Notice of Availability of Proposed Modification of National Pollutant Discharge Elimination System (NPDES) General Permit for Offshore Oil and Gas Exploration, Development and Production Operations Off Southern California, 15267-15269 [E9-6840]
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Federal Register / Vol. 74, No. 63 / Friday, April 3, 2009 / Notices
stop, and is close to Ronald Reagan
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The National Bed Bug Summit
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Persons interested in attending do not
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Dated: March 30, 2009.
Daniel J. Rosenblatt,
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of Pesticide Programs.
[FR Doc. E9–7661 Filed 4–1–09; 4:15 pm]
BILLING CODE 6560–50–S
ENVIRONMENTAL PROTECTION
AGENCY
[FRL–8785–2]
Notice of Availability of Proposed
Modification of National Pollutant
Discharge Elimination System
(NPDES) General Permit for Offshore
Oil and Gas Exploration, Development
and Production Operations Off
Southern California
sroberts on PROD1PC70 with NOTICES
AGENCY: Environmental Protection
Agency (EPA).
ACTION: Notice of Availability of
Proposed NPDES General Permit
Modification.
SUMMARY: EPA Region 9 is proposing
certain modifications of its general
NPDES permit (permit No. CAG280000)
for discharges from offshore oil and gas
exploration, development and
production facilities located in Federal
waters off the coast of Southern
California. The permit, which was
issued on September 22, 2004 (69 FR
56761), required a one-year monitoring
study for discharges of produced water,
cooling water and fire control system
test water to evaluate whether these
discharges would have reasonable
potential to cause or contribute to
exceedances of marine water quality
criteria. For produced water, the permit
required monitoring for 26 pollutants
which may be present in the discharges.
For cooling water and fire control
system test water, monitoring was
required for total residual chlorine
which may be used for anti-fouling.
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The monitoring study has now been
completed and Region 9 is proposing to
modify the permit to include additional
effluent limitations and monitoring
requirements for those discharges for
which the monitoring study showed a
reasonable potential to cause or
contribute to exceedances of marine
water quality criteria.
For produced water discharges,
Region 9 is also proposing to modify the
water quality criterion for undissociated
sulfide in the permit based on the
results of a new study submitted by the
permittees concerning the toxicity of
this material to marine organisms. The
proposed effluent limitations for
undissociated sulfide in the modified
general permit would be based on the
modified water quality criterion.
DATES: Comments on the proposed
permit modifications must be received
or postmarked no later than May 4,
2009.
Public comments on the
proposed permit modifications may be
submitted by U.S. Mail to:
Environmental Protection Agency,
Region 9, Attn: Lisa Honor, NPDES
Permits Office (WTR–5), 75 Hawthorne
Street, San Francisco, California 94105–
3901, or by e-mail to:
honor.lisa@epa.gov.
ADDRESSES:
FOR FURTHER INFORMATION CONTACT:
Eugene Bromley, EPA Region 9, NPDES
Permits Office (WTR–5), 75 Hawthorne
Street, San Francisco, California 94105–
3901, or telephone (415) 972–3510. A
copy of the proposed permit
modifications and fact sheet will be
provided upon request and is also
available on Region 9’s Web site at
https://www.epa.gov/region09/water/.
Additional information concerning the
general permit overall is available in the
fact sheet accompanying the final
issuance of the general permit on
September 22, 2004. The 2004 general
permit and fact sheet are available on
Region 9’s Web site at https://
www.epa.gov/region09/water/.
Administrative Record: The proposed
permit modifications and other related
documents in the administrative record
are on file and may be inspected any
time between 8:30 a.m. and 4 p.m.,
Monday through Friday, excluding legal
holidays, at the following address: U.S.
EPA Region 9, NPDES Permits Office
(WTR–5), 75 Hawthorne Street, San
Francisco, CA 94105–3901.
SUPPLEMENTARY INFORMATION:
A. Reasonable Potential Monitoring
Study. Among other factors, the Ocean
Discharge Criteria regulations (40 CFR
part 125, subpart M) require a
consideration of marine water quality
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15267
criteria for discharges to the ocean
permitted under the NPDES permit
program. In considering these criteria,
particularly in determining permit
conditions that would be needed to
support a determination the resulting
discharges will not cause unreasonable
degradation of the marine environment,
the permit included a study requirement
using the statistical procedures EPA
uses in determining the need for water
quality-based effluent limits for point
source discharges to waters of the
United States, including the territorial
seas. The study, captioned the
‘‘reasonable potential monitoring
study,’’ was required in order to
determine whether the ocean discharges
regulated under the permit would cause,
or have the reasonable potential to
cause, or contribute to non-attainment
of marine water quality criteria at the
boundary of the mixing zone, which is
the location identified in the Ocean
Discharge Criteria regulations at 40 CFR
125.123(d)(1).
General permit No. CAG28000
included the study requirement because
at the time of the issuance insufficient
data were available to evaluate the
reasonable potential for discharges of
produced water, cooling water and fire
control system test water to cause or
contribute to exceedances of the marine
water quality criteria for pollutants
Region 9 had identified as potentially
present in the discharges. The permit’s
study requirements were derived from
the statistical procedures explained in
EPA’s Technical Support Document for
Water Quality-Based Toxics Control
(TSD) (EPA/505/2–90–001). EPA
explained in the permit if a discharge
demonstrated the reasonable potential
to cause non-attainment of a marine
water quality criterion at the boundary
of a mixing zone, the permit could be
reopened and modified to include
additional effluent limitations and
monitoring requirements to ensure
compliance with the water quality
criteria. Today Region 9 is proposing to
reopen and modify the general permit to
include such additional limitations and
requirements, thus enabling its
determination the authorized discharges
will not cause unreasonable degradation
of the marine environment.
For produced water, the permit
required monitoring monthly during the
first year of the permit for 26 pollutants
of concern Region 9 had identified as
potentially present in the discharges.
For cooling water and fire control
system test water, monitoring was also
required monthly during the first year
for total residual chlorine which is used
at some platforms as an anti-fouling
agent. Monitoring results were due by
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March 1, 2006 and were submitted for
all platforms in a timely manner. The
permit also required the submittal of an
analysis by March 1, 2006, using
statistical procedures in the TSD, of the
reasonable potential of the discharges to
cause or contribute to non-attainment of
the previously specified marine water
quality criteria. These analyses also
were submitted for all platforms in a
timely manner.
The general permit authorizes
discharges from 22 offshore platforms.
However, only 15 of the platforms
discharge produced water. Thirteen of
the platforms showed reasonable
potential to exceed applicable marine
water quality criteria for one or more of
the 26 pollutants monitored in
produced water; the applicable water
quality criteria used were the more
stringent of CWA section 304(a) criteria
or the California Ocean Plan objectives
as required by the 2004 final general
permit. One of the platforms (Platform
Irene) rarely discharges produced water
and the operator had not collected the
minimum number of samples (which is
ten samples) recommended by the TSD
to do a reasonable potential analysis.
Moreover, the discharges measured for
this platform were from small scale pilot
tests of potential produced water
treatment systems which may not be
representative of future discharges
resulting from the treatment system
ultimately installed. Thus, Region 9 is
deferring action on this platform until
the general permit is reissued in 2009.
Until then, for the majority of the
pollutants addressed by the reasonable
potential study, Platform Irene would
continue to be subject to effluent limits
in its previous individual permit, and
the platform would continue to conduct
monitoring for all 26 of the pollutants as
required by Part II.B.1.b.2 of the general
permit.
Seven of the 22 platforms use chlorine
in cooling water or fire control system
test water. Six of the seven platforms
showed a reasonable potential to cause
non-attainment of the marine water
quality criteria for chlorine.
Proposed effluent limitations and
monitoring requirements to control the
pollutants in the above discharges and
ensure compliance with marine water
quality criteria are discussed in section
C below.
B. Modified Water Quality Criterion
for Undissociated Sulfide. The general
permit provides a permittee may request
a modified criterion for a pollutant of
concern in produced water discharges
based on additional studies of the
toxicity of the pollutant. On April 20,
2006, several permittees operating
under the general permit requested a
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Jkt 217001
modification of the criterion in the
permit for undissociated sulfide (2 μg/
l). The permittees requested a modified
criterion of 12 μg/l based on a new
study of the toxicity of this material to
marine organisms. Region 9 reviewed
the new study and believes a revised
criterion of 5.79 μg/l is justified by the
data (rather than 12 μg/l). Region 9 is
proposing to modify the water quality
criterion in the permit for undissociated
sulfide to 5.79 μg/l. The proposed
effluent limitations for undissociated
sulfide discussed below are based on
the revised criterion of 5.79 μg/l for this
material.
C. Proposed Effluent Limitations and
Monitoring Requirements. Using the
procedures in the TSD, Region 9
calculated effluent limitations for the
pollutants in discharges of produced
water, cooling water and fire control
system test water for which reasonable
potential was determined to exist based
on the monitoring study. For produced
water, these effluent limitations are
found in a new Appendix C which is
proposed to be added to the general
permit. For cooling water and fire
control system test water, the effluent
limitations are found in a new
Appendix D which would be added to
the permit.
Monitoring once per quarter would
also be required for the pollutants with
reasonable potential in each of the
discharges. The monitoring results
would be reported in the quarterly
discharge monitoring reports. For
pollutants with no reasonable potential
in produced water, monitoring once
during the remainder of the permit term
would be required as set forth in Part
II.B.1.e.3 of the general permit.
D. Requirements Related to the
Coastal Zone Management Act. The
Coastal Zone Management Act (CZMA)
requires Federal activities and projects
affecting the coastal zone of a state,
including Federally permitted activities,
must be consistent with an approved
state Coastal Management Plan (CMP)
(CZMA Sections 307(c)(1) through (3)).
California has a CMP which was
approved in 1978; the CZMA authority
is the California Coastal Commission
(CCC).
In accordance with revised
regulations implementing the CZMA (71
FR 788, January 5, 2006), the issuance
of a general NPDES permit by EPA is
considered a ‘‘Federal agency activity’’
covered by CZMA Section 307(c)(1), and
CZMA regulations at 15 CFR Subpart C.
The regulations at 15 CFR 930.31(e)
further clarify the modification of a
general permit which could affect any
coastal use or resource is also subject to
a consistency review under Subpart C.
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Region 9 believes the proposed permit
modification could affect coastal uses or
resources of the State of California.
Region 9 also believes the proposed
permit modification would be
consistent with the CMP. Region 9
recently submitted a consistency
certification to the CCC for the proposed
permit modification.
In accordance with 15 CFR 930.31(d),
if the CCC concurs with the permit
modification, the modification could
become effective for all platforms
without additional review of individual
platforms by the CCC. However, if the
CCC objects to the permit modification,
the modification would not become
effective for a given platform until an
individual consistency certification had
been submitted by the permittee and
concurred upon by the CCC, or the
Secretary of Commerce had overridden
a CCC objection. The effective date for
the proposed permit modification makes
allowance for these regulatory
requirements.
E. Permit Modification Appeal
Procedures. Within 120 days following
notice of EPA’s final decision for the
general permit modification under 40
CFR 124.15, any interested person may
appeal the permit decision in the
Federal Court of Appeals in accordance
with Section 509(b)(1) of the Clean
Water Act (CWA). Persons affected by a
general permit may not challenge the
conditions of a general permit as a right
in further Agency proceedings. They
may instead either challenge the general
permit in court, or apply for an
individual permit as specified at 40 CFR
122.21 (and authorized at 40 CFR
122.28), and then petition the
Environmental Appeals Board to review
any condition of the individual permit
(40 CFR 124.19 as modified on May 15,
2000, 65 FR 30886).
F. Compliance with the Regulatory
Flexibility Act for General Permits. The
Regulatory Flexibility Act (RFA)
generally requires an agency to prepare
a regulatory flexibility analysis of any
rule subject to notice and comment
rulemaking requirements under the
Administrative Procedure Act or any
other statute unless the agency certifies
that the rule 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.
The legal question of whether a
general permit (including a general
permit modification), as opposed to an
individual permit qualifies as a ‘‘rule’’
or as an ‘‘adjudication’’ under the
Administrative Procedure Act (APA)
has been the subject of periodic
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litigation. In a recent case, the court
held that the CWA Section 404
Nationwide general permit before the
court did qualify as a ‘‘rule’’ and
therefore that the issuance of the general
permit needed to comply with the
applicable legal requirements for the
issuance of a ‘‘rule.’’ National Ass’n of
Home Builders v. US Army Corps of
Engineers, 417 F.3d 1272, 1284–85 (DC
Cir.2005) (Army Corps general permits
under Section 404 of the Clean Water
Act are rules under the APA and the
Regulatory Flexibility Act; ‘‘Each NWP
[nationwide permit] easily fits within
the APA’s definition of a ‘rule.’ * * *
As such, each NWP constitutes a rule
* * *’’).
As EPA stated in 1998, ‘‘the Agency
recognizes that the question of the
applicability of the APA, and thus the
RFA, to the issuance of a general permit
is a difficult one, given the fact that a
large number of dischargers may choose
to use the general permit.’’ 63 FR 36489,
36497 (July 6, 1998). At that time, EPA
‘‘reviewed its previous NPDES general
permitting actions and related
statements in the Federal Register or
elsewhere,’’ and stated that ‘‘[t]his
review suggests that the Agency has
generally treated NPDES general permits
effectively as rules, though at times it
has given contrary indications as to
whether these actions are rules or
permits.’’ Id. at 36496. Based on EPA’s
further legal analysis of the issue, the
Agency ‘‘concluded, as set forth in the
proposal, that NPDES general permits
are permits [i.e., adjudications] under
the APA and thus not subject to APA
rulemaking requirements or the RFA.’’
Id. Accordingly, the Agency stated that
‘‘the APA’s rulemaking requirements are
inapplicable to issuance of such
permits,’’ and thus ‘‘NPDES permitting
is not subject to the requirement to
publish a general notice of proposed
rulemaking under the APA or any other
law * * * [and] it is not subject to the
RFA.’’ Id. at 36497.
However, the Agency went on to
explain that, even though EPA had
concluded that it was not legally
required to do so, the Agency would
voluntarily perform the RFA’s smallentity impact analysis. Id. EPA
explained the strong public interest in
the Agency following the RFA’s
requirements on a voluntary basis:
‘‘[The notice and comment] process also
provides an opportunity for EPA to
consider the potential impact of general
permit terms on small entities and how
to craft the permit to avoid any undue
burden on small entities.’’ Id.
Accordingly, with respect to the NPDES
permit that EPA was addressing in that
Federal Register notice, EPA stated that
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16:07 Apr 02, 2009
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‘‘the Agency has considered and
addressed the potential impact of the
general permit on small entities in a
manner that would meet the
requirements of the RFA if it applied.’’
Id.
Subsequent to EPA’s conclusion in
1998 that general permits are
adjudications, rather than rules, as
noted above, the DC Circuit recently
held that Nationwide general permits
under section 404 are ‘‘rules’’ rather
than ‘‘adjudications.’’ Thus, this legal
question remains ‘‘a difficult one’’
(supra). However, EPA continues to
believe that there is a strong public
policy interest in EPA applying the
RFA’s framework and requirements to
the Agency’s evaluation and
consideration of the nature and extent of
any economic impacts that a CWA
general permit could have on small
entities (e.g., small businesses). In this
regard, EPA believes that the Agency’s
evaluation of the potential economic
impact that a general permit would have
on small entities, consistent with the
RFA framework discussed below, is
relevant to, and an essential component
of, the Agency’s assessment of whether
a CWA general permit would place
requirements on dischargers that are
appropriate and reasonable.
Furthermore, EPA believes that the
RFA’s framework and requirements
provide the Agency with the best
approach for the Agency’s evaluation of
the economic impact of general permits
on small entities. While using the RFA
framework to inform its assessment of
whether permit requirements are
appropriate and reasonable, EPA will
also continue to ensure that all permits
satisfy the requirements of the Clean
Water Act.
Accordingly, EPA has committed that
the Agency will operate in accordance
with the RFA’s framework and
requirements during the Agency’s
issuance of CWA general permits (in
other words, the Agency commits that it
will apply the RFA in its issuance of
general permits as if those permits do
qualify as ‘‘rules’’ that are subject to the
RFA). In satisfaction of this
commitment, during the course of this
general offshore oil and gas exploration,
development and production operations
permit proceeding, the Agency
conducted the analysis and made the
appropriate determinations that are
called for by the RFA. In addition, and
in satisfaction of the Agency’s
commitment, EPA will apply the RFA’s
framework and requirements in any
future issuance of other NPDES general
permits. EPA anticipates that for most
general permits the Agency will be able
to conclude that there is not a
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15269
significant economic impact on a
substantial number of small entities. In
such cases, the requirements of the RFA
framework are fulfilled by including a
statement to this effect in the permit fact
sheet, along with a statement providing
the factual basis for the conclusion. A
quantitative analysis of impacts would
only be required for permits that may
affect a substantial number of small
entities, consistent with EPA guidance
regarding RFA certification.1
G. Analysis of Economic Impacts of
the General Permit for Offshore Oil and
Gas Exploration, Development and
Production Operations off Southern
California. EPA determined, in
consideration of the discussion in
Section F above, the issuance of the
general permit for offshore oil and gas
exploration, development and
production operations off Southern
California would not have a significant
economic impact on a substantial
number of small entities. There are only
22 offshore platforms which could be
affected by the proposed general permit
modification. EPA concludes since this
general permit affects less than 100
small entities, EPA believes it does not
have a significant economic impact on
a substantial number of small entities.
Accordingly, EPA concludes a
quantitative analysis of impacts is not
required for this permit.
Authority: Clean Water Act, 33 U.S.C.
1251 et seq.
Dated: March 12, 2009.
Alexis Strauss,
Director, Water Division, Region 9.
[FR Doc. E9–6840 Filed 4–2–09; 8:45 am]
BILLING CODE 6560–50–P
FEDERAL COMMUNICATIONS
COMMISSION
Notice of Public Information
Collection(s) Being Reviewed by the
Federal Communications Commission
for Extension Under Delegated
Authority, Comments Requested
March 30, 2009.
SUMMARY: The Federal Communications
Commission, as part of its continuing
effort to reduce paperwork burden
1 EPA’s current guidance, entitled Final Guidance
for EPA Rulewriters: Regulatory Flexibility Act as
Amended by the Small Business Regulatory
Enforcement and Fairness Act, was issued in
November 2006 and is available on EPA’s Web site:
https://www.epa.gov/sbrefa/documents/
rfafinalguidance06.pdf. After considering the
Guidance and the purpose of CWA general permits,
EPA concludes that general permits affecting less
than 100 small entities do not have a significant
economic impact on a substantial number of small
entities.
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Agencies
[Federal Register Volume 74, Number 63 (Friday, April 3, 2009)]
[Notices]
[Pages 15267-15269]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E9-6840]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
[FRL-8785-2]
Notice of Availability of Proposed Modification of National
Pollutant Discharge Elimination System (NPDES) General Permit for
Offshore Oil and Gas Exploration, Development and Production Operations
Off Southern California
AGENCY: Environmental Protection Agency (EPA).
ACTION: Notice of Availability of Proposed NPDES General Permit
Modification.
-----------------------------------------------------------------------
SUMMARY: EPA Region 9 is proposing certain modifications of its general
NPDES permit (permit No. CAG280000) for discharges from offshore oil
and gas exploration, development and production facilities located in
Federal waters off the coast of Southern California. The permit, which
was issued on September 22, 2004 (69 FR 56761), required a one-year
monitoring study for discharges of produced water, cooling water and
fire control system test water to evaluate whether these discharges
would have reasonable potential to cause or contribute to exceedances
of marine water quality criteria. For produced water, the permit
required monitoring for 26 pollutants which may be present in the
discharges. For cooling water and fire control system test water,
monitoring was required for total residual chlorine which may be used
for anti-fouling.
The monitoring study has now been completed and Region 9 is
proposing to modify the permit to include additional effluent
limitations and monitoring requirements for those discharges for which
the monitoring study showed a reasonable potential to cause or
contribute to exceedances of marine water quality criteria.
For produced water discharges, Region 9 is also proposing to modify
the water quality criterion for undissociated sulfide in the permit
based on the results of a new study submitted by the permittees
concerning the toxicity of this material to marine organisms. The
proposed effluent limitations for undissociated sulfide in the modified
general permit would be based on the modified water quality criterion.
DATES: Comments on the proposed permit modifications must be received
or postmarked no later than May 4, 2009.
ADDRESSES: Public comments on the proposed permit modifications may be
submitted by U.S. Mail to: Environmental Protection Agency, Region 9,
Attn: Lisa Honor, NPDES Permits Office (WTR-5), 75 Hawthorne Street,
San Francisco, California 94105-3901, or by e-mail to:
honor.lisa@epa.gov.
FOR FURTHER INFORMATION CONTACT: Eugene Bromley, EPA Region 9, NPDES
Permits Office (WTR-5), 75 Hawthorne Street, San Francisco, California
94105-3901, or telephone (415) 972-3510. A copy of the proposed permit
modifications and fact sheet will be provided upon request and is also
available on Region 9's Web site at https://www.epa.gov/region09/water/.
Additional information concerning the general permit overall is
available in the fact sheet accompanying the final issuance of the
general permit on September 22, 2004. The 2004 general permit and fact
sheet are available on Region 9's Web site at https://www.epa.gov/region09/water/.
Administrative Record: The proposed permit modifications and other
related documents in the administrative record are on file and may be
inspected any time between 8:30 a.m. and 4 p.m., Monday through Friday,
excluding legal holidays, at the following address: U.S. EPA Region 9,
NPDES Permits Office (WTR-5), 75 Hawthorne Street, San Francisco, CA
94105-3901.
SUPPLEMENTARY INFORMATION:
A. Reasonable Potential Monitoring Study. Among other factors, the
Ocean Discharge Criteria regulations (40 CFR part 125, subpart M)
require a consideration of marine water quality criteria for discharges
to the ocean permitted under the NPDES permit program. In considering
these criteria, particularly in determining permit conditions that
would be needed to support a determination the resulting discharges
will not cause unreasonable degradation of the marine environment, the
permit included a study requirement using the statistical procedures
EPA uses in determining the need for water quality-based effluent
limits for point source discharges to waters of the United States,
including the territorial seas. The study, captioned the ``reasonable
potential monitoring study,'' was required in order to determine
whether the ocean discharges regulated under the permit would cause, or
have the reasonable potential to cause, or contribute to non-attainment
of marine water quality criteria at the boundary of the mixing zone,
which is the location identified in the Ocean Discharge Criteria
regulations at 40 CFR 125.123(d)(1).
General permit No. CAG28000 included the study requirement because
at the time of the issuance insufficient data were available to
evaluate the reasonable potential for discharges of produced water,
cooling water and fire control system test water to cause or contribute
to exceedances of the marine water quality criteria for pollutants
Region 9 had identified as potentially present in the discharges. The
permit's study requirements were derived from the statistical
procedures explained in EPA's Technical Support Document for Water
Quality-Based Toxics Control (TSD) (EPA/505/2-90-001). EPA explained in
the permit if a discharge demonstrated the reasonable potential to
cause non-attainment of a marine water quality criterion at the
boundary of a mixing zone, the permit could be reopened and modified to
include additional effluent limitations and monitoring requirements to
ensure compliance with the water quality criteria. Today Region 9 is
proposing to reopen and modify the general permit to include such
additional limitations and requirements, thus enabling its
determination the authorized discharges will not cause unreasonable
degradation of the marine environment.
For produced water, the permit required monitoring monthly during
the first year of the permit for 26 pollutants of concern Region 9 had
identified as potentially present in the discharges. For cooling water
and fire control system test water, monitoring was also required
monthly during the first year for total residual chlorine which is used
at some platforms as an anti-fouling agent. Monitoring results were due
by
[[Page 15268]]
March 1, 2006 and were submitted for all platforms in a timely manner.
The permit also required the submittal of an analysis by March 1, 2006,
using statistical procedures in the TSD, of the reasonable potential of
the discharges to cause or contribute to non-attainment of the
previously specified marine water quality criteria. These analyses also
were submitted for all platforms in a timely manner.
The general permit authorizes discharges from 22 offshore
platforms. However, only 15 of the platforms discharge produced water.
Thirteen of the platforms showed reasonable potential to exceed
applicable marine water quality criteria for one or more of the 26
pollutants monitored in produced water; the applicable water quality
criteria used were the more stringent of CWA section 304(a) criteria or
the California Ocean Plan objectives as required by the 2004 final
general permit. One of the platforms (Platform Irene) rarely discharges
produced water and the operator had not collected the minimum number of
samples (which is ten samples) recommended by the TSD to do a
reasonable potential analysis. Moreover, the discharges measured for
this platform were from small scale pilot tests of potential produced
water treatment systems which may not be representative of future
discharges resulting from the treatment system ultimately installed.
Thus, Region 9 is deferring action on this platform until the general
permit is reissued in 2009. Until then, for the majority of the
pollutants addressed by the reasonable potential study, Platform Irene
would continue to be subject to effluent limits in its previous
individual permit, and the platform would continue to conduct
monitoring for all 26 of the pollutants as required by Part II.B.1.b.2
of the general permit.
Seven of the 22 platforms use chlorine in cooling water or fire
control system test water. Six of the seven platforms showed a
reasonable potential to cause non-attainment of the marine water
quality criteria for chlorine.
Proposed effluent limitations and monitoring requirements to
control the pollutants in the above discharges and ensure compliance
with marine water quality criteria are discussed in section C below.
B. Modified Water Quality Criterion for Undissociated Sulfide. The
general permit provides a permittee may request a modified criterion
for a pollutant of concern in produced water discharges based on
additional studies of the toxicity of the pollutant. On April 20, 2006,
several permittees operating under the general permit requested a
modification of the criterion in the permit for undissociated sulfide
(2 [mu]g/l). The permittees requested a modified criterion of 12 [mu]g/
l based on a new study of the toxicity of this material to marine
organisms. Region 9 reviewed the new study and believes a revised
criterion of 5.79 [mu]g/l is justified by the data (rather than 12
[mu]g/l). Region 9 is proposing to modify the water quality criterion
in the permit for undissociated sulfide to 5.79 [mu]g/l. The proposed
effluent limitations for undissociated sulfide discussed below are
based on the revised criterion of 5.79 [mu]g/l for this material.
C. Proposed Effluent Limitations and Monitoring Requirements. Using
the procedures in the TSD, Region 9 calculated effluent limitations for
the pollutants in discharges of produced water, cooling water and fire
control system test water for which reasonable potential was determined
to exist based on the monitoring study. For produced water, these
effluent limitations are found in a new Appendix C which is proposed to
be added to the general permit. For cooling water and fire control
system test water, the effluent limitations are found in a new Appendix
D which would be added to the permit.
Monitoring once per quarter would also be required for the
pollutants with reasonable potential in each of the discharges. The
monitoring results would be reported in the quarterly discharge
monitoring reports. For pollutants with no reasonable potential in
produced water, monitoring once during the remainder of the permit term
would be required as set forth in Part II.B.1.e.3 of the general
permit.
D. Requirements Related to the Coastal Zone Management Act. The
Coastal Zone Management Act (CZMA) requires Federal activities and
projects affecting the coastal zone of a state, including Federally
permitted activities, must be consistent with an approved state Coastal
Management Plan (CMP) (CZMA Sections 307(c)(1) through (3)). California
has a CMP which was approved in 1978; the CZMA authority is the
California Coastal Commission (CCC).
In accordance with revised regulations implementing the CZMA (71 FR
788, January 5, 2006), the issuance of a general NPDES permit by EPA is
considered a ``Federal agency activity'' covered by CZMA Section
307(c)(1), and CZMA regulations at 15 CFR Subpart C. The regulations at
15 CFR 930.31(e) further clarify the modification of a general permit
which could affect any coastal use or resource is also subject to a
consistency review under Subpart C.
Region 9 believes the proposed permit modification could affect
coastal uses or resources of the State of California. Region 9 also
believes the proposed permit modification would be consistent with the
CMP. Region 9 recently submitted a consistency certification to the CCC
for the proposed permit modification.
In accordance with 15 CFR 930.31(d), if the CCC concurs with the
permit modification, the modification could become effective for all
platforms without additional review of individual platforms by the CCC.
However, if the CCC objects to the permit modification, the
modification would not become effective for a given platform until an
individual consistency certification had been submitted by the
permittee and concurred upon by the CCC, or the Secretary of Commerce
had overridden a CCC objection. The effective date for the proposed
permit modification makes allowance for these regulatory requirements.
E. Permit Modification Appeal Procedures. Within 120 days following
notice of EPA's final decision for the general permit modification
under 40 CFR 124.15, any interested person may appeal the permit
decision in the Federal Court of Appeals in accordance with Section
509(b)(1) of the Clean Water Act (CWA). Persons affected by a general
permit may not challenge the conditions of a general permit as a right
in further Agency proceedings. They may instead either challenge the
general permit in court, or apply for an individual permit as specified
at 40 CFR 122.21 (and authorized at 40 CFR 122.28), and then petition
the Environmental Appeals Board to review any condition of the
individual permit (40 CFR 124.19 as modified on May 15, 2000, 65 FR
30886).
F. Compliance with the Regulatory Flexibility Act for General
Permits. The Regulatory Flexibility Act (RFA) generally requires an
agency to prepare a regulatory flexibility analysis of any rule subject
to notice and comment rulemaking requirements under the Administrative
Procedure Act or any other statute unless the agency certifies that the
rule 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.
The legal question of whether a general permit (including a general
permit modification), as opposed to an individual permit qualifies as a
``rule'' or as an ``adjudication'' under the Administrative Procedure
Act (APA) has been the subject of periodic
[[Page 15269]]
litigation. In a recent case, the court held that the CWA Section 404
Nationwide general permit before the court did qualify as a ``rule''
and therefore that the issuance of the general permit needed to comply
with the applicable legal requirements for the issuance of a ``rule.''
National Ass'n of Home Builders v. US Army Corps of Engineers, 417 F.3d
1272, 1284-85 (DC Cir.2005) (Army Corps general permits under Section
404 of the Clean Water Act are rules under the APA and the Regulatory
Flexibility Act; ``Each NWP [nationwide permit] easily fits within the
APA's definition of a `rule.' * * * As such, each NWP constitutes a
rule * * *'').
As EPA stated in 1998, ``the Agency recognizes that the question of
the applicability of the APA, and thus the RFA, to the issuance of a
general permit is a difficult one, given the fact that a large number
of dischargers may choose to use the general permit.'' 63 FR 36489,
36497 (July 6, 1998). At that time, EPA ``reviewed its previous NPDES
general permitting actions and related statements in the Federal
Register or elsewhere,'' and stated that ``[t]his review suggests that
the Agency has generally treated NPDES general permits effectively as
rules, though at times it has given contrary indications as to whether
these actions are rules or permits.'' Id. at 36496. Based on EPA's
further legal analysis of the issue, the Agency ``concluded, as set
forth in the proposal, that NPDES general permits are permits [i.e.,
adjudications] under the APA and thus not subject to APA rulemaking
requirements or the RFA.'' Id. Accordingly, the Agency stated that
``the APA's rulemaking requirements are inapplicable to issuance of
such permits,'' and thus ``NPDES permitting is not subject to the
requirement to publish a general notice of proposed rulemaking under
the APA or any other law * * * [and] it is not subject to the RFA.''
Id. at 36497.
However, the Agency went on to explain that, even though EPA had
concluded that it was not legally required to do so, the Agency would
voluntarily perform the RFA's small-entity impact analysis. Id. EPA
explained the strong public interest in the Agency following the RFA's
requirements on a voluntary basis: ``[The notice and comment] process
also provides an opportunity for EPA to consider the potential impact
of general permit terms on small entities and how to craft the permit
to avoid any undue burden on small entities.'' Id. Accordingly, with
respect to the NPDES permit that EPA was addressing in that Federal
Register notice, EPA stated that ``the Agency has considered and
addressed the potential impact of the general permit on small entities
in a manner that would meet the requirements of the RFA if it
applied.'' Id.
Subsequent to EPA's conclusion in 1998 that general permits are
adjudications, rather than rules, as noted above, the DC Circuit
recently held that Nationwide general permits under section 404 are
``rules'' rather than ``adjudications.'' Thus, this legal question
remains ``a difficult one'' (supra). However, EPA continues to believe
that there is a strong public policy interest in EPA applying the RFA's
framework and requirements to the Agency's evaluation and consideration
of the nature and extent of any economic impacts that a CWA general
permit could have on small entities (e.g., small businesses). In this
regard, EPA believes that the Agency's evaluation of the potential
economic impact that a general permit would have on small entities,
consistent with the RFA framework discussed below, is relevant to, and
an essential component of, the Agency's assessment of whether a CWA
general permit would place requirements on dischargers that are
appropriate and reasonable. Furthermore, EPA believes that the RFA's
framework and requirements provide the Agency with the best approach
for the Agency's evaluation of the economic impact of general permits
on small entities. While using the RFA framework to inform its
assessment of whether permit requirements are appropriate and
reasonable, EPA will also continue to ensure that all permits satisfy
the requirements of the Clean Water Act.
Accordingly, EPA has committed that the Agency will operate in
accordance with the RFA's framework and requirements during the
Agency's issuance of CWA general permits (in other words, the Agency
commits that it will apply the RFA in its issuance of general permits
as if those permits do qualify as ``rules'' that are subject to the
RFA). In satisfaction of this commitment, during the course of this
general offshore oil and gas exploration, development and production
operations permit proceeding, the Agency conducted the analysis and
made the appropriate determinations that are called for by the RFA. In
addition, and in satisfaction of the Agency's commitment, EPA will
apply the RFA's framework and requirements in any future issuance of
other NPDES general permits. EPA anticipates that for most general
permits the Agency will be able to conclude that there is not a
significant economic impact on a substantial number of small entities.
In such cases, the requirements of the RFA framework are fulfilled by
including a statement to this effect in the permit fact sheet, along
with a statement providing the factual basis for the conclusion. A
quantitative analysis of impacts would only be required for permits
that may affect a substantial number of small entities, consistent with
EPA guidance regarding RFA certification.\1\
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\1\ EPA's current guidance, entitled Final Guidance for EPA
Rulewriters: Regulatory Flexibility Act as Amended by the Small
Business Regulatory Enforcement and Fairness Act, was issued in
November 2006 and is available on EPA's Web site: https://www.epa.gov/sbrefa/documents/rfafinalguidance06.pdf. After
considering the Guidance and the purpose of CWA general permits, EPA
concludes that general permits affecting less than 100 small
entities do not have a significant economic impact on a substantial
number of small entities.
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G. Analysis of Economic Impacts of the General Permit for Offshore
Oil and Gas Exploration, Development and Production Operations off
Southern California. EPA determined, in consideration of the discussion
in Section F above, the issuance of the general permit for offshore oil
and gas exploration, development and production operations off Southern
California would not have a significant economic impact on a
substantial number of small entities. There are only 22 offshore
platforms which could be affected by the proposed general permit
modification. EPA concludes since this general permit affects less than
100 small entities, EPA believes it does not have a significant
economic impact on a substantial number of small entities. Accordingly,
EPA concludes a quantitative analysis of impacts is not required for
this permit.
Authority: Clean Water Act, 33 U.S.C. 1251 et seq.
Dated: March 12, 2009.
Alexis Strauss,
Director, Water Division, Region 9.
[FR Doc. E9-6840 Filed 4-2-09; 8:45 am]
BILLING CODE 6560-50-P