Notice of Final 2008 Effluent Guidelines Program Plan, 53218-53241 [E8-21484]
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53218
Federal Register / Vol. 73, No. 179 / Monday, September 15, 2008 / Notices
(866) 208–3676 (toll free). For TTY, call
(202) 502–8659.
Comment Date: 5 p.m. Eastern Time
on September 19, 2008.
Kimberly D. Bose,
Secretary.
[FR Doc. E8–21389 Filed 9–12–08; 8:45 am]
BILLING CODE 6717–01–P
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Comment Date: 5 p.m. Eastern Time
on September 30, 2008.
Kimberly D. Bose,
Secretary.
[FR Doc. E8–21390 Filed 9–12–08; 8:45 am]
DEPARTMENT OF ENERGY
Federal Energy Regulatory
Commission
BILLING CODE 6717–01–P
[Docket No. EL08–87–000]
ENVIRONMENTAL PROTECTION
AGENCY
September 8, 2008.
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Electric Power Supply Association;
Notice of Petition
[FRL–8715–5]
Take notice that on September 2,
2008, the Electric Power Supply
Association filed a petition pursuant to
Rule 207 of the Commission’s Rules of
Practice and Procedure (18 CFR
385.207) requesting guidance with
respect to the question of when
investments in publicly-held companies
will be deemed to convey ‘‘control’’ or
to result in ‘‘affiliation’’ for purposes of
the Commission’s market-based rate
requirements under section 205 of the
Federal Power Act (16 U.S.C. 824d) and
the requirements of section 203 of the
Federal Power Act (16 U.S.C. 824b) and
the Commission’s regulations
thereunder.
Any person desiring to intervene or to
protest this filing must file in
accordance with Rules 211 and 214 of
the Commission’s Rules of Practice and
Procedure (18 CFR 385.211 and
385.214). Protests will be considered by
the Commission in determining the
appropriate action to be taken, but will
not serve to make protestants parties to
the proceeding. Any person wishing to
become a party must file a notice of
intervention or motion to intervene, as
appropriate. Motions to intervene and
protests must be served on the
petitioner.
The Commission encourages
electronic submission of protests and
interventions in lieu of paper using the
‘‘eFiling’’ link at https://www.ferc.gov.
Persons unable to file electronically
should submit an original and 14 copies
of the protest or intervention to the
Federal Energy Regulatory Commission,
888 First Street, NE., Washington, DC
20426.
This filing is accessible on-line at
https://www.ferc.gov, using the
‘‘eLibrary’’ link and is available for
review in the Commission’s Public
Reference Room in Washington, DC.
There is an ‘‘eSubscription’’ link on the
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Clean Water Act Section 303(d):
Availability of List Decisions
Environmental Protection
Agency (EPA).
ACTION: Notice of Availability.
AGENCY:
SUMMARY: This notice announces the
availability of EPA’s Responsiveness
Summary Concerning EPA’s June 17,
2008 Public Notice of Final Decisions
To Add Waters and Pollutants to
Arkansas’ 2006 Section 303(d) List.
On June 17, 2008, EPA published a
notice in the Federal Register at Volume
73, Number 117, pages 34295–34296
providing the public the opportunity to
review its final decisions to add waters
and pollutants to Arkansas’ 2006
Section 303(d) List as required by EPA’s
Public Participation regulations (40 CFR
Part 25). Based on the Responsiveness
Summary, EPA has decided to remove
six waterbody pollutant combinations
identified in EPA’s Final Action on
Arkansas’ 2006 Section 303(d) list based
on additional information provided by
the Arkansas Department of
Environmental Quality. Therefore, EPA
has revised its decision to disapprove
Arkansas’ decisions not to list 73 water
body-pollutant combinations instead of
79 waterbody pollutant combinations. A
listing of these 73 water body pollutantcombinations along with priority
rankings for inclusion on the 2006
Section 303(d) List can be found in
Table 2 of EPA’s Responsiveness
Summary.
Copies of EPA’s
Responsiveness Summary Concerning
EPA’s June 17, 2008 Public Notice of
Final Decisions to Add Waters and
Pollutants to Arkansas; 2006 Section
303(d) List and the list of 73 waterbodypollutant pairs can be obtained at EPA
Region 6’s Web site at https://
www.epa.gov/region06/water/npdes/
tmdl/index.htm, or by writing or calling
Ms. Diane Smith at Water Quality
Protection Division, U.S. Environmental
Protection Agency Region 6, 1445 Ross
Ave., Dallas, TX 75202–2733, telephone
(214) 665–2145, facsimile (214) 665–
6490, or e-mail: smith.diane@epa.gov.
Underlying documents from the
administrative record for these
decisions are available for public
inspection at the above address. Please
contact Ms. Smith to schedule an
inspection.
FOR FURTHER INFORMATION CONTACT:
Diane Smith at (214) 665–2145.
SUPPLEMENTARY INFORMATION: Section
303(d) of the Clean Water Act (CWA)
requires that each state identify those
waters for which existing technologybased pollution controls are not
stringent enough to attain or maintain
state water quality standards. For those
waters, states are required to establish
Total Maximum Daily Loads (TMDLs)
according to a priority ranking.
Consistent with EPA’s regulations,
Arkansas submitted to EPA its listing
decisions under Section 303(d) on April
28, 2008. On June 6, 2008, EPA
approved Arkansas’ listing of 321 water
body-pollutant combinations and
associated priority rankings. EPA took
neither an approval or disapproval
action on 36 waters listed for beryllium.
EPA disapproved Arkansas’ decisions
not to list 79 water body-pollutant
combinations. Based on the public
comments, EPA has revised its decision
to disapprove Arkansas’s decision not to
list 73 water body-pollutant
combinations. A listing of these 73
water body pollutant-combinations
along with priority rankings for
inclusion on the 2006 Section 303(d)
List can be found in Table 2 of EPA’s
Responsiveness Summary.
Dated: September 5, 2008.
William K. Honker,
Deputy Director, Water Quality Protection
Division, Region 6.
[FR Doc. E8–21498 Filed 9–12–08; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
[EPA–HQ–OW–2006–0771; FRL–8715–4]
RIN 2040–AE89
ADDRESSES:
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Notice of Final 2008 Effluent
Guidelines Program Plan
Environmental Protection
Agency (EPA).
ACTION: Notice of Final 2008 Effluent
Guidelines Program Plan.
AGENCY:
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SUMMARY: EPA establishes national
technology-based regulations known as
effluent guidelines and pretreatment
standards to reduce pollutant discharges
from categories of industry discharging
directly to waters of the United States or
discharging indirectly through Publicly
Owned Treatment Works (POTWs). The
Clean Water Act (CWA) sections 301(d),
304(b), 304(g), and 307(b) require EPA
to review these effluent guidelines and
pretreatment standards. This notice
presents EPA’s 2008 review of existing
effluent guidelines and pretreatment
standards. It also presents EPA’s
evaluation of indirect dischargers
without categorical pretreatment
standards to identify potential new
categories for pretreatment standards
under CWA sections 304(g) and 307(b).
This notice also presents the final 2008
Effluent Guidelines Program Plan (‘‘final
2008 Plan’’), which, as required under
CWA section 304(m), identifies any new
or existing industrial categories selected
for effluent guidelines rulemaking and
provides a schedule for such
rulemaking. CWA section 304(m)
requires EPA to biennially publish such
a plan after public notice and comment.
The Agency published the preliminary
2008 Plan on October 30, 2007 (72 FR
61335). This notice also provides EPA’s
preliminary thoughts concerning its
2009 annual reviews under CWA
sections 304(b) and 304(g) as well as its
reviews under 301(d) and 307(b) and
solicits comments, data and information
to assist EPA in performing these
reviews. EPA intends to continue its
detailed studies of the steam electric
power generating industry, the health
services industry, and the coalbed
methane extraction industry, which is
part of the oil and gas extraction
industry. Finally, EPA is using this
notice to solicit public comment to
identify industry sectors and facilities
that use water efficiency practices that
promote water efficiency, re-use, and
recycling because such practices can be
related to reducing overall pollutant
discharges.
Docket ID No. EPA–HQ–OW–2008–
0517. Please include a total of 3 copies.
(4) Hand Delivery: Water Docket, EPA
Docket Center, EPA West, Room 3334,
1301 Constitution Ave., NW.,
Washington, DC, Attention Docket ID
No. EPA–HQ–OW–2008–0517. Such
deliveries are only accepted during the
Docket’s normal hours of operation and
special arrangements should be made.
Instructions: Direct your comments to
Docket ID No. EPA–HQ–OW–2008–
0517. 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 regulations.gov or email. The federal 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 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 index at
www.regulations.gov. Although listed in
the index, some information is not
publicly available, i.e., CBI or other
ADDRESSES: Submit your comments,
information whose disclosure is
data and information for the 2009
restricted by statute. Certain other
annual review, identified by Docket ID
No. EPA–HQ–OW–2008–0517, by one of material, such as copyrighted material,
is not placed on the Internet and will be
the following methods:
publicly available only in hard copy
(1) www.regulations.gov. Follow the
form. Publicly available docket
on-line instructions for submitting
materials are available either
comments.
electronically at www.regulations.gov or
(2) E-mail: OW-Docket@epa.gov,
Attention Docket ID No. EPA–HQ–OW– in hard copy at the Water Docket in the
EPA Docket Center, EPA/DC, EPA West,
2008–0517.
(3) Mail: Water Docket, Environmental Room 3334, 1301 Constitution Ave.,
NW., Washington, DC. The Public
Protection Agency, Mailcode: 4203M,
Reading Room is open from 8:30 a.m. to
1200 Pennsylvania Ave., NW.,
4:30 p.m., Monday through Friday,
Washington, DC 20460, Attention
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excluding legal holidays. The telephone
number for the Public Reading Room is
(202) 566–1744, and the telephone
number for the Water Docket is (202)
566–2426.
Key documents providing additional
information about EPA’s annual reviews
and the final 2008 Effluent Guidelines
Program Plan include the following:
• Technical Support Document for
the 2008 Effluent Guidelines Program
Plan, EPA–821–R–08–015, DCN 05515;
• Steam Electric Power Generating
Point Source Category: 2007/2008
Detailed Study Report, EPA–821–R–08–
011, DCN 05516;
• Coal Mining Detailed Study, EPA–
821–R–08–012, DCN 05517;
• Health Services Industry Detailed
Study: Dental Amalgam, EPA–821–R–
08–014, DCN 05518; and
• Health Services Industry Detailed
Study: Management and Disposal of
Unused Pharmaceuticals (Interim
Technical Report), EPA–821–R–08–013,
DCN 05519.
Mr.
Carey A. Johnston at (202) 566–1014 or
johnston.carey@epa.gov.
FOR FURTHER INFORMATION CONTACT:
SUPPLEMENTARY INFORMATION:
How Is This Document Organized?
The outline of this notice follows.
I. General Information
II. Legal Authority
III. What Is the Purpose of This Federal
Register Notice?
IV. Background
V. EPA’s 2008 Annual Review of Existing
Effluent Guidelines and Pretreatment
Standards Under CWA Sections 301(d),
304(b), 304(g), and 307(b)
VI. EPA’s 2009 Annual Review of Existing
Effluent Guidelines and Pretreatment
Standards Under CWA Sections 301(d),
304(b), 304(g), and 307(b)
VII. EPA’s Evaluation of Categories of
Indirect Dischargers Without Categorical
Pretreatment Standards To Identify
Potential New Categories for
Pretreatment Standards
VIII. The Final 2008 Effluent Guidelines
Program Plan Under Section 304(m)
IX. Request for Comment and Information
I. General Information
A. Does This Action Apply to Me?
This notice simply provides a
statement of the Agency’s effluent
guidelines review and planning
processes and priorities at this time, and
does not contain any regulatory
requirements.
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B. What Should I Consider as I Prepare
My Comments for EPA for the 2009
Annual Review?
1. Submitting Confidential Business
Information
Do not submit this information to EPA
through www.regulations.gov or e-mail.
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.
2. Tips for Preparing Your Comments
When submitting comments,
remember to:
• Identify the rulemaking by docket
number and other identifying
information (subject heading, Federal
Register date and page number).
• Follow directions—The agency may
ask you to respond to specific questions
or organize comments by referencing a
Code of Federal Regulations (CFR) part
or section number.
• Explain why you agree or disagree;
suggest alternatives and substitute
language for your requested changes.
• Describe any assumptions and
provide any technical information and/
or data that you used.
• If you estimate potential costs or
burdens, explain how you arrived at
your estimate in sufficient detail to
allow for it to be reproduced.
• Provide specific examples to
illustrate your concerns, and suggest
alternatives.
• Explain your views as clearly as
possible.
• Make sure to submit your
comments by the comment period
deadline identified.
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II. Legal Authority
This notice is published under the
authority of the CWA, 33 U.S.C. 1251,
et seq., and in particular sections 301(d),
304(b), 304(g), 304(m), 306, 307(b), 308,
33 U.S.C. 1311(d), 1314(b), 1314(g),
1314(m), 1316, 1317(b), and 1318.
III. What Is the Purpose of This Federal
Register Notice?
This notice presents EPA’s 2008
review of existing effluent guidelines
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and pretreatment standards under CWA
sections 301(d), 304(b), 304(g) and
307(b). It also presents EPA’s evaluation
of indirect dischargers without
categorical pretreatment standards to
identify potential new categories for
pretreatment standards under CWA
sections 304(g) and 307(b). This notice
also presents the final 2008 Effluent
Guidelines Program Plan (‘‘final 2008
Plan’’), which, as required under CWA
section 304(m), identifies any new or
existing industrial categories selected
for effluent guidelines rulemaking and
provides a schedule for such
rulemaking. CWA section 304(m)
requires EPA to biennially publish such
a plan after public notice and comment.
The Agency published the preliminary
2008 Plan on October 30, 2007 (72 FR
61335). This notice also provides EPA’s
preliminary thoughts concerning its
2009 annual reviews under CWA
sections 301(d), 304(b), 304(g) and
307(b) and solicits comments, data and
information to assist EPA in performing
these reviews.
IV. Background
A. What Are Effluent Guidelines and
Pretreatment Standards?
The CWA directs EPA to promulgate
effluent limitations guidelines and
standards (‘‘effluent guidelines’’) that
reflect pollutant reductions that can be
achieved by categories or subcategories
of industrial point sources using
technologies that represent the
appropriate level of control. See CWA
sections 301(b)(2), 304(b), 306, 307(b),
and 307(c). For point sources that
introduce pollutants directly into the
waters of the United States (direct
dischargers), the effluent limitations
guidelines and standards promulgated
by EPA are implemented through
National Pollutant Discharge
Elimination System (NPDES) permits.
See CWA sections 301(a), 301(b), and
402. For sources that discharge to
POTWs (indirect dischargers), EPA
promulgates pretreatment standards that
apply directly to those sources and are
enforced by POTWs and State and
Federal authorities. See CWA sections
307(b) and (c).
1. Best Practicable Control Technology
Currently Available (BPT)— CWA
Sections 301(b)(1)(A) & 304(b)(1)
EPA defines Best Practicable Control
Technology Currently Available (BPT)
effluent limitations for conventional,
toxic, and non-conventional pollutants.
Section 304(a)(4) designates the
following as conventional pollutants:
Biochemical oxygen demand (BOD5),
total suspended solids, fecal coliform,
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pH, and any additional pollutants
defined by the Administrator as
conventional. The Administrator
designated oil and grease as an
additional conventional pollutant on
July 30, 1979 (44 FR 44501). EPA has
identified 65 pollutants and classes of
pollutants as toxic pollutants, of which
126 specific substances have been
designated priority toxic pollutants. See
Appendix A to part 423. All other
pollutants are considered to be nonconventional.
In specifying BPT, EPA looks at a
number of factors. EPA first considers
the total cost of applying the control
technology in relation to the effluent
reduction benefits. The Agency also
considers the age of the equipment and
facilities, the processes employed, and
any required process changes,
engineering aspects of the control
technologies, non-water quality
environmental impacts (including
energy requirements), and such other
factors as the EPA Administrator deems
appropriate. See CWA section
304(b)(1)(B). Traditionally, EPA
establishes BPT effluent limitations
based on the average of the best
performances of facilities within the
industry of various ages, sizes,
processes, or other common
characteristics. Where existing
performance is uniformly inadequate,
BPT may reflect higher levels of control
than currently in place in an industrial
category if the Agency determines that
the technology can be practically
applied.
2. Best Conventional Pollutant Control
Technology (BCT)—CWA Sections
301(b)(2)(E) & 304(b)(4)
The 1977 amendments to the CWA
required EPA to identify effluent
reduction levels for conventional
pollutants associated with Best
Conventional Pollutant Control
Technology (BCT) for discharges from
existing industrial point sources. In
addition to considering the other factors
specified in section 304(b)(4)(B) to
establish BCT limitations, EPA also
considers a two part ‘‘costreasonableness’’ test. EPA explained its
methodology for the development of
BCT limitations in 1986. See 51 FR
24974 (July 9, 1986).
3. Best Available Technology
Economically Achievable (BAT)—CWA
Sections 301(b)(2)(A) & 304(b)(2)(B)
For toxic pollutants and nonconventional pollutants, EPA
promulgates effluent guidelines based
on the Best Available Technology
Economically Achievable (BAT). See
CWA section 301(b)(2)(A), (C), (D) and
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(F). The factors considered in assessing
BAT include the cost of achieving BAT
effluent reductions, the age of
equipment and facilities involved, the
process employed, potential process
changes, non-water quality
environmental impacts, including
energy requirements, and other such
factors as the EPA Administrator deems
appropriate. See CWA section
304(b)(2)(B). The technology must also
be economically achievable. See CWA
section 301(b)(2)(A). The Agency retains
considerable discretion in assigning the
weight accorded to these factors. BAT
limitations may be based on effluent
reductions attainable through changes
in a facility’s processes and operations.
Where existing performance is
uniformly inadequate, BAT may reflect
a higher level of performance than is
currently being achieved within a
particular subcategory based on
technology transferred from a different
subcategory or category. BAT may be
based upon process changes or internal
controls, even when these technologies
are not common industry practice.
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4. New Source Performance Standards
(NSPS)—CWA Section 306
New Source Performance Standards
(NSPS) reflect effluent reductions that
are achievable based on the best
available demonstrated control
technology. New sources have the
opportunity to install the best and most
efficient production processes and
wastewater treatment technologies. As a
result, NSPS should represent the most
stringent controls attainable through the
application of the best available
demonstrated control technology for all
pollutants (i.e., conventional, nonconventional, and priority pollutants).
In establishing NSPS, EPA is directed to
take into consideration the cost of
achieving the effluent reduction and any
non-water quality environmental
impacts and energy requirements.
5. Pretreatment Standards for Existing
Sources (PSES)—CWA Section 307(b)
Pretreatment Standards for Existing
Sources (PSES) are designed to prevent
the discharge of pollutants that pass
through, interfere with, or are otherwise
incompatible with the operation of
publicly owned treatment works
(POTWs), including sludge disposal
methods at POTWs. Pretreatment
standards for existing sources are
technology-based and are analogous to
BAT effluent limitations guidelines.
The General Pretreatment
Regulations, which set forth the
framework for the implementation of
national pretreatment standards, are
found at 40 CFR part 403.
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6. Pretreatment Standards for New
Sources (PSNS)—CWA Section 307(c)
Like PSES, Pretreatment Standards for
New Sources (PSNS) are designed to
prevent the discharges of pollutants that
pass through, interfere with, or are
otherwise incompatible with the
operation of POTWs. PSNS are to be
issued at the same time as NSPS. New
indirect dischargers have the
opportunity to incorporate into their
facilities the best available
demonstrated technologies. The Agency
considers the same factors in
promulgating PSNS as it considers in
promulgating NSPS.
B. What Are EPA’s Review and Planning
Obligations Under Sections 301(d),
304(b), 304(g), 304(m), and 307(b)?
1. EPA’s Review and Planning
Obligations Under Sections 301(d),
304(b), and 304(m)—Direct Dischargers
Section 304(b) requires EPA to review
its existing effluent guidelines for direct
dischargers each year and to revise such
regulations ‘‘if appropriate.’’ Section
304(m) supplements the core
requirement of section 304(b) by
requiring EPA to publish a plan every
two years announcing its schedule for
performing this annual review and its
schedule for rulemaking for any effluent
guidelines selected for possible revision
as a result of that annual review. Section
304(m) also requires the plan to identify
categories of sources discharging toxic
or non-conventional pollutants for
which EPA has not published effluent
limitations guidelines under section
304(b)(2) or NSPS under section 306.
See CWA section 304(m)(1)(B); S. Rep.
No. 50, 99th Cong., 1st Sess. (1985);
WQA87 Leg. Hist. 31 (indicating that
section 304(m)(1)(B) applies to ‘‘nontrivial discharges.’’). Finally, under
section 304(m), the plan must present a
schedule for promulgating effluent
guidelines for industrial categories for
which it has not already established
such guidelines, providing for final
action on such rulemaking not later than
three years after the industrial category
is identified in a final Plan.1 See CWA
section 304(m)(1)(C). EPA is required to
publish its preliminary Plan for public
1 EPA recognizes that one court—the U.S. District
Court for the Central District of California—has
found that EPA has a duty to promulgate effluent
guidelines within three years for new categories
identified in the Plan. See NRDC et al. v. EPA, 437
F.Supp.2d 1137 (C.D. Ca, 2006). However, EPA
continues to believe that the mandatory duty under
section 304(m)(1)(C) is limited to providing a
schedule for taking final action in effluent
guidelines rulemaking—not necessarily
promulgating effluent guidelines—within three
years, and has appealed this decision.
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comment prior to taking final action on
the plan. See CWA section 304(m)(2).
In addition, CWA section 301(d)
requires EPA to review every five years
the effluent limitations required by
CWA section 301(b)(2) and to revise
them if appropriate pursuant to the
procedures specified in that section.
Section 301(b)(2), in turn, requires point
sources to achieve effluent limitations
reflecting the application of the best
practicable control technology (all
pollutants), best available technology
economically achievable (for toxic
pollutants and non-conventional
pollutants) and the best conventional
pollutant control technology (for
conventional pollutants), as determined
by EPA under sections 304(b)(1),
304(b)(2) and 304(b)(4), respectively.
For over three decades, EPA has
implemented sections 301 and 304
through the promulgation of effluent
limitations guidelines, resulting in
regulations for 56 industrial categories.
See E.I. du Pont de Nemours & Co. v.
Train, 430 U.S. 113 (1977).
Consequently, as part of its annual
review of effluent limitations guidelines
under section 304(b), EPA is also
reviewing the effluent limitations they
contain, thereby fulfilling its obligations
under sections 301(d) and 304(b)
simultaneously.
2. EPA’s Review and Planning
Obligations Under Sections 304(g) and
307(b)—Indirect Dischargers
Section 307(b) requires EPA to revise
its pretreatment standards for indirect
dischargers ‘‘from time to time, as
control technology, processes, operating
methods, or other alternatives change.’’
See CWA section 307(b)(2). Section
304(g) requires EPA to annually review
these pretreatment standards and revise
them ‘‘if appropriate.’’ Although section
307(b) only requires EPA to revise
existing pretreatment standards ‘‘from
time to time,’’ section 304(g) requires an
annual review. Therefore, EPA meets its
304(g) and 307(b) requirements by
reviewing all industrial categories
subject to existing categorical
pretreatment standards on an annual
basis to identify potential candidates for
revision.
Section 307(b)(1) also requires EPA to
promulgate pretreatment standards for
pollutants not susceptible to treatment
by POTWs or that would interfere with
the operation of POTWs, although it
does not provide a timing requirement
for the promulgation of such new
pretreatment standards. EPA, in its
discretion, periodically evaluates
indirect dischargers not subject to
categorical pretreatment standards to
identify potential candidates for new
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Guidelines Program Plan (October 30,
2007; 72 FR 61335). EPA also continued
work on four detailed studies as part of
the 2008 annual review: Steam Electric
Power Generating (Part 423), Coal
Mining (Part 434), Oil and Gas
Extraction (Part 435) (for the purpose of
assessing whether to include coalbed
methane extraction as a new
subcategory), and Hospitals (Part 460).2
These reviews discharged EPA’s
obligations to annually review both
existing effluent limitations guidelines
for direct dischargers and existing
pretreatment standards for indirect
dischargers under CWA sections 304(b)
and (g), as well as other review
requirements under CWA section 301(d)
and 307(b).
Based on this review and prior annual
reviews, and in light of the ongoing
effluent guidelines rulemakings and
detailed studies currently in progress,
EPA is not identifying any existing
categories for effluent guidelines
V. EPA’s 2008 Review of Existing
rulemaking at this time, and is thus not
Effluent Guidelines and Pretreatment
Standards Under CWA Sections 301(d), establishing a schedule for further
rulemaking at this time. EPA does,
304(b), 304(g), and 307(b)
however, intend to continue its more
A. What Process Did EPA Use To Review
focused detailed reviews in the 2009
Existing Effluent Guidelines and
and 2010 annual reviews of the effluent
Pretreatment Standards Under CWA
guidelines for the following categories:
Section 301(d), 304(b), 304(g), and
Steam Electric Power Generating (Part
307(b)?
423), Oil and Gas Extraction category
1. Overview
(Part 435) (for the purpose of assessing
whether to revise the limits to include
In its 2008 annual review, EPA
Coalbed Methane extraction as a new
reviewed all industrial categories
subcategory), and Hospitals (Part 460)
subject to existing effluent limitations
(which is part of the Health Services
guidelines and pretreatment standards,
Industry detailed study). As part of its
representing a total of 56 point source
categories and over 450 subcategories.
detailed study of the Coalbed Methane
EPA uses four factors in a phased
extraction industry, EPA is seeking
approach to review existing effluent
approval from the Office of Management
limitations guidelines and pretreatment and Budget (OMB) for an Information
standards: Pollutants discharged in an
Collection Request (ICR) to gather data
industrial category’s discharge, current
from the industry (July 15, 2008; 73 FR
and potential pollution prevention and
40575). EPA is also planning to submit
control technology options, category
a proposed ICR to OMB for the Health
growth and economic considerations of
Services Industry; in particular, a study
technology options, and implementation of unused pharmaceuticals from
and efficiency considerations of revising medical and veterinary facilities. This is
existing effluent guidelines or
a request for a new collection. Before
publishing new effluent guidelines (see
submitting the ICR to OMB for review
December 21, 2006; 71 FR 76666).
and approval, EPA is soliciting
Examining these factors also helps the
comments on specific aspects of the
Agency to assess the extent to which
proposed information collection
additional regulation may contribute
(August 12, 2008; 73 FR 46903). See
reasonable further progress toward the
Sections V.B.2 and VII.D.
CWA’s objective of restoring and
maintaining the chemical, physical and
2 Based on available information, hospitals
biological integrity of the nation’s
consist mostly of indirect dischargers for which
waters, consistent with section 101 of
EPA has not established pretreatment standards. As
discussed in Section VII.B, EPA is including
the CWA.
EPA used this 2008 review to confirm hospitals in its review of the Health Services
potential
category for pretreatment
the Agency’s identification of industrial Industry, a As part of new process, EPA will review
standards.
that
categories prioritized for further review
the existing effluent guidelines for the few direct
dischargers in the category.
in the preliminary 2008 Effluent
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pretreatment standards. The CWA does
not require EPA to publish its review of
pretreatment standards or identification
of potential new categories, although
EPA is exercising its discretion to do so
in this notice.
EPA intends to repeat this publication
schedule for future pretreatment
standards reviews (e.g., EPA will
publish the 2009 annual pretreatment
standards review in the notice
containing the Agency’s 2009 annual
review of existing effluent guidelines
and the preliminary 2010 plan). EPA
intends that these contemporaneous
reviews will provide meaningful insight
into EPA’s effluent guidelines and
pretreatment standards program
decision-making. Additionally, by
providing a single notice for these and
future reviews, EPA hopes to provide a
consolidated source of information for
the Agency’s current and future effluent
guidelines and pretreatment standards
program reviews.
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2. How Did EPA’s 2007 Annual Review
Influence Its 2008 Annual Review of
Point Source Categories With Existing
Effluent Guidelines and Pretreatment
Standards?
In view of the annual nature of its
reviews of existing effluent guidelines
and pretreatment standards, EPA
believes that each annual review can
and should influence succeeding annual
reviews, e.g., by indicating data gaps,
identifying new pollutants or pollution
reduction technologies, or otherwise
highlighting industrial categories for
additional scrutiny in subsequent years.
During its 2007 annual review, which
concluded in October 2007, EPA started
or continued detailed studies of the
existing effluent guidelines and
pretreatment standards for the four
industrial categories mentioned in the
previous discussion: Steam Electric
Power Generating (Part 423), Coal
Mining (Part 434), Oil and Gas
Extraction category (Part 435) (for the
purpose of assessing whether to revise
the limits to include Coalbed Methane
extraction as a new subcategory), and
Hospitals (Part 460) (which is part of the
Health Services Industry detailed
study). In addition, EPA used its 2007
annual reviews to identify three other
industrial categories as candidates for
further study in the 2008 reviews based
on the toxic discharges reported to the
Toxics Release Inventory (TRI) and
Permit Compliance System (PCS): Ore
Mining and Dressing (Part 440),
Centralized Waste Treatment (Part 437),
and Waste Combustors (Part 444). EPA
published the findings from its 2007
annual review with its preliminary 2008
Plan (October 30, 2007; 72 FR 61335),
making the pollutant discharge and
industry profile data available for public
comment. Docket No. EPA–HQ–OW–
2006–0771. EPA used the findings, data
and comments on the 2007 annual
review to inform its 2008 annual review.
The 2008 review also built on the
previous reviews by incorporating some
refinements to assigning discharges to
categories and updating toxic weighting
factors used to estimate the significance
of toxic pollutant discharges. In its 2008
reviews, EPA completed its Coal Mining
detailed study and the dental amalgam
management detailed study for the
Health Services Industry. As discussed
below, EPA is not identifying these two
industry sectors for an effluent
guidelines rulemaking at this time. EPA
does, however, intend to continue its
more focused detailed reviews for the
following categories and industry
sectors in the next biennial planning
cycle: Steam Electric Power Generating
category, Oil and Gas Extraction
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category (only to assess whether to
revise the limits to include Coalbed
Methane extraction as a new
subcategory), and unused
pharmaceutical management for the
Health Services Industry (which
includes the Hospital category).
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3. What Actions Did EPA Take in
Performing Its 2008 Annual Reviews of
Existing Effluent Guidelines and
Pretreatment Standards?
a. Screening-Level Review
The first component of EPA’s 2008
annual review consisted of a screeninglevel review of all industrial categories
subject to existing effluent guidelines or
pretreatment standards. As a starting
point for this review, EPA examined
screening-level data from its 2007
annual reviews. In its 2007 annual
reviews, EPA focused its efforts on
collecting and analyzing data to identify
industrial categories whose pollutant
discharges potentially are the most
significant. EPA primarily uses TRI and
PCS data to estimate the mass of
pollutant discharges from different
industrial facilities. Because pollutant
toxicities are different, EPA converted
the toxic and non-conventional
pollutant discharges that are reported in
a mass unit (pounds) into a measure of
relative toxicity (toxic-weighted pound
equivalent or TWPE). EPA calculated
the TWPE for each pollutant discharged
by multiplying the pollutant specific
toxic weighting factor (TWF) and the
mass of the pollutant discharge. Where
data are available, these TWFs reflect
both aquatic life and human health
effects. EPA ranked point source
categories according to their discharges
of toxic and non-conventional
pollutants (reported in units of TWPE)
to assess the significance of these toxic
and non-conventional pollutant
discharges to human health or the
environment. EPA repeated this process
for the 2008 annual reviews using the
most recent TRI data (2005).
Next, EPA considered the availability
of technologies to reduce pollutant
discharges. EPA does not have, for all of
the 56 existing industrial categories,
information about the availability of
treatment or process technologies to
reduce pollutant wastewater discharges
beyond the performance of the
technologies upon which existing
effluent guidelines and standards were
developed. At present 46 states and one
U.S. territory are authorized to
administer the CWA NPDES program.
Under the CWA, permitting authorities
must include water-quality based
effluent limits where the technologybased effluent limits are not sufficient to
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meet applicable water quality standards.
Therefore, dischargers may have already
installed technologies that reduce
pollutant discharges to a level below the
original technology-based requirements
in order to meet such water-quality
based effluent limitations.
A commenter on the preliminary 2008
Plan argued that EPA should conduct
rulemaking to amend its effluent
guidelines even where water qualitybased controls have already controlled
pollutant discharges (see EPA–HQ–OW–
2006–0771–0847). EPA disagrees.
Analyzing the significance of the
remaining pollutant discharges is most
useful for assessing the potential
effectiveness of additional technologies
because such an analysis focuses on the
amount and significance of pollutant
discharges that would actually be
removed through new, technology-based
nationally-applicable regulations for
these categories. Where potential
pollutant discharge reductions are not
significant, there are likely few effective
technology options for a technologybased rule. Once EPA determined which
industries have the potential for
significant additional pollutant
removals, EPA further examined the
availability of technologies for certain
industries. For example, EPA identified
technologies to minimize pollutant
discharges from Steam Electric facilities
(see Steam Electric Power Generating
Point Source Category: 2007/2008
Detailed Study Report, EPA–821–R–08–
011, DCN 05516).
EPA also considered whether there
was a way to develop a suitable tool for
comprehensively evaluating the
availability and affordability of
treatment or process technologies, but
determined that there is not, because the
universe of facilities is too broad and
complex. EPA could not find a
reasonable way to prioritize the
industrial categories based on readily
available engineering and economic
data. In the past, EPA has gathered
information regarding technologies and
economic achievability for one
industrial category at a time through
detailed questionnaires distributed to
hundreds of facilities within a category
or subcategory for which EPA has
commenced rulemaking. Such
information-gathering is subject to the
requirements of the Paperwork
Reduction Act (PRA), 33 U.S.C. 3501, et
seq. The information acquired in this
way is valuable to EPA in its rulemaking
efforts, but the process of gathering,
validating and analyzing the data can
consume considerable time and
resources. To study one industry with
this level of analysis generally takes 3
years at a cost to EPA of 1.5 to 3 million
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53223
dollars. EPA does not think it is
appropriate or feasible to conduct this
level of analysis for all point source
categories in conducting an annual
review. Rather, EPA uses its analyses of
existing pollutant discharges to identify
the categories with the largest toxic
weighted discharges. From this smaller
list of categories, EPA evaluates the
possibility of effective technologies and
selects certain industries for
examination (e.g., Preliminary Category
Reviews, Detailed Studies). In these
more detailed reviews EPA evaluates
technology options for better control of
pollutant discharges and may conduct
surveys or other data collection
activities in order to better inform the
decision on whether to initiate an
effluent guidelines rulemaking. EPA
solicits comment on how to develop
tools for directly assessing technological
and economic achievability in future
annual reviews under section 301(d),
304(b), and 307(b) (see EPA–HQ–OW–
2004–0032–2344). The full description
of EPA’s methodology for the 2008
review is presented in the Technical
Support Document (TSD) for the final
2008 Plan (see DCN 05515).
EPA is continuously investigating and
solicits comment on how to improve its
analyses. EPA made a few such
improvements to the review
methodology from the 2007 to the 2008
annual review. As part of the 2008
review, EPA corrected the
PCSLoads2004 and TRIReleases2004
databases, by addressing issues raised in
comments (e.g., updating TWFs and
average POTW pollutant removal
efficiencies for a number of pollutants)
and collecting additional information
from individual facilities that report to
TRI or PCS.
EPA also continued to use the quality
assurance project plan (QAPP)
developed for the 2007 annual review to
document the type and quality of data
needed to make the decisions in this
2008 annual review and to describe the
methods for collecting and assessing
those data (see EPA–HQ–OW–2006–
0771–0208). EPA performed quality
assurance checks on the data used to
develop estimates of toxic-weighted
pollutant discharges (i.e., verifying 2005
discharge data reported to TRI) to
determine whether any of the pollutant
discharge estimates relied on incorrect
or suspect data. For example, EPA
contacted facilities and permit writers to
confirm and, as necessary, correct TRI
data for facilities that EPA had
identified in its screening-level review
as the significant dischargers.
Based on this methodology, EPA
assigned those industrial categories with
the lowest estimates of toxic-weighted
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pollutant discharges a lower priority for
revision (i.e., industrial categories
marked ‘‘(3)’’ in the ‘‘Findings’’ column
in Table V–1 in section V.B.4 of today’s
notice).
Because there are 56 point source
categories (including over 450
subcategories) with existing effluent
guidelines and pretreatment standards
that must be reviewed annually, EPA
believes it is important to prioritize its
review so as to focus on industries
where changes to the existing effluent
guidelines or pretreatment standards are
most likely to result in further pollutant
discharge reduction. In general,
industries for which effluent guidelines
or pretreatment standards have recently
been promulgated are less likely to
warrant such changes. However, when
EPA becomes aware of the growth of a
new industrial activity within an
existing category or where new concerns
are identified for previously
unevaluated pollutants discharged by
facilities within an industrial category,
EPA would apply more scrutiny to the
category in a subsequent review. EPA
identified no such instance during the
2008 annual review. In order to further
focus its inquiry during the 2008 annual
review, EPA assigned a lower priority
for potential revision to categories for
which effluent guidelines had been
recently promulgated or revised, or for
which effluent guidelines rulemaking
was currently underway (i.e., industrial
categories marked ‘‘(1)’’ in the
‘‘Findings’’ column in Table V–1 in
section V.B.4 of today’s notice). EPA
removed an industrial point source
category from further consideration
during the current review cycle if EPA
established, revised, or reviewed in a
rulemaking context the category’s
effluent guidelines after August 2001
(i.e., seven years prior to August 2008,
the expected publication of the final
2008 Effluent Guidelines Program). EPA
chose seven years because this is the
time it customarily takes for the effects
of effluent guidelines or pretreatment
standards to be fully reflected in
pollutant loading data and TRI reports
(in large part because effluent
limitations guidelines are often
incorporated into NPDES permits only
upon re-issuance, which could be up to
five years after the effluent guidelines or
pretreatment standards are
promulgated). EPA also applied a lower
priority for potential revision at this
time to the Ore Mining and Dressing
category as EPA lacked sufficient data to
determine whether revision would be
appropriate (i.e., this category is marked
with ‘‘(5)’’ in the ‘‘Findings’’ column in
Table V–1 in section V.B.4 of today’s
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notice). EPA lacks sufficient information
at this time on the magnitude of the
toxic-weighted pollutant discharges
associated with this category. EPA will
seek additional information on the
discharges from this category in the next
annual review in order to determine
whether a detailed study is warranted.
EPA typically performs a further
assessment of the pollutant discharges
before starting a detailed study of an
industrial category. This assessment
(‘‘preliminary category review’’)
provides an additional level of quality
assurance on the reported pollutant
discharges and number of facilities that
represent the majority of toxic-weighted
pollutant discharges. See the
appropriate section in the TSD for the
final 2008 Plan (see DCN 05515) for
EPA’s data needs for these industrial
categories.
For industrial categories marked ‘‘(4)’’
in the ‘‘Findings’’ column in Table V–
1 in section V.B.4 of today’s notice, EPA
had sufficient information on the toxicweighted pollutant discharges
associated with these categories to
continue a detailed study of these
industrial categories in the 2008 annual
review. EPA intends to use the detailed
study to obtain information on hazard,
availability and cost of technology
options, and other factors in order to
determine if it would be appropriate to
identify the category for possible
effluent guidelines revision. EPA will
continue three detailed studies in the
2009 annual review: Steam Electric
Power Generating category, Oil and Gas
Extraction category (only to assess
whether to revise the limits to include
Coalbed Methane extraction as a new
subcategory), and unused
pharmaceutical management for the
Health Services Industry (which
includes the Hospital category).
As part of its 2008 annual review,
EPA also considered the number of
facilities responsible for the majority of
the estimated toxic-weighted pollutant
discharges associated with an industrial
activity. Where only a few facilities in
a category accounted for the vast
majority of toxic-weighted pollutant
discharges (i.e., categories marked ‘‘(2)’’
in the ‘‘Findings’’ column in Table V–
1 in section V.B.4 of today’s notice),
EPA applied a lower priority for
potential revision. EPA believes that
revision of individual permits for such
facilities may be more effective than a
revised national effluent guidelines
rulemaking. Individual permit
requirements can be better tailored to
these few facilities and may take
considerably less time and resources to
establish than a national effluent
guidelines rulemaking. The Docket
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accompanying this notice lists facilities
that account for the vast majority of the
estimated toxic-weighted pollutant
discharges for particular categories (see
DCN 05515). For these facilities, EPA
will consider identifying pollutant
control and pollution prevention
technologies that will assist permit
writers in developing facility-specific,
technology-based effluent limitations on
a best professional judgment (BPJ) basis.
For example, EPA developed and
distributed a 2007 technical document
to NPDES permit writers in order to
support the development of effluent
limitations for facilities in the
dissolving kraft (Subpart A) and
dissolving sulfite (Subpart D)
subcategories of the pulp and paper
point source category (40 CFR Part 430)
(see EPA–HQ–OW–2006–0771–0774). In
future annual reviews, EPA also intends
to re-evaluate each category based on
the information available at the time in
order to evaluate the effectiveness of the
BPJ permit-based support.
EPA received comments in previous
biennial planning cycles urging the
Agency to encourage and recognize
voluntary efforts by industry to reduce
pollutant discharges, especially when
the voluntary efforts have been widely
adopted within an industry and the
associated pollutant reductions have
been significant. EPA agrees that
industrial categories demonstrating
significant progress through voluntary
efforts to reduce hazard to human health
or the environment associated with their
effluent discharges would be a
comparatively lower priority for effluent
guidelines or pretreatment standards
revision, particularly where such
reductions are achieved by a significant
majority of individual facilities in the
industry. Although during this annual
review EPA could not complete a
systematic review of voluntary pollutant
loading reductions, EPA’s review did
indirectly account for the effects of
successful voluntary programs because
any significant reductions in pollutant
discharges should be reflected in TRI
2005 discharge data, as well as any data
provided directly by commenters, that
EPA used to assess the toxic-weighted
pollutant discharges.
In summary, EPA’s review enables
EPA to concentrate its resources on
conducting more in-depth reviews of
certain industries, as discussed below.
b. Further Review of Prioritized
Categories
In the publication of the preliminary
2008 Plan, EPA identified three
categories with potentially high TWPE
discharge estimates for further
investigation (‘‘preliminary category
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review’’) as a result of the 2007 annual
review: Ore Mining and Dressing (Part
440), Centralized Waste Treatment (Part
437), and Waste Combustors (Part 444)
(i.e., EPA identified these categories
with ‘‘(5)’’ in the column entitled
‘‘Findings’’ in Table V–1, Page 61345 of
the preliminary 2008 Plan). EPA
reviewed these three categories in its
2008 annual review.
EPA typically performs a further
assessment of the pollutant discharges
before starting a detailed study of an
industrial category. In conducting these
preliminary category reviews, EPA used
the same types of data sources used for
the detailed studies but in less depth.
This assessment provides confirmation
of the reported pollutant discharges and
number of facilities that represent the
majority of toxic-weighted pollutant
discharges. EPA may also develop a
preliminary list of potential wastewater
pollutant control technologies before
conducting a detailed study.
c. Detailed Study of Four Categories
EPA continued detailed studies of
four categories: Steam Electric Power
Generating (Part 423), Coal Mining (Part
434), Oil and Gas Extraction (Part 435)
(only to assess whether to include
coalbed methane extraction as a new
subcategory), and Hospitals (Part 460)
(which is part of the Health Services
Industry detailed study). For these
industries, EPA gathered and analyzed
additional data on pollutant discharges,
economic factors, and technology
issues. EPA examined: (1) Wastewater
characteristics and pollutant sources; (2)
the pollutants discharged from these
sources and the toxic weights associated
with these discharges; (3) treatment
technology and pollution prevention
information; (4) the geographic
distribution of facilities in the industry;
(5) any pollutant discharge trends
within the industry; and (6) any relevant
economic factors.
EPA relied on many different sources
of data including: (1) The 2002 U.S.
Economic Census; (2) TRI and PCS data;
(3) contacts with reporting facilities to
verify reported releases and facility
categorization; (4) contacts with
regulatory authorities (states and EPA
regions) to understand how category
facilities are permitted; (5) NPDES
permits and their supporting fact sheets;
(6) monitoring data included in facility
applications for NPDES permit renewals
(Form 2C data); (7) EPA effluent
guidelines technical development
documents; (8) relevant EPA
preliminary data summaries or study
reports; (9) technical literature on
pollutant sources and control
technologies; (10) information provided
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by industry including industry
conducted survey and sampling data;
(11) CWA section 308 data requests and
surveys; and (12) stakeholder comments
(see DCN 06109). Additionally, in order
to evaluate available and affordable
treatment technology options for the
coalbed methane extraction industry
sector, EPA is seeking approval from the
Office of Management and Budget
(OMB) for an Information Collection
Request (ICR) to gather data from the
industry (July 15, 2008; 73 FR 40757).
EPA is also planning to submit a
proposed ICR to OMB for the Health
Services Industry; in particular, a study
of unused pharmaceuticals from
medical and veterinary facilities. This is
a request for a new collection. Before
submitting the ICR to OMB for review
and approval, EPA is soliciting
comments on specific aspects of the
proposed information collection
(August 12, 2008; 73 FR 46903).
d. Public Comments
EPA’s annual review process
considers information provided by
stakeholders regarding the need for new
or revised effluent limitations
guidelines and pretreatment standards.
To that end, EPA established a docket
at the time of publication of the final
2006 Plan to provide the public with an
opportunity to submit additional
information to assist the Agency in its
2007 and 2008 annual reviews. These
public comments are in the supporting
docket (EPA–HQ–OW–2006–0771,
www.regulations.gov) and summarized
in the TSD for the final 2008 Plan (see
DCN 05515).
B. What Were EPA’s Findings From Its
2008 Annual Review for Categories
Subject to Existing Effluent Guidelines
and Pretreatment Standards?
1. Screening-Level Review
In its 2008 screening level review,
EPA considered significance of
remaining pollutant discharges and the
other factors described in section A.3.a.
above in prioritizing effluent guidelines
for potential revision. See Table V–1 in
section V.B.4 of today’s notice for a
summary of EPA’s findings with respect
to each existing category; see also the
TSD for the final 2008 Plan. Out of the
categories subject only to the screening
level review in 2008, EPA is not
identifying any for effluent guidelines
rulemaking at this time, based on the
factors described in section A.3.a above
and in light of the resources EPA is
currently expending in effluent
guidelines rulemakings and detailed
studies. Specifically, EPA is engaged in
rulemaking relating to the Construction
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53225
and Development Point Source
Category, the Airport De-icing Point
Source Category; and the Concentrated
Animal Feeding Operations Point
Source Category.
2. Detailed Studies
In its 2008 annual review, EPA
continued detailed studies of four
industrial point source categories with
existing effluent guidelines and
pretreatment standards: Steam Electric
Power Generating (Part 423), Coal
Mining (Part 434), Oil and Gas
Extraction (Part 435) (to assess whether
to include coalbed methane extraction
as a new subcategory), and Hospitals
(Part 460) (which is part of the Health
Services Industry detailed study). EPA
is investigating whether the pollutant
discharges reported to TRI and PCS for
2004 and 2005 accurately reflect the
current discharges of the industry. EPA,
through these detailed studies, analyzes
the reported pollutant discharges,
technology innovation, and process
changes in these industrial categories.
Additionally, EPA considers whether
there are industrial activities not
currently subject to effluent guidelines
or pretreatment standards that should be
included with these existing categories,
either as part of existing subcategories
or as potential new subcategories.
EPA completed the Coal Mining
detailed study and the dental amalgam
management detailed study for the
Health Services Industry. As described
below in more detail, EPA is not
identifying either of these industries for
an effluent guidelines rulemaking in
this final 2008 Plan. EPA will continue
the other detailed studies (i.e., Steam
Electric Power Generating, Coalbed
Methane Extraction, and Health
Services Industry (unused
pharmaceutical management)) to
determine whether EPA should identify
in the future any of these industries for
possible revision of their existing
effluent guidelines and pretreatment
standards. Three of these four industries
are described below. EPA’s review of
hospitals (including dental amalgam
and unused pharmaceuticals) is
described in section VII.B (Health
Services Industry detailed study).
a. Steam Electric Power Generating (Part
423)
The Steam Electric Power Generating
effluent guidelines (40 CFR 423) apply
to a subset of the electric power
industry, namely those facilities
‘‘primarily engaged in the generation of
electricity for distribution and sale
which results primarily from a process
utilizing fossil-type fuel (coal, oil, or
gas) or nuclear fuel in conjunction with
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a thermal cycle employing the steam
water system as the thermodynamic
medium.’’ See 40 CFR 423.10. EPA’s
most recent revisions to the effluent
guidelines and standards for this
category were promulgated in 1982 (see
47 FR 52290; November 19, 1982).
EPA has focused efforts for the 2007/
2008 Detailed Study for the Steam
Electric Power Generating point source
category on certain discharges from
coal-fired power plants. The study
sought to: (1) characterize the mass and
concentrations of pollutants in
wastewater discharges from coal-fired
steam electric facilities; and (2) identify
the pollutants that comprise a
significant portion of the category’s
TWPE discharge estimate and the
corresponding industrial operation.
EPA’s previous annual reviews have
indicated that the toxic-weighted
loadings for this category are
predominantly driven by the metals
present in wastewater discharges, and
that the waste streams contributing the
majority of these metals are associated
with ash handling and wet flue gas
desulfurization (FGD) systems (see
EPA–HQ–OW–2004–0032–2781). Other
potential sources of metals include coal
pile runoff, metal/chemical cleaning
wastes, coal washing, and certain low
volume wastes. EPA is continuing to
collect data for the detailed study
through facility inspections, wastewater
sampling, a data request that was sent
to a limited number of companies, and
various secondary data sources (see
Steam Electric Power Generating Point
Source Category: 2007/2008 Detailed
Study Report, EPA–821–R–08–011, DCN
05516).
EPA’s data collection efforts are
primarily focused on coal-fired power
plants, with particular interest in FGD
wastewater treatment, the management
of ash sluice water, and water reuse
opportunities. EPA’s site visit program
gathers information on the types of
wastewaters generated by coal-fired
steam electric power plants, as well as
the methods of managing these
wastewaters to allow for recycle, reuse,
or discharge. EPA conducted site visits
at 16 coal-fired power plants and is
continuing to identify potential site visit
candidates to assess FGD systems using
different scrubber designs or sorbents,
and facilities operating or planning to
install different types of treatment and
water reuse options.
Between July and October of 2007,
EPA conducted five sampling episodes
to characterize untreated wastewaters
generated by coal-fired power plants,
including FGD scrubber purge, fly ash
sluice, bottom ash sluice, and combined
fly- and bottom ash sluice. EPA also
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collected samples to assess the effluent
quality from different types of treatment
systems currently in place at these
operations. Samples collected during
the five episodes were analyzed for
metals and other pollutants, such as
total suspended solids and nitrogen.
Site-specific sampling episode reports
are in the docket for the 2008 Plan
(EPA–HQ–OW–2006–0771,
www.regulations.gov). These reports
discuss the specific sample points and
analytes, the sample collection methods
used, the field quality control (QC)
samples collected, and the analytical
results for the wastewater samples.
EPA is continuing to identify
potential sampling candidates to
evaluate additional types of FGD
wastewater treatment systems,
including advanced biological metals
removal processes and chemical
precipitation systems. EPA plans to
conduct wastewater sampling at one or
more additional plants in 2008 or early
2009.
EPA also collected facility-specific
information using a data request
conducted under authority of CWA
section 308 (see EPA–HQ–OW–2006–
0771–0417). In May 2007, EPA
distributed this data request to nine
companies that operate a number of
coal-fired power plants with wet FGD
systems. The data request complements
the wastewater sampling effort as it
requested facility-specific information
about wastewaters, and identifies
management practices, for facilities not
included in EPA’s sampling program.
Responses were received in August and
October 2007 and characterized
operations at 30 coal-fired power plants.
EPA conducted technical reviews of the
data received and resolved questions
with the individual companies before
entering the information into a database
(see DCNs 05754 and 05755). The data
request collected information on
selected wastewater sources, air
pollution controls, wastewater
management and treatment practices,
water reuse/recycle, and treatment
system capital and operating costs.
The Utility Water Act Group (UWAG)
provided EPA with a database that
contains selected NPDES Form 2C data
for 86 coal-fired plants operated by
UWAG’s member companies, namely
those plants that operate wet FGD
systems or wet fly ash sluice systems.
The database provides facility
information, data on facility outfalls,
process flow diagrams, wastewater
treatment information, and intake and
effluent characteristics. Data are
provided for the FGD, ash sluice, and
coal pile runoff wastestreams.
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EPA is also in the process of
contacting vendors and conducting
literature searches to collect additional
information on wastewater treatment
technology options and wastewater
reuse opportunities for particular waste
streams. The Electric Power Research
Institute (EPRI) is conducting benchand pilot-scale tests on FGD wastewater
treatment technologies, including
chemical precipitation, ion exchange,
and biological metals removal.
EPA intends to continue its detailed
review of the Steam Electric Power
Generating point source category in the
2009 and 2010 annual reviews of
effluent guidelines. Wastewater
sampling at a facility operating a
treatment system of interest was delayed
by nearly one year due to operational
conditions at the plant. In addition,
several other plants recently began
operating a new generation of FGD
wastewater treatment technology that
may achieve substantially better
pollutant reductions of metals and
nutrients than EPA has evaluated to
date. EPA believes it is important to
evaluate the performance of these
technologies, as well as the processes
being investigated by EPRI, prior to
concluding the detailed study. As noted
above, EPA has not yet completed its
wastewater sampling activities. The
UWAG Form 2C database was recently
delivered to EPA; however, EPA has not
had sufficient time to fully evaluate this
data. The database provides substantial
information on wastewater generation
and wastewater management and
treatment practices for a large number of
plants. EPA believes it is important to
take additional time to evaluate the
Form 2C data, in concert with EPA’s
sampling data and the responses to
EPA’s data request. EPA also intends to
continue investigating water reuse
opportunities to assess the degree to
which they may yield pollutant
reductions for discharges of ash sluice
and FGD wastewater.
b. Coal Mining (Part 434)
As discussed in the final 2006 Plan
and preliminary 2008 Plan, EPA
conducted a detailed study during the
2007 and 2008 annual reviews to
evaluate the merits of comments
received from a public interest group
and from states and industry urging
revisions to pollutant limitations in the
Coal Mining effluent guidelines (40 CFR
Part 434) (see December 21, 2006; 71 FR
76644–76667, and October 30, 2007; 72
FR 61342–61343).
The public interest group, the
Environmental Law and Policy Center,
asked EPA to place more stringent
controls on Total Dissolved Solids
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(TDS) (e.g., sulfates and chlorides),
mercury, cadmium, manganese, and
selenium in coal mining discharges.
They referenced a study by EPA Region
5 on potential adverse impacts of the
discharge of sulfates on aquatic life (see
EPA–HQ–OW–2004–0032–2614 through
2617).
The Interstate Mining Compact
Commission, which represents mining
regulatory agencies in 28 states, state
mine permitting agencies in
Pennsylvania and Virginia, and a few
mining companies, asked EPA to
remove the current manganese
limitations. They made the following
requests and assertions: (1) Permittees
should be allowed to employ best
management practices as necessary to
reduce manganese discharges based on
the water quality of receiving
waterbodies; (2) manganese treatment is
unnecessary to protect aquatic life and
there are no widespread toxicity
problems from discharges of manganese;
(3) manganese treatment doubles or
triples overall treatment costs resulting
in the forfeiture of Surface Mining
Control and Reclamation Act (SMCRA)
bonds; (4) EPA should reconsider its
rationale for setting manganese limits to
ensure surrogate removal of other metals
because data show that other metals
occur only in low concentrations; (5)
manganese treatment sometimes results
in environmental harm because mining
operators must add excessive chemicals
to meet the discharge limits; and (6)
because manganese limits are overly
stringent they discourage the use of
passive treatment technologies which
are more environmentally beneficial
than active treatment.
Individual state and industry
commenters cited the following factors
in support of their comments: (1) More
stringent state-imposed coal mining
reclamation bonding requirements,
enacted after the promulgation of
SMCRA, to control water discharges
from mines undergoing reclamation; (2)
studies supporting their contention that
manganese is not harmful to aquatic life
at levels above the current effluent
limits; and (3) perception that active
treatment with chemical additions may
complicate permit compliance and may
cause environmental harm.
EPA initiated the Coal Mining
Detailed Study in January 2007. The
study is consistent with the framework
presented in the Detailed Study Plan, a
draft of which the Agency placed into
the docket (see EPA–HQ–OW–2004–
0032–2312) during the fall of 2006. EPA
revised and finalized the Detailed Study
Plan in April 2007 to reflect public
comments. The study evaluated
treatment technologies, costs, and
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pollutant discharge loads, as well as the
effects of manganese and other
pollutants on aquatic life. The study
also addressed the question of whether
bonds are being forfeited because of the
cost of manganese treatment by
examining bonding and trust fund
requirements, past bond forfeiture rates,
future potential bond forfeiture rates,
and the issues related to state
assumption of long-term water
treatment responsibilities for mines
where the bonds have been forfeited.
As outlined in the Detailed Study
Plan, EPA framed study questions based
on public comment, identified data
sources to help answer the study
questions, developed a methodology for
estimating treatment costs and discharge
loads, and initiated data collection
activities with the Interstate Mining
Compact Commission, state agencies,
and the Office of Surface Mining,
Reclamation, and Enforcement within
the U.S. Department of the Interior. In
responding to these public comments
the study used Part 434 definitions to
describe the industry. In particular,
proper understanding of the following
terms is useful in understanding the
following discussion and EPA’s
response to the public commenters:
• The term ‘‘acid or ferruginous mine
drainage’’ means mine drainage which,
before any treatment, either has a pH of
less than 6.0 or a total iron
concentration equal to or greater than 10
mg/l (see 40 CFR 434.11(a)).
• The term ‘‘active mining area’’
means the area, on and beneath land,
used or disturbed in activity related to
the extraction, removal, or recovery of
coal from its natural deposits. This term
excludes coal preparation plants, coal
preparation plant associated areas and
post-mining areas (see 40 CFR
434.11(b)).
• The term ‘‘alkaline mine drainage’’
means mine drainage which, before any
treatment, has a pH equal to or greater
than 6.0 and total iron concentration of
less than 10 mg/l (see 40 CFR 434.11(c)).
• The term ‘‘bond release’’ means the
time at which the appropriate regulatory
authority returns a reclamation or
performance bond based upon its
determination that reclamation work
(including, in the case of underground
mines, mine sealing and abandonment
procedures) has been satisfactorily
completed (see 40 CFR 434.11(d)).
• The term ‘‘post-mining area’’
means: (1) A reclamation area or (2) the
underground workings of an
underground coal mine after the
extraction, removal, or recovery of coal
from its natural deposit has ceased and
prior to bond release (see 40 CFR
434.11(k)).
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• The term ‘‘reclamation area’’ means
the surface area of a coal mine which
has been returned to required contour
and on which re-vegetation
(specifically, seeding or planting) work
has commenced (see 40 CFR 434.11(l)).
The study also notes that EPA has
promulgated manganese effluent
guidelines only for a subset of coal
mining operations at Part 434: (1) Active
surface and underground mining areas
with acid mine drainage discharges (see
Subpart C—Acid or Ferruginous Mine
Drainage); and (2) post-mining areas
with underground acid mine drainage
discharges (see Subpart E—Post Mining
Areas). Finally, as part of this study EPA
identified the technology basis from
prior Coal Mining effluent guidelines
rulemakings that supported the
promulgation of manganese effluent
guidelines (‘‘chemical precipitation and
settling’’) and reviewed the current
application of this technology.
EPA also reviewed scientific literature
and conducted interviews with state
regulatory personnel in order to assess
comments concerning the toxic effects
of manganese and whether coal mining
discharges of other pollutants are of
concern. EPA’s review found that
manganese discharges to surface water
may have widely varying effects
depending on water chemistry, and that
manganese impacts are not well
understood. Different aquatic species
have a wide range of tolerance limits
(see DCN 05517). The toxic effects of
manganese are chronic rather than
acute. Manganese may cause long-term
population declines through reduced
fertility and survivability. Headwaters
areas, where most Appalachian coal
mining has occurred and will continue
to occur, are especially sensitive to
manganese toxicity.
EPA clarified States’ comments
regarding the costs of EPA’s coal mining
manganese effluent guidelines. In their
initial public comments, State
commenters did not distinguish the
costs of manganese removal among the
three phases of coal mining: Active
mining areas, post-mining areas, and
post-bond release areas. This is
important as EPA’s manganese effluent
guidelines only apply to a subset of coal
mining areas. As documented in EPA’s
meetings and site visits, States indicated
that they are most concerned about the
cost of manganese treatment at surface
post-mining areas where bonds cannot
be released because water discharges
exceed permit limits (see DCN 05517).
States expressed a concern that
operators at such mines may default
rather than renew their bonds as
required every five years. States
indicated that reduced manganese
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treatment costs at such mines can
decrease the number of potential bond
forfeitures. However, EPA is not able to
address this issue through revisions to
the Coal Mining effluent guideline
because there are no manganese effluent
guidelines for surface post-mining areas.
EPA’s review of State data indicates that
these manganese effluent limits are
derived from State manganese waterquality standards or site specific best
professional judgment (BPJ) technologybased effluent limits. There are
manganese effluent guidelines for postmining areas with underground acid
mine drainage discharges. As discussed
below, EPA is not reopening those
existing effluent guidelines applicable
to underground acid mine drainage
because the record continues to indicate
that these existing guidelines are
appropriate for these discharges.
EPA reviewed the Technical
Development Documents supporting the
Coal Mining effluent guidelines and did
not identify any discussion regarding
promulgating manganese effluent
guidelines to ensure surrogate removal
of other metals (see DCN 06117). EPA’s
review of these documents showed that
EPA’s rationale for requiring manganese
control for a subset of coal mines was
to address drinking water organoleptic
effects. Additionally, EPA found no
evidence to support state and industry
comments that over-dosages or spills of
treatment chemicals have caused fish
kills and other significant stream
damage.
EPA reviewed the cost and
performance of passive treatment
systems and concluded that they are
less expensive than active treatment
systems, but their effectiveness is
generally limited to removal of
manganese from alkaline discharges. As
noted above, there are no manganese
Coal Mining effluent guidelines for
alkaline discharges for all three phases
of coal mining. As for surface postmining areas, EPA’s review of State data
indicates that manganese effluent limits
for alkaline discharges are derived from
State manganese water-quality
standards or site specific BPJ
technology-based effluent limits.
In conducting its study EPA also
reviewed the costs of manganese
treatment, which coal mining
companies use to comply with
manganese effluent limits derived from
State manganese water-quality
standards or site-specific BPJ
technology-based effluent limits. Based
on information received from the States
of Pennsylvania and West Virginia, EPA
concluded that only a small percentage
of coal mine bond forfeitures are due to
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the cost of manganese treatment (see
DCN 05517).
Overall, EPA found that there is little
potential for future forfeiture of bonds
on SMCRA permits that have been
granted during the past five years or will
be granted in the future. EPA’s analysis
indicates that forfeitures are largely a
legacy of the first decade of SMCRA
implementation during the 1980s and
early 1990s. In particular, SMCRA
requires an analysis of Probable
Hydrologic Consequence (PHC) prior to
approval of the SMCRA permit approval
in order to identify regional hydrologic
impacts associated with the coal mining
and reclamation operation. The PHC is
a determination of baseline ground
water and surface water quality and
quantity conditions and the impact the
proposed mining will have on these
baseline conditions. When potential
adverse impacts are identified (e.g., acid
mine drainage (AMD)) through use of
the PHC, appropriate protection,
mitigation, and rehabilitation plans are
developed and included in mining and
reclamation permit requirements or if
the potential adverse impacts cannot be
sufficiently mitigated the SMCRA
permit may be denied. The ultimate goal
of using the PHC in the SMCRA permit
review is to prevent acid mine drainage
(AMD) after land reclamation is
complete and the SMCRA bond is
released. PHC analytical techniques
were not sophisticated enough during
the 1980s to adequately predict AMD
and this lack of accuracy led to
inadequate controls on AMD. Science
supporting the PHC analysis has
subsequently improved to the point
where the Pennsylvania Department of
Environmental Protection anticipates
that less than 1 percent of recently
SMCRA permitted mines will develop
AMD after reclamation and bond
release.
In response to comments from the
Environmental Law and Policy Center,
which asked EPA to place more
stringent controls on manganese, TDS,
selenium, mercury, and cadmium in
coal mining discharges, EPA conducted
a literature review regarding these
pollutants in coal mining discharges. In
particular, EPA reviewed recently
initiated, long-term studies of coal
mining discharges of TDS, being
conducted by EPA Region 3 and Office
of Research and Development (see DCN
06110).
EPA is not identifying its existing
effluent guidelines for the Coal Mining
point source category (Part 434) for an
effluent guidelines rulemaking at this
time. In response to State and industry
comments, EPA’s review indicated that
manganese removal does double or
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triple treatment costs, but for active
surface and underground mining areas
with acid mine drainage discharges
(regulated by Subpart C) and postmining areas with underground acid
mine drainage discharges (regulated by
Subpart E) manganese treatment
technology is available, economically
achievable, and compliance rates with
permit limits derived from the
management effluent guidelines are
high (see DCN 05517). In response to
comments from the Environmental Law
and Policy Center, EPA did not have
sufficient information at this time to
identify this category for an effluent
guidelines rulemaking to regulate these
pollutants. Additionally, commenters
did not provide any such data for this
annual review. As with all categories
subject to existing effluent guidelines,
EPA will continue to examine the
effluent guidelines for this industrial
category in future annual reviews to
determine if revision may be
appropriate.
c. Oil and Gas Extraction (Part 435)
EPA identified the coalbed methane
(CBM) sector as a candidate for a
detailed study in the final 2006 Effluent
Guidelines Program Plan (71 FR 76656;
December 21, 2006). As part of that
announcement EPA made it clear that it
would conduct data collection through
an information collection request (ICR)
to support this detailed study. In
accordance with the Paperwork
Reduction Act (PRA) EPA must seek
Office of Management and Budget
(OMB) approval for an ICR. EPA also
provided notice of this ICR in the
preliminary 2008 Plan (72 FR 61343;
October 30, 2007) and in two separate
Federal Register notices (January 25,
2008; 73 FR 4556 and July 15, 2008; 73
FR 40757). EPA is conducting this
detailed study and data collection to
determine whether it would be
appropriate to initiate an effluent
guidelines rulemaking to control
pollutants discharged in coalbed
methane (CBM) produced water.
CBM extraction requires removal of
large amounts of water from
underground coal seams before CBM
can be released. CBM wells have a
distinctive production history
characterized by an early stage when
large amounts of water are produced to
reduce reservoir pressure which in turn
encourages release of gas. This is
followed by a stable stage when
quantities of produced gas increase as
the quantities of produced water
decrease; and a late stage when the
amount of gas produced declines and
water production remains low (see
EPA–HQ–OW–2004–0032–1904). The
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quantity and quality of water that is
produced in association with CBM
development varies from basin to basin,
within a particular basin, from coal
seam to coal seam, and over the lifetime
of a CBM well.
Pollutants often found in these
wastewaters include chloride, sodium,
sulfate, bicarbonate, fluoride, iron,
barium, magnesium, ammonia, and
arsenic. Total dissolved solids (TDS)
and electrical conductivity (EC) are bulk
parameters that States typically use for
quantifying and controlling the amount
of pollutants in CBM produced waters.
Controlling the sodicity of the CBM
produced waters is equally important in
preventing environmental damage.
Sodicity is often quantified as the
sodium adsorption ratio (SAR), which is
expressed as the ratio of sodium ions to
calcium and magnesium ions. Sodicity
is an important factor in controlling the
produced water’s suitability for
irrigation as sodic soils are subject to
severe structural degradation and
restrict plant performance through poor
soil-water and soil-air relations. All of
these dissolved inorganic parameters
can potentially affect environmental
impacts as well as potential beneficial
uses of CBM produced water.
Impacts to surface water from
discharges of CBM produced waters can
be severe depending upon the quality of
the CBM produced waters. These
discharges have variable effects
depending on the biology of the
receiving stream. Some waterbodies and
watersheds may be able to absorb the
discharged water while others are
sensitive to CBM produced water
discharges. For example, large lakes or
rivers with sufficient dilution capacity
or marine waters are less sensitive to
saline discharges than smaller receiving
water bodies. Discharge of these CBM
produced waters may also cause erosion
and in some cases irreversible soil
damage from elevated TDS
concentrations and SAR values. This
may limit future agricultural and
livestock uses of the water and
watershed.
Currently, regulatory controls for
CBM produced waters vary from State to
State and permit to permit (see EPA–
HQ–OW–2004–0032–2782, 2540). There
is very limited permit information (e.g.,
effluent limits, restrictions) in PCS and
TRI for this industrial sector.
Consequently, EPA is gathering
additional information from State
NPDES permit programs and industry
on the current regulatory controls across
the different CBM basins.
Coalbed methane (CBM) extraction
activities accounted for about 10 percent
of the total U.S. natural gas production
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in 2006 and are expanding in multiple
basins across the U.S. Currently, the
Department of Energy’s Energy
Information Administration (EIA)
expects CBM production to remain an
important source of domestic natural
gas over the next few decades.
As discussed in section A.1, EPA’s
review of existing effluent guidelines
considers four factors: pollutants
discharged in an industrial category’s
effluent, current and potential pollution
prevention and control technology
options, category growth and economic
considerations of technology options,
and implementation and efficiency
considerations of revising existing
effluent guidelines or publishing new
effluent guidelines. EPA will use the
CBM ICR to collect technical and
economic information from a wide
range of CBM operations to address
these factors in greater detail (e.g.,
geographical and geologic differences in
the characteristics of CBM produced
waters, environmental data, current
regulatory controls, availability and
affordability of treatment technology
options). Response to EPA’s
questionnaire is mandatory for
recipients and EPA will administer the
questionnaire using its authority under
Section 308 of the CWA, 33 U.S.C. 1318.
In 2007 and 2008, EPA worked with
a range of stakeholders (e.g., industry
representatives; Federal, State, and
Tribal representatives; public interest
groups and landowners; and water
treatment experts) to obtain information
on the industry and its CBM produced
water management practices. EPA’s
outreach started with teleconferences
and then continued with a series of
meetings and site visits in the major
CBM basins. In total, EPA contacted
over 700 people in eight states during
more than 60 outreach and data
collection activities in 2007 and 2008
(e.g., meetings, teleconferences, site
visits) (see EPA–HQ–OW–2006–0771–
0977 and 1124). EPA also solicited
public comment through two separate
Federal Register notices on the draft
survey and supporting statement
(January 25, 2008; 73 FR 4556 and July
15, 2008; 73 FR 40757). This outreach
helped the development of the ICR as
EPA incorporated data, comments, and
suggestions from industry and other
stakeholders into the questionnaire.
EPA intends to distribute the twophased questionnaire to industry
following OMB approval (see Section
5(d) of the ICR’s Supporting Statement,
Part A, EPA–HQ–OW–2006–0771–
1119). EPA will process the survey data
it collects and plans to present
preliminary results on available and
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affordable technology options in the
preliminary 2010 Plan.
3. Results of Further Review of
Prioritized Categories
During the 2007 annual review, EPA
identified three categories with
potentially high TWPE discharge
estimates (i.e., industrial point source
categories with existing effluent
guidelines identified with ‘‘(5)’’ in the
column entitled ‘‘Findings’’ in Table V–
1, Page 61345 of the preliminary 2008
Plan). During the 2008 annual review
EPA continued to collect and analyze
information on these three industrial
categories: Ore Mining and Dressing
(Part 440), Centralized Waste Treatment
(Part 437), and Waste Combustors (Part
444). EPA is not identifying any of these
three categories for an effluent
guidelines rulemaking in this final 2008
Plan (see Sections 6, 8, and 11 of DCN
05515). EPA concluded its preliminary
category review of the Centralized
Waste Treatment and Waste Combustors
categories in the 2008 annual review
and has determined that these categories
are no longer among those industrial
categories, currently regulated by
existing effluent guidelines, that
cumulatively comprise 95% of the
reported discharges (reported in units of
toxic-weighted pound equivalent or
TWPE) (see DCN 05515). Since these
two are not among the list of industry
categories that cumulatively comprise
95% of the reported discharges, EPA has
identified these two categories as low
priorities for effluent guideline revisions
at this time. EPA will maintain its
preliminary category review for the Ore
Mining and Dressing category in the
2009 annual review (i.e., this category is
marked with ‘‘(5)’’ in the ‘‘Findings’’
column in Table V–1 in section V.B.4 of
today’s notice). The docket
accompanying this notice presents a
summary of EPA’s findings on these
three industrial categories (see DCN
05515).
For the Ore Mining and Dressing
category (Part 440), EPA lacks sufficient
information at this time on the
magnitude of the toxic-weighted
pollutant discharges. EPA will seek
additional information on the
discharges from this category in the next
annual review in order to determine
whether a detailed study is warranted.
EPA typically performs a further
assessment of the pollutant discharges
before starting a detailed study of an
industrial category. This assessment
provides an additional level of quality
assurance on the reported pollutant
discharges and number of facilities that
represent the majority of toxic-weighted
pollutant discharges. EPA may also
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develop a preliminary list of potential
wastewater pollutant control
technologies before conducting a
detailed study. See the appropriate
section in the TSD for the final 2008
Plan (see DCN 05515) for EPA’s data
needs for these industrial categories.
For the Waste Combustors category
(Part 444), EPA used information from
TRI and PCS databases, as well as
facility contacts, in its preliminary
category review. TRI-reported
discharges of pesticides accounted for
the vast majority of the Waste
Combustors category’s TWPE identified
in the 2008 preliminary plan. EPA
contacted six waste combustor facilities
to collect information on pesticides and
received confirmation that pesticides
were not detected in combustor
wastewaters. Specifically, EPA
determined that the TRI-reported
pesticide releases from waste combustor
facilities are generally estimated using
characterization reports from clients and
treatment efficiency data, rather than
actual sampling data. Chapter 11 of the
2008 Technical Support Document for
this Plan presents more details on EPA’s
findings on the Waste Combustors
category (see DCN 05515). Based on this
review EPA is not identifying this
category for an effluent guidelines
rulemaking at this time.
For the Centralized Waste Treatment
category (Part 437), EPA also used
information from TRI and PCS
databases, as well as facility contacts, in
its preliminary category review. TRIreported discharges of pesticides
accounted for the vast majority of the
Centralized Waste Treatment category’s
TWPE identified in the 2008
preliminary plan. EPA contacted five
Centralized Waste Treatment facilities
to collect information on pesticides and
received confirmation that pesticides
were not detected in four of the five
facility wastewaters. Specifically, EPA
determined that the TRI-reported
pesticide releases from centralized
waste treatment facilities are generally
estimated using characterization reports
from clients and treatment efficiency
data, rather than actual sampling data.
Only one of the five Centralized Waste
Treatment facilities contacted detected
pesticides; however, the amount
reported to TRI was greater than the
amount actually measured. This error
will be corrected in future TRI reports
from the facility. Chapter 6 of the 2008
Technical Support Document for this
Plan presents more details on EPA’s
findings on the Centralized Waste
Treatment Category (see DCN 05515).
Based on this review EPA is not
identifying this category for an effluent
guidelines rulemaking at this time.
4. Summary of 2008 Annual Review
Findings
EPA reviewed all categories subject to
existing effluent guidelines and
pretreatment standards in order to
identify appropriate candidates for
revision. Based on this review, and in
light of effluent guidelines rulemakings
and detailed studies currently in
progress, EPA is not identifying any
existing categories for effluent
guidelines rulemaking. EPA is, however,
conducting detailed studies for three
existing categories: Steam Electric
Power Generating category, Oil and Gas
Extraction category (only to assess
whether to revise the limits to include
Coalbed Methane extraction as a new
subcategory), and unused
pharmaceutical management for the
Health Services Industry (which
includes the Hospital category).
A summary of the findings of the 2008
annual review is presented below in
Table V–1. This table uses the following
codes to describe the Agency’s findings
with respect to each existing industrial
category.
(1) Effluent guidelines or pretreatment
standards for this industrial category
were recently revised or reviewed
through an effluent guidelines
rulemaking, or a rulemaking is currently
underway.
(2) Revising the national effluent
guidelines or pretreatment standards is
not the best tool for this industrial
category because most of the toxic and
non-conventional pollutant discharges
are from one or a few facilities in this
industrial category. EPA will consider
assisting permitting authorities in
identifying pollutant control and
pollution prevention technologies for
the development of technology-based
effluent limitations by best professional
judgment (BPJ) on a facility-specific
basis.
(3) Not identified as a priority based
on data available at this time (e.g., not
among industries that cumulatively
comprise 95% of discharges as
measured in units of TWPE).
(4) EPA intends to continue a detailed
study of this industry in its 2009 annual
review to determine whether to identify
the category for effluent guidelines
rulemaking.
(5) EPA is continuing or initiating a
preliminary category review because
incomplete data are available to
determine whether to conduct a detailed
study or identify for possible revision.
EPA typically performs a further
assessment of the pollutant discharges
before starting a detailed study of the
industrial category. This assessment
provides an additional level of quality
assurance on the reported pollutant
discharges and number of facilities that
represent the majority of toxic-weighted
pollutant discharges. EPA may also
develop a preliminary list of potential
wastewater pollutant control
technologies before conducting a
detailed study. See the appropriate
section in the TSD (see DCN 05515) for
EPA’s data needs for industries with
this Finding (5).
TABLE V–1—FINDINGS FROM THE 2008 ANNUAL REVIEW OF EFFLUENT GUIDELINES AND PRETREATMENT STANDARDS
CONDUCTED UNDER SECTION 301(D), 304(B), 304(G), AND 307(B)
Industry category
(listed alphabetically)
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No.
1
2
3
4
5
6
7
8
9
.........
.........
.........
.........
.........
.........
.........
.........
.........
40 CFR part
Aluminum Forming ..................................................................................................................................
Asbestos Manufacturing ..........................................................................................................................
Battery Manufacturing .............................................................................................................................
Canned and Preserved Fruits and Vegetable Processing .....................................................................
Canned and Preserved Seafood Processing .........................................................................................
Carbon Black Manufacturing ...................................................................................................................
Cement Manufacturing ............................................................................................................................
Centralized Waste Treatment .................................................................................................................
Coal Mining .............................................................................................................................................
3 Based on available information, hospitals
consist mostly of indirect dischargers for which
EPA has not established pretreatment standards. As
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discussed in section VII.D, EPA is including
hospitals in its review of the health Services
Industry, a potential new category for pretreatment
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467
427
461
407
408
458
411
437
434
Findings*
(3)
(3)
(3)
(3)
(3)
(3)
(3)
(3)
(3)
standards. As part of that process, EPA will review
the existing effluent guidelines for the few direct
dischargers in the category.
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TABLE V–1—FINDINGS FROM THE 2008 ANNUAL REVIEW OF EFFLUENT GUIDELINES AND PRETREATMENT STANDARDS
CONDUCTED UNDER SECTION 301(D), 304(B), 304(G), AND 307(B)—Continued
Industry category
(listed alphabetically)
No.
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
26
27
28
29
30
31
32
33
34
35
36
37
38
39
40
41
42
43
44
45
46
47
48
49
50
51
52
53
54
55
56
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
.......
40 CFR part
Coil Coating .............................................................................................................................................
Concentrated Animal Feeding Operations (CAFO) ................................................................................
Concentrated Aquatic Animal Production ...............................................................................................
Copper Forming ......................................................................................................................................
Dairy Products Processing ......................................................................................................................
Electrical and Electronic Components ....................................................................................................
Electroplating ...........................................................................................................................................
Explosives Manufacturing .......................................................................................................................
Ferroalloy Manufacturing ........................................................................................................................
Fertilizer Manufacturing ...........................................................................................................................
Glass Manufacturing ...............................................................................................................................
Grain Mills ...............................................................................................................................................
Gum and Wood Chemicals .....................................................................................................................
Hospitals 3 ...............................................................................................................................................
Ink Formulating .......................................................................................................................................
Inorganic Chemicals‡ ..............................................................................................................................
Iron and Steel Manufacturing ..................................................................................................................
Landfills ...................................................................................................................................................
Leather Tanning and Finishing ...............................................................................................................
Meat and Poultry Products .....................................................................................................................
Metal Finishing ........................................................................................................................................
Metal Molding and Casting .....................................................................................................................
Metal Products and Machinery ...............................................................................................................
Mineral Mining and Processing ...............................................................................................................
Nonferrous Metals Forming and Metal Powders ....................................................................................
Nonferrous Metals Manufacturing ...........................................................................................................
Oil and Gas Extraction ............................................................................................................................
Ore Mining and Dressing ........................................................................................................................
Organic Chemicals, Plastics, and Synthetic Fibers‡ ..............................................................................
Paint Formulating ....................................................................................................................................
Paving and Roofing Materials (Tars and Asphalt) ..................................................................................
Pesticide Chemicals ................................................................................................................................
Petroleum Refining ..................................................................................................................................
Pharmaceutical Manufacturing ................................................................................................................
Phosphate Manufacturing .......................................................................................................................
Photographic ...........................................................................................................................................
Plastic Molding and Forming ..................................................................................................................
Porcelain Enameling ...............................................................................................................................
Pulp, Paper, and Paperboard .................................................................................................................
Rubber Manufacturing .............................................................................................................................
Soaps and Detergents Manufacturing ....................................................................................................
Steam Electric Power Generating ...........................................................................................................
Sugar Processing ....................................................................................................................................
Textile Mills .............................................................................................................................................
Timber Products Processing ...................................................................................................................
Transportation Equipment Cleaning .......................................................................................................
Waste Combustors ..................................................................................................................................
465
412
451
468
405
469
413
457
424
418
426
406
454
460
447
415
420
445
425
432
433
464
438
436
471
421
435
440
414
446
443
455
419
439
422
459
463
466
430
428
417
423
409
410
429
442
444
Findings*
(3)
(1)
(1)
(3)
(3)
(3)
(1)
(3)
(3)
(3)
(3)
(3)
(3)
(4)
(3)
(1) and (3)
(1)
(3)
(3)
(1)
(1)
(3)
(1)
(3)
(3)
(3)
(4)
(5)
(1) and (3)
(3)
(3)
(3)
(3)
(3)
(3)
(3)
(3)
(3)
(3)
(3)
(3)
(4)
(3)
(3)
(3)
(3)
(3)
* Note: The descriptions of the ‘‘Findings’’ codes are presented immediately prior to this table.
‡ Note: Two codes (‘‘(1)’’ and ‘‘(3)’’) are used for this category as both codes are applicable to this category and do not overlap. The first code
(‘‘(1)’’) refers to the on-going effluent guidelines rulemaking for the Chlorinated Hydrocarbon (CCH) manufacturing sector, which includes facilities
currently regulated by the OCSPF and Inorganics effluent guidelines. The second code (‘‘(3)’’) indicates that the discharges from the remaining
facilities in these two categories do not represent priorities at this time.
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VI. EPA’s 2009 Review of Existing
Effluent Guidelines and Pretreatment
Standards Under CWA Sections 301(d),
304(b), 304(g), and 307(b)
As discussed in section V and further
in section VIII, EPA is coordinating its
annual and periodic reviews of existing
effluent guidelines and pretreatment
standards under CWA sections 301(d),
304(b), 307(b) and 304(g) with the
publication of preliminary Plans and
biennial Plans under section 304(m).
Public comments received on EPA’s
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prior reviews and Plans helped the
Agency prioritize its analysis of existing
effluent guidelines and pretreatment
standards during the 2008 review. The
information gathered during the 2008
annual review, including the
identification of data gaps in the
analysis of certain categories with
existing regulations, in turn, provides a
starting point for EPA’s 2009 annual
review. See Table V–1 above. In 2009,
EPA intends to again conduct a
screening-level analysis of all 56
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categories and compare the results
against those from previous years. EPA
will also conduct more detailed
analyses of those industries that rank
high in terms of the significance of their
toxic and non-conventional discharges
among all point source categories.
Additionally, EPA intends to continue
its detailed studies of the following
categories: Steam Electric Power
Generating category, Oil and Gas
Extraction category (only to assess
whether to revise the limits to include
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Coalbed Methane extraction as a new
subcategory), and unused
pharmaceutical management for the
Health Services Industry (which
includes the Hospital category). EPA is
identifying the Ore Mining and Dressing
category for a preliminary category
review in the 2009 annual review. EPA
invites comment and data on the three
detailed studies, the preliminary
category review, and all remaining point
source categories.
As part of the 2009 annual review
EPA is also taking the opportunity to
solicit information on industrial sectors
that use water efficiency practices that
promote water efficiency, re-use, or
recycling. EPA is seeking this
information to inform its evaluation of
technology options across multiple
industrial sectors.
Water efficiency practices can reduce
the amount of pollutants discharged by
industrial facilities, especially for those
facilities that have on-site wastewater
treatment systems, but also for those
without them. EPA’s effluent guidelines
rulemakings and reviews have
documented numerous examples of
industrial facilities employing water
conservation as a means to meet effluent
limitations based on promulgated
effluent guidelines (see documents
listed in Section 12.1 of EPA–HQ–OW–
2004–0032–2783.1).
In addition, reducing water use will
also reduce associated costs (and energy
requirements) for industry. As
significant users of water, industry is
becoming aware of the importance of
measuring, managing, and controlling
water use. Water scarcity can limit
industrial growth and many industrial
sectors have substantially increased
water re-use in the past 15 years,
through reclaiming industrial
wastewater for non-potable applications
(where reclaimed industrial wastewater
is used for non-potable applications).
Moreover, the cost savings of
implementing water re-use and
reduction technologies and pollution
prevention practices can be significant,
with payback periods often measured
within a few months or years.
In addition, this data solicitation will
also help implement EPA’s National
Water Program strategy for responding
to climate change (see DCN 06114). The
National Water Program is developing a
draft strategy to identify potential
impacts of climate change for clean
water and drinking water programs and
define actions to respond to these
impacts (see Key Action #5 in DCN
06115). A March 28, 2008,
memorandum signed by the Assistant
Administrator for Water requests
comments on the draft strategy (see DCN
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06116). Section IX solicits specific
information on industrial sectors and
facilities that use model water efficiency
practices that promote water efficiency,
re-use, or recycling.
VII. EPA’s Evaluation of Categories of
Indirect Dischargers Without
Categorical Pretreatment Standards To
Identify Potential New Categories for
Pretreatment Standards
A. EPA’s Evaluation of Pass Through
and Interference of Toxic and Nonconventional Pollutants Discharged to
POTWs
All indirect dischargers are subject to
general pretreatment standards (40 CFR
403), including a prohibition on
discharges causing ‘‘pass through’’ or
‘‘interference.’’ See 40 CFR 403.5. All
POTWs with approved pretreatment
programs must develop local limits to
implement the general pretreatment
standards. All other POTWs must
develop such local limits where they
have experienced ‘‘pass through’’ or
‘‘interference’’ and such a violation is
likely to recur. There are approximately
1,500 POTWs with approved
pretreatment programs and 13,500 small
POTWs that are not required to develop
and implement pretreatment programs.
In addition, EPA establishes
technology-based national regulations,
termed ‘‘categorical pretreatment
standards,’’ for categories of industry
discharging pollutants to POTWs that
may pass through, interfere with or
otherwise be incompatible with POTW
operations. CWA section 307(b).
Generally, categorical pretreatment
standards are designed such that
wastewaters from direct and indirect
industrial dischargers are subject to
similar levels of treatment. EPA has
promulgated such pretreatment
standards for 35 industrial categories.
One of the tools traditionally used by
EPA in evaluating whether pollutants
‘‘pass through’’ a POTW, is a
comparison of the percentage of a
pollutant removed by POTWs with the
percentage of the pollutant removed by
discharging facilities applying BAT.
Pretreatment standards for existing
sources are technology based and are
analogous to BAT effluent limitations
guidelines. In most cases, EPA has
concluded that a pollutant passes
through the POTW when the median
percentage removed nationwide by
representative POTWs (those meeting
secondary treatment requirements) is
less than the median percentage
removed by facilities complying with
BAT effluent limitations guidelines for
that pollutant. This approach to the
definition of ‘‘pass through’’ satisfies
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two competing objectives set by
Congress: (1) That standards for indirect
dischargers be equivalent to standards
for direct dischargers; and (2) that the
treatment capability and performance of
POTWs be recognized and taken into
account in regulating the discharge of
pollutants from indirect dischargers.
The term ‘‘interference’’ means a
discharge which, alone or in
conjunction with a discharge or
discharges from other sources, both: (1)
Inhibits or disrupts the POTW, its
treatment processes or operations, or its
sludge processes, use or disposal; and
(2) therefore is a cause of a violation of
any requirement of the POTW’s NPDES
permit (including an increase in the
magnitude or duration of a violation) or
of the prevention of sewage sludge use
or disposal in compliance with
applicable regulations or permits. See
40 CFR 403.3(i). To determine the
potential for ‘‘interference,’’ EPA
generally evaluates the industrial
indirect discharges in terms of: (1) The
compatibility of industrial wastewaters
and domestic wastewaters (e.g., type of
pollutants discharged in industrial
wastewaters compared to pollutants
typically found in domestic
wastewaters); (2) concentrations of
pollutants discharged in industrial
wastewaters that might cause
interference with the POTW collection
system, the POTW treatment system, or
biosolids disposal options; and (3) the
potential for variable pollutant loadings
to cause interference with POTW
operations (e.g., batch discharges or slug
loadings from industrial facilities
interfering with normal POTW
operations).
If EPA determines a category of
indirect dischargers causes pass through
or interference, EPA would then
consider the BAT and BPT factors
(including ‘‘such other factors as the
Administrator deems appropriate’’)
specified in section 304(b) to determine
whether to establish pretreatment
standards for these activities. Examples
of ‘‘such other factors’’ include a
consideration of the magnitude of the
hazard posed by the pollutants
discharged as measured by: (1) The total
annual TWPE discharged by the
industrial sector; and (2) the average
TWPE discharge among facilities that
discharge to POTWs. Additionally, EPA
would consider whether other
regulatory tools (e.g., use of local limits
under Part 403) or voluntary measures
would better control the pollutant
discharges from this category of indirect
dischargers. For example, EPA relied on
a similar evaluation of ‘‘pass through
potential’’ in its prior decision not to
promulgate national categorical
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pretreatment standards for the Industrial
Laundries industry. See 64 FR 45071
(August 18, 1999). EPA noted in this
1999 final action that, ‘‘While EPA has
broad discretion to promulgate such
[national categorical pretreatment]
standards, EPA retains discretion not to
do so where the total pounds removed
do not warrant national regulation and
there is not a significant concern with
pass through and interference at the
POTW.’’ See 64 FR 45077 (August 18,
1999).
EPA reviewed TRI 2005 discharge
data in order to identify industry
categories without categorical
pretreatment standards that are
discharging pollutants to POTWs that
may pass through, interfere with or
otherwise be incompatible with POTW
operations (see DCN 05515). This
review did not identify any such
industrial categories. EPA also
evaluated stakeholder comments and
pollutant discharge information in the
previous annual reviews to inform this
review.
In particular, commenters on the 2004
and 2006 annual reviews raised
concerns about discharges of pollutants
of emerging concern such as endocrine
disruptors from health service facilities
and mercury discharges from dentists
and urged EPA to consider establishing
effluent guidelines and pretreatment
standards for such discharges. In
response to these comments, EPA
investigated the Health Services
Industry in its 2005 and 2006 annual
reviews and found that it did not have
readily available information to make an
informed decision on the potential for
‘‘pass through’’ or ‘‘interference.’’
Consequently, EPA identified this
industrial category for detailed study in
its preliminary 2006 Plan. EPA also
received stakeholder comments on the
issues of dental amalgam and unused
pharmaceuticals management for the
Health Services Industry in response to
the 2007 annual review.
As discussed below EPA is not
identifying dental facilities for an
effluent guidelines rulemaking in this
notice. However, EPA is continuing its
study of unused pharmaceutical
management for the Health Services
Industry. EPA also solicits comment and
data on all industrial sectors not
currently subject to categorical
pretreatment standards for its 2009
review. Finally, EPA solicits comment
on methods for collecting and
aggregating pollutant discharge data
collected by pretreatment programs to
further inform its future review of
industry categories without categorical
pretreatment standards.
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B. Health Services Industry
EPA identified the Health Services
Industry as a candidate for a detailed
study in the final 2006 Effluent
Guidelines Program Plan (see 71 FR
76656; December 21, 2006). The Health
Services Industry includes
establishments engaged in various
aspects of human health (e.g., hospitals,
hospices, long-term care facilities,
dentists) and animal health (e.g.,
veterinarians). Health services
establishments fall under SIC major
group 80 ‘‘Health Services’’ and
industry group 074 ‘‘Veterinary
Services.’’ According to the 2002
Census, there are over 475,000 facilities
in the Health Services Industry (see
EPA–HQ–OW–2004–0032–1615). EPA
is including the following sectors within
the Health Services Industry in its
detailed study: Offices and Clinics of
Dentists; Doctors and Mental Health
Practitioners; Nursing and Personal Care
Facilities (long-term care facilities);
Hospitals, Hospices and Clinics;
Medical Laboratories and Diagnostic
Centers; and Veterinary Care Services
(see August 29, 2005; 70 FR 51054). As
discussed below, EPA is focusing on
two main issues for these sectors within
this industry.
All these sectors require services to be
delivered by trained professionals for
the purpose of providing health care
and social assistance for individuals or
animals. These entities may be free
standing or part of a hospital or health
system and may be privately or publicly
owned. The services can include
diagnostic, preventative, cosmetic, and
curative health services.
The vast majority of establishments in
the health services industries are not
subject to categorical limitations and
standards. In 1976, EPA promulgated 40
CFR 460, which only applies to direct
discharging hospitals. Part 460 did not
establish pretreatment standards for
indirect discharging facilities.
In evaluating the health services
industries to date, EPA has found little
readily available information from EPA
databases. Both PCS and TRI contain
sparse information on health care
service establishments. For 2002, PCS
only has data for two facilities that are
considered ‘‘major’’ sources of
pollutants, and only Federal facilities in
the healthcare industry are required to
report to TRI.
Based on preliminary information,
major pollutants of concern in
discharges from health care service
establishments include solvents,
mercury, pharmaceuticals, and
biohazards (e.g., items contaminated
with blood) (see EPA–HQ–OW–2004–
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53233
0032–0729). The majority of the
mercury originates from the following
sources: Amalgam used in dental
facilities and medical equipment,
laboratory reagents, and cleaning
supplies used in healthcare facilities
(see EPA–HQ–OW 2004 0032 0038 and
2391). EPA found little to no
quantitative information on wastewater
discharges of pollutants of emerging
concern such as pharmaceuticals but
was able to identify some information
on biohazards (see DCN EPA–HQ–OW–
2006–0771–0533).
As described above, the Health
Services Industry is expansive and
contains approximately half a million
facilities. Because of the size and
diversity of this category and other
resource constraints, EPA decided to
focus its detailed study on certain types
of dischargers. EPA selected its focus
areas, for the most part, to respond to
stakeholder concerns. The focus areas
are:
• Dental mercury: EPA focused its
evaluation on mercury discharges from
the offices and clinics of dentists due to
the potential hazard and
bioaccumulative properties associated
with mercury.
• Unused pharmaceuticals: EPA is
focusing its evaluation on the
management of unused or leftover
pharmaceuticals from health service
facilities due to the growing concern
over the discharge of pharmaceuticals
into water and the potential
environmental effects.
1. Dental Mercury
The Agency notes that it has an
overall interest in mercury reduction
and on July 5, 2006, issued a report
titled, ‘‘EPA’s Roadmap for Mercury,’’
(see EPA–HQ–OW–2004–0032–1612).
Among other things, EPA’s report
highlights mercury sources and
describes progress to date in addressing
mercury sources. As part of the 2008
Health Services Industry detailed study,
EPA researched the following questions/
topics for the 2008 final plan as they
relate to disposal of mercury into
municipal sewer systems:
• What are current industry practices
regarding the mercury disposal? To
what extent are each of these practices
applied? What factors drive current
practices?
• Are there federal, state, or local
requirements or guidance for disposal of
mercury? What are these requirements?
• How are control authorities
currently controlling (or not controlling)
disposal of mercury via wastewater?
• To what extent do POTWs report
pass through or interference problems
related to mercury discharges?
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• What technologies are available: (1)
As alternatives to wastewater disposal;
and (2) to control pollutant discharges.
Is there any qualitative or quantitative
information on their efficiency?
• What Best Management Practices
(BMPs) are used as alternatives to
wastewater disposal and/or to control
discharges and is there any qualitative
or quantitative information on their
efficiency?
• Is there any quantitative or
qualitative information on the costs
associated with identified technologies
and/or BMPs?
Across the United States, many States
and municipal wastewater treatment
plants (publicly owned treatment
works—POTWs) are working toward the
goal of reducing discharges of mercury
into collection systems. Many studies
have been conducted in an attempt to
identify the sources of mercury entering
these collection systems. According to
the 2002 Mercury Source Control and
Pollution Prevention Program Final
Report prepared for the National
Association of Clean Water Agencies
(NACWA), dental clinics are the main
source of mercury discharges to POTWs.
The American Dental Association
(ADA) estimated in 2003 that up to 50%
of mercury entering POTWs was
contributed by dental offices (see DCN
04698).
EPA estimates there are
approximately 160,000 dentists working
in 120,000 dental offices that use or
remove amalgam in the United States—
almost all of which discharge their
wastewater exclusively to POTWs.
Mercury in dental wastewater originates
from waste particles associated with the
placement and removal of amalgam
fillings. Most dental offices currently
use some type of basic filtration system
to reduce the amount of mercury solids
passing into the sewer system. However,
best management practices and the
installation of amalgam separators,
which generally have a removal
efficiency of 95%, have been shown to
reduce discharges even further. A recent
study funded by NACWA (see DCN
04225) concluded that the use of
amalgam separators results in
reductions in POTW influent
concentrations and biosolids mercury
concentrations. Use of amalgam
separators does not always result in
reductions in POTW effluent, however,
since most amalgam particles are
removed with biosolids. Mercury that
partitions to wastewater sludge may be
incinerated or disposed to a landfill.
States, Regions, and localities have
implemented mandatory and voluntary
programs to reduce dental mercury
discharges. Specifically, 11 states and at
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least 19 localities have mandatory
pretreatment programs that require the
use of dental mercury amalgam
separators (see DCN 05518).
Additionally, at least 20 POTWs have
voluntary programs to reduce mercury
discharges from dental offices. Success
rates for these voluntary programs vary
greatly, and are usually higher when
there is a mandatory ‘‘second phase’’ to
the voluntary program. EPA Region 5
published guidance for permitting
dental mercury discharges (see EPA–
HQ–OW–2006–0771–0460). The ADA
has also adopted and published best
management practices for its members.
On October 2, 2007, the ADA updated
its best management practices to include
the use of amalgam separators (see EPA–
HQ–OW–2006–0771–0211). The
document titled ‘‘Health Services
Industry Detailed Study: Dental
Amalgam,’’ compiles the information
EPA has collected to date on existing
guidance and requirements for dental
mercury (see DCN 05518).
In 2007 and 2008, EPA focused its
efforts on collecting and compiling
information on current mercury
discharges from dental offices, best
management practices (BMPs), and
amalgam separators. For amalgam
separators, EPA looked at the frequency
with which they are currently used;
their effectiveness in reducing
discharges to POTWs; and the capital
and annual costs associated with their
installation and operation (see DCN
05518). EPA also conducted a POTW
pass-through analysis on mercury for
the industry.
EPA received comments from 32
stakeholders on the preliminary 2008
Plan. Most commenters were from
pretreatment programs that provided
useful information on their mandatory
and voluntary pretreatment programs
that include the use of amalgam
separators. EPA used this information to
update its final report on management
and best practices for the control of
dental mercury (see DCN 05518). ADA
and NACWA commented that although
they do not support development of
national pretreatment standards, they
are willing to work with one another
and EPA to increase the use of amalgam
separators by dental facilities. EPA is
exploring options with ADA and
NACWA to promote the use of amalgam
separators.
In response to mercury water quality
and pollution prevention concerns,
there is progress at the State and local
level as amalgam separators and other
BMPs are increasingly being mandated
by States and local governments. ADA’s
recently revised BMPs will likely help
in convincing dentists to install
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amalgam separators and employ other
BMPs to recover dental amalgam and
prevent the discharge of mercury to
POTWs. This will help POTWs reduce
the amount of mercury in their biosolids
and the potential for mercury emissions
when biosolids are incinerated.
Additionally, due to mercury-free
fillings and improved overall dental
health, the use of mercury in dentistry
is decreasing in the U.S. (see DCN
05518).
At this time EPA is not identifying
this sector for an effluent guidelines
rulemaking. As previously noted above,
industrial categories demonstrating
significant progress through voluntary
efforts to reduce hazard to human health
or the environment associated with their
effluent discharges are a lower priority
for effluent guidelines or pretreatment
standards revision, particularly where
such reductions are achieved by a
significant majority of individual
facilities in the industry. As an example,
in the final 2006 Plan EPA relied on a
national voluntary partnership program
for the industrial laundries sector as a
factor in not identifying the industrial
laundries sector for an effluent
guidelines rulemaking (see EPA–HQ–
OW–2004–0032–2782, Section 19.9). In
future annual reviews, EPA will
continue to examine the percentage of
dentists using amalgam separators and
their effectiveness at recovering dental
amalgam and reducing mercury
discharges to POTWs. EPA notes ADA’s
recent positive step in revising their
BMPs to include the recommendation
for dentists to use amalgam separators.
In particular, EPA will examine whether
a significant majority of dentists are
utilizing amalgam separators. After such
examination, EPA may re-evaluate its
current view not to initiate an effluent
guidelines rulemaking for this sector.
2. Unused Pharmaceuticals
To date, scientists have identified
more than 160 pharmaceutical
compounds at discernable
concentrations in our nation’s rivers,
lakes, and streams (see Section 3 of DCN
05519). To address this issue at the
source, EPA is studying how the drugs
are entering our waterways and what
factors contribute to the current
situation. Towards this end, EPA
initiated a study on pharmaceutical
disposal practices at health care
facilities, such as hospitals, hospices,
long-term care facilities, and veterinary
hospitals. Unused pharmaceuticals
include dispensed prescriptions that
patients do not use as well as materials
that are beyond their expiration dates.
Another potential source of unused
pharmaceuticals is the residuals
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remaining in used and partially used
dispensers, containers, and devices.
Many of these dispensers, containers,
and devices are bulky and are likely not
disposed to the sewer as they could
create blockages in the sewer; however,
some might be sewered (e.g., medical
patches). As a point of clarification, the
term ‘‘unused pharmaceuticals’’ does
not include excreted pharmaceuticals.
For many years, a standard practice at
many health care facilities was to
dispose of unused pharmaceuticals by
flushing them down the toilet or drain.
Through this study, EPA seeks to
investigate the following questions:
• What are the current industry
practices for disposing of unused
pharmaceuticals?
• Which pharmaceuticals are being
disposed of and at what quantities?
• What are the options for disposing
of unused pharmaceuticals other than
down the drain or toilet?
• What factors influence disposal
decisions?
• Do disposal practices differ within
industry sectors?
• What Best Management Practices
(BMPs) could facilities implement to
reduce the generation of unused
pharmaceuticals?
• What reductions in the quantities of
pharmaceuticals discharged to POTWs
would be achieved by implementing
BMPs or alternative disposal methods?
• What are the costs of current
disposal practices compared to the costs
of implementing BMPs or alternative
disposal methods?
In a related effort, EPA also seeks to
determine the effectiveness with which
publicly-owned treatment works
(POTWs) can remove pharmaceuticals
from incoming sewage. Upon
completion of the health services study,
EPA hopes to understand what factors
contribute to unused pharmaceutical
disposal methods at health service
facilities and which disposal methods
represent best practices to minimize
environmental impacts.
To date, EPA has completed an
interim study of the health services
industry (see DCN 05519). To gather
data for the study, EPA completed site
visits to two hospitals and a
pharmaceutical reverse distributor;
investigated secondary data sources
such as existing institutional surveys on
disposal practices; and conducted a
series of meetings and teleconferences
with other Federal agencies and health
care stakeholder groups.
The study focused on hospitals and
long-term care facilities (LTCFs) because
these facilities are likely responsible for
the largest amounts of unused
pharmaceuticals being disposed into
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sewage collection systems within this
industry sector. In 2005, there were
about 7,000 hospitals and 35,000 LTCFs
in the United States (see DCN 05519).
EPA’s four preliminary findings
include:
(1) Federal, state, and local laws and
regulations often require special
handling of pharmaceutical waste.
These laws and regulations can
influence the options hospitals and
long-term care facilities have for
disposing of unused pharmaceuticals.
• Some federal regulations may
inadvertently encourage disposal of
unused pharmaceuticals via the sewer.
The Controlled Substances Act (CSA),
enforced by the Drug Enforcement
Administration (DEA), establishes a
closed distribution system for controlled
substances. The CSA prohibits the
return of controlled substances from
end-users to any person except, in
certain cases, a law-enforcement agent
and CSA registrants. Disposal of
controlled substances by CSA
registrants is carefully regulated to
ensure that the substance is destroyed or
rendered unrecoverable. One acceptable
method of destruction is witnessed
disposal of controlled substances in a
drain or toilet.
• Some unused pharmaceuticals are
regulated as hazardous wastes and
subject to the nation’s hazardous waste
disposal requirements. Pharmaceutical
wastes may be hazardous waste (under
the Resource Conservation and
Recovery Act (RCRA)) if they are: (1) the
pharmaceutical or its sole active
ingredient is specifically listed in 40
CFR part 261.33(e) or (f) (commonly
referred to as the P or U lists,
respectively); and/or (2) the waste
exhibits one or more characteristics of
hazardous waste (ignitability,
corrosivity, reactivity, or toxicity as
defined in 40 CFR parts 261.21–24,
respectively). Common pharmaceutical
wastes that are RCRA hazardous waste
when disposed of include epinephrine,
nitroglycerin, warfarin, nicotine, and
some chemotherapeutic agents.4
Healthcare facilities must determine if
these wastes are RCRA hazardous
wastes, and if so, must comply with all
applicable RCRA Subtitle C
requirements, including many special
4 The Agency clarified its regulation at 40 CFR
261.33, explaining that epinephrine salts are not
included in the epinephrine P042 listing (since the
listing only specifies epinephrine and not
epinephrine salts); the salts, therefore, would be
hazardous only if the waste epinephrine salt
exhibited one or more of the hazardous waste
characteristics (see ‘‘Scope of Hazardous Waste
Listing P042 (Epinephrine),’’ October 15, 2007,
RCRA Online# 14778)’’
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handling and transportation
requirements.
• State regulations vary widely and
influence disposal practices. State
regulations of the disposal of unused
pharmaceuticals and controlled
substances vary widely (see DCNs 04952
and 04953). Many state regulations
require both hospitals and LTCFs to
destroy unused pharmaceuticals but
often do not specify the process of
destruction; however, many states (33
states according to DCN 04953) have
requirements for the types of facility
personnel required to conduct and
oversee the destruction. Some states
have hazardous waste regulations that
are more stringent than EPA (see DCN
04944). For example, some wastes are
regulated as hazardous under state law
but not RCRA (see Table 4–1 of DCN
05519). State regulations for reuse of
medications vary widely. Many states
allow re-use of uncontaminated
pharmaceuticals (excluding controlled
substances) that have been in a
controlled environment, such as an
automatic dispensing system (see DCN
04952). At least five states strictly
prohibit hospitals and LTCFs from
reusing pharmaceuticals entirely. These
states include Arizona, Kentucky,
Mississippi, New Mexico, and Texas.
California allows county health
departments to collect unused
pharmaceuticals from LTCFs,
wholesalers, and manufacturers and
redistribute them for dispensing to the
uninsured poor. Some State Medicare
and Medicaid requirements often deter
LTCFs from donating or redistributing
their unused medications (see DCN
05961).
• Medicare and Medicaid
requirements also influence hospital
disposal practices. The Centers for
Medicare and Medicaid Services (CMS),
the federal agency within the
Department of Health and Human
Services, administers the Medicare and
Medicaid programs. Medicare provides
health insurance to elderly and disabled
Americans, while Medicaid provides
health insurance for low income
Americans, including long-term care
coverage (see DCN 05074). In a March
22, 2006 letter, CMS provided guidance
to State Medicaid programs encouraging
states to require LTCFs to return unused
medications to pharmacies and to
ensure Medicaid is repaid for unused
treatments when nursing home patients
die, are discharged, or have their
prescriptions changed. In addition,
some state Medicaid programs require
LTC pharmacies to accept returned
unused pharmaceuticals (excluding
controlled substances) from LTCFs. The
LTC pharmacy then credits Medicaid for
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the unused doses. However, LTC
pharmacies typically receive little
payment for these return services and
have not found them to be cost effective.
For example, when a pharmacy takes
back a previously dispensed medication
for disposal, it must pay to have the
medication destroyed, but it is not
compensated for this service (see DCN
04952). Therefore, few LTC pharmacies
participate in these programs.
(2) Organization size, ease and access
of disposal, and cost are also factors
influencing the disposal of unused
pharmaceuticals.
Some facilities use flushing to sewers
as a primary means of disposal since it
is both easy and complies with CSA
requirements for destruction. Facilities
are most likely to flush pharmaceuticals
if they do not have an on-site pharmacy
and/or do not have a pre-existing
contract with a hazardous waste hauler
to dispose of the pharmaceuticals. In the
past, public health agencies and healthrelated non-government organizations
guided the public to destroy unused
medications by flushing them down the
toilet. Many LTCFs have adopted this
method for destruction of unused
controlled substances. Many LTCFs
have also extended this practice to
include flushing all unused
medications—controlled and non
controlled substances (see EPA-HQOW–2006–0771–0851).
(3) Fewer disposal opportunities exist
for long-term care facilities because they
are often not CSA registrants and cannot
generally return pharmaceuticals to the
manufacturer or use reverse distributors.
Hospitals typically have on-site
pharmacies. It is common practice at
hospitals to return some unused
pharmaceuticals to the hospital
pharmacy and then on to the
manufacturer for credit or disposal.
However, this option extends only to
those pharmaceuticals for which the
hospital can receive credit and does not
include unused pharmaceuticals that
are considered waste (e.g.,
pharmaceuticals in an intravenous bag,
drug samples brought into the hospital).
Also, hospitals typically do not
prescribe medication far in advance or
in large quantities. As a result, the
potential for pharmaceuticals to be
wasted is reduced. In addition, hospitals
typically have pre-existing arrangements
for disposal of unused pharmaceuticals
as hazardous waste (see EPA-HQ-OW–
2006–0771–0851).
(4) Best management practices, if
widely implemented, have the potential
to reduce the amount of unused
pharmaceuticals entering our nation’s
waters from disposal.
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Three organizations provide guidance
in the form of Best Management
Practices (BMPs) to medical facilities on
managing pharmaceutical waste:
Hospitals for a Healthy Environment
(H2E), Product Stewardship Institute
(PSI), and Joint Commission on
Accreditation of Healthcare
Organizations (JCAHO). The guidelines
provided by these organizations all aim
to reduce health and environmental
impacts due to current disposal
practices of pharmaceutical waste, as
discussed in Section 5.2 of the Interim
Technical Report (see DCN 05519).
Examples of model BMPs identified to
date include waste minimization and
reverse distribution systems used by
hospitals in California, Minnesota, and
Washington. Waste minimization
techniques include maintaining
inventories of high-use pharmaceuticals
and identifying those that are close to
expiring. Short-dated pharmaceuticals
are redistributed to other areas of the
hospitals where they are needed. Also,
dispensed pharmaceuticals can go
unused at a hospital or LTCF if the
patient has an allergic or adverse
reaction to the medication, no longer
requires treatment, refuses treatment, or
the medication expires. Hospitals and
LTCFs can reduce the amount of
pharmaceutical waste generated by
limiting the amount of pharmaceuticals
dispensed to patients and residents at
one time. This can be accomplished by
using unit dose packaging, limited
quantity dispensing, automatic
dispensing systems, and standardized
medication dosages, as discussed in
Section 5.2 of the Interim Technical
Report (see DCN 05519). Hospitals and
LTCFs have the option of hiring reverse
distributors to manage their unused
and/or expired medication that the
facility believes could be returned to the
manufacturer or wholesaler for credit.
The reverse distributor determines
which medications may be returned to
the manufacturer or wholesaler for
credit and arranges for disposal of
unused medications that are waste.
However, there are CSA limitations for
reverse distributors and controlled
substances. In most cases, reverse
distributors cannot handle controlled
substances.
EPA is concerned about
pharmaceuticals in the environment and
is working on this issue in many
different areas. Over the last few years,
EPA has increased its work in a number
of areas to better understand
pharmaceuticals. EPA has an overall
strategy to address the risks associated
with emerging contaminants. This fourpronged strategy is aimed at improving
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science, improving public
understanding, identifying partnership
and stewardship opportunities, and
taking regulatory action as appropriate.
We are focused on learning more about
the occurrence and health effects of
pharmaceuticals in water. In addition,
we are working to better understand
what treatment technologies may
remove them from wastewater and
drinking water. We are developing
analytical methods to improve detection
capabilities. We are conducting national
studies and surveys to help direct our
course of action. We are also partnering
with government agencies, stakeholders,
and the private sector, and increasing
public awareness about product
stewardship and pollution prevention
(see DCN 06111). Additionally, the
Agency is considering amending its
hazardous waste regulations to add
hazardous pharmaceutical wastes to the
universal waste system to facilitate its
oversight of the disposal of
pharmaceutical waste (40 CFR 273) (see
RIN 2050–AG39, April 30, 2007; 72 FR
23170). In addition, the inclusion of
hazardous pharmaceutical wastes in the
universal waste rule may encourage
health care facilities to manage all their
pharmaceutical wastes as universal
wastes, even wastes that are not
regulated as hazardous but which
nonetheless pose hazards. Finally, EPA
has identified the issue of
pharmaceuticals in wastewater is part of
the Agency’s Strategic Plan (2006–2011)
to meet its goals of clean and safe
water.5
EPA continues to study the issue of
how health care facilities are managing
and disposing of unused
pharmaceuticals and POTW treatment
effectiveness in an effort to identify the
root cause and potential solutions to
address the issue of pharmaceuticals in
our waterways. Over the coming year,
EPA will need to gather more technical
and economic information on unused
pharmaceutical management in the
Health Services Industry. To aid its
decision-making, EPA intends to submit
an Information Collection Request (ICR)
to the Office of Management and Budget
(OMB) for their review and approval
under the Paperwork Reduction Act
(PRA), 33 U.S.C. 3501, et seq., during
the 2009 annual review. EPA will use
this ICR to collect technical and
economic information on unused
pharmaceutical management and
identify technologies and BMPs that
reduce or eliminate the discharge of
unused pharmaceuticals to POTWs. In
designing this industry survey EPA
5 See ‘‘2006–2011 EPA Strategic Plan,’’ https://
www.epa.gov/ocfo/plan/plan.htm.
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expects to work closely with industry
representatives from hospitals, hospices,
long-term care facilities, veterinary
hospitals and other affected
stakeholders. EPA has published a
separate Federal Register notice for this
ICR and solicits comment on the
potential scope of this ICR (see August
12, 2008; 73 FR 46903).
EPA also plans to conduct additional
site visits to facilities to obtain more
detailed information on how
pharmaceuticals are managed, tracked,
and disposed as well as influences on
behavior. In addition, EPA is
considering collecting data from other
types of health care facilities (e.g.,
medical and dental offices, university
and prison health clinics, and veterinary
clinics). EPA is also reviewing studies
on POTW effectiveness. EPA remains
concerned about this issue and plans to
expedite completion of this study.
VIII. The Final 2008 Effluent
Guidelines Program Plan Under Section
304(m)
In accordance with CWA section
304(m)(2), EPA published the
preliminary 2008 Plan for public
comment prior to this publication of the
final 2008 Plan. See October 30, 2007
(72 FR 61335). The Agency received 32
comments from a variety of commenters
including industry and industry trade
associations, municipalities and
sewerage agencies, environmental
groups, and State government agencies.
Many of these public comments are
discussed in this notice. The Docket
accompanying this notice includes a
complete set of all of the comments
submitted, as well as the Agency’s
responses (see DCN 06109). EPA
carefully considered all public
comments and information submitted to
EPA in developing the final 2008 Plan.
A. EPA’s Schedule for Annual Review
and Revision of Existing Effluent
Guidelines Under Section 304(b)
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1. Schedule for 2007 and 2008 Annual
Reviews Under Section 304(b)
As noted in section IV.B, CWA
section 304(m)(1)(A) requires EPA to
publish a Plan every two years that
establishes a schedule for the annual
review and revision, in accordance with
section 304(b), of the effluent guidelines
that EPA has promulgated under that
section. This final 2008 Plan announces
EPA’s schedule for performing its
section 304(b) reviews. The schedule is
as follows: EPA will coordinate its
annual review of existing effluent
guidelines under section 304(b) with its
publication of the preliminary and final
Plans under CWA section 304(m). In
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other words, in odd-numbered years,
EPA intends to complete its annual
review upon publication of the
preliminary Plan that EPA must publish
for public review and comment under
CWA section 304(m)(2). In evennumbered years, EPA intends to
complete its annual review upon the
publication of the final Plan. EPA’s 2008
annual review is the review cycle
ending upon the publication of this final
2008 Plan.
EPA is coordinating its annual
reviews under section 304(b) with
publication of Plans under section
304(m) for several reasons. First, the
annual review is inextricably linked to
the planning effort, because the results
of each annual review can inform the
content of the preliminary and final
Plans, e.g., by identifying candidates for
effluent guidelines revision for which
EPA can schedule rulemaking in the
Plan, or by calling to EPA’s attention
point source categories for which EPA
has not promulgated effluent guidelines.
Second, even though not required to do
so under either section 304(b) or section
304(m), EPA believes that the public
interest is served by periodically
presenting to the public a description of
each annual review (including the
review process employed) and the
results of the review. Doing so at the
same time EPA publishes preliminary
and final plans makes both processes
more transparent. Third, by requiring
EPA to review all existing effluent
guidelines each year, Congress appears
to have intended that each successive
review would build upon the results of
earlier reviews. Therefore, by describing
the 2008 annual review along with the
final 2008 Plan, EPA hopes to gather
and receive data and information that
will inform its reviews for 2009 and
2010 and the final 2010 Plan.
2. Schedule for Possible Revision of
Effluent Guidelines Promulgated Under
Section 304(b)
EPA is currently conducting
rulemakings to potentially revise
existing effluent guidelines and
pretreatment standards for three
categories. For the Organic Chemicals,
Plastics and Synthetic Fibers (OCPSF)
and Inorganic Chemicals categories, the
effluent guidelines rulemaking is
focused on discharges from Vinyl
Chloride and Chlor-Alkali facilities.
EPA first identified this effluent
guidelines rulemaking in the final 2004
Plan and refers to it as the ‘‘Chlorine
and Chlorinated Hydrocarbon (CCH)
manufacturing’’ rulemaking. EPA
emphasizes that identification of the
rulemaking schedules for these effluent
guidelines does not constitute a final
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53237
decision to revise the guidelines. EPA
may conclude at the end of the formal
rulemaking process—supported by an
administrative record and following an
opportunity for public comment—that
effluent guidelines revisions are not
appropriate for these categories. EPA is
not scheduling any other existing
effluent guidelines for rulemaking at
this time.
B. Identification of Potential New Point
Source Categories Under CWA Section
304(m)(1)(B)
The final Plan must also identify
categories of sources discharging toxic
or non-conventional pollutants for
which EPA has not published effluent
limitations guidelines under section
304(b)(2) or new source performance
standards (NSPS) under section 306. See
CWA section 304(m)(1)(B). The final
Plan must also establish a schedule for
the promulgation of effluent guidelines
for the categories identified under
section 304(m)(1)(B), providing for final
action on such rulemaking not later than
three years after the identification of the
category in a final Plan.6 See CWA
section 304(m)(1)(C).
EPA is currently conducting effluent
guidelines rulemakings for two potential
new categories (see September 2, 2004;
69 FR 53705). One of these categories—
Airport Deicing Operations—was
identified as a potential new category in
the final 2004 Plan. EPA plans to
propose these effluent guidelines for
Airport Deicing Operations later this
calendar year. EPA initiated new
rulemaking for the other category—
Construction and Development—
because it was directed to do so by a
district court order. Natural Resources
Defense Council et al. v. U.S.
Environmental Protection Agency, No.
04–8307, order (C.D. Ca. December 6,
2006). EPA disagrees with the district
court’s decision and an appeal is
currently pending before the Ninth
Circuit; however, in order to comply
with the district court’s order EPA is
conducting the rulemaking ordered by
the court. The district court order
requires EPA to propose a rule by
December 1, 2008 and finalize it by
December 1, 2009. EPA expects to meet
this court order with the publication of
6 EPA recognizes that one court—the U.S. District
Court for the Central District of California—has
found that EPA has a duty to promulgate effluent
guidelines within three years for new categories
identified in the Plan. See NRDC et al. v. EPA, 437
F.Supp.2d 1137 (C.D. Ca. 2006). However, an
appeal is currently pending before the Ninth Circuit
and EPA continues to believe that the mandatory
duty under section 304(m)(1)(c) is limited to
mandating a schedule for concluding the effluent
guidelines rulemaking—not for promulgating new
effluent guidelines—within three years.
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the proposed rule for Construction and
Development no later than December 1,
2008 and publication of the final rule
one year later.
For the reasons discussed below, EPA
is not identifying any potential new
category for effluent guidelines
rulemaking. Therefore, EPA is not
scheduling effluent guidelines
rulemaking for any category is this final
Plan. In the 2004 Plan, EPA announced
that it would begin development of a
regulation to control the pollutants
discharged from drinking water
treatment plants. See 69 FR 53720
(September 2, 2004). Based on
preliminary study and on public
comments, EPA was interested in the
potential volume of discharges
associated with drinking water facilities.
The preliminary data were not
conclusive, and the Agency proceeded
with additional study and analysis of
treatability, including an industry
survey. The additional analysis
included extensive information about
the industry, its treatment residuals,
wastewater treatment options, and
discharge characteristics. EPA is
evaluating a range of effluent guidelines
priorities, including court-mandated
actions, and plans to make a decision
shortly on whether to continue work on
this rulemaking.
In order to identify industries not
currently subject to effluent guidelines,
EPA primarily used data from TRI and
PCS. Facilities with data in TRI and PCS
are identified by a four-digit SIC code
(see DCN 05515). EPA performed a
crosswalk between the TRI and PCS
data, identified with the four-digit SIC
code, and the 56 point source categories
with effluent guidelines or pretreatment
standards to determine if a four-digit
SIC code is currently regulated by
existing effluent guidelines (see DCN
05515). EPA also relied on comments
received on its previous 304(m) plans to
identify potential new categories. EPA
then assessed whether these industrial
sectors not currently regulated by
effluent guidelines meet the criteria
specified in section 304(m)(1)(B), as
discussed below (see DCN 06112). EPA
notes that the Ninth Circuit has recently
held that the precise number and kind
of categories identified by EPA in its
304(m) planning process is
discretionary with the Administrator.
Our Children’s Earth v. EPA, 527F.3d
842, 852 (9th Cir. 2008).
The first criterion for identifying
industries under section 304(m)(1)(B) is
whether they are ‘‘categories of sources’’
for which EPA has not promulgated
effluent guidelines. Because this section
does not define the term ‘‘categories,’’
EPA interprets this term based on the
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use of the term in other sections of the
Clean Water Act, legislative history, and
Supreme Court case law, and in light of
longstanding Agency practice. These
sources indicate that the term
‘‘categories’’ refers to an industry as a
whole based on similarity of product
produced or service provided, and is not
meant to refer to specific industrial
activities or processes involved in
generating the product or service. EPA
therefore identifies in its biennial Plan
only those new industries that it
determines are properly considered
stand-alone ‘‘categories’’ within the
meaning of the Act—not those that are
properly considered potential new
subcategories of existing categories
based on similarity of product or
service.
EPA’s interpretation of the term
‘‘categories’’ is consistent with
longstanding Agency practice. Pursuant
to CWA section 304(b), which requires
EPA to establish effluent guidelines for
‘‘classes and categories of point
sources,’’ EPA has promulgated effluent
guidelines for 56 industrial
‘‘categories.’’ Each of these ‘‘categories’’
consists of a broad array of facilities that
produce a similar product or perform a
similar service—and is broken down
into smaller subsets, termed
‘‘subcategories,’’ that reflect variations
in the processes, treatment technologies,
costs and other factors associated with
the production of that product that EPA
is required to consider in establishing
effluent guidelines under section 304(b).
For example, the ‘‘Pulp, Paper and
Paperboard point source category’’ (40
CFR part 430) encompasses a diverse
range of industrial facilities involved in
the manufacture of a like product
(paper); the facilities range from mills
that produce the raw material (pulp) to
facilities that manufacture end-products
such as newsprint or tissue paper. EPA’s
classification of this ‘‘industry by major
production processes used many of the
statutory factors set forth in CWA
Section 304(b), including manufacturing
processes and equipment (e.g.,
chemical, mechanical, and secondary
fiber pulping; pulp bleaching; paper
making); raw materials (e.g., wood,
secondary fiber, non-wood fiber,
purchased pulp); products
manufactured (e.g., unbleached pulp,
bleached pulp, finished paper
products); and, to a large extent,
untreated and treated wastewater
characteristics (e.g., BOD loadings,
presence of toxic chlorinated
compounds from pulp bleaching) and
process water usage and discharge
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rates.’’ 7 Each subcategory reflects
differences in the pollutant discharges
and treatment technologies associated
with each process. Similarly, the ‘‘Iron
and Steel Manufacturing point source
category’’ (40 CFR part 420) consists of
various subcategories that reflect the
diverse range of processes involved in
the manufacture of iron and steel,
ranging from facilities that make the
basic fuel used in the smelting of iron
ore (subpart A—Cokemaking) to those
that cast the molten steel into molds to
form steel products (subpart F—
Continuous Casting). An example of an
industry category based on similarity of
service provided is the Transportation
Equipment Cleaning Point Source
Category (40 CFR Part 442), which is
subcategorized based on the type of tank
(e.g., rail cars, trucks, barges) or cargo
transported by the tanks cleaned by
these facilities, reflecting variations in
wastewaters and treatment technologies
associated with each.
The second criterion EPA considers
when implementing section
304(m)(1)(B) also derives from the plain
text of that section. By its terms, CWA
section 304(m)(1)(B) applies only to
industrial categories to which effluent
guidelines under section 304(b)(2) or
section 306 would apply, if
promulgated. Therefore, for purposes of
section 304(m)(1)(B), EPA would not
identify in the biennial Plan any
industrial categories comprised
exclusively or almost exclusively of
indirect discharging facilities regulated
under section 307.
Third, CWA section 304(m)(1)(B)
applies only to industrial categories of
sources that discharge toxic or nonconventional pollutants to waters of the
United States. EPA therefore did not
identify in the Plan industrial activities
for which conventional pollutants,
rather than toxic or non-conventional
pollutants, are the pollutants of concern.
In addition, even when toxic and nonconventional pollutants might be
present in an industrial category’s
discharge, section 304(m)(1)(B) does not
apply when those discharges occur in
trivial amounts. This decision criterion
leads EPA to focus on those remaining
industrial categories where, based on
currently available information, new
effluent guidelines have the potential to
address a non-trivial discharge of toxic
or non-conventional pollutants.
Finally, EPA interprets section
304(m)(1)(B) to give EPA the discretion
to identify in the Plan only those
7 U.S. EPA, 1997. Supplemental Technical
Development Document for Effluent Limitations
Guidelines and Standards for the Pulp, Paper, and
Paperboard Category, Page 5–3, EPA–821–R–97–
011, October 1997.
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potential new categories for which an
effluent guidelines rulemaking may be
an appropriate tool for controlling
discharges. Therefore, EPA does not
identify in the Plan all potential new
categories discharging toxic and nonconventional pollutants. Rather, EPA
identifies only those potential new
categories for which it believes that
effluent guidelines may be appropriate,
taking into account Agency priorities,
resources and the full range of other
CWA tools available for addressing
industrial discharges.
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IX. Request for Comment and
Information
A. EPA Requests Information on the
Steam Electric Power Generating
Category (Part 423)
EPA solicits public comments on the
following areas of interest to support the
Steam Electric Power Generating
Detailed Study.
• Treatment technologies for
wastewaters from wet FGD systems. EPA
solicits information and data regarding
the costs and performance of treatment
technologies for wastewater from wet
FGD systems. Treatment technologies of
interest include, but are not limited to,
chemical precipitation, biological
systems, evaporation/brine
concentration zero liquid discharge,
underground injection, and complete
recycle. Both capital and annual
operations and maintenance costs are
requested, as well as information on key
variables that determine these costs for
any particular facility and how they
would vary as a function of plant
electric generating capacity, wastewater
flow rate, pollutant characteristics, or
other factors. To help evaluate efficacy
of the treatment technologies, EPA seeks
both influent and effluent data from full
scale or pilot applications. Data
submitted should include details on: (1)
Date for the sample collection and
analysis; (2) identification of laboratory
analytical methods; and (3) detailed
descriptions of the wastewater treatment
system and sample collection points.
The description of the treatment system
should also include design and
operational information such as flow
rate (design maximum and average flow
rates for the influent scrubber purge and
treatment system effluent; typical
operating flow rate for the influent
purge and effluent; and actual flow rate
corresponding to sampling data
submitted), residence time, chemical
additives, and the flow rates for
recirculation flows within the treatment
system.
• Effect of SCR/SNCR on FGD
wastewater characteristics. EPA solicits
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data quantifying how the operation of
selective catalytic reduction (SCR) or
selective non-catalytic reduction (SNCR)
NOX emission reduction technologies
affects FGD wastewater characteristics.
In particular, EPA solicits concentration
and mass data for metals, ammonia, and
other nitrogen compounds. In addition
to data for other metals, EPA solicits
information to assess the degree to
which SCR or SNCR operation may
increase levels of hexavalent chromium
in the FGD wastewater.
• Effects of scrubber additives on
FGD wastewater characteristics and
treatability. EPA solicits information on
the effect scrubber additives (e.g.,
dibasic acid (DBA) or formic acid) have
on the characteristics of FGD
wastewater, and how these additives
may positively or negatively affect the
treatability of the wastewater. EPA also
solicits information on the reasons
operators use these additives and why
one additive may be considered
preferentially over the other (for
instance, why an operator would choose
to use DBA instead of formic acid, or
vice versa).
• Ash pond management. EPA
solicits information that would help
identify best management practices for
ash ponds. For example, EPA is aware
of information suggesting that managing
pyritic wastes in ash ponds should be
avoided because it can contribute to
lowering pH of the ash pond
impoundment, potentially liberating
metals in ash sediments and elevating
the level of metals released to surface
waters. In addition, introducing certain
other wastes such as coal pile runoff can
substantially affect ash pond pH,
similarly producing conditions that
favor releasing metals present in ash
pond sediments and suspended
particulates. EPA solicits information on
best management practices for
minimizing the potential for such
wastes to adversely impact ash pond
operation and discharges.
EPA solicits data on pollutant
removal performance of ash ponds.
Such data should include influent and
effluent concentration, mass and flow
data. EPA solicits such data for total and
dissolved metals, nitrogen compounds
(ammonia, total Kjeldahl nitrogen,
nitrates, nitrites, and total nitrogen),
total dissolved solids, and effluent
toxicity.
EPA also solicits information on
seasonal effects on ash pond discharges,
such as those resulting from seasonal
turnover. EPA is particularly interested
in the magnitude of the seasonal effects
on the concentration and mass of
pollutants discharged.
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53239
Finally, EPA solicits information that
quantify how ash pond discharges have
been affected by introducing FGD
wastewater into ash ponds that
previously did not receive this
wastewater.
• Environmental assessments/
impacts. EPA solicits information on
environmental assessments that have
been conducted for discharges from
steam electric power plants. In
particular, EPA seeks information
linking the environmental assessments
to discharges of metals (e.g., mercury,
arsenic, selenium, boron, and
magnesium), ammonia and other
nitrogen compounds, phosphorus, total
dissolved solids, or biocide residuals
(e.g., chlorinated or brominated
compounds, or non-oxidizing chemical
biocides). EPA also solicits information
on the toxicity of discharges from power
plants, particularly for FGD and ash
pond wastewater. EPA also seeks more
general information regarding the
potential environmental hazard
associated with discharges of these
pollutants from steam electric power
plants.
• Integrated gasification combined
cycle (IGCC) facilities. EPA solicits
comment on the wastewaters that may
be generated or otherwise affected by
the coal gasification process. What are
the sources and characteristics of
wastewaters generated by coal
gasification and related processes at
IGCC plants? How do these wastewaters
compare to those of traditional coalfired steam electric processes? What
treatment technologies are being used to
treat IGCC wastewaters, and what are
the pollutant removal efficiencies of
these systems?
• Carbon dioxide (CO2) capture
processes. EPA solicits information
describing and characterizing
wastewaters that may be generated at
power plants when implementing
processes to capture and dispose of CO2
emissions.
B. EPA Requests Information on the
Coalbed Methane Extraction Sector of
the Oil and Gas Extraction Category
(Part 435)
EPA is researching the following
questions and topics as they relate to the
quantity and toxicity of pollutants
discharged and the environmental
impacts of these discharges to support
the Oil and Gas Extraction/Coalbed
Methane detailed study.
• What is the range of pollutant
concentrations in CBM produced water?
• What is the toxicity of these
pollutants to human health and the
environment?
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• What is the range of pollutant
concentrations and what are the CBM
produced water flow rates for the major
CBM basins?
• What CBM produced water
pollutants are typically controlled
through permit limits and what is the
range of these permit limits?
• What are the observed and potential
impacts of CBM produced water
discharges on aquatic environments and
communities, riparian zones, and other
wetlands?
• How does the composition of CBM
produced water change when
discharged to normally dry draws or
ephemeral streams?
• To what extent do CBM produced
water discharges mobilize metals, soil
nutrients, pesticides and other organic
contaminants present in soil and carry
these constituents to surface waters?
• What are measures that can mitigate
potential impacts to uses of surface
waters that are used for irrigation?
EPA is researching the following
questions and topics as they relate to the
potential technology options and
beneficial use practices for this
industrial sector.
• What are the current industry
treatment technologies for CBM
produced water?
• What are the potential beneficial
use applications of CBM produced
water and what are the corresponding
criteria for such uses?
• How effectively do these treatment
technologies and beneficial use
practices reduce the potential impacts of
CBM produced water discharges?
• What is the range of incremental
annualized compliance costs associated
with these technologies and practices?
How do these costs differ between
existing and new sources?
• What is the demonstrated use and
economic affordability (e.g., production
losses, firm failures, employment
impacts resulting from production
losses and firm failures, impacts on
small businesses) of these technologies
across the different CBM basins?
• What are the types of non-water
quality environmental impacts
(including energy impacts) associated
with the current industry treatment
technologies and beneficial use
practices for CBM produced water?
EPA is researching the following
questions and topics as they relate to the
expansion of CBM exploration and
development and the affordability of
potential technology options for this
industrial sector.
• What is the near-term and long-term
growth rate for this industry sector?
Which CBM basins are likely to
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experience the most growth within the
next ten years?
• What are the current industry
drilling and infrastructure expansion
plans for CBM exploration and
development?
• What is the predicted range of CBM
reserves across the different basins that
would be economically recoverable at
different natural gas prices?
• What are the potential impacts on
developing CBM reserves and operator
profitability and rates of return on
investment of any increased costs
associated with potential industry
treatment technologies and beneficial
use practices for CBM produced water
discharges?
• What is the difference between
potential impacts on existing sources
versus new sources?
• What percentage of CBM operators
are considered small entities?
EPA is researching the following
questions and topics as they relate to
current regulatory controls.
• How do NPDES permit programs
regulate CBM produced water
discharges (e.g., individual permits,
general permits)?
• What is the BPJ basis for existing
technology-based effluent limits for
CBM produced water discharges?
• To what extent and how do current
regulatory controls ensure the beneficial
use of CBM produced water?
• What other statutes might affect the
ability to discharge, treat, or beneficially
use CBM produced water (e.g., SDWA,
RCRA)?
C. EPA Requests Comments and
Information on the Following as it
Relates to Unused Pharmaceutical
Management for the Health Services
Industry
• EPA solicits identification of any
policies, procedures or guidelines that
govern the disposal of unused
pharmaceuticals from hospitals and
hospices; offices of doctors and mental
health practitioners; nursing, long-term
care, re-habilitation, and personal care
facilities; medical laboratories and
diagnostic service facilities; and
veterinary care facilities.
• EPA solicits information on the
most likely sub-sectors within the
Health Service sector that would
accumulate unused pharmaceuticals for
management and disposal.
• When applicable, to what extent are
unused pharmaceuticals disposed
according to the Resource Conservation
and Recovery Act (RCRA)?
• EPA solicits comment and data on:
(1) The main factors that drive current
disposal practices; and (2) any barriers
preventing the reduction or elimination
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of unused pharmaceuticals to POTWs
and/or surface waters. In particular,
EPA solicits comment on the extent to
which that the Controlled Substances
Act (21 U.S.C. 801 et seq.) complicates
the design of an efficacious solution to
drug disposal.
• EPA solicits quantitative
information or tracking sheets for the
past year on the disposal of unused
pharmaceuticals via the toilet, drain, or
sewer.
• EPA solicits data on how control
authorities are currently controlling
disposal of unused pharmaceuticals via
wastewater.
• EPA solicits information on any
technologies or BMPs that are available
to control, reduce, or eliminate the
disposal of unused pharmaceuticals to
POTWs.
• EPA solicits qualitative and
quantitative data on the effectiveness
and annualized costs of the technologies
or BMPs that health service facilities use
to control or eliminate the discharge of
unused pharmaceuticals from their
wastewater. EPA is also interested in
obtaining information on the current
costs (including labor) associated with
disposal of unused pharmaceuticals via
the drain or toilet.
• EPA solicits any studies or
information on the potential for unused
pharmaceuticals that are disposed of in
non-hazardous-waste landfills to
contaminate underground resources of
drinking water.
EPA will need to gather more
technical and economic information on
unused pharmaceutical management in
the Health Services Industry. To aid its
decision-making, EPA intends to submit
an Information Collection Request (ICR)
to the Office of Management and Budget
(OMB) for their review and approval
under the Paperwork Reduction Act
(PRA), 33 U.S.C. 3501, et seq., in the
2009 annual review. EPA will use this
ICR to collect technical and economic
information on unused pharmaceutical
management and identify technologies
and BMPs that reduce or eliminate the
discharge of unused pharmaceuticals to
POTWs. In designing this industry
survey EPA expects to work closely
with industry representatives and other
affected stakeholders. EPA has
published a separate Federal Register
notice for this ICR and solicits comment
on the potential scope of this ICR (see
August 12, 2008; 73 FR 46903).
D. Preliminary Category Reviews for the
2008 Annual Review
EPA requests information on the Ore
Mining and Dressing category for which
it is continuing a preliminary category
review (i.e., industrial point source
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categories with existing effluent
guidelines identified with ‘‘(5)’’ in the
column entitled ‘‘Findings’’ in Table V–
1 in section V.B.4 of today’s notice).
EPA will need to collect more
information for the 2009 annual review.
Specifically, EPA hopes to gather the
following information:
• What toxic pollutants are
discharged from this industry in nontrivial amounts on an industry and perfacility basis?
• What raw material(s) or process(es)
are the sources of these pollutants?
• What technologies or management
practices are available (technically and
economically) to control or prevent the
generation and/or release of these
pollutants.
E. Data Sources and Methodologies
EPA solicits comments on whether
EPA used the correct evaluation factors,
criteria, and data sources in conducting
its annual review and developing this
final Plan. EPA also solicits comment on
other data sources EPA can use in its
annual reviews and biennial planning
process. Please see the docket for a more
detailed discussion of EPA’s analysis
supporting the reviews in this notice
(see DCN 05515).
F. BPJ Permit-Based Support
EPA solicits comments on whether,
and if so, how the Agency should
provide EPA Regions and States with
permit-based support instead of revising
effluent guidelines (e.g., when the vast
majority of the hazard is associated with
one or a few facilities). EPA solicits
comment on categories for which the
Agency should provide permit-based
support.
mstockstill on PROD1PC66 with NOTICES
G. Implementation Issues Related to
Existing Effluent Guidelines and
Pretreatment Standards
As a factor in its decision-making,
EPA considers opportunities to
eliminate inefficiencies or impediments
to pollution prevention or technological
innovation, or opportunities to promote
innovative approaches such as water
quality trading, including within-plant
trading. Consequently, EPA solicits
comment on implementation issues
related to existing effluent guidelines
and pretreatment standards.
H. EPA’s Evaluation of Categories of
Indirect Dischargers Without
Categorical Pretreatment Standards To
Identify Potential New Categories for
Pretreatment Standards
EPA solicits comments on its
evaluation of categories of indirect
dischargers without categorical
pretreatment standards. Specifically,
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EPA solicits wastewater characterization
data (e.g., wastewater volumes,
concentrations of discharged
pollutants), current examples of
pollution prevention, treatment
technologies, and local limits for all
industries without pretreatment
standards. EPA also solicits comment on
whether there are industrial sectors
discharging pollutants that cause
interference issues that cannot be
adequately controlled through the
general pretreatment standards. Finally,
EPA solicits comment on how better to
access and aggregate discharge data
reported to local pretreatment programs.
Currently, pollutant discharge data are
collected by the local pretreatment
program to demonstrate compliance
with pretreatment standards and local
limits but are not typically
electronically transmitted to the States
or EPA Regions.
I. Industrial Water Conservation, Reuse
and Recycling Technology Transfer
EPA requests data to evaluate the
costs, benefits, and impacts of industrial
water conservation practices. In
particular, EPA solicits the following
industrial sector or facility level data on
water re-use and reduction technologies
and pollution prevention practices:
• The main reasons why these
technologies and practices were adopted
(e.g., limitations to source water,
increased water purchasing or treatment
costs), and whether these technologies
and practices are transferable to other
facilities.
Notice of Final 2008 Effluent Guidelines
Program Plan
• Descriptions of the water
conservation technologies and practices
employed at industrial unit operations;
wastewater flow and pollutant data; and
descriptions of the extent to which these
water conservation technologies and
practices reduce the amount of
wastewater volume, the mass of
wastewater pollutants resulting from an
industrial unit operation, or both.
• Detailed descriptions of the
wastewater treatment and the annual
costs of operating wastewater treatment
to maintain compliance with the
facility’s effluent limits.
• Detailed descriptions of the capital
and annual costs associated with
implementing water conservation
technologies and practices and any cost
savings resulting from water
conservation technologies and practices.
Additionally, EPA solicits estimates
of the amount of increased water
conservation and the number of
facilities that will likely adopt more
advanced water conservation
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53241
technologies and practices over the next
five years as a result of limitations on
water source availability or potential
costs savings.
Dated: September 5, 2008.
Benjamin H. Grumbles,
Assistant Administrator for Water.
[FR Doc. E8–21484 Filed 9–12–08; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
[EPA–HQ–ORD–2008–0649; FRL–8715–6]
Board of Scientific Counselors
(BOSC), Human Health Subcommittee
Meetings—Fall 2008 and Winter 2009
Environmental Protection
Agency (EPA).
ACTION: Notice of meetings.
AGENCY:
SUMMARY: Pursuant to the Federal
Advisory Committee Act, Public Law
92–463, the Environmental Protection
Agency, Office of Research and
Development (ORD), gives notice of
three meetings of the Board of Scientific
Counselors (BOSC) Human Health
Subcommittee.
DATES: The first meeting (a
teleconference call) will be held on
Friday, October 10, 2008, from 12:30
p.m. to 2:30 p.m. EDT. The second
meeting (a teleconference call) will be
held on Monday, December 1, 2008,
from 11 a.m. to 2 p.m. EST. The third
meeting (face-to-face) will begin on
Tuesday, January 13, 2009 and conclude
on Thursday, January 15, 2009. The
meetings may adjourn early if all
business is finished. Requests for the
draft agendas or for making oral
presentations at the meetings will be
accepted up to one business day before
each meeting.
ADDRESSES: The face-to-face meeting
will be held at the EPA’s RTP Main
Campus Facility, 109 T.W. Alexander
Drive, Research Triangle Park, North
Carolina 27711. Submit your comments,
identified by Docket ID No. EPA–HQ–
ORD–2008–0649, by one of the
following methods:
• https://www.regulations.gov: Follow
the on-line instructions for submitting
comments.
• E-mail: Send comments by
electronic mail (e-mail) to:
ORD.Docket@epa.gov, Attention Docket
ID No. EPA–HQ–ORD–2008–0649.
• Fax: Fax comments to: (202) 566–
0224, Attention Docket ID No. EPA–
HQ–ORD–2008–0649.
• Mail: Send comments by mail to:
Board of Scientific Counselors (BOSC),
Human Health Subcommittee
E:\FR\FM\15SEN1.SGM
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Agencies
[Federal Register Volume 73, Number 179 (Monday, September 15, 2008)]
[Notices]
[Pages 53218-53241]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E8-21484]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
[EPA-HQ-OW-2006-0771; FRL-8715-4]
RIN 2040-AE89
Notice of Final 2008 Effluent Guidelines Program Plan
AGENCY: Environmental Protection Agency (EPA).
ACTION: Notice of Final 2008 Effluent Guidelines Program Plan.
-----------------------------------------------------------------------
[[Page 53219]]
SUMMARY: EPA establishes national technology-based regulations known as
effluent guidelines and pretreatment standards to reduce pollutant
discharges from categories of industry discharging directly to waters
of the United States or discharging indirectly through Publicly Owned
Treatment Works (POTWs). The Clean Water Act (CWA) sections 301(d),
304(b), 304(g), and 307(b) require EPA to review these effluent
guidelines and pretreatment standards. This notice presents EPA's 2008
review of existing effluent guidelines and pretreatment standards. It
also presents EPA's evaluation of indirect dischargers without
categorical pretreatment standards to identify potential new categories
for pretreatment standards under CWA sections 304(g) and 307(b). This
notice also presents the final 2008 Effluent Guidelines Program Plan
(``final 2008 Plan''), which, as required under CWA section 304(m),
identifies any new or existing industrial categories selected for
effluent guidelines rulemaking and provides a schedule for such
rulemaking. CWA section 304(m) requires EPA to biennially publish such
a plan after public notice and comment. The Agency published the
preliminary 2008 Plan on October 30, 2007 (72 FR 61335). This notice
also provides EPA's preliminary thoughts concerning its 2009 annual
reviews under CWA sections 304(b) and 304(g) as well as its reviews
under 301(d) and 307(b) and solicits comments, data and information to
assist EPA in performing these reviews. EPA intends to continue its
detailed studies of the steam electric power generating industry, the
health services industry, and the coalbed methane extraction industry,
which is part of the oil and gas extraction industry. Finally, EPA is
using this notice to solicit public comment to identify industry
sectors and facilities that use water efficiency practices that promote
water efficiency, re-use, and recycling because such practices can be
related to reducing overall pollutant discharges.
ADDRESSES: Submit your comments, data and information for the 2009
annual review, identified by Docket ID No. EPA-HQ-OW-2008-0517, by one
of the following methods:
(1) www.regulations.gov. Follow the on-line instructions for
submitting comments.
(2) E-mail: OW-Docket@epa.gov, Attention Docket ID No. EPA-HQ-OW-
2008-0517.
(3) Mail: Water Docket, Environmental Protection Agency, Mailcode:
4203M, 1200 Pennsylvania Ave., NW., Washington, DC 20460, Attention
Docket ID No. EPA-HQ-OW-2008-0517. Please include a total of 3 copies.
(4) Hand Delivery: Water Docket, EPA Docket Center, EPA West, Room
3334, 1301 Constitution Ave., NW., Washington, DC, Attention Docket ID
No. EPA-HQ-OW-2008-0517. Such deliveries are only accepted during the
Docket's normal hours of operation and special arrangements should be
made.
Instructions: Direct your comments to Docket ID No. EPA-HQ-OW-2008-
0517. 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 regulations.gov or e-mail. The
federal 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 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 index at
www.regulations.gov. Although listed in the index, some information is
not publicly available, i.e., CBI or other information whose disclosure
is restricted by statute. Certain other material, such as copyrighted
material, is not placed on the Internet and will be publicly available
only in hard copy form. Publicly available docket materials are
available either electronically at www.regulations.gov or in hard copy
at the Water Docket in the EPA Docket Center, EPA/DC, EPA West, Room
3334, 1301 Constitution Ave., NW., Washington, DC. The Public Reading
Room is open from 8:30 a.m. to 4:30 p.m., Monday through Friday,
excluding legal holidays. The telephone number for the Public Reading
Room is (202) 566-1744, and the telephone number for the Water Docket
is (202) 566-2426.
Key documents providing additional information about EPA's annual
reviews and the final 2008 Effluent Guidelines Program Plan include the
following:
Technical Support Document for the 2008 Effluent
Guidelines Program Plan, EPA-821-R-08-015, DCN 05515;
Steam Electric Power Generating Point Source Category:
2007/2008 Detailed Study Report, EPA-821-R-08-011, DCN 05516;
Coal Mining Detailed Study, EPA-821-R-08-012, DCN 05517;
Health Services Industry Detailed Study: Dental Amalgam,
EPA-821-R-08-014, DCN 05518; and
Health Services Industry Detailed Study: Management and
Disposal of Unused Pharmaceuticals (Interim Technical Report), EPA-821-
R-08-013, DCN 05519.
FOR FURTHER INFORMATION CONTACT: Mr. Carey A. Johnston at (202) 566-
1014 or johnston.carey@epa.gov.
SUPPLEMENTARY INFORMATION:
How Is This Document Organized?
The outline of this notice follows.
I. General Information
II. Legal Authority
III. What Is the Purpose of This Federal Register Notice?
IV. Background
V. EPA's 2008 Annual Review of Existing Effluent Guidelines and
Pretreatment Standards Under CWA Sections 301(d), 304(b), 304(g),
and 307(b)
VI. EPA's 2009 Annual Review of Existing Effluent Guidelines and
Pretreatment Standards Under CWA Sections 301(d), 304(b), 304(g),
and 307(b)
VII. EPA's Evaluation of Categories of Indirect Dischargers Without
Categorical Pretreatment Standards To Identify Potential New
Categories for Pretreatment Standards
VIII. The Final 2008 Effluent Guidelines Program Plan Under Section
304(m)
IX. Request for Comment and Information
I. General Information
A. Does This Action Apply to Me?
This notice simply provides a statement of the Agency's effluent
guidelines review and planning processes and priorities at this time,
and does not contain any regulatory requirements.
[[Page 53220]]
B. What Should I Consider as I Prepare My Comments for EPA for the 2009
Annual Review?
1. Submitting Confidential Business Information
Do not submit this information to EPA through www.regulations.gov
or e-mail. 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.
2. Tips for Preparing Your Comments
When submitting comments, remember to:
Identify the rulemaking by docket number and other
identifying information (subject heading, Federal Register date and
page number).
Follow directions--The agency may ask you to respond to
specific questions or organize comments by referencing a Code of
Federal Regulations (CFR) part or section number.
Explain why you agree or disagree; suggest alternatives
and substitute language for your requested changes.
Describe any assumptions and provide any technical
information and/or data that you used.
If you estimate potential costs or burdens, explain how
you arrived at your estimate in sufficient detail to allow for it to be
reproduced.
Provide specific examples to illustrate your concerns, and
suggest alternatives.
Explain your views as clearly as possible.
Make sure to submit your comments by the comment period
deadline identified.
II. Legal Authority
This notice is published under the authority of the CWA, 33 U.S.C.
1251, et seq., and in particular sections 301(d), 304(b), 304(g),
304(m), 306, 307(b), 308, 33 U.S.C. 1311(d), 1314(b), 1314(g), 1314(m),
1316, 1317(b), and 1318.
III. What Is the Purpose of This Federal Register Notice?
This notice presents EPA's 2008 review of existing effluent
guidelines and pretreatment standards under CWA sections 301(d),
304(b), 304(g) and 307(b). It also presents EPA's evaluation of
indirect dischargers without categorical pretreatment standards to
identify potential new categories for pretreatment standards under CWA
sections 304(g) and 307(b). This notice also presents the final 2008
Effluent Guidelines Program Plan (``final 2008 Plan''), which, as
required under CWA section 304(m), identifies any new or existing
industrial categories selected for effluent guidelines rulemaking and
provides a schedule for such rulemaking. CWA section 304(m) requires
EPA to biennially publish such a plan after public notice and comment.
The Agency published the preliminary 2008 Plan on October 30, 2007 (72
FR 61335). This notice also provides EPA's preliminary thoughts
concerning its 2009 annual reviews under CWA sections 301(d), 304(b),
304(g) and 307(b) and solicits comments, data and information to assist
EPA in performing these reviews.
IV. Background
A. What Are Effluent Guidelines and Pretreatment Standards?
The CWA directs EPA to promulgate effluent limitations guidelines
and standards (``effluent guidelines'') that reflect pollutant
reductions that can be achieved by categories or subcategories of
industrial point sources using technologies that represent the
appropriate level of control. See CWA sections 301(b)(2), 304(b), 306,
307(b), and 307(c). For point sources that introduce pollutants
directly into the waters of the United States (direct dischargers), the
effluent limitations guidelines and standards promulgated by EPA are
implemented through National Pollutant Discharge Elimination System
(NPDES) permits. See CWA sections 301(a), 301(b), and 402. For sources
that discharge to POTWs (indirect dischargers), EPA promulgates
pretreatment standards that apply directly to those sources and are
enforced by POTWs and State and Federal authorities. See CWA sections
307(b) and (c).
1. Best Practicable Control Technology Currently Available (BPT)-- CWA
Sections 301(b)(1)(A) & 304(b)(1)
EPA defines Best Practicable Control Technology Currently Available
(BPT) effluent limitations for conventional, toxic, and non-
conventional pollutants. Section 304(a)(4) designates the following as
conventional pollutants: Biochemical oxygen demand (BOD5),
total suspended solids, fecal coliform, pH, and any additional
pollutants defined by the Administrator as conventional. The
Administrator designated oil and grease as an additional conventional
pollutant on July 30, 1979 (44 FR 44501). EPA has identified 65
pollutants and classes of pollutants as toxic pollutants, of which 126
specific substances have been designated priority toxic pollutants. See
Appendix A to part 423. All other pollutants are considered to be non-
conventional.
In specifying BPT, EPA looks at a number of factors. EPA first
considers the total cost of applying the control technology in relation
to the effluent reduction benefits. The Agency also considers the age
of the equipment and facilities, the processes employed, and any
required process changes, engineering aspects of the control
technologies, non-water quality environmental impacts (including energy
requirements), and such other factors as the EPA Administrator deems
appropriate. See CWA section 304(b)(1)(B). Traditionally, EPA
establishes BPT effluent limitations based on the average of the best
performances of facilities within the industry of various ages, sizes,
processes, or other common characteristics. Where existing performance
is uniformly inadequate, BPT may reflect higher levels of control than
currently in place in an industrial category if the Agency determines
that the technology can be practically applied.
2. Best Conventional Pollutant Control Technology (BCT)--CWA Sections
301(b)(2)(E) & 304(b)(4)
The 1977 amendments to the CWA required EPA to identify effluent
reduction levels for conventional pollutants associated with Best
Conventional Pollutant Control Technology (BCT) for discharges from
existing industrial point sources. In addition to considering the other
factors specified in section 304(b)(4)(B) to establish BCT limitations,
EPA also considers a two part ``cost-reasonableness'' test. EPA
explained its methodology for the development of BCT limitations in
1986. See 51 FR 24974 (July 9, 1986).
3. Best Available Technology Economically Achievable (BAT)--CWA
Sections 301(b)(2)(A) & 304(b)(2)(B)
For toxic pollutants and non-conventional pollutants, EPA
promulgates effluent guidelines based on the Best Available Technology
Economically Achievable (BAT). See CWA section 301(b)(2)(A), (C), (D)
and
[[Page 53221]]
(F). The factors considered in assessing BAT include the cost of
achieving BAT effluent reductions, the age of equipment and facilities
involved, the process employed, potential process changes, non-water
quality environmental impacts, including energy requirements, and other
such factors as the EPA Administrator deems appropriate. See CWA
section 304(b)(2)(B). The technology must also be economically
achievable. See CWA section 301(b)(2)(A). The Agency retains
considerable discretion in assigning the weight accorded to these
factors. BAT limitations may be based on effluent reductions attainable
through changes in a facility's processes and operations. Where
existing performance is uniformly inadequate, BAT may reflect a higher
level of performance than is currently being achieved within a
particular subcategory based on technology transferred from a different
subcategory or category. BAT may be based upon process changes or
internal controls, even when these technologies are not common industry
practice.
4. New Source Performance Standards (NSPS)--CWA Section 306
New Source Performance Standards (NSPS) reflect effluent reductions
that are achievable based on the best available demonstrated control
technology. New sources have the opportunity to install the best and
most efficient production processes and wastewater treatment
technologies. As a result, NSPS should represent the most stringent
controls attainable through the application of the best available
demonstrated control technology for all pollutants (i.e., conventional,
non-conventional, and priority pollutants). In establishing NSPS, EPA
is directed to take into consideration the cost of achieving the
effluent reduction and any non-water quality environmental impacts and
energy requirements.
5. Pretreatment Standards for Existing Sources (PSES)--CWA Section
307(b)
Pretreatment Standards for Existing Sources (PSES) are designed to
prevent the discharge of pollutants that pass through, interfere with,
or are otherwise incompatible with the operation of publicly owned
treatment works (POTWs), including sludge disposal methods at POTWs.
Pretreatment standards for existing sources are technology-based and
are analogous to BAT effluent limitations guidelines.
The General Pretreatment Regulations, which set forth the framework
for the implementation of national pretreatment standards, are found at
40 CFR part 403.
6. Pretreatment Standards for New Sources (PSNS)--CWA Section 307(c)
Like PSES, Pretreatment Standards for New Sources (PSNS) are
designed to prevent the discharges of pollutants that pass through,
interfere with, or are otherwise incompatible with the operation of
POTWs. PSNS are to be issued at the same time as NSPS. New indirect
dischargers have the opportunity to incorporate into their facilities
the best available demonstrated technologies. The Agency considers the
same factors in promulgating PSNS as it considers in promulgating NSPS.
B. What Are EPA's Review and Planning Obligations Under Sections
301(d), 304(b), 304(g), 304(m), and 307(b)?
1. EPA's Review and Planning Obligations Under Sections 301(d), 304(b),
and 304(m)--Direct Dischargers
Section 304(b) requires EPA to review its existing effluent
guidelines for direct dischargers each year and to revise such
regulations ``if appropriate.'' Section 304(m) supplements the core
requirement of section 304(b) by requiring EPA to publish a plan every
two years announcing its schedule for performing this annual review and
its schedule for rulemaking for any effluent guidelines selected for
possible revision as a result of that annual review. Section 304(m)
also requires the plan to identify categories of sources discharging
toxic or non-conventional pollutants for which EPA has not published
effluent limitations guidelines under section 304(b)(2) or NSPS under
section 306. See CWA section 304(m)(1)(B); S. Rep. No. 50, 99th Cong.,
1st Sess. (1985); WQA87 Leg. Hist. 31 (indicating that section
304(m)(1)(B) applies to ``non-trivial discharges.''). Finally, under
section 304(m), the plan must present a schedule for promulgating
effluent guidelines for industrial categories for which it has not
already established such guidelines, providing for final action on such
rulemaking not later than three years after the industrial category is
identified in a final Plan.\1\ See CWA section 304(m)(1)(C). EPA is
required to publish its preliminary Plan for public comment prior to
taking final action on the plan. See CWA section 304(m)(2).
---------------------------------------------------------------------------
\1\ EPA recognizes that one court--the U.S. District Court for
the Central District of California--has found that EPA has a duty to
promulgate effluent guidelines within three years for new categories
identified in the Plan. See NRDC et al. v. EPA, 437 F.Supp.2d 1137
(C.D. Ca, 2006). However, EPA continues to believe that the
mandatory duty under section 304(m)(1)(C) is limited to providing a
schedule for taking final action in effluent guidelines rulemaking--
not necessarily promulgating effluent guidelines--within three
years, and has appealed this decision.
---------------------------------------------------------------------------
In addition, CWA section 301(d) requires EPA to review every five
years the effluent limitations required by CWA section 301(b)(2) and to
revise them if appropriate pursuant to the procedures specified in that
section. Section 301(b)(2), in turn, requires point sources to achieve
effluent limitations reflecting the application of the best practicable
control technology (all pollutants), best available technology
economically achievable (for toxic pollutants and non-conventional
pollutants) and the best conventional pollutant control technology (for
conventional pollutants), as determined by EPA under sections
304(b)(1), 304(b)(2) and 304(b)(4), respectively. For over three
decades, EPA has implemented sections 301 and 304 through the
promulgation of effluent limitations guidelines, resulting in
regulations for 56 industrial categories. See E.I. du Pont de Nemours &
Co. v. Train, 430 U.S. 113 (1977). Consequently, as part of its annual
review of effluent limitations guidelines under section 304(b), EPA is
also reviewing the effluent limitations they contain, thereby
fulfilling its obligations under sections 301(d) and 304(b)
simultaneously.
2. EPA's Review and Planning Obligations Under Sections 304(g) and
307(b)--Indirect Dischargers
Section 307(b) requires EPA to revise its pretreatment standards
for indirect dischargers ``from time to time, as control technology,
processes, operating methods, or other alternatives change.'' See CWA
section 307(b)(2). Section 304(g) requires EPA to annually review these
pretreatment standards and revise them ``if appropriate.'' Although
section 307(b) only requires EPA to revise existing pretreatment
standards ``from time to time,'' section 304(g) requires an annual
review. Therefore, EPA meets its 304(g) and 307(b) requirements by
reviewing all industrial categories subject to existing categorical
pretreatment standards on an annual basis to identify potential
candidates for revision.
Section 307(b)(1) also requires EPA to promulgate pretreatment
standards for pollutants not susceptible to treatment by POTWs or that
would interfere with the operation of POTWs, although it does not
provide a timing requirement for the promulgation of such new
pretreatment standards. EPA, in its discretion, periodically evaluates
indirect dischargers not subject to categorical pretreatment standards
to identify potential candidates for new
[[Page 53222]]
pretreatment standards. The CWA does not require EPA to publish its
review of pretreatment standards or identification of potential new
categories, although EPA is exercising its discretion to do so in this
notice.
EPA intends to repeat this publication schedule for future
pretreatment standards reviews (e.g., EPA will publish the 2009 annual
pretreatment standards review in the notice containing the Agency's
2009 annual review of existing effluent guidelines and the preliminary
2010 plan). EPA intends that these contemporaneous reviews will provide
meaningful insight into EPA's effluent guidelines and pretreatment
standards program decision-making. Additionally, by providing a single
notice for these and future reviews, EPA hopes to provide a
consolidated source of information for the Agency's current and future
effluent guidelines and pretreatment standards program reviews.
V. EPA's 2008 Review of Existing Effluent Guidelines and Pretreatment
Standards Under CWA Sections 301(d), 304(b), 304(g), and 307(b)
A. What Process Did EPA Use To Review Existing Effluent Guidelines and
Pretreatment Standards Under CWA Section 301(d), 304(b), 304(g), and
307(b)?
1. Overview
In its 2008 annual review, EPA reviewed all industrial categories
subject to existing effluent limitations guidelines and pretreatment
standards, representing a total of 56 point source categories and over
450 subcategories. EPA uses four factors in a phased approach to review
existing effluent limitations guidelines and pretreatment standards:
Pollutants discharged in an industrial category's discharge, current
and potential pollution prevention and control technology options,
category growth and economic considerations of technology options, and
implementation and efficiency considerations of revising existing
effluent guidelines or publishing new effluent guidelines (see December
21, 2006; 71 FR 76666). Examining these factors also helps the Agency
to assess the extent to which additional regulation may contribute
reasonable further progress toward the CWA's objective of restoring and
maintaining the chemical, physical and biological integrity of the
nation's waters, consistent with section 101 of the CWA.
EPA used this 2008 review to confirm the Agency's identification of
industrial categories prioritized for further review in the preliminary
2008 Effluent Guidelines Program Plan (October 30, 2007; 72 FR 61335).
EPA also continued work on four detailed studies as part of the 2008
annual review: Steam Electric Power Generating (Part 423), Coal Mining
(Part 434), Oil and Gas Extraction (Part 435) (for the purpose of
assessing whether to include coalbed methane extraction as a new
subcategory), and Hospitals (Part 460).\2\ These reviews discharged
EPA's obligations to annually review both existing effluent limitations
guidelines for direct dischargers and existing pretreatment standards
for indirect dischargers under CWA sections 304(b) and (g), as well as
other review requirements under CWA section 301(d) and 307(b).
---------------------------------------------------------------------------
\2\ Based on available information, hospitals consist mostly of
indirect dischargers for which EPA has not established pretreatment
standards. As discussed in Section VII.B, EPA is including hospitals
in its review of the Health Services Industry, a potential new
category for pretreatment standards. As part of that process, EPA
will review the existing effluent guidelines for the few direct
dischargers in the category.
---------------------------------------------------------------------------
Based on this review and prior annual reviews, and in light of the
ongoing effluent guidelines rulemakings and detailed studies currently
in progress, EPA is not identifying any existing categories for
effluent guidelines rulemaking at this time, and is thus not
establishing a schedule for further rulemaking at this time. EPA does,
however, intend to continue its more focused detailed reviews in the
2009 and 2010 annual reviews of the effluent guidelines for the
following categories: Steam Electric Power Generating (Part 423), Oil
and Gas Extraction category (Part 435) (for the purpose of assessing
whether to revise the limits to include Coalbed Methane extraction as a
new subcategory), and Hospitals (Part 460) (which is part of the Health
Services Industry detailed study). As part of its detailed study of the
Coalbed Methane extraction industry, EPA is seeking approval from the
Office of Management and Budget (OMB) for an Information Collection
Request (ICR) to gather data from the industry (July 15, 2008; 73 FR
40575). EPA is also planning to submit a proposed ICR to OMB for the
Health Services Industry; in particular, a study of unused
pharmaceuticals from medical and veterinary facilities. This is a
request for a new collection. Before submitting the ICR to OMB for
review and approval, EPA is soliciting comments on specific aspects of
the proposed information collection (August 12, 2008; 73 FR 46903). See
Sections V.B.2 and VII.D.
2. How Did EPA's 2007 Annual Review Influence Its 2008 Annual Review of
Point Source Categories With Existing Effluent Guidelines and
Pretreatment Standards?
In view of the annual nature of its reviews of existing effluent
guidelines and pretreatment standards, EPA believes that each annual
review can and should influence succeeding annual reviews, e.g., by
indicating data gaps, identifying new pollutants or pollution reduction
technologies, or otherwise highlighting industrial categories for
additional scrutiny in subsequent years. During its 2007 annual review,
which concluded in October 2007, EPA started or continued detailed
studies of the existing effluent guidelines and pretreatment standards
for the four industrial categories mentioned in the previous
discussion: Steam Electric Power Generating (Part 423), Coal Mining
(Part 434), Oil and Gas Extraction category (Part 435) (for the purpose
of assessing whether to revise the limits to include Coalbed Methane
extraction as a new subcategory), and Hospitals (Part 460) (which is
part of the Health Services Industry detailed study). In addition, EPA
used its 2007 annual reviews to identify three other industrial
categories as candidates for further study in the 2008 reviews based on
the toxic discharges reported to the Toxics Release Inventory (TRI) and
Permit Compliance System (PCS): Ore Mining and Dressing (Part 440),
Centralized Waste Treatment (Part 437), and Waste Combustors (Part
444). EPA published the findings from its 2007 annual review with its
preliminary 2008 Plan (October 30, 2007; 72 FR 61335), making the
pollutant discharge and industry profile data available for public
comment. Docket No. EPA-HQ-OW-2006-0771. EPA used the findings, data
and comments on the 2007 annual review to inform its 2008 annual
review. The 2008 review also built on the previous reviews by
incorporating some refinements to assigning discharges to categories
and updating toxic weighting factors used to estimate the significance
of toxic pollutant discharges. In its 2008 reviews, EPA completed its
Coal Mining detailed study and the dental amalgam management detailed
study for the Health Services Industry. As discussed below, EPA is not
identifying these two industry sectors for an effluent guidelines
rulemaking at this time. EPA does, however, intend to continue its more
focused detailed reviews for the following categories and industry
sectors in the next biennial planning cycle: Steam Electric Power
Generating category, Oil and Gas Extraction
[[Page 53223]]
category (only to assess whether to revise the limits to include
Coalbed Methane extraction as a new subcategory), and unused
pharmaceutical management for the Health Services Industry (which
includes the Hospital category).
3. What Actions Did EPA Take in Performing Its 2008 Annual Reviews of
Existing Effluent Guidelines and Pretreatment Standards?
a. Screening-Level Review
The first component of EPA's 2008 annual review consisted of a
screening-level review of all industrial categories subject to existing
effluent guidelines or pretreatment standards. As a starting point for
this review, EPA examined screening-level data from its 2007 annual
reviews. In its 2007 annual reviews, EPA focused its efforts on
collecting and analyzing data to identify industrial categories whose
pollutant discharges potentially are the most significant. EPA
primarily uses TRI and PCS data to estimate the mass of pollutant
discharges from different industrial facilities. Because pollutant
toxicities are different, EPA converted the toxic and non-conventional
pollutant discharges that are reported in a mass unit (pounds) into a
measure of relative toxicity (toxic-weighted pound equivalent or TWPE).
EPA calculated the TWPE for each pollutant discharged by multiplying
the pollutant specific toxic weighting factor (TWF) and the mass of the
pollutant discharge. Where data are available, these TWFs reflect both
aquatic life and human health effects. EPA ranked point source
categories according to their discharges of toxic and non-conventional
pollutants (reported in units of TWPE) to assess the significance of
these toxic and non-conventional pollutant discharges to human health
or the environment. EPA repeated this process for the 2008 annual
reviews using the most recent TRI data (2005).
Next, EPA considered the availability of technologies to reduce
pollutant discharges. EPA does not have, for all of the 56 existing
industrial categories, information about the availability of treatment
or process technologies to reduce pollutant wastewater discharges
beyond the performance of the technologies upon which existing effluent
guidelines and standards were developed. At present 46 states and one
U.S. territory are authorized to administer the CWA NPDES program.
Under the CWA, permitting authorities must include water-quality based
effluent limits where the technology-based effluent limits are not
sufficient to meet applicable water quality standards. Therefore,
dischargers may have already installed technologies that reduce
pollutant discharges to a level below the original technology-based
requirements in order to meet such water-quality based effluent
limitations.
A commenter on the preliminary 2008 Plan argued that EPA should
conduct rulemaking to amend its effluent guidelines even where water
quality-based controls have already controlled pollutant discharges
(see EPA-HQ-OW-2006-0771-0847). EPA disagrees. Analyzing the
significance of the remaining pollutant discharges is most useful for
assessing the potential effectiveness of additional technologies
because such an analysis focuses on the amount and significance of
pollutant discharges that would actually be removed through new,
technology-based nationally-applicable regulations for these
categories. Where potential pollutant discharge reductions are not
significant, there are likely few effective technology options for a
technology-based rule. Once EPA determined which industries have the
potential for significant additional pollutant removals, EPA further
examined the availability of technologies for certain industries. For
example, EPA identified technologies to minimize pollutant discharges
from Steam Electric facilities (see Steam Electric Power Generating
Point Source Category: 2007/2008 Detailed Study Report, EPA-821-R-08-
011, DCN 05516).
EPA also considered whether there was a way to develop a suitable
tool for comprehensively evaluating the availability and affordability
of treatment or process technologies, but determined that there is not,
because the universe of facilities is too broad and complex. EPA could
not find a reasonable way to prioritize the industrial categories based
on readily available engineering and economic data. In the past, EPA
has gathered information regarding technologies and economic
achievability for one industrial category at a time through detailed
questionnaires distributed to hundreds of facilities within a category
or subcategory for which EPA has commenced rulemaking. Such
information-gathering is subject to the requirements of the Paperwork
Reduction Act (PRA), 33 U.S.C. 3501, et seq. The information acquired
in this way is valuable to EPA in its rulemaking efforts, but the
process of gathering, validating and analyzing the data can consume
considerable time and resources. To study one industry with this level
of analysis generally takes 3 years at a cost to EPA of 1.5 to 3
million dollars. EPA does not think it is appropriate or feasible to
conduct this level of analysis for all point source categories in
conducting an annual review. Rather, EPA uses its analyses of existing
pollutant discharges to identify the categories with the largest toxic
weighted discharges. From this smaller list of categories, EPA
evaluates the possibility of effective technologies and selects certain
industries for examination (e.g., Preliminary Category Reviews,
Detailed Studies). In these more detailed reviews EPA evaluates
technology options for better control of pollutant discharges and may
conduct surveys or other data collection activities in order to better
inform the decision on whether to initiate an effluent guidelines
rulemaking. EPA solicits comment on how to develop tools for directly
assessing technological and economic achievability in future annual
reviews under section 301(d), 304(b), and 307(b) (see EPA-HQ-OW-2004-
0032-2344). The full description of EPA's methodology for the 2008
review is presented in the Technical Support Document (TSD) for the
final 2008 Plan (see DCN 05515).
EPA is continuously investigating and solicits comment on how to
improve its analyses. EPA made a few such improvements to the review
methodology from the 2007 to the 2008 annual review. As part of the
2008 review, EPA corrected the PCSLoads2004 and TRIReleases2004
databases, by addressing issues raised in comments (e.g., updating TWFs
and average POTW pollutant removal efficiencies for a number of
pollutants) and collecting additional information from individual
facilities that report to TRI or PCS.
EPA also continued to use the quality assurance project plan (QAPP)
developed for the 2007 annual review to document the type and quality
of data needed to make the decisions in this 2008 annual review and to
describe the methods for collecting and assessing those data (see EPA-
HQ-OW-2006-0771-0208). EPA performed quality assurance checks on the
data used to develop estimates of toxic-weighted pollutant discharges
(i.e., verifying 2005 discharge data reported to TRI) to determine
whether any of the pollutant discharge estimates relied on incorrect or
suspect data. For example, EPA contacted facilities and permit writers
to confirm and, as necessary, correct TRI data for facilities that EPA
had identified in its screening-level review as the significant
dischargers.
Based on this methodology, EPA assigned those industrial categories
with the lowest estimates of toxic-weighted
[[Page 53224]]
pollutant discharges a lower priority for revision (i.e., industrial
categories marked ``(3)'' in the ``Findings'' column in Table V-1 in
section V.B.4 of today's notice).
Because there are 56 point source categories (including over 450
subcategories) with existing effluent guidelines and pretreatment
standards that must be reviewed annually, EPA believes it is important
to prioritize its review so as to focus on industries where changes to
the existing effluent guidelines or pretreatment standards are most
likely to result in further pollutant discharge reduction. In general,
industries for which effluent guidelines or pretreatment standards have
recently been promulgated are less likely to warrant such changes.
However, when EPA becomes aware of the growth of a new industrial
activity within an existing category or where new concerns are
identified for previously unevaluated pollutants discharged by
facilities within an industrial category, EPA would apply more scrutiny
to the category in a subsequent review. EPA identified no such instance
during the 2008 annual review. In order to further focus its inquiry
during the 2008 annual review, EPA assigned a lower priority for
potential revision to categories for which effluent guidelines had been
recently promulgated or revised, or for which effluent guidelines
rulemaking was currently underway (i.e., industrial categories marked
``(1)'' in the ``Findings'' column in Table V-1 in section V.B.4 of
today's notice). EPA removed an industrial point source category from
further consideration during the current review cycle if EPA
established, revised, or reviewed in a rulemaking context the
category's effluent guidelines after August 2001 (i.e., seven years
prior to August 2008, the expected publication of the final 2008
Effluent Guidelines Program). EPA chose seven years because this is the
time it customarily takes for the effects of effluent guidelines or
pretreatment standards to be fully reflected in pollutant loading data
and TRI reports (in large part because effluent limitations guidelines
are often incorporated into NPDES permits only upon re-issuance, which
could be up to five years after the effluent guidelines or pretreatment
standards are promulgated). EPA also applied a lower priority for
potential revision at this time to the Ore Mining and Dressing category
as EPA lacked sufficient data to determine whether revision would be
appropriate (i.e., this category is marked with ``(5)'' in the
``Findings'' column in Table V-1 in section V.B.4 of today's notice).
EPA lacks sufficient information at this time on the magnitude of the
toxic-weighted pollutant discharges associated with this category. EPA
will seek additional information on the discharges from this category
in the next annual review in order to determine whether a detailed
study is warranted. EPA typically performs a further assessment of the
pollutant discharges before starting a detailed study of an industrial
category. This assessment (``preliminary category review'') provides an
additional level of quality assurance on the reported pollutant
discharges and number of facilities that represent the majority of
toxic-weighted pollutant discharges. See the appropriate section in the
TSD for the final 2008 Plan (see DCN 05515) for EPA's data needs for
these industrial categories.
For industrial categories marked ``(4)'' in the ``Findings'' column
in Table V-1 in section V.B.4 of today's notice, EPA had sufficient
information on the toxic-weighted pollutant discharges associated with
these categories to continue a detailed study of these industrial
categories in the 2008 annual review. EPA intends to use the detailed
study to obtain information on hazard, availability and cost of
technology options, and other factors in order to determine if it would
be appropriate to identify the category for possible effluent
guidelines revision. EPA will continue three detailed studies in the
2009 annual review: Steam Electric Power Generating category, Oil and
Gas Extraction category (only to assess whether to revise the limits to
include Coalbed Methane extraction as a new subcategory), and unused
pharmaceutical management for the Health Services Industry (which
includes the Hospital category).
As part of its 2008 annual review, EPA also considered the number
of facilities responsible for the majority of the estimated toxic-
weighted pollutant discharges associated with an industrial activity.
Where only a few facilities in a category accounted for the vast
majority of toxic-weighted pollutant discharges (i.e., categories
marked ``(2)'' in the ``Findings'' column in Table V-1 in section V.B.4
of today's notice), EPA applied a lower priority for potential
revision. EPA believes that revision of individual permits for such
facilities may be more effective than a revised national effluent
guidelines rulemaking. Individual permit requirements can be better
tailored to these few facilities and may take considerably less time
and resources to establish than a national effluent guidelines
rulemaking. The Docket accompanying this notice lists facilities that
account for the vast majority of the estimated toxic-weighted pollutant
discharges for particular categories (see DCN 05515). For these
facilities, EPA will consider identifying pollutant control and
pollution prevention technologies that will assist permit writers in
developing facility-specific, technology-based effluent limitations on
a best professional judgment (BPJ) basis. For example, EPA developed
and distributed a 2007 technical document to NPDES permit writers in
order to support the development of effluent limitations for facilities
in the dissolving kraft (Subpart A) and dissolving sulfite (Subpart D)
subcategories of the pulp and paper point source category (40 CFR Part
430) (see EPA-HQ-OW-2006-0771-0774). In future annual reviews, EPA also
intends to re-evaluate each category based on the information available
at the time in order to evaluate the effectiveness of the BPJ permit-
based support.
EPA received comments in previous biennial planning cycles urging
the Agency to encourage and recognize voluntary efforts by industry to
reduce pollutant discharges, especially when the voluntary efforts have
been widely adopted within an industry and the associated pollutant
reductions have been significant. EPA agrees that industrial categories
demonstrating significant progress through voluntary efforts to reduce
hazard to human health or the environment associated with their
effluent discharges would be a comparatively lower priority for
effluent guidelines or pretreatment standards revision, particularly
where such reductions are achieved by a significant majority of
individual facilities in the industry. Although during this annual
review EPA could not complete a systematic review of voluntary
pollutant loading reductions, EPA's review did indirectly account for
the effects of successful voluntary programs because any significant
reductions in pollutant discharges should be reflected in TRI 2005
discharge data, as well as any data provided directly by commenters,
that EPA used to assess the toxic-weighted pollutant discharges.
In summary, EPA's review enables EPA to concentrate its resources
on conducting more in-depth reviews of certain industries, as discussed
below.
b. Further Review of Prioritized Categories
In the publication of the preliminary 2008 Plan, EPA identified
three categories with potentially high TWPE discharge estimates for
further investigation (``preliminary category
[[Page 53225]]
review'') as a result of the 2007 annual review: Ore Mining and
Dressing (Part 440), Centralized Waste Treatment (Part 437), and Waste
Combustors (Part 444) (i.e., EPA identified these categories with
``(5)'' in the column entitled ``Findings'' in Table V-1, Page 61345 of
the preliminary 2008 Plan). EPA reviewed these three categories in its
2008 annual review.
EPA typically performs a further assessment of the pollutant
discharges before starting a detailed study of an industrial category.
In conducting these preliminary category reviews, EPA used the same
types of data sources used for the detailed studies but in less depth.
This assessment provides confirmation of the reported pollutant
discharges and number of facilities that represent the majority of
toxic-weighted pollutant discharges. EPA may also develop a preliminary
list of potential wastewater pollutant control technologies before
conducting a detailed study.
c. Detailed Study of Four Categories
EPA continued detailed studies of four categories: Steam Electric
Power Generating (Part 423), Coal Mining (Part 434), Oil and Gas
Extraction (Part 435) (only to assess whether to include coalbed
methane extraction as a new subcategory), and Hospitals (Part 460)
(which is part of the Health Services Industry detailed study). For
these industries, EPA gathered and analyzed additional data on
pollutant discharges, economic factors, and technology issues. EPA
examined: (1) Wastewater characteristics and pollutant sources; (2) the
pollutants discharged from these sources and the toxic weights
associated with these discharges; (3) treatment technology and
pollution prevention information; (4) the geographic distribution of
facilities in the industry; (5) any pollutant discharge trends within
the industry; and (6) any relevant economic factors.
EPA relied on many different sources of data including: (1) The
2002 U.S. Economic Census; (2) TRI and PCS data; (3) contacts with
reporting facilities to verify reported releases and facility
categorization; (4) contacts with regulatory authorities (states and
EPA regions) to understand how category facilities are permitted; (5)
NPDES permits and their supporting fact sheets; (6) monitoring data
included in facility applications for NPDES permit renewals (Form 2C
data); (7) EPA effluent guidelines technical development documents; (8)
relevant EPA preliminary data summaries or study reports; (9) technical
literature on pollutant sources and control technologies; (10)
information provided by industry including industry conducted survey
and sampling data; (11) CWA section 308 data requests and surveys; and
(12) stakeholder comments (see DCN 06109). Additionally, in order to
evaluate available and affordable treatment technology options for the
coalbed methane extraction industry sector, EPA is seeking approval
from the Office of Management and Budget (OMB) for an Information
Collection Request (ICR) to gather data from the industry (July 15,
2008; 73 FR 40757). EPA is also planning to submit a proposed ICR to
OMB for the Health Services Industry; in particular, a study of unused
pharmaceuticals from medical and veterinary facilities. This is a
request for a new collection. Before submitting the ICR to OMB for
review and approval, EPA is soliciting comments on specific aspects of
the proposed information collection (August 12, 2008; 73 FR 46903).
d. Public Comments
EPA's annual review process considers information provided by
stakeholders regarding the need for new or revised effluent limitations
guidelines and pretreatment standards. To that end, EPA established a
docket at the time of publication of the final 2006 Plan to provide the
public with an opportunity to submit additional information to assist
the Agency in its 2007 and 2008 annual reviews. These public comments
are in the supporting docket (EPA-HQ-OW-2006-0771, www.regulations.gov)
and summarized in the TSD for the final 2008 Plan (see DCN 05515).
B. What Were EPA's Findings From Its 2008 Annual Review for Categories
Subject to Existing Effluent Guidelines and Pretreatment Standards?
1. Screening-Level Review
In its 2008 screening level review, EPA considered significance of
remaining pollutant discharges and the other factors described in
section A.3.a. above in prioritizing effluent guidelines for potential
revision. See Table V-1 in section V.B.4 of today's notice for a
summary of EPA's findings with respect to each existing category; see
also the TSD for the final 2008 Plan. Out of the categories subject
only to the screening level review in 2008, EPA is not identifying any
for effluent guidelines rulemaking at this time, based on the factors
described in section A.3.a above and in light of the resources EPA is
currently expending in effluent guidelines rulemakings and detailed
studies. Specifically, EPA is engaged in rulemaking relating to the
Construction and Development Point Source Category, the Airport De-
icing Point Source Category; and the Concentrated Animal Feeding
Operations Point Source Category.
2. Detailed Studies
In its 2008 annual review, EPA continued detailed studies of four
industrial point source categories with existing effluent guidelines
and pretreatment standards: Steam Electric Power Generating (Part 423),
Coal Mining (Part 434), Oil and Gas Extraction (Part 435) (to assess
whether to include coalbed methane extraction as a new subcategory),
and Hospitals (Part 460) (which is part of the Health Services Industry
detailed study). EPA is investigating whether the pollutant discharges
reported to TRI and PCS for 2004 and 2005 accurately reflect the
current discharges of the industry. EPA, through these detailed
studies, analyzes the reported pollutant discharges, technology
innovation, and process changes in these industrial categories.
Additionally, EPA considers whether there are industrial activities not
currently subject to effluent guidelines or pretreatment standards that
should be included with these existing categories, either as part of
existing subcategories or as potential new subcategories.
EPA completed the Coal Mining detailed study and the dental amalgam
management detailed study for the Health Services Industry. As
described below in more detail, EPA is not identifying either of these
industries for an effluent guidelines rulemaking in this final 2008
Plan. EPA will continue the other detailed studies (i.e., Steam
Electric Power Generating, Coalbed Methane Extraction, and Health
Services Industry (unused pharmaceutical management)) to determine
whether EPA should identify in the future any of these industries for
possible revision of their existing effluent guidelines and
pretreatment standards. Three of these four industries are described
below. EPA's review of hospitals (including dental amalgam and unused
pharmaceuticals) is described in section VII.B (Health Services
Industry detailed study).
a. Steam Electric Power Generating (Part 423)
The Steam Electric Power Generating effluent guidelines (40 CFR
423) apply to a subset of the electric power industry, namely those
facilities ``primarily engaged in the generation of electricity for
distribution and sale which results primarily from a process utilizing
fossil-type fuel (coal, oil, or gas) or nuclear fuel in conjunction
with
[[Page 53226]]
a thermal cycle employing the steam water system as the thermodynamic
medium.'' See 40 CFR 423.10. EPA's most recent revisions to the
effluent guidelines and standards for this category were promulgated in
1982 (see 47 FR 52290; November 19, 1982).
EPA has focused efforts for the 2007/2008 Detailed Study for the
Steam Electric Power Generating point source category on certain
discharges from coal-fired power plants. The study sought to: (1)
characterize the mass and concentrations of pollutants in wastewater
discharges from coal-fired steam electric facilities; and (2) identify
the pollutants that comprise a significant portion of the category's
TWPE discharge estimate and the corresponding industrial operation.
EPA's previous annual reviews have indicated that the toxic-weighted
loadings for this category are predominantly driven by the metals
present in wastewater discharges, and that the waste streams
contributing the majority of these metals are associated with ash
handling and wet flue gas desulfurization (FGD) systems (see EPA-HQ-OW-
2004-0032-2781). Other potential sources of metals include coal pile
runoff, metal/chemical cleaning wastes, coal washing, and certain low
volume wastes. EPA is continuing to collect data for the detailed study
through facility inspections, wastewater sampling, a data request that
was sent to a limited number of companies, and various secondary data
sources (see Steam Electric Power Generating Point Source Category:
2007/2008 Detailed Study Report, EPA-821-R-08-011, DCN 05516).
EPA's data collection efforts are primarily focused on coal-fired
power plants, with particular interest in FGD wastewater treatment, the
management of ash sluice water, and water reuse opportunities. EPA's
site visit program gathers information on the types of wastewaters
generated by coal-fired steam electric power plants, as well as the
methods of managing these wastewaters to allow for recycle, reuse, or
discharge. EPA conducted site visits at 16 coal-fired power plants and
is continuing to identify potential site visit candidates to assess FGD
systems using different scrubber designs or sorbents, and facilities
operating or planning to install different types of treatment and water
reuse options.
Between July and October of 2007, EPA conducted five sampling
episodes to characterize untreated wastewaters generated by coal-fired
power plants, including FGD scrubber purge, fly ash sluice, bottom ash
sluice, and combined fly- and bottom ash sluice. EPA also collected
samples to assess the effluent quality from different types of
treatment systems currently in place at these operations. Samples
collected during the five episodes were analyzed for metals and other
pollutants, such as total suspended solids and nitrogen. Site-specific
sampling episode reports are in the docket for the 2008 Plan (EPA-HQ-
OW-2006-0771, www.regulations.gov). These reports discuss the specific
sample points and analytes, the sample collection methods used, the
field quality control (QC) samples collected, and the analytical
results for the wastewater samples.
EPA is continuing to identify potential sampling candidates to
evaluate additional types of FGD wastewater treatment systems,
including advanced biological metals removal processes and chemical
precipitation systems. EPA plans to conduct wastewater sampling at one
or more additional plants in 2008 or early 2009.
EPA also collected facility-specific information using a data
request conducted under authority of CWA section 308 (see EPA-HQ-OW-
2006-0771-0417). In May 2007, EPA distributed this data request to nine
companies that operate a number of coal-fired power plants with wet FGD
systems. The data request complements the wastewater sampling effort as
it requested facility-specific information about wastewaters, and
identifies management practices, for facilities not included in EPA's
sampling program. Responses were received in August and October 2007
and characterized operations at 30 coal-fired power plants. EPA
conducted technical reviews of the data received and resolved questions
with the individual companies before entering the information into a
database (see DCNs 05754 and 05755). The data request collected
information on selected wastewater sources, air pollution controls,
wastewater management and treatment practices, water reuse/recycle, and
treatment system capital and operating costs.
The Utility Water Act Group (UWAG) provided EPA with a database
that contains selected NPDES Form 2C data for 86 coal-fired plants
operated by UWAG's member companies, namely those plants that operate
wet FGD systems or wet fly ash sluice systems. The database provides
facility information, data on facility outfalls, process flow diagrams,
wastewater treatment information, and intake and effluent
characteristics. Data are provided for the FGD, ash sluice, and coal
pile runoff wastestreams.
EPA is also in the process of contacting vendors and conducting
literature searches to collect additional information on wastewater
treatment technology options and wastewater reuse opportunities for
particular waste streams. The Electric Power Research Institute (EPRI)
is conducting bench- and pilot-scale tests on FGD wastewater treatment
technologies, including chemical precipitation, ion exchange, and
biological metals removal.
EPA intends to continue its detailed review of the Steam Electric
Power Generating point source category in the 2009 and 2010 annual
reviews of effluent guidelines. Wastewater sampling at a facility
operating a treatment system of interest was delayed by nearly one year
due to operational conditions at the plant. In addition, several other
plants recently began operating a new generation of FGD wastewater
treatment technology that may achieve substantially better pollutant
reductions of metals and nutrients than EPA has evaluated to date. EPA
believes it is important to evaluate the performance of these
technologies, as well as the processes being investigated by EPRI,
prior to concluding the detailed study. As noted above, EPA has not yet
completed its wastewater sampling activities. The UWAG Form 2C database
was recently delivered to EPA; however, EPA has not had sufficient time
to fully evaluate this data. The database provides substantial
information on wastewater generation and wastewater management and
treatment practices for a large number of plants. EPA believes it is
important to take additional time to evaluate the Form 2C data, in
concert with EPA's sampling data and the responses to EPA's data
request. EPA also intends to continue investigating water reuse
opportunities to assess the degree to which they may yield pollutant
reductions for discharges of ash sluice and FGD wastewater.
b. Coal Mining (Part 434)
As discussed in the final 2006 Plan and preliminary 2008 Plan, EPA
conducted a detailed study during the 2007 and 2008 annual reviews to
evaluate the merits of comments received from a public interest group
and from states and industry urging revisions to pollutant limitations
in the Coal Mining effluent guidelines (40 CFR Part 434) (see December
21, 2006; 71 FR 76644-76667, and October 30, 2007; 72 FR 61342-61343).
The public interest group, the Environmental Law and Policy Center,
asked EPA to place more stringent controls on Total Dissolved Solids
[[Page 53227]]
(TDS) (e.g., sulfates and chlorides), mercury, cadmium, manganese, and
selenium in coal mining discharges. They referenced a study by EPA
Region 5 on potential adverse impacts of the discharge of sulfates on
aquatic life (see EPA-HQ-OW-2004-0032-2614 through 2617).
The Interstate Mining Compact Commission, which represents mining
regulatory agencies in 28 states, state mine permitting agencies in
Pennsylvania and Virginia, and a few mining companies, asked EPA to
remove the current manganese limitations. They made the following
requests and assertions: (1) Permittees should be allowed to employ
best management practices as necessary to reduce manganese discharges
based on the water quality of receiving waterbodies; (2) manganese
treatment is unnecessary to protect aquatic life and there are no
widespread toxicity problems from discharges of manganese; (3)
manganese treatment doubles or triples overall treatment costs
resulting in the forfeiture of Surface Mining Control and Reclamation
Act (SMCRA) bonds; (4) EPA should reconsider its rationale for setting
manganese limits to ensure surrogate removal of other metals because
data show that other metals occur only in low concentrations; (5)
manganese treatment sometimes results in environmental harm because
mining operators must add excessive chemicals to meet the discharge
limits; and (6) because manganese limits are overly stringent they
discourage the use of passive treatment technologies which are more
environmentally beneficial than active treatment.
Individual state and industry commenters cited the following
factors in support of their comments: (1) More stringent state-imposed
coal mining reclamation bonding requirements, enacted after the
promulgation of SMCRA, to control water discharges from mines
undergoing reclamation; (2) studies supporting their contention that
manganese is not harmful to aquatic life at levels above the current
effluent limits; and (3) perception that active treatment with chemical
additions may complicate permit compliance and may cause environmental
harm.
EPA initiated the Coal Mining Detailed Study in January 2007. The
study is consistent with the framework presented in the Detailed Study
Plan, a draft of which the Agency placed into the docket (see EPA-HQ-
OW-2004-0032-2312) during the fall of 2006. EPA revised and finalized
the Detailed Study Plan in April 2007 to reflect public comments. The
study evaluated treatment technologies, costs, and pollutant discharge
loads, as well as the effects of manganese and other pollutants on
aquatic life. The study also addressed the question of whether bonds
are being forfeited because of the cost of manganese treatment by
examining bonding and trust fund requirements, past bond forfeiture
rates, future potential bond forfeiture rates, and the issues related
to state assumption of long-term water treatment responsibilities for
mines where the bonds have been forfeited.
As outlined in the Detailed Study Plan, EPA framed study questions
based on public comment, identified data sources to help answer the
study questions, developed a methodology for estimating treatment costs
and discharge loads, and initiated data collection activities with the
Interstate Mining Compact Commission, state agencies, and the Office of
Surface Mining, Reclamation, and Enforcement within the U.S. Department
of the Interior. In responding to these public comments the study used
Part 434 definitions to describe the industry. In particular, proper
understanding of the following terms is useful in understanding the
following discussion and EPA's response to the public commenters:
The term ``acid or ferruginous mine drainage'' means mine
drainage which, before any treatment, either has a pH of less than 6.0
or a total iron concentration equal to or greater than 10 mg/l (see 40
CFR 434.11(a)).
The term ``active mining area'' means the area, on and
beneath land, used or disturbed in activity related to the extraction,
removal, or recovery of coal from its natural deposits. This term
excludes coal preparation plants, coal preparation plant associated
areas and post-mining areas (see 40 CFR 434.11(b)).
The term ``alkaline mine drainage'' means mine drainage
which, before any treatment, has a pH equal to or greater than 6.0 and
total iron concentration of less than 10 mg/l (see 40 CFR 434.11(c)).
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