policies and Programs Division,
Coatings and Chemicals Group (E143-01), Environmental Protection
Agency, Research Triangle Park, North Carolina 27711, telephone number
(919) 541-0884; fax number (919) 541-0246; e-mail address:
lucas.bob@epa.gov.
SUPPLEMENTARY INFORMATION:
I. General Information
A. Does this action apply to me?
The regulated category and entities affected by this proposed
action include:
----------------------------------------------------------------------------------------------------------------
Category NAICS \1\ code Examples of regulated entities
----------------------------------------------------------------------------------------------------------------
Industry............................ 32411 Petroleum refineries located at a major source that are
subject to 40 CFR part 63, subpart CC.
----------------------------------------------------------------------------------------------------------------
\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 regulated by the
proposed rule. To determine whether your facility would be regulated by
the proposed amendments, you should carefully examine the applicability
criteria in 40 CFR 63.100 of subpart CC (National Emission Standards
for Hazardous Air Pollutants From Petroleum Refineries). If you have
any questions regarding the applicability of this action to a
particular entity, contact either the air permit authority for the
entity or your
[[Page 66695]]
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 for EPA?
Do not submit information containing CBI to EPA through
www.regulations.gov or e-mail. Send or deliver information as CBI only
to the following address: Roberto Morales, OAQPS Document Control
Officer (C404-02), Office of Air Quality Planning and Standards,
Environmental Protection Agency, Research Triangle Park, NC 27711,
Attention Docket ID No. EPA-HQ-OAR-2003-0146 (for petroleum
refineries). 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
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 supplemental proposal by November 20, 2008, we will hold
a public hearing on November 25, 2008. If you are interested in
attending the public hearing, contact Janet Eck at (919) 541-7946 to
verify that a hearing will be held. If a public hearing is held, it
will be held at 10 a.m. at the EPA's Environmental Research Center
Auditorium, Research Triangle Park, NC, or an alternate site nearby.
E. How is this document organized?
I. General Information
A. Does this action apply to me?
B. What should I consider as I prepare my comments for EPA?
C. Where can I get a copy of this document?
D. When would a public hearing occur?
II. Background Information
III. Summary of Supplemental Proposal
A. What are the proposed requirements to meet CAA sections
112(f)(2) and (d)(6) for Group 1 storage vessels?
B. What are the proposed requirements for cooling towers under
CAA sections 112(d)(2) and (f)(2)?
C. What other revisions and clarifications are we proposing?
IV. Rationale for Supplemental Proposed Amendments
A. Storage Vessels
B. Cooling Towers
V. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory Planning and Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation and Coordination with
Indian Tribal Governments
G. Executive Order 13045: Protection of Children from
Environmental Health Risks and Safety Risks
H. Executive Order 13211: Actions Concerning Regulations That
Significantly Affect Energy Supply, Distribution, or Use
I. National Technology Transfer and Advancement Act
J. Executive Order 12898: Federal Actions to Address
Environmental Justice in Minority Populations and Low-Income
Populations
II. Background Information
On September 4, 2007 (72 FR 50716), EPA proposed several actions
under section 112 of the Clean Air Act (CAA) with respect to petroleum
refineries subject to the 1995 Refinery MACT 1 Rule (40 CFR part 63,
subpart CC). Please refer to the 2007 proposal for additional
background material. See 72 FR 50717-18. In response to comments
received on the 2007 proposed rule, EPA further evaluated that proposal
and is now supplementing its proposal with respect to cooling towers
and storage vessels. In addition, as part of this notice, we are
providing proposed revisions to the regulatory text to clarify and
correct definitions, tables, and regulatory citations.
III. Summary of Supplemental Proposal
A. What are the proposed requirements to meet CAA sections 112(f)(2)
and (d)(6) for Group 1 storage vessels?
In the September 2007 proposed rule, EPA initially proposed two
regulatory options for storage vessels under CAA sections 112(f)(2) and
(d)(6): Option 1 would require no revisions to the Refinery MACT 1 rule
and Option 2 would add the requirements in 40 CFR 63.119(c)(2)(ix) and
(x) for slotted guide poles on existing external floating roof (EFR)
storage vessels (Refinery MACT 1 currently provides an exemption from
these requirements for existing storage vessels). For more detail on
the proposed options, please see 72 FR 50726-27.
Many commenters agreed that, of EPA's proposed options, Option 2,
controls for slotted guide poles, is an appropriate and cost-effective
level of control. However, several commenters supporting Option 2
requested that EPA revise the regulatory text associated with Option 2
to use clear terminology consistent with the most recent rules and
technologies for storage vessels, i.e., the rules at 40 CFR part 63,
subpart WW and the Storage Tank Emission Reduction Partnership Program
(STERPP) (described at 65 FR 19891). Specifically, commenters noted
that subpart WW and STERPP include clearer descriptions and definitions
of control options and provide clear and specific criteria for
requirements such as the required height of a pole float and the
position of a gasket.
Based on our review of public comments and subsequent analysis, we
are proposing an additional option under CAA sections 112(f)(2) and
(d)(6) for storage vessels. Specifically, we are proposing to remove
the exemptions for existing EFR storage vessels and amend the
requirements for all Group 1 storage vessels to be consistent with, and
refer directly to, the requirements of 40 CFR part 63, subpart WW. The
subpart WW requirements include the requirements for fitting controls
on slotted guide poles, which were originally proposed under Option 2,
as well as additional requirements for fittings for unslotted guide
poles and other openings on EFR storage vessels. The proposed
amendments also include the inspection, recordkeeping, and reporting
requirements in subpart WW to account for the additional requirements
for fitting controls for EFR storage vessels. It should be noted that,
while subpart WW was preferred by the commenters and its stringency is
equivalent to the HON, the existing 40 CFR part 63, subpart CC does not
require all the specific tank fitting control requirements in the HON.
While proposed Option 2 in the September 2007 proposal included some
tank fitting control requirements not currently included in subpart CC,
Option 2 did not include all of the tank fitting control requirements
in the HON and subpart WW. Consequently, by proposing to require
compliance with subpart WW, we are proposing full tank
[[Page 66696]]
fitting controls for Group 1 storage vessels, and, therefore, today's
proposed amendments are more stringent than the existing subpart CC
rules and the subpart CC amendments proposed in September 2007.
The subpart WW requirements are being proposed because, in addition
to providing clearer language for fitting controls, they provide an
ample margin of safety to protect public health. This option reduces
hazardous air pollutants (HAP) emissions and risks beyond the current
maximum achievable control technology (MACT) standard using controls
that are technically and economically feasible and that pose no adverse
environmental impacts. We estimate that these changes would reduce the
number of people at cancer risk greater than 1-in-1 million by 20,000
individuals and the cancer incidence by 0.002--0.003 cases per year
(i.e., prevent one cancer case every 400 years). This option would
reduce emissions of volatile organic compounds (VOC) by 14,800 tons per
year (tpy). Reducing VOC provides the added benefit of reducing ambient
concentrations of ozone and may reduce fine particulate matter. The
annualized cost impacts of this option are estimated to be a cost
savings of $6.8 million. Our economic analysis (summarized later in
this preamble) indicates that this cost will have little impact on the
price and output of petroleum products.
Under this option, we are proposing that the owner or operator of
an existing Group 1 storage vessel comply with the requirements in
subpart WW of this part no later than 90 days after promulgation of
these amendments. As provided in 40 CFR part 63, subpart WW, and for
the reasons provided in Section IV, we are proposing that retrofitting
floating roof tanks with the guide pole controls and certain other
requirements is not required until the next time the vessel is emptied
and degassed, or 10 years from the promulgation date of the final
standards, whichever is sooner.
B. What are the proposed requirements for cooling towers under CAA
sections 112(d)(2) and (f)(2)?
Under CAA sections 112(d)(2) and (d)(3), we proposed work practice
standards for cooling towers that would require the owner or operator
of a new or existing source to monitor for leaks in the cooling tower
return lines from heat exchangers in organic HAP service (i.e., lines
that contain or contact fluids with 5 weight percent or greater of
total organic HAP listed in Table 1 of the rule) and, where leaks are
detected, to repair such leaks within a specified period of time. We
proposed two options for new and existing sources, one based on the
MACT floor analysis that accompanied the proposal, i.e., the average
emissions limitations achieved by the top 12 percent of the affected
sources, and the other based on an analysis of beyond-the-floor
techniques. For more detail on those options, please see 72 FR 50722-
24.
In response to public comments that the terms used in the proposed
cooling tower requirements needed to be defined and should focus on
heat exchange systems, we are proposing to add several definitions to
clarify the cooling tower monitoring requirements. We are proposing
that the cooling tower requirements would apply to each ``heat exchange
system.'' A ``heat exchange system'' means a device or series of
devices used to transfer heat from process fluids to water without
intentional direct contact of the process fluid with the water (i.e.,
non-contact heat exchangers) and to transport and/or cool the water in
a closed loop recirculation system (cooling tower system) or a once
through system (e.g., river or pond water). A ``heat exchange system''
can include one or more heat exchangers, all water lines to and from
the heat exchanger(s), and, for recirculating systems, the cooling
tower or towers that receive water from the heat exchanger(s).
In response to public comments that our floor analysis did not
include existing State standards, we collected new information on
existing State and local cooling towers provisions and revised our MACT
floor analysis. More detail regarding the development of the revised
MACT floor for existing and new sources based on review of these
existing State requirements is provided in Section IV.B. of this
preamble and in the docket memorandum entitled ``Cooling Towers:
Control Alternatives and Impact Estimates'' (EPA-HQ-OAR-2003-0146). The
revised proposed requirements are described below and are based on the
revised MACT floor determination. Control techniques considered as
beyond-the-floor options are described in Section IV.B of this
preamble; we are not proposing any of these options because they were
determined not to be cost-effective.
We are proposing that owners and operators of heat exchange systems
that are in organic HAP service at new and existing sources would be
required to conduct monthly sampling and analyses using the Texas
Commission on Environmental Quality's (TCEQ) Modified El Paso method,
Revision Number One, dated January 2003.\1\ For existing sources,
monthly cooling tower monitoring would begin within 18 months of
promulgation of the final amendments. For new sources, monthly cooling
tower monitoring would begin upon start-up or on the date of
promulgation of these amendments, whichever is later. For existing
sources, a leak would be defined as 6.2 parts per million by volume
(ppmv) total strippable VOC in the stripping gas collected via the
Modified El Paso method. For new sources, a leak would be defined as
3.1 ppmv total strippable VOC collected via the Modified El Paso
method. The proposed amendments would require the repair of leaks in
heat exchangers in organic HAP service within 45 days of the sampling
event in which the leak was detected, unless a delay in repair is
allowed. Delay in repair of the leak would be allowed until the next
shutdown if the repair of the leak would require the process unit
served by the leaking heat exchanger to be shut down and the total
strippable VOC concentration is less than 62 ppmv. Delay in repair of
the leak would also be allowed for up to 120 days if the total
strippable VOC concentration is less than 62 ppmv and if critical parts
or personnel are not available. The owner or operator would be required
to continue monthly monitoring and repair the heat exchanger within 45
days if sampling results show that the leak exceeds 62 ppmv total
strippable VOC. Within the first 3 years after promulgation of these
amendments, delay in repair of a leak would also be allowed if the leak
exceeds 62 ppmv total strippable VOC and the repair of the leak would
require the process unit served by the leaking heat exchanger to be
shut down and a shutdown is planned within 60 days or if critical parts
or personnel are not available. Starting 3 years after promulgation of
these amendments, delay of repair beyond 45 days would not be allowed
if the leak exceeds 62 ppmv total strippable VOC.
---------------------------------------------------------------------------
\1\ ``Air Stripping Method (Modified El Paso Method) for
Determination of Volatile Organic Compound Emissions from Water
Sources,'' Revision Number One, dated January 2003, Sampling
Procedures Manual, Appendix P: Cooling Tower Monitoring, prepared by
Texas Commission on Environmental Quality, January 31, 2003
(incorporated by reference-see Sec. 63.14).
---------------------------------------------------------------------------
Sampling for leaks would be conducted either at individual heat
exchanger return lines (i.e., water lines returning the water from the
heat exchanger to the cooling tower) or the combined cooling tower
inlet water location. That is, if the cooling tower services multiple
heat exchangers, the
[[Page 66697]]
owner or operator may elect to monitor only the heat exchangers ``in
organic HAP service'' or monitor at the combined cooling tower inlet.
If a leak is detected at the combined cooling tower inlet, the owner or
operator may elect to fix the leak regardless of its location or begin
monitoring at each heat exchanger ``in organic HAP service'' to
document that the leak is not originating from a heat exchanger ``in
organic HAP service.''
All new or existing refineries with a heat exchange system ``in
organic HAP service'' would be required to maintain records of the heat
exchangers in organic HAP service, the cooling towers associated with
heat exchangers in organic HAP service, monthly monitoring results, and
information for any delays in repair of a leak.
C. What other revisions and clarifications are we proposing?
In the September 2007 proposal, we proposed to amend Table 6 to 40
CFR part 63, subpart CC (General Provisions Applicability to Subpart
CC) to bring the table up-to-date with current requirements of the
General Provisions and clarify certain requirements. In conjunction
with the publication of Table 6 in the proposal, we erroneously
included a Table 11. We are clarifying that we are not proposing to
include Table 11 and, thus, do not plan to include it as part of the
final rule.
We received public comments that methyl ethyl ketone (also known as
2-butanone) has been delisted as a HAP. We are, therefore, proposing to
revise Table 1 to delete methyl ethyl ketone from the HAP listed in
Table 1.
We also received several public comments noting that cross-
references to other subparts should be updated. Therefore, we are also
proposing amendments to correct cross-references to subparts R and Y of
part 63 in the rule text, as well as to correct the recordkeeping and
reporting requirement cross-references in Tables 4 and 5 of subpart CC
to part 63. We are also proposing to clarify applicability sections by
specifying the promulgation date of the original subpart CC. Finally,
we are proposing amendments to clarify how owners and operators should
comply with overlapping standards for equipment leaks. These proposed
amendments are included to clarify the requirements of subpart CC.
IV. Rationale for Supplemental Proposed Amendments
A. Storage Vessels
In response to public comments on the original proposal, we revised
and updated the analysis of the options we proposed in September 2007.
We also evaluated a wider range of control options, such as the
requirements included in the Generic Storage Vessel MACT (40 CFR part
63, subpart WW) and STERPP, as well as other specific controls
suggested by the commenters. A detailed explanation of our impacts
analysis for each of the options described in this section is provided
in ``Storage Vessels: Revised Control Options and Impact Estimates'' in
Docket ID No. EPA-HQ-OAR-2003-0146.
The storage vessel controls in 40 CFR part 63, subpart WW and for
STERPP include several compliance options for controlling slotted guide
poles as well as requirements for additional fitting controls on other
EFR deck openings. We determined that, based on emission modeling runs
using a model gasoline storage vessel, the STERPP and subpart WW
requirements for slotted guide poles achieve the same or better
emission reduction efficiencies as the originally proposed Option 2 for
Group 1 storage vessels. And, while additional deck fitting controls on
EFR storage vessels contained in the STERPP and subpart WW provide only
a tenth of the emission reductions as the guide pole controls, these
controls (primarily use of gaskets) are inexpensive. As seen in Table 1
of this preamble, our cost analysis indicates that these fitting
controls are cost-effective. Therefore, we are proposing an additional
option that would require these additional fitting controls for
existing Group 1 storage vessels covered by Refinery MACT 1.
Based on our evaluation of the STERPP and 40 CFR part 63, subpart
WW control requirements, we determined that those standards require
solid, or unslotted, guide poles to be gasketed and have a wiper
system, and we evaluated the impacts of also adding these requirements
to Refinery MACT 1. We determined that, provided the retrofits could be
performed without additional emissions and cost associated with an
unplanned emptying and degassing of the storage vessel (i.e., during a
turnaround or when the vessel is taken out of service for maintenance/
repair), the control requirements for solid guide poles were cost-
effective. That is, over a 10-year cycle using a 7-percent annual
interest rate, these controls yield a net cost savings (from reduced
product losses). The combination of additional deck fitting controls
and full guide pole controls is presented in Table 1 as ``full deck and
guide pole controls.'' Consequently, we are proposing as an additional
option to amend Refinery MACT 1 to refer directly to the storage vessel
control requirements in subpart WW. As the cost-effectiveness of the
control retrofits are predicated on a lack of additional emissions and
cost associated with emptying and degassing the storage vessel, we are
providing up to 10 years for compliance with these requirements as
provided for in 40 CFR 63.1063(a)(ix) of subpart WW. Because these
controls are cost-effective and incrementally reduce public exposure,
we believe this option, in addition to the two options proposed
earlier, would provide an ample margin of safety and meet the
requirements of the technology review.
Table 1--Nationwide Impacts of Various Storage Vessel Regulatory Options
--------------------------------------------------------------------------------------------------------------------------------------------------------
Total
Total annualized Total HAP
capital cost Product annualized HAP emission Cost-
Control option investment without recovery costs ($ emissions reductions effectiveness
($ recovery credit ($ million/ (tons per (tons per ($/ton HAP)
million) ($ million) yr) year) a year)
million)
--------------------------------------------------------------------------------------------------------------------------------------------------------
Option 1: Baseline (proposed at 72 FR 50726-27) a.................. 0 0 0 0 2,970 0 (b)
Option 2: Slotted guide pole sleeves (proposed at 72 FR 50726-27) b 5.3 0.76 -3.3 -2.6 2,300 660 -3,900
Option 3: Full deck and guide pole controls........................ 10 1.5 -8.3 -6.8 1,300 1,640 -4,100
--------------------------------------------------------------------------------------------------------------------------------------------------------
a Costs and emission reductions have been revised since September 2007 proposal; see memorandum entitled ``Storage Vessels: Revised Control Options and
Impact Estimates'' in Docket ID No. EPA-HQ-OAR-2003-0146 for details on these revisions.
b Not applicable.
[[Page 66698]]
Table 2 of this preamble presents the risk reduction associated
with the control option for storage vessels.
Table 2--Inhalation Risk Impacts of Regulatory Alternative for Storage Vessels
----------------------------------------------------------------------------------------------------------------
Control Control
Parameter Baseline option 1 option 2 option 3
-----------------------------------------------------------------------------------------------------
Risk to Most Exposed Individual:
Cancer (in 1 million)................ 30.............................. 30 30
Noncancer (HI)....................... 0.3............................. 0.3 0.3
Size of Population at Cancer Risk:
> 100-in-1 million................... 0............................... 0 0
> 10-in-1 million.................... 4,000........................... 3,900 3,800
> 1-in-1 million..................... 460,000......................... 450,000 440,000
Number of Plants at Cancer Risk Level:
> 100-in-1 million................... 0............................... 0
> 10-in-1 million.................... 23.............................. 23 22
> 1-in-1 million..................... 88.............................. 88 87
Population with HI > 1 1............... 0............................... 0 0
No of Plants with HI > 1................. 0............................... 0 0
Annual Cancer Incidence 2................ 0.032-0.049..................... 0.031-0.048 0.030-0.046
Cancer Incidence Reduction (Percent)..... (3)............................. 2 5
HAP Emission Reduction (Percent)......... (3)............................. 4 10
----------------------------------------------------------------------------------------------------------------
1 If the Hazard Index (HI) is calculated to be less than or equal to 1, then no adverse non-cancer chronic
health effects are expected as a result of the exposure. However, an HI exceeding 1 does not translate to a
probability that adverse effects occur. Rather, it suggests the possibility that adverse health effects may
occur. Acute non-cancer effects not estimated in this analysis.
2 The range of cancer incidence reflects the cancer potency range of benzene, either end of which is considered
equally plausible.
3 Not applicable.
B. Cooling Towers
To respond to public comments that our floor analysis did not
include existing State standards, we collected additional information
on cooling tower requirements for multiple petroleum refineries in
several States. Using these data, we reanalyzed the MACT floor for new
and existing sources and identified 39 petroleum refineries in
California, Illinois, Indiana, Louisiana, Minnesota, and Texas with
permit requirements for HAP and/or VOC in cooling tower return water
along with cooling tower monitoring requirements. We note that the
permit requirements are based on calculated emission estimates using
the water recirculation rates and monitored concentrations in the
cooling waters. Consequently, the permit requirements effectively
define a maximum allowable concentration limit of strippable organics
in the cooling water so that the effective leak definition could be
determined for each cooling tower. We further note that no refineries
directly measure cooling tower emissions, and we reaffirm our
conclusion that cooling tower work practice standards are appropriate
because the emissions are not emitted through a stack or other
conveyance and are, therefore, not practically measurable.
We ranked cooling tower requirements based on the projected
emissions that would occur given the specific cooling tower monitoring
provision. Based on preliminary calculations performed using the
cooling tower impacts model (see ``Cooling Towers: Control Alternatives
and Impact Estimates'' memorandum in Docket ID No. EPA-HQ-OAR-2003-
0146), the leak definition was the primary factor influencing the
emissions limitations achieved by a cooling tower monitoring program;
the second most important factor was the specification of time frames
for completing repairs and provisions or limitations for delay of
repair. Monitoring frequency, while a contributing factor to overall
cooling tower emissions performance, was not as important as the leak
definition and specified repair deadlines. We selected the 6th
percentile cooling tower as indicative of the average emission
limitation achieved by the best performing 12 percent of cooling
towers. Based on this, we determined that the MACT floor for cooling
towers at existing sources is cooling water sampling on a monthly basis
for total strippable VOC compounds, where a leak is defined as 6.2 ppmv
of total strippable VOC compounds in the stripping air of the TCEQ
Modified El Paso method. We note that this leak definition is
equivalent to the controlled emission factor in AP-42,\2\ and that many
refineries use this controlled emission factor when estimating and
reporting their cooling tower emissions.
---------------------------------------------------------------------------
\2\ U.S. EPA (Environmental Protection Agency). 1995.
Compilation of Air Pollutant Emission Factors. Sections 5.1. AP-42.
Office of Air Quality Planning and Standards, Research Triangle
Park, NC.
---------------------------------------------------------------------------
Additionally, based on this MACT floor analysis, we determined that
the existing source MACT floor repair requirements include identifying
the source of the leak and repairing within 45 days of originally
finding the leak. Delay of repair is allowed under certain conditions
if the total strippable VOC is less than 62 ppmv, but is not allowed if
the total strippable VOC concentration is equal to or greater than 62
ppmv. When total strippable VOC is less than 62 ppmv, delay of repair
is allowed for up to 120 days if the necessary equipment, parts, or
personnel are not available, and delay of repair is allowed until the
next shutdown if a shutdown is required to effect the repair. For delay
of repair, the refinery must document the basis for the delay,
including the reason for delaying repair, provide a schedule for
completing the repair, and determine the emissions of HAP during the
time duration of the delay.
While these delay of repair provisions are based on our MACT floor
assessment, we note that some of the permits for facilities in the top
12 percent provide time to implement the monitoring requirements before
the ban on delay of repairs for leaks exceeding 62 ppmv becomes
effective. We recognize that when facilities first start to monitor
their cooling towers, the likelihood of finding large leaks is much
greater than after a monthly monitoring program has been implemented.
As
[[Page 66699]]
such, when first implementing the monthly monitoring, they may identify
heat exchange systems that have leaks exceeding 62 ppmv, but may not
have the spare parts or adequate time to plan for the repair of the
heat exchange system that would typically be available after the
monthly monitoring program has been in place for some time. As such, we
propose to phase-in the cooling tower requirements for existing
sources. The monitoring and leak repair provisions for existing sources
would become effective no later than 18 months after promulgation of
the final rule; however, the delay of repair is allowed regardless of
the leak size for the first 18 months of the monitoring program. No
later than 3 years from the promulgation date of these amendments, no
delay of repair is allowed for leaks exceeding 62 ppmv total strippable
VOC.
The new source MACT for cooling towers must be no less stringent
than the best-performing refinery cooling towers. In our ranking of the
information collected on monitoring requirements, the best-performing
cooling tower has a leak definition of 3.1 ppmv of strippable total
organics as methane in the stripping air using monthly Modified El Paso
method sampling and analysis. As such, the MACT floor for cooling
towers at new sources is monthly cooling water sampling for total
strippable VOC, where a leak is defined as 3.1 ppmv of total strippable
VOC in the stripping air using the Modified El Paso method. The repair
requirements for the top-performing cooling towers include identifying
the source of the leak and repairing within 45 days of originally
finding the leak. Delay of repair for the top-performing cooling towers
is allowed if strippable total VOC concentration is less than 62 ppmv,
but not allowed if strippable total VOC concentration is equal to or
greater than 62 ppmv. That is, the delay of repair provisions for the
new source MACT floor cooling towers are the same as those for an
existing source MACT floor cooling towers.
We revised our cooling tower emissions estimates since the 2007
proposal based on reanalysis of the emissions inventory information
obtained from TCEQ for the 2004 reporting year, as well as other
information collected regarding cooling tower monitoring provisions and
flow data from the Industrial Cooling Tower National Emission Standards
for Hazardous Air Pollutants (NESHAP). Model cooling tower emissions
for each refinery facility in the nation were estimated based on crude
throughput data which were used to estimate total cooling water flow
rates and generic refinery stream VOC and HAP compositions. These data
were used with controlled and uncontrolled AP-42 emission factors for
VOC emissions from cooling towers and the fraction of cooling towers
with specific monitoring requirements to estimate cooling tower
baseline HAP emissions. The nationwide baseline HAP emissions were
estimated at 770 tpy as compared to a baseline estimate of greater than
3,000 tpy in the 2007 proposal. These emissions compare reasonably well
with the organic HAP emissions estimate based on the TCEQ data, as
revised, to correct a reporting error identified by a public commenter.
From the updated TCEQ 2004 database, we estimated the organic HAP
emissions from cooling towers to be 95 tpy for Texas refineries alone.
Extrapolation of the Texas data based on direct crude distillation
capacity provides a nationwide emissions estimate for cooling towers of
352 tpy of organic HAP. However, refineries in Texas had the most
stringent cooling tower monitoring provisions of any of the State
requirements, and the Texas refineries used the controlled AP-42
emission factor for their cooling tower emission estimates. If the non-
Texas refineries operate nearer the uncontrolled AP-42 emission factor,
nationwide cooling tower emissions are projected to be 2,300 tpy of
organic HAP. While there is significant uncertainty in the actual
cooling tower emission estimate, the projected baseline emissions fall
easily within the range expected based on reanalysis of the Texas
dataset.
Following reanalysis of the MACT floor for cooling towers, we also
conducted a revised cost analysis for the MACT floor level of control.
We included costs for a strippable total VOC monitoring system,
increased the time needed for sampling and analysis for each cooling
tower, and added costs for sampling and analysis for specific heat
exchangers for triggered monitoring following identification of a
cooling tower leak. We also increased the cost associated with
repairing a leaking heat exchanger. The cost-effectiveness of the MACT
floor control for cooling towers at both new and existing sources was
approximately $4,700 per ton of HAP reduced when considering product
recovery credits and approximately $8,200 per ton when product recovery
credits were not included. See Table 3 of this preamble.
We also evaluated the costs of applying the new source leak
definition to existing sources and implementing this option with
continuous strippable total VOC monitoring systems as a beyond-the-MACT
floor control options. The first alternative reduces an additional 40
tpy of HAP emissions at an incremental cost-effectiveness of almost
$6,000 per ton on HAP emission reduction and the second option with
continuous monitoring reduces HAP emissions by an additional 10 tpy and
has an incremental cost-effectiveness of almost $600,000 per ton of HAP
reduced.
Based on this analysis, we conclude that the beyond-the-MACT floor
control options are not cost-effective and we are proposing standards
for cooling towers commensurate with the MACT floor determinations
under CAA sections 112(d)(2) and (3). Further, we are proposing that
the MACT floor level of control also provides an ample margin of safety
and satisfies the risk review requirements under CAA section 112(f)(2).
For more information on the costing methodology, see Table 3 of this
preamble and the ``Cooling Towers: Control Alternatives and Impact
Estimates'' memorandum in the docket (Docket ID No. EPA-HQ-OAR-2003-
0146).
Table 3--Nationwide Impacts for Cooling Tower Options
--------------------------------------------------------------------------------------------------------------------------------------------------------
Total Cost- effectiveness
Total annualized Product ($/ton HAP)
capital cost recovery Total HAP HAP -----------------------
Control option investment without credit annualized emissions emission
($ recovery ($ costs ($ (tpy) reductions
million) ($ million) million) (tpy) Overall Incremental
million)
--------------------------------------------------------------------------------------------------------------------------------------------------------
MACT Floor................................................ 16 5.2 -2.2 3.0 140 630 4,700 4,700
Beyond-the-floor Alternative 1............................ 16 5.5 -2.3 3.2 100 670 4,700 5,700
Beyond-the-floor Alternative 2............................ 72 11 -2.2 8.8 90 680 13,000 580,000
--------------------------------------------------------------------------------------------------------------------------------------------------------
[[Page 66700]]
Table 4 of this preamble provides information relevant to our
proposed ample margin of safety determination under CAA section
112(f)(2). Specifically, the table presents the pre-MACT risk, the risk
associated with the proposed MACT floor which is the baseline for our
residual risk analysis, and the risk reduction for the first beyond the
MACT floor alternative for cooling towers. Reductions in risk for the
second alternative are not shown because this alternative is clearly
not cost-effective.
Table 4--Inhalation Risk Impacts for Cooling Towers
----------------------------------------------------------------------------------------------------------------
Beyond the MACT
Parameter Baseline pre-MACT MACT floor (risk floor
baseline) alternative 1
----------------------------------------------------------------------------------------------------------------
Risk to Most Exposed Individual:
Cancer (in 1 million).............................. 30 30 30
Noncancer (HI)..................................... 0.3 0.3 0.3
Size of Population at Cancer Risk:
> 100-in-1 million................................. 0 0 0
> 10-in-1 million.................................. 4,000 3,900 3,800
> 1-in-1 million................................... 460,000 450,000 440,000
Number of Plants at Cancer Risk Level:
> 100-in-1 million................................. 0 0 0
> 10-in-1 million.................................. 23 22 22
> 1-in-1 million................................... 88 88 87
Population with HI > 1 \a\............................. 0 0 0
No of Plants with HI > 1............................... 0 0 0
Annual Cancer Incidence \b\............................ 0.032-0.049 0.031-0.047 0.030-0.047
Cancer Incidence Reduction (Percent)................... NA 3 4
HAP Emission Reduction (Percent)....................... NA 4 6
----------------------------------------------------------------------------------------------------------------
\a\ If the Hazard Index (HI) is calculated to be less than or equal to 1, then no adverse non-cancer chronic
health effects are expected as a result of the exposure. However, an HI exceeding 1 does not translate to a
probability that adverse effects occur. Rather, it suggests the possibility that adverse health effects may
occur. Acute non-cancer effects not estimated in this analysis.
\b\ The range of cancer incidence reflects the cancer potency range of benzene, either end of which is
considered equally plausible.
V. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory Planning and Review
Under Executive Order 12866 (58 FR 51735, October 4, 1993), this
action is a ``significant regulatory action'' because it may raise
novel legal or policy issues. Accordingly, EPA submitted this action to
OMB for review under Executive Order 12866, and any changes made in
response to OMB recommendations have been documented in the docket for
this action.
B. Paperwork Reduction Act
The information collection requirements in this proposed rule have
been submitted for approval to the OMB under the Paperwork Reduction
Act, 44 U.S.C. 3501, et seq. The Information Collection Request (ICR)
document prepared by EPA has been assigned ICR number 2334.01.
The information requirements in the proposed amendments include
monitoring, recordkeeping, and reporting provisions for storage vessels
and cooling towers. Owners or operators of storage vessels must comply
with the inspection, recordkeeping, and reporting requirements in 40
CFR part 63, subpart WW. Owners or operators of cooling towers must
conduct monthly monitoring of each heat exchanger to identify and
repair leaks. Records of monitoring and repair data also must be kept.
All respondents must submit one-time notifications and semiannual
compliance reports.
The information collection requirements in the proposed amendments
are needed by EPA and delegated authorities to determine that
compliance has been achieved. The recordkeeping and reporting
requirements in this proposed rule are based on the information
collection requirements in the part 63 General Provisions (40 CFR part
63, subpart A). The recordkeeping and reporting requirements in the
General Provisions are mandatory pursuant to section 114 of the CAA (42
U.S.C. 7414). All information submitted to EPA pursuant to the
information collection requirements for which a claim of
confidentiality is made is safeguarded according to CAA section 114(c)
and the Agency's implementing regulations at 40 CFR part 2, subpart B.
The annual burden for this information collection averaged over the
first 3 years of this ICR is estimated to total 13,714 labor hours per
year at a cost of $1,056,081 for one new refinery and 153 existing
refineries. The average annual reporting burden is 353.9 labor hours
for 205.9 total annual responses; the average annual burden per
response is 1.72 hours. Responses include notifications of compliance
status for cooling towers and storage vessels at new and existing
refineries, notification of initial startup for storage vessels at one
new refinery, and semiannual compliance reports containing information
on cooling towers and storage vessels at new and existing refineries.
Capital/startup costs are estimated at $16,306,000. The operation and
maintenance costs associated with the proposed rule amendments are
estimated at $61,711. Burden is defined at 5 CFR 1320.3(b).
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 are listed in 40 CFR part 9.
To comment on the EPA's need for this information, the accuracy of
the provided burden estimates, and any suggested methods for minimizing
respondent burden, including the use of automated collection
techniques, EPA has established a public docket for this action, which
includes this ICR, under Docket ID No. EPA-HQ-OAR-2003-0146. Submit any
comments related to the ICR for the proposed rule to EPA and OMB. See
the ADDRESSES section at the beginning of this preamble for where to
submit comments to EPA. Send comments to OMB at the Office of
Information and Regulatory Affairs, Office of Management and Budget,
725 17th Street, NW., Washington, DC
[[Page 66701]]
20503, Attention: Desk Office for EPA. Because OMB is required to make
a decision concerning the ICR between 30 and 60 days after November 10,
2008, a comment to OMB is best assured of having its full effect if OMB
receives it by December 10, 2008. The final rule will respond to any
OMB or public comments on the information collection requirements
contained in this proposal.
C. Regulatory Flexibility Act
The Regulatory Flexibility Act generally requires an agency to
prepare a regulatory flexibility analysis of any rule subject to notice
and comment rulemaking requirements under the Administrative Procedure
Act or any other statute unless the agency certifies that the rule will
not have a significant economic impact on a substantial number of small
entities. Small entities include small businesses, small organizations,
and small governmental jurisdictions.
For the purposes of assessing the impacts of this proposed rule on
small entities, small entity is defined as: (1) A small business that
meets the Small Business Administration size standards for small
businesses at 13 CFR 121.201 (a firm having no more than 1,500
employees; (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 this proposed rule on
small entities, I certify that this action will not have a significant
economic impact on a substantial number of small entities. Based on our
economic impact analysis, the proposed amendments will result in a
nationwide net annualized cost savings of about $3.8 million due to a
return of about $10.5 million per year from reductions in product
losses. Only one oil refining entity would incur net annualized costs
as a result of the proposed amendments; all other refinery entities
would have net savings. This refinery entity is a small parent entity.
Net annualized costs for this affected small entity are well below 0.01
percent of their revenue; therefore, no ``significant'' adverse
economic impacts are expected for any small entity. Thus, the costs
associated with the proposed amendments will not result in any
``significant'' adverse economic impact for any small entity. For more
information, please refer to the economic impact analysis that is in
the docket for this rulemaking.
Although the proposed rule will not have a significant economic
impact on a substantial number of small entities, we nonetheless tried
to reduce the impact of the proposed rule on small entities. We held
meetings with industry trade associations and company representatives
to discuss the proposed rule and have included provisions for small
facilities that address their concerns. 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
This action contains no Federal mandates under the provisions of
Title II of the Unfunded Mandates Reform Act of 1995 (UMRA), 2 U.S.C.
1531-1538 for State, local, or tribal governments or the private
sector.
The proposed rule does not contain a Federal mandate that may
result in expenditures of $100 million or more for State, local, and
tribal governments, in the aggregate, or to the private sector in any
one year. As discussed earlier in this preamble, these amendments
result in nationwide net savings to the private sector. Therefore, the
proposed rule is not subject to the requirements of sections 202 or 205
of the UMRA.
This proposed rule is also not subject to the requirements of
section 203 of UMRA because it contains no regulatory requirements that
might significantly or uniquely affect small governments. 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, entitled Federalism (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'' is 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 add control and monitoring requirements. They do not modify
existing responsibilities or create new responsibilities among EPA
Regional offices, States, or local enforcement agencies. 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
governments, EPA specifically solicits comment on this proposed rule
from State and local officials.
F. Executive Order 13175: Consultation and Coordination With Indian
Tribal Governments
This action does not have tribal implications, as specified in
Executive Order 13175 (65 FR 67249, November 9, 2000). The proposed
amendments will not have substantial direct effects on tribal
governments, on the relationship between the Federal Government and
Indian tribes, or on the distribution of power and responsibilities
between the Federal government and Indian tribes, as specified in
Executive Order 13175. The proposed amendments impose no requirements
on tribal governments. Thus, Executive Order 13175 does not apply to
this action.
EPA specifically solicits additional comment on this proposed
action From tribal officials.
G. Executive Order 13045: Protection of Children From Environmental
Health Risks and Safety Risks
This action is not subject to Executive Order 13045 (62 FR 19885,
April 23, 1997) because it is not economically significant as defined
in Executive Order 12866, and because the Agency does not believe the
environmental health or safety risks addressed by this action present a
disproportionate risk to children. This action's health and risk
assessments are contained in the revised Residual Risk Assessment for
MACT 1 Petroleum Refining Sources, which is available in the docket.
H. Executive Order 13211: Actions That Significantly Affect Energy
Supply, Distribution, or Use
The proposed amendments are not a ``significant energy action'' as
defined in Executive Order 13211 (66 FR 28355, May 22, 2001) because
they are not likely to have a significant adverse effect on the supply,
distribution, or use of energy. Further, we have concluded that the
proposed amendments are not likely to have any adverse energy effects
[[Page 66702]]
because they result in overall savings due to product recovery.
I. National Technology Transfer and Advancement Act
Section 12(d) of the National Technology Transfer and Advancement
Act (NTTAA) of 1995 (Pub. L. No. 104-113, 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. VCS are technical standards (e.g., materials
specifications, test methods, sampling procedures, and business
practices) that are developed or adopted by VCS bodies. NTTAA directs
EPA to provide Congress, through OMB, explanations when the Agency does
not use available and applicable VCS.
This proposed rule involves technical standards. EPA proposes to
use ``Air Stripping Method (Modified El Paso Method) for Determination
of Volatile Organic Compound Emissions from Water Sources,'' Revision
Number One, dated January 2003, and will incorporate the method by
reference (see 40 CFR 63.14). This method is available at https://
www.tceq.state.tx.us/assets/public/implementation/air/sip/sipdocs/2002-
12-HGB/02046sipapp_ado.pdf , or from the Texas Commission on
Environmental Quality (TCEQ) Library, Post Office Box 13087, Austin,
Texas, 78711-3087, telephone number (512) 239-0028. This method was
chosen based on public comments regarding the sampling and analysis of
air emissions from cooling towers, and is required in these proposed
amendments instead of the originally proposed requirements in 40 CFR
61.355(c) for water sample collection, and EPA Method 8260B for
analysis of water samples taken from cooling tower return lines.
This TCEQ method utilizes a dynamic or flow-through system for air
stripping a sample of the water and analyzing the resultant off-gases
for VOC using a common flame ionization detector (FID) analyzer. While
direct water analyses, such as purge and trap analyses of water samples
utilizing gas chromatography and/or mass spectrometry techniques, have
been shown to be effective for cooling tower measurements of heavier
molecular weight organic compounds with relatively high boiling points,
it has been determined that this approach may be ineffective for
capture and measurement of VOC with lower boiling points, such as
ethylene, propylene, 1,3-butadiene, and butenes. The VOC with a low
molecular weight and boiling point are generally lost in the sample
collection step of purge/trap type analyses. Consequently, this TCEQ
air stripping method is used for cooling tower and other applicable
water matrix emission measurements when VOC with boiling points below
140o F need to be evaluated.
Under 40 CFR 63.7(f) and 40 CFR 63.8(f) of subpart A of the General
Provisions, 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 in
the proposed amendments.
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 the regulations.
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 becaus