Revised National Pollutant Discharge Elimination System Permit Regulations for Concentrated Animal Feeding Operations; Supplemental Notice of Proposed Rulemaking, 12321-12340 [E8-4504]
Download as PDF
Federal Register / Vol. 73, No. 46 / Friday, March 7, 2008 / Proposed Rules
all persons and vessels must comply
with the instructions of the Captain of
the Port or his or her designated
representative.
(3) The U.S. Coast Guard may be
assisted in the patrol and enforcement
of the security zone by Federal, State
and local agencies.
(c) Effective period. This section is
effective from 7:30 a.m. through 2 p.m.
on April 17, 2008.
Dated: February 25, 2008.
Brian D. Kelley,
Captain, U.S. Coast Guard, Captain of the
Port, Baltimore, Maryland.
[FR Doc. E8–4463 Filed 3–6–08; 8:45 am]
BILLING CODE 4910–15–P
POSTAL SERVICE
39 CFR Part 111
New Standards Prohibit the Mailing of
Replica or Inert Munitions
Postal Service TM.
Proposed rule.
AGENCY:
rwilkins on PROD1PC63 with PROPOSALS
ACTION:
SUMMARY: The Postal Service is
proposing new standards to prohibit the
mailing of replica or inert munitions
such as grenades or other simulated
explosive devices.
DATES: We must receive your comments
on or before April 7, 2008.
ADDRESSES: Mail or deliver written
comments to the Manager, Mailing
Standards, U.S. Postal Service, 475
L’Enfant, Plaza, SW., Room 3436,
Washington, DC 20260–3436. You may
inspect and photocopy all written
comments at USPS Headquarters
Library, 475 L’Enfant, Plaza, SW., 11th
Floor N, Washington, DC between 9 a.m.
and 4 p.m., Monday through Friday.
FOR FURTHER INFORMATION CONTACT:
Michael F. Lee, 202–268–7263.
SUPPLEMENTARY INFORMATION: Current
Postal Service standards do not prohibit
look-alike weapons from the mail. In
order to ensure safety of postal
employees and prevent damage to postal
property or other mailpieces, inert
munitions have been handled as ‘‘live
ammunition’’ when found in the mail.
In the past, facilities have been
evacuated when inert replicas have been
identified in the mailstream. In 2006,
the Postal Service recorded 849
suspicious incidents involving mail that
exhibited characteristics of possible
explosives. Postal facilities were
evacuated on 100 separate occasions
due to these occurrences. Postal
Inspectors or local emergency first
responders reacted to each of these
occurrences to assess the items.
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Evacuations cost the Postal Service time
and money, create unnecessary stress
for employees, and can impact service
commitments.
Most importantly, employee safety
can be jeopardized when facsimiles of
potentially dangerous items are
permitted in the mail. Both real and
replica explosives have been found in
the mail and the replicas often are not
readily distinguishable from the real
articles. The Postal Service is concerned
that without prohibition of these types
of mail pieces, continued exposure to
replicated munitions, over time, will
lead to desensitized reactions should an
employee encounter items in the mail
that should be regarded as dangerous.
This proposed rule is part of our
ongoing commitment to increase the
safety of the mail and provide a safe
working environment for our
employees.
Although we are exempt from the
notice and comment requirements of the
Administrative Procedure Act [5 U.S.C.
of 553(b), (c)] regarding proposed
rulemaking by 39 U.S.C. 410(a), the
Postal Service invites public comment
on the following proposed revisions to
Mailing Standards of the United States
Postal Service, Domestic Mail Manual
(DMM), incorporated in the Code of
Federal Regulations. See 39 CFR 111.1.
List of Subjects in 39 CFR Part 111
Administrative practice and
procedure, Postal Service.
PART 111—[AMENDED]
1. The authority citation for 39 CFR
part 111 continues to read as follows:
Authority: 5 U.S.C. 552(a); 39 U.S.C. 101,
401, 403, 404, 414, 416, 3001–3011, 3201–
3219, 3403–3406, 3621, 3622, 3626, 3632,
3633 and 5001.
2. Revise the following sections of
Mailing Standards of the United States
Postal Service, Domestic Mail Manual
(DMM) as follows:
*
*
*
*
*
600 Basic Standards for All Mailing
Services
601
Mailability
*
*
*
*
*
11.0 Other Restricted and
Nonmailable Matter
*
*
*
*
*
[Renumber current 11.5 through 11.20
as 11.6 through 11.21. Insert new 11.5
to read as follows:]
11.5
Replica or Inert Munitions
Replica or inert munitions that bear a
realistic appearance, such as simulated
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12321
grenades or other simulated explosive
devices, are not permitted in the mail.
*
*
*
*
*
We will publish an appropriate
amendment to 39 CFR part 111 to reflect
these changes if the proposal is adopted.
Neva R. Watson,
Attorney, Legislative.
[FR Doc. E8–4459 Filed 3–6–08; 8:45 am]
BILLING CODE 7710–12–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 122
[EPA–HQ–OW–2005–0037; FRL–8539–9]
RIN 2040–AE94
Revised National Pollutant Discharge
Elimination System Permit Regulations
for Concentrated Animal Feeding
Operations; Supplemental Notice of
Proposed Rulemaking
Environmental Protection
Agency (EPA).
ACTION: Supplemental notice of
proposed rulemaking.
AGENCY:
SUMMARY: This action is a supplemental
notice of proposed rulemaking (SNPRM)
to EPA’s June 30, 2006, notice of
proposed rulemaking (NPRM) revising
the National Pollutant Discharge
Elimination System (NPDES) permitting
requirements for concentrated animal
feeding operations (CAFOs), in response
to the order issued by the U.S. Court of
Appeals for the Second Circuit in
Waterkeeper Alliance et al. v. EPA, 399
F.3d 486 (2d Cir. 2005). In the June 2006
NPRM, EPA proposed to require only
CAFOs that discharge or propose to
discharge to seek coverage under a
permit. In this SNPRM, EPA is
proposing a voluntary option for CAFOs
to certify that the CAFO does not
discharge or propose to discharge based
on an objective assessment of the
CAFO’s design, construction, operation,
and maintenance. The June 2006
proposal also discussed the terms of the
nutrient management plan (NMP) that
would need to be incorporated into
NPDES permits. This SNPRM proposes
a framework for identifying the terms of
the NMP and three alternative
approaches for addressing rates of
application of manure, litter, and
process wastewater when identifying
terms of the NMP to be included in the
permit. This supplemental proposal
focuses solely on certification and terms
of the NMP and is not opening any other
provisions of the June 2006 proposal
and existing NPDES regulations or
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Federal Register / Vol. 73, No. 46 / Friday, March 7, 2008 / Proposed Rules
Effluent Limitations Guidelines and
Standards for public comment.
DATES: Comments must be received on
or before April 7, 2008.
ADDRESSES: Submit your comments,
identified by Docket ID No. EPA–HQ–
OW–2005–0037 by one of the following
methods:
(1) https://www.regulations.gov:
Follow the online instructions for
submitting comments.
(2) E-mail: ow-docket@epa.gov,
Attention Docket ID No. EPA–HQ–OW–
2005–0037.
(3) Mail: Send the original and three
copies of your comments to: Water
Docket, Environmental Protection
Agency, Mail Code 2822T, 1200
Pennsylvania Ave., NW., Washington,
DC 20460, Attention Docket ID No. OW–
2005–0037.
(4) Hand Delivery: Deliver your
comments to: EPA Docket Center, EPA
West, Room B102, 1301 Constitution
Avenue, NW., Washington, DC,
Attention Docket ID No. OW–2005–
0037. Such deliveries are only accepted
during the Docket’s normal hours of
operation and special arrangements
should be made for deliveries of boxed
information.
Instructions: Direct your comments to
Docket ID No. EPA–HQ–OW–2005–
0037. EPA’s policy is that all comments
received will be included in the public
docket without change and may be
made available online at
www.regulations.gov, including any
personal information provided, unless
the comment includes information
claimed to be Confidential Business
Information (CBI) or other information
whose disclosure is restricted by statute.
Do not submit information that you
consider to be CBI or otherwise
protected through www.regulations.gov
or e-mail. The www.regulations.gov Web
site is an ‘‘anonymous access’’ system,
which means EPA will not know your
identity or contact information unless
you provide it in the body of your
comment. If you send an e-mail
comment directly to EPA without going
through www.regulations.gov your email address will be automatically
captured and included as part of the
comment that is placed in the public
docket and made available on the
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. For additional information
about EPA’s public docket visit the EPA
Docket Center homepage at https://
www.epa.gov/epahome/dockets.htm.
Docket: All documents in the docket
are listed in the www.regulations.gov
index. Although listed in the index,
some information is not publicly
available, e.g., CBI or other information
whose disclosure is restricted by statute.
Certain other material, such as
copyrighted material, will be publicly
available only in hard copy. Publicly
available docket materials are available
either electronically in
www.regulations.gov or in hard copy at
the Water Docket, EPA Docket Center,
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.
FOR FURTHER INFORMATION CONTACT:
Rebecca Roose, Water Permits Division,
Office of Wastewater Management
(4203M), Environmental Protection
Agency, 1200 Pennsylvania Ave., NW.,
Washington, DC 20460; telephone
number: (202) 564–0758; e-mail address:
roose.rebecca@epa.gov.
SUPPLEMENTARY INFORMATION:
I. General Information
A. Does This Action Apply to Me?
B. What Should I Consider as I Prepare my
Comments for EPA?
II. Background
III. This Proposal
A. No Discharge Certification
B. Terms of Nutrient Management Plan
C. Compliance Deadlines
IV. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory
Planning and Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
G. Executive Order 13045: Protection of
Children From Environmental Health
and Safety Risks
H. Executive Order 13211: Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use
I. National Technology Transfer and
Advancement Act
I. General Information
A. Does This Action Apply to Me?
This action applies to concentrated
animal feeding operations (CAFOs),
included as point sources in section
502(14) of the Clean Water Act and
defined in the NPDES regulations at 40
CFR 122.23. The following table
provides a list of standard industrial
codes for operations covered under this
revised rule.
TABLE 1.—ENTITIES POTENTIALLY REGULATED BY THIS RULE
Category
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Federal, State, and Local Government:
Industry .....................................
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North
American industry code
(NAIC)
Examples of regulated entities
Operators of animal production operations that meet the definition of a
CAFO:
Beef cattle feedlots (including veal) ...................................................
Beef cattle ranching and farming .......................................................
Hogs ...................................................................................................
Sheep .................................................................................................
General livestock except dairy and poultry ........................................
Dairy farms .........................................................................................
Broilers, fryers, and roaster chickens ................................................
Chicken eggs .....................................................................................
Turkey and turkey eggs .....................................................................
Poultry hatcheries ..............................................................................
Poultry and eggs ................................................................................
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11299
11212
11232
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industrial
classification
code
0211
0212
0213
0214
0219
0241
0251
0252
0253
0254
0259
Federal Register / Vol. 73, No. 46 / Friday, March 7, 2008 / Proposed Rules
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TABLE 1.—ENTITIES POTENTIALLY REGULATED BY THIS RULE—Continued
Category
North
American industry code
(NAIC)
Examples of regulated entities
Ducks .................................................................................................
Horses and other equines ..................................................................
This table is not intended to be
exhaustive, but rather provides a guide
for readers regarding entities likely to be
regulated by this action. This table lists
the types of entities that EPA is now
aware could potentially be regulated by
this action. Other types of entities not
listed in the table could also be
regulated. To determine whether your
facility may be regulated under this
rulemaking, you should carefully
examine the applicability criteria in 40
CFR 122.23. If you have questions
regarding the applicability of this action
to a particular entity, consult the person
listed in the preceding FOR FURTHER
INFORMATION CONTACT section.
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B. What Should I Consider as I Prepare
my Comments for EPA?
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.
It will be helpful if you follow these
guidelines as you prepare your written
comments:
i. Identify the rulemaking by docket
number and other identifying
information (subject heading, Federal
Register date and page number).
ii. 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.
iii. Explain why you agree or disagree;
suggest alternatives and substitute
language for your requested changes.
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iv. Describe any assumptions and
provide any technical information and/
or data that you used.
v. If you estimate potential costs or
burdens, explain how you arrived at
your estimate in sufficient detail to
allow for it to be reproduced.
vi. Provide specific examples to
illustrate your concerns, and suggest
alternatives.
vii. Explain your views as clearly as
possible.
viii. Make sure to submit your
comments by the comment period
deadline identified.
II. Background
Congress enacted the Federal Water
Pollution Control Act (1972), also
known as the Clean Water Act (CWA),
to ‘‘restore and maintain the chemical,
physical, and biological integrity of the
nation’s waters’’ (CWA section 101(a)).
Among the core provisions, the CWA
establishes the NPDES permit program
to authorize and regulate the discharge
of pollutants from point sources to
waters of the U.S. (CWA section 402).
Section 502(14) of the CWA specifically
includes CAFOs in the definition of the
term ‘‘point source.’’ Section 502(12)
defines the term ‘‘discharge of a
pollutant’’ to mean ‘‘any addition of any
pollutant to navigable waters from any
point source’’ (emphasis added). EPA
has issued comprehensive regulations
that implement the NPDES program at
40 CFR part 122. The Act also provides
for the development of technologybased and water quality-based effluent
limitations that are imposed through
NPDES permits to control the discharge
of pollutants from point sources. CWA
sections 301(a) and (b).
EPA began regulating wastewater and
manure from CAFOs in the 1970s. EPA
initially issued national effluent
limitations guidelines and standards for
feedlots on February 14, 1974 (39 FR
5,704), and NPDES CAFO regulations on
March 18, 1976 (41 FR 11,458).
In February 2003, EPA issued
revisions to these regulations, focusing
on the 5% of the nation’s animal feeding
operations (AFOs) that present the
highest risk of impairing water quality
and public health (68 FR 7,176) (‘‘the
2003 CAFO rule’’). The 2003 CAFO rule
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11292
Standard
industrial
classification
code
0259
0272
required the owners or operators of all
CAFOs 1 with a potential to discharge to
apply for an NPDES permit. A number
of CAFO industry organizations
(American Farm Bureau Federation,
National Pork Producers Council,
National Chicken Council, and National
Turkey Federation (NTF), although NTF
later withdrew its petition) and several
environmental groups (Waterkeeper
Alliance, Natural Resources Defense
Council, Sierra Club, and American
Littoral Society) filed petitions for
judicial review of certain aspects of the
2003 CAFO rule. This case was brought
before the U.S. Court of Appeals for the
Second Circuit. On February 28, 2005,
the court ruled on these petitions and
upheld most provisions of the 2003 rule
but vacated and remanded others.
Waterkeeper Alliance, et al. v. EPA, 399
F.3d 486 (2d Cir. 2005). Provisions of
the 2003 CAFO rule that were
challenged by the petitioners but upheld
by the court include the Agency’s land
application regulatory framework and
interpretation of ‘‘agricultural
stormwater,’’ and the Agency’s
determination regarding effluent
limitations guidelines pertaining to
groundwater controls and best available
technology for waste management. The
court vacated the 2003 rule requirement
that all CAFOs must apply for permits
or demonstrate that they do not have the
potential to discharge. The court also
found that the terms of the nutrient
management plan (NMP) are themselves
‘‘effluent limitations’’ and, therefore,
must be made part of the permit and be
enforceable as required by CWA
sections 301 and 402, made subject to
public comment, and reviewed and
approved by the permitting authority.
The court also remanded several aspects
of the 2003 CAFO rule for further
clarification and analysis.
On June 30, 2006, EPA published a
proposed rule to revise several aspects
of the Agency’s regulations governing
discharges from CAFOs in response to
1 The Clean Water Act regulates the conduct of
persons, which includes the owners and operators
of CAFOs, rather than the facilities or their
discharges. To improve readability in this preamble,
reference is made to ‘‘CAFOs’’ as well as ‘‘owners
and operators of CAFOs.’’ No change in meaning is
intended.
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Federal Register / Vol. 73, No. 46 / Friday, March 7, 2008 / Proposed Rules
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the Waterkeeper decision. 71 FR 37,744.
EPA is briefly describing the proposed
revisions to the 2003 CAFO here for
context only. The proposed provisions
in response to the Waterkeeper decision
are beyond the scope of this final rule,
and EPA is not addressing those
provisions in this final rule.
In summary, EPA proposed to require
only owners or operators of those
CAFOs that discharge or propose to
discharge to seek authorization to
discharge under a permit. Second, EPA
proposed to require CAFOs seeking
authorization to discharge under
individual permits to submit their
NMPs with their permit applications or,
under general permits, with their
notices of intent. Permitting authorities
would be required to review the NMP
and provide the public with an
opportunity for meaningful public
review and comment. Permitting
authorities would also be required to
incorporate terms of the NMP as NPDES
permit conditions. The proposed rule
also addressed the remand of issues for
further clarification and analysis. These
issues concern clarifications regarding
the applicability of water quality-based
effluent limitations (WQBELs); new
source performance standards for swine,
poultry, and veal CAFOs; and ‘‘best
conventional technology’’ effluent
limitations guidelines for fecal coliform.
In addition to the proposed revisions
in the 2006 proposed rule, EPA has
extended certain deadlines in the
NPDES permitting requirements and
ELGs in two separate rulemakings in
order to allow the Agency adequate time
to complete this rulemaking in response
to the Waterkeeper decision, in advance
of those deadlines. The first rule revised
dates established in the 2003 CAFO rule
by which facilities newly defined as
CAFOs were required to seek permit
coverage and by which all permitted
CAFOs were required to develop and
implement nutrient management plans.
71 FR 6978. Because EPA was unable to
complete this final rule prior to July 31,
2007, EPA again revised the compliance
dates on July 24, 2007, further extending
those dates from July 31, 2007, to
February 27, 2009. 72 FR 40248.
III. This Proposal
This notice supplements the 2006
proposed rule by proposing additional
options being considered by EPA for
inclusion in the rulemaking to respond
to the Second Circuit’s decision in the
Waterkeeper case. EPA is only seeking
comment on the issues presented in this
supplemental proposal. No provisions
promulgated in the 2003 final rule are
affected or reopened by this
supplemental proposal, nor is EPA
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reopening the comment period on the
2006 proposed rule. In addition, EPA is
taking comment on the compliance
deadlines established in the second date
change rule.
A. No Discharge Certification
In this notice, the Agency is
proposing a new provision that would
allow CAFOs to voluntarily certify that
the CAFO does not discharge or propose
to discharge. This supplemental
proposal seeks comment on this
voluntary certification option, described
below.
1. Background
The 2003 CAFO rule required all
CAFOs to seek coverage under an
NPDES permit unless the Director
determined that the CAFO has no
potential to discharge. 68 FR 7176 (Feb.
12, 2003). This duty to apply for a
permit based on a potential discharge
was successfully challenged.
Waterkeeper Alliance et al. v. EPA, 399
F.3d 486 (2nd Cir. 2005). The court
found that the duty to apply, which the
Agency had based on a presumption
that most CAFOs have at least a
potential to discharge, was invalid
because the CWA subjects only actual
discharges to permitting requirements
rather than potential discharges.
Waterkeeper, 399 F.3d at 506. The court
acknowledged EPA’s policy
considerations for seeking to impose a
duty to apply solely on the basis of a
CAFO’s potential to discharge but found
that the Agency lacked statutory
authority to do so.
In June 2006, in response to the
Waterkeeper decision, EPA proposed to
amend the duty to apply provision for
CAFOs, found at 40 CFR 122.23(d), to
require all CAFOs that ‘‘discharge or
propose to discharge’’ to seek NPDES
permit coverage. 71 FR 37744 (June 30,
2006). As discussed in the preamble to
the 2006 proposed rule, the CAFO
operator would decide whether or not to
apply for a permit. 71 FR 37749. EPA
received several hundred comments on
the 2006 proposed rule related to how
a CAFO operator would decide whether
to seek permit coverage. In particular,
many commenters asked EPA to specify
conditions at a CAFO that would clearly
trigger the requirement to apply for a
permit, while others stated the position
that there is no ‘‘duty to apply’’ for
CAFOs in advance of any discharge
because an NPDES permit is only
required for actual discharges. In
response to these comments EPA has
developed an option that would allow a
CAFO that determines it does not need
to seek permit coverage to certify to the
Director that the operation does not
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discharge or propose to discharge. The
proposal would establish clear criteria,
described in detail below, that a CAFO
must meet in order to be eligible for the
certification. The certification option
proposed in this notice would not
change the duty to apply requirement
proposed in 2006 that CAFOs that
discharge or propose to discharge would
be required to seek permit coverage. It
would, however, provide a structured
process for CAFOs that wish to certify
to establish that they do not discharge
or propose to discharge. EPA believes
that such a structured process would be
helpful to CAFOs as they determine
whether or not to seek permit coverage.
Furthermore, a CAFO with a valid no
discharge certification would not be
subject to liability for violation of the
duty to apply at 122.23(d) in the
unlikely event that a discharge should
occur, though it would still be liable for
violation of the prohibition on
unpermitted discharges in CWA section
301. EPA wishes to emphasize that
submission of a no discharge
certification is voluntary. Only CAFOs
that discharge or propose to discharge
would be subject to NPDES permit
requirements, whether or not they
submit a certification.
2. Overview of Certification
EPA is proposing a voluntary option
for CAFOs to certify to the Director that
the CAFO does not discharge or propose
to discharge based on an objective
assessment of the CAFO’s design,
construction, operation, and
maintenance. This objective assessment
would take into account the CAFO’s
production area design and construction
and its operating parameters as
described in its nutrient management
plan (NMP). The CAFO operator would
certify that the CAFO does not discharge
or propose to discharge by signing and
submitting a certification statement to
the Director. A CAFO’s no discharge
certification would not be subject to
approval by the permitting authority
and there would not be an opportunity
for the public to comment and request
a hearing regarding the certification.
The proposed eligibility requirements,
submission requirements, and
conditions for a valid certification are
discussed in detail below.
3. Certification Eligibility Criteria
EPA is proposing to establish specific
eligibility criteria for CAFO certification
at 40 CFR 122.23(h)(2). Meeting these
criteria would establish that the CAFO
does not ‘‘discharge or propose to
discharge’’ for purposes of proposed
§ 122.23(d), for as long as the
certification is valid. The two proposed
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criteria are as follows: (1) An objective
evaluation of the production area
design, construction, operation, and
maintenance, which shows that the
production area will not discharge, and
(2) development, implementation, and
maintenance on-site of a nutrient
management plan (NMP) that addresses
the elements set forth in 40 CFR
122.42(e)(1) and 412.37(c), including
operation and maintenance practices for
the production area and land
application areas under the control of
the CAFO. While a description of how
the CAFO meets the eligibility criteria
would be required to be submitted to
the Director, this proposed rule would
not require that the documents
necessary to meet the eligibility criteria
be submitted to the permitting
authority, nor would they be subject to
permitting authority approval. However,
during the certification period a
properly certified CAFO would be
required to maintain such documents on
site or make them readily available,
along with any associated records
created to support the basis for the
certification. Certified CAFOs, like any
other permitted or unpermitted CAFO,
would be subject to potential inspection
by EPA or State inspectors, during
which they could be required to
produce the documentation showing
that the CAFO meets the eligibility
criteria, including that the CAFO has
been and is being operated and
maintained in accordance with the
NMP.
The first proposed eligibility criterion
for valid certification would cover the
design, construction, operation, and
maintenance of the CAFO’s production
area. Proposed § 122.23(h)(2)(i) would
require the CAFO to maintain
documentation on site to demonstrate
that the CAFO’s production area is
designed, constructed, operated, and
maintained so as not to discharge. This
demonstration would be the same as the
demonstration provided for in proposed
40 CFR 412.46 (71 FR 37786), which
would allow swine, poultry, and veal
calf operations subject to new source
performance standards (NSPS) to
demonstrate that there will be no
discharge from their production area.
However, the no discharge certification
would be available to all unpermitted
CAFOs that do not discharge or propose
to discharge, not just new sources in the
swine, poultry and veal calf sectors with
open storage. Due to the variations in
production area design based on the
type of containment system used at the
operation, the proposed regulatory text
for the first eligibility criterion has two
parts: the first for open manure storage
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structures and the second for any part
of the production area not considered to
be open containment.
EPA is proposing that any CAFO with
an open surface manure storage
structure seeking to certify that it does
not discharge or propose to discharge
would be required to perform a
technical evaluation. This evaluation
would include the same elements as the
technical evaluation required for open
storage new source swine, poultry and
veal calf operations seeking to
demonstrate no discharge under 40 CFR
412.46(a)(1). In the 2006 proposed rule,
EPA proposed to revise the provisions at
40 CFR 412.46(a)(1) to allow such new
sources with open containment to meet
the no discharge requirement for their
NPDES permit using best management
practices based in part on a rigorous
site-specific technical evaluation that
includes use of the Soil Plant Air Water
(SPAW) Hydrology Tool or equivalent
model. See the 2006 proposed
regulation at 71 FR 37786–87 and
corresponding preamble discussion at
71 FR 37760–62. Under this proposed
certification, any unpermitted CAFO
with open storage seeking to certify its
operation as no discharge, not just new
source swine, poultry, and veal calf
operations, would be required to
undertake a technical evaluation in
accordance with the elements of the
technical evaluation in § 412.46(a)(1)(i)–
(vii) to demonstrate that it meets the
production area requirement for
certification under proposed
§ 122.23(h)(2)(i)(A). Today’s proposed
rule does not reopen for additional
comment the 2006 proposed revisions to
section 412.46 relating to NSPS. The
comment period on the revised NSPS
requirements is closed. Rather, EPA is
now seeking comment on whether the
elements of the technical evaluation set
forth in proposed § 412.46(a)(1)(i)–(vii)
provide an appropriate basis for an
unpermitted CAFO to certify, on the
basis of its design, construction,
operation, and maintenance, that its
open surface manure storage structure
will not discharge.
In order to meet the second part of the
first eligibility criterion, this proposed
rule would require, in
§ 122.23(h)(2)(i)(B), that any certifying
CAFO must demonstrate that all of its
production area, as defined at 40 CFR
122.23(b)(8), not just open surface
containment structures, is designed,
constructed, operated, and maintained
such that there will be no discharge of
manure, litter, process wastewater, or
raw materials, such as feed, to surface
waters. For a CAFO without open
containment, this provision would
require a demonstration of no discharge
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from the entire production area. For a
CAFO that has an open containment
structure, this provision would require
a demonstration that the remainder of
the production area (other than the open
containment structure subject to the
demonstration in 122.23(h)(2)(i)(A)),
also will not discharge. Because of the
special risk of discharge from open
manure storage structures, greater
specificity is provided regarding the
elements of the demonstration in
122.23(h)(2)(i)(A); however, the
demonstration in 122.23(h)(2)(i)(B) must
also be technically sound and must be
adequate to demonstrate that the
production area is designed,
constructed, operated and maintained
for no discharge. This demonstration
must be based on an evaluation of sitespecific characteristics, including,
among others, the amount of manure
generated during the storage period, the
size of the storage structure, control
measures to ensure diversion of clean
water, and seasonal restrictions on land
application. Some CAFOs may have a
combination of open manure storage
structures and covered structures, while
others will house all animals and store
all manure, feed and by-products under
cover. In either case, all parts of the
production area will need to be covered
by the demonstrations required under
§ 122.23(h)(2)(i)(A) and (B). In addition,
like permitted new source swine,
poultry, and veal calf operations, any
unpermitted CAFO seeking to certify no
discharge would be required to
implement the measures set forth in 40
CFR 412.37(a) and (b) for the production
area. These additional measures pertain
to operation and maintenance and
include provisions for visual
inspections, depth markers for all open
surface liquid impoundments,
corrective action, mortality handling
and recordkeeping. Since both these
permitted new source operations and
unpermitted certified CAFOs would
need to ensure no discharge from the
production area under the permit and
certification requirements, respectively,
EPA believes it is appropriate to rely, in
part, on those provisions to establish
eligibility criteria for no discharge
certification. The documents that would
be necessary to satisfy this eligibility
requirement would include design
documentation and all recordkeeping
and operation and maintenance
planning necessary to address the
elements of proposed § 122.23(h)(2)(i),
which includes the measures set forth in
§ 412.37(a) and (b). EPA is considering
developing a recordkeeping checklist for
use by certified CAFOs. Such a checklist
would be made available to all CAFO
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operators through EPA guidance
published subsequent to issuance of the
final CAFO rule. EPA requests comment
on whether such a checklist would be
useful.
The second eligibility criterion would
require the CAFO to develop,
implement, and maintain on site an
NMP that addresses, at a minimum, the
elements set forth in 40 CFR
122.42(e)(1) and 40 CFR 412.37(c), and
addresses all operation and
maintenance practices necessary to
ensure that the CAFO will not
discharge. The NMP would include
provisions regarding nutrient
management in the production area as
well as in all land application areas
under the control of the CAFO where
the CAFO will land-apply manure. EPA
believes that implementation of an NMP
is an essential component of any
CAFO’s efforts to ensure that it will not
discharge from its production or land
application areas. EPA notes that a
comprehensive nutrient management
plan (CNMP), developed in accordance
with Natural Resources Conservation
Service (NRCS) technical guidance for
CNMPs,2 would be sufficient to meet
this eligibility criterion as long as the
CNMP addresses the minimum elements
set forth in 40 CFR 122.42(e)(1) and
§ 412.37(c), and the CAFO addresses all
the necessary operation and
maintenance protocols either in the
CNMP or one or more operation and
maintenance plans. It is common for an
operation to have one or more operation
and maintenance plans in order to
properly implement a number of NRCS
conservation practice standards
simultaneously. Also, to the extent that
the necessary operation and
maintenance requirements to implement
any provision of the NMP are not
included in the NMP itself, those
requirements would need to be included
in an operation and maintenance plan to
be implemented and maintained on site.
Proper certification would require the
CAFO to revise its NMP if any of the
design specifications, practices or other
NMP provisions changed over time. For
example, if the CAFO decided to landapply manure on a field that was not
included in the NMP, the CAFO would
need to calculate rates of application in
accordance with the protocols required
by § 122.42(e)(1)(viii) and revise the
NMP to include the new field and the
corresponding application rates.
Because valid certification would
require the CAFO to at all times be
2 Technical Guidance for Developing
Comprehensive Nutrient Management Plans, USDA
Natural Resources Conservation Service (2003),
available at https://policy.nrcs.usda.gov/
viewerFS.aspx?id=3073.
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designed, constructed, operated, and
maintained such that it meets the
eligibility criteria to establish that the
operation does not discharge or propose
to discharge (see proposed
§ 122.23(h)(4), discussed below), to
maintain a valid certification, a CAFO
should make the adjustments necessary
to accommodate a change in
circumstances, before the circumstances
change. For example, if an increase in
animals would cause the operation to
exceed the existing storage capacity for
precipitation, manure and process
wastewater required for no discharge, to
remain certified the CAFO would need
to remedy the storage capacity problem
prior to bringing the additional animals
to the operation.
EPA would encourage a CAFO
preparing the documents necessary for
the proposed certification to consult
with a professional engineer and an
NRCS-certified technical service
provider (TSP) or other qualified
nutrient management planner. Any
professional consulted by the CAFO
should have the requisite training,
experience and expertise to conduct
and/or substantively review the
required analyses, and to advise the
owner or operator as to whether the
CAFO is, in fact, designed, constructed,
operated, and maintained such that it
will not discharge.
4. Submitting the Certification
Under the proposed certification
option, a CAFO seeking to certify that it
does not discharge or propose to
discharge would be required to submit
the certification to the permitting
authority. Under proposed
§ 122.23(h)(3), the submission to the
Director would include: (1) The CAFO
owner or operator’s name, address and
phone number; (2) information
regarding the CAFO’s location,
including latitude and longitude; (3) a
description of the manner in which the
CAFO satisfies the eligibility
requirements of § 122.23(h)(2); (4) the
certification statement set forth in
proposed § 122.23(h)(3)(iv); and (5) an
official signature that meets the
signatory requirements of 40 CFR
122.22. The signed certification would
make the CAFO legally responsible for
its representations to the Director
regarding the design, construction,
operation, and maintenance of the
CAFO. The language regarding legal
liability for making a false statement
under the proposed option is consistent
with language in 40 CFR 122.26(g)
which applies to facilities seeking to
obtain a ‘‘no exposure’’ exclusion for
industrial storm water.
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Today’s proposed rule would make no
changes to the existing regulations
concerning how CAFOs may make
Confidential Business Information (CBI)
claims with respect to information they
must submit to the permitting authority
and how those claims will be evaluated.
A facility may make a claim of
confidentiality under the existing
regulations at 40 CFR part 2, subpart B.
The third item the Agency is
proposing for submission to the
Director, as listed above, is a statement
describing the manner in which the
CAFO satisfies the certification
eligibility criteria. EPA believes that, at
a minimum, the description to be
submitted to the Director should
include: (1) The type and number of
animals; (2) the type and capacity of
manure and wastewater storage and/or
containment; (3) storm size used as
basis for containment design; (4)
whether the CAFO consulted with a
professional engineer or TSP; (5)
identification of the documents
maintained on site in accordance with
the eligibility criteria; and (6) any
technical standards, tools (e.g., RUSLE
and Phosphorus Index) and formulas
used to calculate application rates of
manure, litter, and process wastewater.
EPA seeks comment on whether this is
the scope and type of information that
should be submitted, as well as
suggestions of other information that
should be included in the eligibility
description submitted for certification.
The authority given to the permitting
authority under section 308 of the CWA
to conduct inspections at point source
operations would not be affected by this
proposed rule. Therefore, any CAFO,
whether it is certified, permitted, or
neither, may be subject to an
information gathering request or
inspection, at the Director’s discretion
and for any of the reasons provided by
section 308 of the Clean Water Act. 33
U.S.C. 1318.
Under the proposal, the certification
would become effective upon
submission to the Director. The
proposed rule would require the use of
certified mail or equivalent method of
documentation for identifying the date
of submission.
5. Limitations on Certification
This proposed rule also includes
several limitations on certification
related to the term of a valid
certification, reporting, and recertification when a certification
becomes invalid. EPA proposes that the
certification would be valid for five
years from the date of certification or
would terminate when the CAFO has
either discharged or ceases to be
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designed, constructed, operated and
maintained in accordance with the
documentation supporting the
certification (i.e., its production area
design documentation and nutrient
management plan), whichever is sooner.
See proposed § 122.23(h)(4). EPA is
proposing that a valid certification
would need to be renewed, if desired by
the CAFO, every five years. This is the
maximum statutory term of an NPDES
permit. The permit renewal process
provides the opportunity for operations
of a permitted CAFO to be reviewed to
ensure that they still meet the
requirements of the Clean Water Act
and for new conditions to be imposed
as necessary. EPA believes that a fiveyear term for no discharge certifications
will similarly prompt the CAFO to
periodically reevaluate whether it is
designed, constructed, operated, and
maintained so as not to discharge and
make adjustments to operations where
necessary. EPA seeks comment on
whether five years is an appropriate
length of time for a no discharge
certification.
In the unlikely event of a discharge
from a certified CAFO, the CAFO
operator, although subject to liability for
the discharge itself, would not be liable
for a violation of the duty to apply in
§ 122.23(d), but the certification would
cease to be valid. Similarly, should a
CAFO fail to continue to meet any of the
eligibility criteria, the CAFO’s
certification would no longer be valid.
Circumstances that could result in the
certification becoming invalid would
include, for example, an increase in
animals that exceeds the capacity of the
production area for manure storage and
handling, a loss of land application
areas such that the assumptions in the
NMP concerning land application
would no longer be appropriate, and a
discharge of pollutants to waters of the
United States (other than discharges of
agricultural stormwater from the land
application area, which is exempt from
permitting requirements).
Once a certification ceased to be
valid, the operator would not be able to
rely on it if an enforcement action were
brought for a subsequent violation of the
duty to apply for a permit. In sum, a
discharge by the CAFO or failure of a
certified CAFO to continue to be
designed, constructed, operated, and
maintained in accordance with the
eligibility criteria and certification
statement would render the certification
invalid and put the CAFO in the same
position as any other unpermitted and
uncertified CAFO.
Failure to continue to meet the
eligibility requirements for certification
in proposed § 122.23(h)(2) would not, in
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and of itself, be a violation of any
regulatory requirement, since
certification would be strictly voluntary.
For example, failure to implement the
measures set forth in § 412.37(a)–(b),
which would be required for no
discharge certification eligibility under
proposed § 122.23(h)(2)(i), would not be
a violation of § 412.37(a)–(b) but would
render the certification invalid.
Under proposed § 122.23(h)(5) a
CAFO could withdraw its certification
at anytime by notifying the Director, by
certified mail or equivalent method of
documentation, that it was withdrawing
its certification. The certification would
be withdrawn on the date the
notification was submitted to the
Director. If a CAFO certification
becomes invalid, proposed
§ 122.23(h)(5) would require the CAFO
operator to withdraw its certification
within three days of the date on which
the CAFO’s no discharge certification
became invalid.
The CAFO operator would not be
required to notify the Director of the
reason for withdrawing the certification,
or even if it was withdrawn because
some change in circumstances had
rendered it invalid or merely because
the operator no longer chooses to
maintain it. For example, an operator
might decide that particular
recordkeeping requirements needed for
certification were more burdensome
than the certification was worth, and
choose to withdraw the certification so
as not to have to keep such records.
While EPA believes it is important for
permitting authorities to have an
accurate and up-to-date record of which
unpermitted CAFOs have a valid no
discharge certification, and thus to
require operators to withdraw any
certification which ceases to be valid,
EPA also wishes to emphasize that
certification is strictly voluntary, and
can be withdrawn by the operator
without explanation at any time.
If a certification is withdrawn because
it ceases to be valid, the operator could
seek to re-certify that the CAFO does not
discharge or propose to discharge by
revising its operations to address the
deficiency and submitting a new
certification statement. If the
certification was rendered invalid by a
discharge, under proposed
§ 122.23(h)(5), in order to re-certify, a
CAFO would have to submit to the
Director the information required under
§ 122.23(h)(3) and additional
information describing the discharge,
including the time, date, cause, and
approximate volume of the discharge,
and the steps taken by the CAFO to
permanently address the cause of the
discharge, i.e., to ensure that no
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discharge from this cause occurs in the
future. While review and approval of
the technical basis for certification by
the permitting authority is not generally
required, EPA believes it is appropriate
in situations where a certified CAFO has
in fact discharged and still believes that
it can certify that it does not discharge
or propose to discharge, for the operator
to provide sufficient information to
assure the Director that the cause of the
discharge has been adequately
addressed to ensure that there will not
be future such discharges. EPA would
generally consider a recurring discharge
as evidence that a CAFO is not eligible
for certification or re-certification and
would need to seek permit coverage.
6. Additional Rationale
As stated above, under the 2006
proposed revisions to 40 CFR
122.23(d)(1), a CAFO that does not
discharge or propose to discharge would
not be subject to the duty to apply for
an NPDES permit. However, as
discussed in the preamble to the 2006
proposed rule, if an unpermitted CAFO
discharges, the CAFO would be in
violation of section 301(a) of the CWA
due to the unpermitted discharge and
could be in violation of the duty to
apply if the CAFO could have
reasonably foreseen that the discharge
would occur and did not seek permit
coverage prior to discharge. A valid
certification, however, would document
the CAFO operator’s basis for making an
informed decision not to seek permit
coverage because the CAFO does not
discharge or propose to discharge, and
would protect the CAFO from being
held liable for not applying for the
permit prior to discharge. In the
unlikely event that a properly certified
CAFO discharges, the CAFO would not
be subject to liability for failure to seek
permit coverage prior to discharge in
violation of 40 CFR 122.23(d) and
section 308 of the CWA. However, any
discharge even from a properly certified
CAFO would be an unpermitted
discharge in violation of CWA section
301 subject to applicable injunctive
relief and penalties.
EPA believes that providing
protection from liability for violation of
40 CFR 122.23(d) and section 308 for a
properly certified CAFO is reasonable
and justified. Certification would
require a CAFO owner or operator to
undertake and document a rigorous
analysis of the operation’s structure and
design, and to be committed to
operation and maintenance protocols
designed to ensure no discharge. As
stated above, certification is entirely
voluntary for a CAFO that does not
discharge or propose to discharge. EPA
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believes that a CAFO owner or operator
that would make the effort and take the
steps needed to certify no discharge
should be afforded protection from
enforcement for failure to have applied
for a permit prior to discharge if, in the
future, there is an unanticipated
discharge from the CAFO, so long as
there has been no lapse in the CAFO’s
eligibility for certification. The operator
of an unpermitted CAFO choosing not
to make and document this certification
in accordance with each element listed
in 40 CFR 122.23(h)(2)–(3) would not
receive the liability protection provided
by a no discharge certification.
Unlike the 2003 rule that required all
CAFOs to seek permit coverage in order
to operate unless they obtained a
determination of ‘‘no potential to
discharge,’’ the certification provision
proposed here would be entirely
voluntary. The purpose of the
certification would be to provide a
mechanism by which a CAFO can
document that it does not discharge or
propose to discharge and be assured that
even if the CAFO does discharge in the
future, it would not face an enforcement
action for failure to apply for a permit.
The certification process would not, in
and of itself, establish whether the
CAFO must apply for a permit. As
proposed in 2006, the requirement for a
CAFO to apply for a permit would be
triggered only when a CAFO discharges
or proposes to discharge. 71 FR 37,784.
The decision to seek permit coverage or
no discharge certification would be
made by the operator based on an
objective assessment of conditions at the
facility, in contrast to the 2003 rule,
which required the operator either to
seek permit coverage or prove to the
satisfaction of the Director that the
CAFO had no potential to discharge.
Therefore, under this proposed rule and
§ 122.23(d)(1), the operator would
decide whether (1) to obtain permit
coverage; (2) to certify under the
provisions at 122.23(h); or (3) to operate
without either a permit or certification.
EPA notes that a CAFO that chooses to
operate without a permit implicitly
faces more stringent requirements than
permitted CAFOs because discharges in
any size storm event are prohibited from
unpermitted CAFOs, while certain
exceptions may be applicable to
permitted CAFOs. NPDES permit
coverage reduces CAFO operator risk
and provides certainty to CAFO
operators regarding activities and
actions that are necessary to comply
with the Clean Water Act.
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B. Terms of the Nutrient Management
Plan
In this notice, the Agency is
proposing a framework for identifying
the terms of the nutrient management
plan (NMP) that must be enforceable
requirements of a CAFO’s NPDES
permit. The proposed framework
includes three alternative approaches
for specifying terms of the NMP with
respect to rates of application, which are
needed to satisfy the requirement that
the NMP include ‘‘protocols to land
apply manure, litter or process
wastewater * * * that ensure
appropriate agricultural utilization of
the nutrients.’’ 40 CFR 122.42(e)(1)(viii).
For Large CAFOs, these proposed
alternatives would also satisfy the
requirements set forth in 40 CFR 412.4.
The proposed framework would include
supplemental annual reporting
requirements for permitted CAFOs to
accompany these proposed alternative
approaches. In addition, this
supplemental proposal includes two
revisions to the 2006 proposed rule with
respect to changes to a CAFO’s NMP,
including revisions to the proposed
conditions that would constitute
substantial change to the terms of the
NMP. This supplemental proposal seeks
comment on the proposed framework
for specifying terms of the NMP to be
included in an NPDES permit, and on
the proposals for changes to the NMP
included in this notice. No NMP
provisions promulgated in the 2003
final rule are affected or reopened by
this supplemental proposal, nor is EPA
reopening the comment period on the
2006 proposed rule.
1. Background
As discussed in the June 2006
proposed rule, the Waterkeeper court
held that the ‘‘terms of the NMP’’ are
effluent limitations that must be
included in the permit. Waterkeeper
Alliance v. EPA, 399 F.3d 486, 502 (2d
Cir. 2005). In the preamble to the
proposed rule, EPA discussed how the
‘‘terms’’ of a CAFO’s NMP could be
identified and included in the permit.
As stated in the June 2006 proposed
rule, the terms of the NMP would need
to address the nine minimum required
elements in 40 CFR 122.42(e)(1)(i)–(ix)
and 412.4(c) (for Large CAFOs, as
applicable). 71 FR 37753.
The 2006 proposed rule preamble
identified a number of factors that are
necessary to the development of an
NMP, including: The maximum amount
of manure that the CAFO may apply to
land application areas under its control;
an inventory of the fields for land
application and the associated acreage,
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soil types, soil tests and testing
protocols; setbacks and other
conservation measures; and a list of all
of the crops the CAFO may wish to grow
on each of those fields with a matrix of
the associated realistic yield
expectations and land application rates
consistent with the various field
conditions. 71 FR 37755. The Agency
also stated that the NMP should include
calculations necessary to determine
rates of application for the array of crops
most likely to be planted in accordance
with the cropping system utilized by the
CAFO operator and could include likely
alternative scenarios for other crops that
could be planted. In the Agency’s view,
listing alternative cropping plans would
allow a CAFO some flexibility in
utilizing different combinations of crops
and crop rotations for land application.
However, the Agency added that the
NMP should reasonably forecast the
practices most likely to be utilized by
the CAFO. In the proposed rule
preamble, EPA solicited comment on
the degree of flexibility that should be
allowed in NMPs, particularly regarding
the terms of the NMP included as
permit conditions, and highlighted the
advantages and disadvantages of
allowing some flexibility to the CAFO
operator. 71 FR 37753–55.
With respect to portions of the NMP
that would be incorporated as permit
terms, the Agency also proposed
regulatory language for accommodating
changes to the NMP that involve
changes to the terms during the permit
period. The proposed rule identified
changes to the terms of the NMP that
would be considered substantial
changes and those that would be
considered nonsubstantial changes. The
items listed as constituting a substantial
change to the terms of the NMP
included changes that could result in an
increase in runoff of manure, litter, or
process wastewater from the facility and
changes that could result in an increase
in the rate of nutrients from manure,
litter, or process wastewater applied to
the land application area that is
significant in relation to technical
standards established by the Director. 71
FR 37,756.
EPA received many comments on the
NMP issues highlighted in the proposed
rule preamble. Commenters stressed the
complexity associated with nutrient
management planning, particularly with
respect to land application, and the
need to address changes in operation as
well as changes due to circumstances
beyond the CAFO’s control arising
during the permit term, especially
where such changes would lead to
different rates of application of manure,
litter, and process wastewater. Many
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commenters wanted clarification of the
terms associated with land application,
and a number of commenters suggested
factors that should be included as terms
of the NMP.
In reviewing these comments, the
Agency has determined that a provision
specifically identifying the terms of the
NMP required to be included in the
permit would address a number of these
concerns. In particular, the comments
indicated a need to clarify what
constitutes the terms of the NMP
regarding rates of application, given the
complexity of factors used to determine
rates of application and the dynamics
associated with such factors. This
clarification would facilitate a common
understanding of the terms of the NMP
required in a CAFO’s permit, and
thereby reduce the likelihood of
confusion and promote better awareness
of what the permitting authority must
do to ensure that the permit complies
with the Clean Water Act and these
regulations and of what a CAFO must
do to comply with its permit. Moreover,
specifically identifying the terms that
must be included for each CAFO would
enhance the public’s ability to
participate meaningfully in the
development, revision, and enforcement
of the terms of the NMP as called for by
the Second Circuit in the Waterkeeper
decision.
2. Supplemental Proposal for Terms of
the NMP To Be Included in the Permit
In light of these concerns, EPA is
supplementing the June 2006 proposed
rule with a proposal to specify in the
regulation what elements of the NMP
would be terms of the NMP that would
be required to be included as
enforceable terms of a CAFO’s NPDES
permit. The rule would require that the
terms of the NMP must include the
information, protocols, best
management practices, and other
conditions identified in a CAFO’s
nutrient management plan and
determined by the permitting authority
to be necessary to meet the requirements
of 40 CFR 122.42(e)(1). For Large CAFOs
subject to the land application
requirements of the effluent limitations
guideline, the terms would include the
best management practices in 40 CFR
412.4(c) in addition to the requirements
of part 122.
The ‘‘information, protocols, best
management practices, and other
conditions’’ that would constitute the
terms of the NMP would include what
the CAFO operator would be required to
do to properly implement its NMP and
determinative conditions upon which
such actions are based. For example,
both the structural design capacity
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necessary to satisfy the storage
requirement of § (e)(1)(i) and the
associated operational and maintenance
conditions necessary to ensure adequate
storage, would be considered terms of
the NMP. Likewise, the terms of the
NMP would need to ensure, for
example, proper management of
mortalities and diversion of clean water.
However, the number of animals
confined would not necessarily need to
be a term of the NMP because a CAFO
operator would be required to properly
operate and maintain the CAFO’s
storage facilities regardless of the
number of animals or the volume of
manure, litter, or process wastewater
generated. On the other hand, the
Director could, for example, include an
upper limit on the number of animals as
a term.
For CAFOs that land apply manure,
litter, and process wastewater, the fields
the CAFO plans to use for land
application would be a term of the
NMP. Similarly, as discussed in greater
detail below, field-specific, cropspecific application rates would be
terms of the NMP, as would certain
factors needed to determine the rates.
However, background information that
is fixed and unchangeable, such as
actual historic yields used in the
development of an NMP, while
important for determining rates of
application, would not need to be terms
of the NMP.
3. Rates of Application
40 CFR 122.42(e)(1)(viii) requires the
nutrient management plan to include
‘‘protocols to land apply manure, litter
or process wastewater in accordance
with site specific nutrient management
practices that ensure appropriate
agricultural utilization of the nutrients
in the manure, litter or process
wastewater.’’ As EPA noted in the June
2006 proposed rule, the Waterkeeper
court focused on rates of application as
perhaps the most important term of the
NMP, in particular the provisions of the
effluent limitations guidelines in 40
CFR 412.4(c), and emphasized their sitespecific nature. 71 FR 37753. In
considering the elements of an NMP
that should be identified as the
minimum terms with respect to land
application rates, in light of comments
received on the 2006 proposed rule, two
general principles emerged. First, rates
of application depend on the
information on which they are based,
such as information about the field,
crops, and nutrient content of the
manure. Second, this information can
change, and in order to address
changing circumstances during the
period of a permit (ordinarily five
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12329
years), there is a need for some
flexibility in establishing rates of
application. The Agency proposes three
alternative approaches, discussed
below, which vary in the degree of
flexibility with respect to expressing
rates of application and factors to be
included in the permit as terms of the
NMP. However, all three approaches
would ensure that legally-enforceable
field- and crop-specific application rates
are included in the permit.
Rates of application are field-specific
and are designed to ensure that crops
receive sufficient nutrients to meet yield
goals, while minimizing the amounts of
nutrients that could be transported from
the field. The total amount of plant
available nutrients necessary to meet
yield goals includes residual nutrients
already in the field and the nutrients
added for a particular crop. Residual
nutrients are those in the soil or on the
field remaining from prior applications
of manure, litter, process wastewater, or
chemical fertilizer, or from other
sources such as crop residues and
nitrogen fixing legumes. The addition of
nutrients to a field includes application
of chemical fertilizer, as well as
application of manure, litter, or process
wastewater.
The NMP must consider the capacity
of the field for manure, litter, or process
wastewater application, generally
depending on the capacity of the soil to
retain phosphorus. State technical
standards generally require the use of
the phosphorus index or a similar tool
for assessing the potential for nutrient
transport from a field and for
determining the limiting nutrient
(phosphorus or nitrogen) for application
of manure, litter, or process wastewater.
The outcome of the assessment of the
potential for phosphorus transport does
not typically change from year to year.
However, because soil phosphorus
levels tend to change incrementally
depending upon the buffering capacity
of the soil, this assessment may limit the
amount of phosphorus, and thus the
amount of manure, litter, and process
wastewater, that may be added to a
field.
Once the residual nutrients and
potential for nutrient transport from the
fields has been determined, the next
step is to identify the crops to be
planted, or other uses, for each field
where land application will occur and
the nitrogen and phosphorus needs of
these crops or other uses. The NMP also
must identify the realistic yield
expected from the crop or crops planted
in the field, in order to calculate the
proper amount of nutrients to apply. A
crop’s nutrient needs are generally
determined in accordance with the
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nutrient recommendations for a given
crop (or other planting, such as forage
or pasture) and the per acre realistic
yield goal for such crop, both of which
are typically set by the State land grant
university or based on equations
provided by the land grant university.
The realistic yield rate can also be based
on historic field-specific yield data.
Finally, the amount of manure, litter,
or process wastewater, in tons or
gallons, to be land applied in order to
meet, but not exceed, crop nutrient
needs (after considering residual
nutrients and potential for nutrient
transport from fields) depends on the
nutrient content of the manure, litter,
and process wastewater, as well as the
source and form of nutrients to be land
applied and the method and timing of
land application. Whereas one CAFO
operator may wish to follow the
planned sequence of steps for planting
crops and applying manure, litter, and
process wastewater described in the
NMP submitted to the Director, another
operator may want or need to vary from
that linear sequence of events, due to
choices made in the course of normal
operations, or in response to events or
circumstances beyond the CAFO’s
control, such as weather, crop failure, or
market conditions. EPA addressed these
concerns in the preamble to the 2006
proposed rule, and stated that the
proposed approach could accommodate
such changes.
In the proposed rule preamble
discussion concerning changes to the
terms of the nutrient management plan,
EPA encouraged CAFO operators to
develop NMPs that anticipate
contingencies and changes in operations
that may occur over the term of the
permit. Such contingencies may include
other potential crops that could be
planted, or possible crop rotations or
other alterations in cropping patterns
with accompanying field-specific
calculations for manure, litter, and
process wastewater application rates
based on realistic crop yield goals, soil
characteristics, typical weather patterns,
and other site-specific field conditions.
The Agency noted that the public would
then have the opportunity to review all
anticipated operational scenarios and
associated field-specific manure, litter,
and process wastewater application
rates, including the calculations on
which these rates were based. The
Agency viewed this approach as
allowing an NMP to address most yearto-year changes in nutrient management
practices anticipated during the period
of permit coverage and greatly reduce
the need for NMP and associated permit
modifications, as the NMP would have
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already accounted for a range of
potential operational scenarios.
With respect to identifying annual
rates of application as terms of the NMP,
a number of commenters stated that it
was unrealistic for EPA to expect all
CAFOs to be able to establish rates of
application as terms of the NMP for the
full period of permit coverage and asked
EPA for a process to establish rates on
an annual basis. They based their
comments on the variability, range, and
interdependency of factors associated
with the determination of rates of
application. Some commenters
preferred greater flexibility for CAFO
operators in setting such rates, while
others thought that application rates
should be made available for public
comment each year.
In this supplemental proposal, EPA is
proposing to include in the rule three
distinct alternative approaches for
expressing the terms of the nutrient
management plan with respect to rates
of application. Each approach would
establish annual maximum rates of
application of manure, litter, and
process wastewater by field and crop for
each year of permit coverage and would
identify the minimum required terms of
the NMP specific to that approach. Each
approach would also require annual
reporting requirements to provide actual
data that would be publicly available
concerning compliance with permit
requirements during the previous year.
The three approaches would express
field-specific maximum rates of
application, respectively, as follows: (1)
As tons or gallons of manure, litter, and
process wastewater to be applied; (2) as
the amount of nitrogen and phosphorus
from manure, litter, and process
wastewater to be applied; or (3) as a
narrative rate for calculating the amount
of manure, litter, and process
wastewater to be applied. The first
approach would require a permit
modification to exceed the amount of
manure, litter, and process wastewater
specified for a particular crop or field in
the original permit. The second
approach is more flexible in that it
would allow CAFOs to adjust the level,
method and timing of manure, litter,
and process wastewater application as
long as the field- and crop-specific
amounts of nutrients were not exceeded
without having to seek permit
modifications. The third approach is the
most flexible, because it would use a
methodology and actual field data to
calculate in real time the amount of
manure, litter, and process wastewater
to be land applied, and is thus best
suited to allow the operator to adjust
application rates in response to changes
in field specific conditions.
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All three approaches would require
the CAFO operator to develop an NMP
that projects for each field and for each
year of permit coverage the crops to be
planted, crop rotation, crop nutrient
needs, expected yield, and projected
rates of application of manure, litter,
and process wastewater. However, each
approach is different in identifying
which of these projections would be
required to be ‘‘terms of the NMP.’’ Each
approach would result in annual rates of
application of manure, litter, and
process wastewater that are maximum
application rates stated in the permit
and that would be enforceable, and each
would require that application rates be
specific for each crop that would be
planted on a specific field.
A properly developed NMP must
evaluate the condition of the fields to be
used for land application based on soil
test levels, the form(s) and amount(s) of
manure, litter, or process wastewater
generated by the CAFO, and the uses for
each field; for example, crop, pasture, or
fallow land. An NMP must also describe
on a field-by-field basis how the
application rates are calculated, which
for large CAFOs must be in accordance
with State technical standards.
These calculations must also take into
account, with respect to each crop to be
grown or other agricultural use, the
source and form of nutrients to be land
applied, the method of application of
manure, litter, and process wastewater,
and the timing of when application will
occur. Although a properly developed
NMP involves consideration of all of
these factors, some operators may have
multiple sources of manure, litter, or
process wastewater and may need to
make the determination as to which
source to draw from for land application
to a particular field in a given year at
some point in time after the NMP has
been developed. The method of
application depends on the source and
form of manure, litter, or process
wastewater, on the location of a
particular field and the equipment
available for such field, and on the crop
to be planted. For example, wastewater
may be spray-irrigated, surface applied,
or injected, whereas poultry litter is
most likely to be surface applied by a
manure spreader.
The forms of plant available nitrogen
and phosphorus to be factored into
calculations for rates of application
should be identified in the technical
standards established by the Director or
in other documentation referenced in
the State’s technical standards.
Typically, the amounts of plant
available phosphorus are determined
based on the amount of phosphate and
the amount of organic phosphorus that
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will mineralize during the growing
season, and the amount of plant
available nitrogen is based on the
amount of nitrate and ammoniumnitrogen and the amount of organic
nitrogen that will mineralize during the
growing season. As previously
discussed, it is the plant available forms
of nitrogen and phosphorus that are
relevant in determining rates of
application. If there is any disagreement
as to the appropriate forms of nitrogen
and phosphorus to be factored into
these calculations, the Director would
determine the acceptable approach. The
amount of plant available nitrogen also
depends on the nitrogen volatilization
rate associated with the source of
nutrients and the timing and method of
land application.
EPA expects a complete NMP to also
account for any other additions of crop
available nutrients during the crop year,
such as chemical fertilizer, irrigation
water (groundwater may have
measurable concentrations of nutrients),
and biosolids, where applied. Crediting
for all residual nitrogen and phosphorus
in the field that will be plant available,
including crediting for additions from
each prior year of the permit term, as
well as accounting for other additions of
nitrogen and phosphorus, should be
done in accordance with the directions
provided in the technical standards
(required for all permitted Large
CAFOs). Since organic forms of
nutrients typically become plant
available when they are converted to
inorganic forms, such as nitrate,
ammonium, and phosphate, crediting
generally identifies the amount of
organic nutrients likely to be converted
to inorganic forms that will be plant
available. Credits would be based on the
soil test results included in the NMP
and projected applications of nutrients
from manure, litter, and process
wastewater during intervening years, as
well as other additions, including from
crops (e.g., where crops are plowed
under or residues are left on the field),
commercial fertilizer, and other sources
of nutrients remaining on the field that
would be plant available during the next
growing season. Credits would also be
based on mineralization rates and crop
uptake of nutrients.
Because a CAFO operator could plant
more than one crop on a field in a given
year, the plant available amount of
nitrogen and phosphorus would need to
be calculated with reference to the
nutrient needs of all the crops to be
planted on such field in a given year in
order to be accurate. This would include
accounting for other field uses for
agricultural purposes, such as pasture
and cover crops, because EPA expects a
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complete NMP to account for other uses
of a field.
Under all three of the proposed
approaches, the terms of the NMP
would be required to include specific
factors used for the development of rates
of application. These would include:
• The outcome of the field-specific
assessment of the potential for nitrogen
and phosphorus transport from each
field;
• The crop or crops to be planted in
each field or any other uses such as
pasture or fallow fields;
• The realistic annual yield goal for
each crop or use identified for each
field; and
• The nitrogen and phosphorus
recommendations from sources
acceptable to the Director for each crop
or use identified for each field.
The phrase ‘‘outcome of the fieldspecific assessment of the potential for
nitrogen and phosphorus transport from
each field’’ reflects the terminology
typically associated with the use of the
phosphorus index in accordance with
the USDA conservation practice
standard 590 that has been adopted by
many States. However, EPA
contemplates that, since the 590
standard allows States to use other
methodologies, such as soil test
phosphorus and phosphorus threshold,
any one of these would satisfy the
requirements of this proposed rule.
Ultimately, the purpose of the fieldspecific assessment of the potential for
nitrogen and phosphorus transport is to
determine the appropriate limiting
nutrient for developing land application
rates, i.e., whether phosphorus or
nitrogen limits the amount of manure,
litter, or process wastewater that can be
applied and the degree to which the
limiting nutrient restricts land
application.
Each of the three approaches differ in
the way that they would account for
other information necessary for
determining the appropriate rates of
application. This information relates to:
(1) Credits for residual nitrogen and
phosphorus available in each successive
year during the five-year term of the
permit; (2) accounting for additions of
commercial fertilizer and other
additions of nitrogen and phosphorus
during each successive year; (3) the
form (liquid, solid) and source (e.g.,
lagoon, compost, process wastewater) of
the material to be land applied; (4)
nitrogen and phosphorus content of the
manure, litter, or process wastewater;
(5) timing of application; and (6)
method of application (e.g. spreading,
spray, injection).
The following three sections of the
preamble describe the specific aspects
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of each of the approaches and how each
approach accounts for these factors. See
the table that summarizes what the
terms would be for each of the three
approaches, available in the docket for
this rulemaking, EPA–HQ–OW–2005–
0037.
(a) Linear Approach—Rates Expressed
in Tons and Gallons of Manure, Litter,
and Process Wastewater
The first proposed approach would
allow the CAFO to express rates of
application as tons of manure or litter,
and gallons of manure or wastewater.
The terms of the NMP would include
maximum application rates for each
year of permit coverage, for each crop
identified in the NMP, in tons of
manure or litter, or gallons of manure or
process wastewater, per acre, per year,
for each field to be used for land
application. In addition, the terms of the
NMP would include:
• The outcome of the field-specific
assessment of the potential for nitrogen
and phosphorus transport from each
field;
• The crop or crops to be planted in
each field or any other uses such as
pasture or fallow fields;
• The realistic annual yield goal for
each crop or use identified for each
field;
• The nitrogen and phosphorus
recommendations from sources
acceptable to the Director for each crop
or use identified for each field;
• Credits for all nitrogen and
phosphorus in the field that will be
plant available;
• Accounting for all other additions
of plant available nitrogen and
phosphorus to the field;
• The form and source of manure,
litter, and process wastewater to be land
applied; and
• The timing and method of land
application.
This approach is considered a
‘‘linear’’ approach because it is based on
the use of only those crops included in
the planned crop rotations in the NMP;
the amounts of manure, litter, and
process wastewater to be land applied
according to the planned schedule for
land application (including source and
method and timing of application); and
the projected values for plant available
nitrogen and phosphorus from other
sources. Under this approach, rates
would follow the conventions by which
NMPs have been developed and would
require the CAFO to follow the
sequence identified in the NMP for each
field-specific crop rotation and each
planned step for land application of
manure, litter or process wastewater.
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While important to the development
of the NMP, some underlying factors
necessary for calculating rates of
application using this linear approach
in the NMP, and necessary to be
included in the NMP, would not be
required to be terms of the NMP. These
factors include the methodology for
determining rates of application, and
the values and formulas used in the
methodology for calculating
volatilization rates for nitrogen and
mineralization rates for organic nitrogen
and phosphorus. Because the maximum
rates of application using this approach
are expressed as amounts of manure,
litter, or process wastewater and are
terms of the NMP, and are based on the
use of these factors, these factors
themselves do not need to be terms of
the NMP. Whether these factors been
applied correctly and whether the rates
as calculated in the NMP are consistent
with applicable requirements, are issues
which are properly addressed when the
NMP is subject to review by the Director
and by the public. These are analogous
to the types of calculations and data
submitted in a permit application and
found in the fact sheet that accompanies
a draft NPDES permit for other types of
permitted point sources.
Under this approach, the CAFO
would land apply manure, litter, and
process wastewater, in the amounts
specified for each field in the NMP,
following the schedule and the methods
of application described in the NMP.
However, Large CAFOs would need to
take into account the annual manure
test results required by the 2003 final
rule, so as to not exceed the nutrient
needs of the crops, and limit actual rates
of application by adjusting the amount
of manure, litter, and process
wastewater to be applied if the
concentrations of nitrogen or
phosphorus in the manure were higher
than those projected in the plan.
The environmental and operational
integrity of this approach hinges on the
CAFO making accurate predictions in
the NMP that are not disrupted by
changes to the CAFO’s operation or by
circumstances beyond the control of the
CAFO operator. Any changes to the
terms of the NMP would constitute a
change to the terms of the permit, which
would require a permit modification.
(See discussion of substantial changes
below.) For example, any changes to the
planned crop sequence, such as the
addition of a second crop to a field,
where a CAFO might need to land apply
more than the maximum amount of
manure, litter, or process wastewater in
a given year would require a permit
modification.
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On the other hand, the advantage of
this approach is simplicity for the CAFO
operators with predicable land
application needs and for the public.
This would be particularly suitable for
operations that consistently plant one
crop or two crops in rotation on the
same fields, using the same source and
form of manure, litter, or process
wastewater, and that land apply on a
regular annual schedule using the same
application method(s).
EPA notes that even under the linear
approach, operators could retain some
flexibility by specifying more than one
field-specific crop rotation plan in the
NMP, with application rates of manure,
litter, and process wastewater specified
for each alternative plan and included
in the permit. This might be practical
for operators who are reasonably
confident that they will follow one of
two or three potential crop rotations.
EPA has developed the other two
approaches for operators needing a
greater degree of flexibility.
(b) Matrix Approach: Application Rates
Expressed as Pounds of Phosphorus and
Nitrogen
The second proposed approach
(‘‘matrix approach’’) would express, for
each year of permit coverage, rates of
application as the maximum amount of
plant available nitrogen and
phosphorus, in pounds, from manure,
litter, and process wastewater that could
be land applied for a particular crop on
a given field in a given year, rather than
amounts, in tons or gallons, of the
manure, litter, and process wastewater.
Also, under this approach, operators
would be able to identify for each field
alternative crops that they would
reasonably expect to plant in a given
year, along with allowable rates of
application for nitrogen and phosphorus
for each specified crop on the field.
This option would provide more
flexibility to operators than the first
approach because it would allow the
operator to vary the sequence of crops
in the planned rotation or substitute
other crops for those identified in the
planned rotation if the permit specified
different maximum rates of application
of nitrogen and phosphorus for each
crop and field for a given year, without
relying on permit modifications to allow
such changes. Such flexibility would be
possible because credits, when utilizing
such flexibility, would be based on the
‘‘baseline’’ amount of residual nitrogen
and phosphorus determined when the
NMP was developed and then used to
calculate maximum rates of application
for each of the crops identified in the
NMP for a given field. Addition or
substitution of other crops identified in
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the NMP and changes to the sequence
described in the NMP would then result
in the CAFO being limited to use of the
crop-specific maximum rates of nitrogen
and phosphorus from manure litter and
process wastewater for the crop actually
planted.
Typically, an NMP is written with
crop rotations that extend over several
years and generalized schedules for land
application of manure, litter, or process
wastewater. EPA is proposing that
CAFO operators who choose this
approach for expressing rates of
application would be allowed to
identify in the NMP other crops that
could be planted on a field in the form
of a matrix, with field-specific yield
goals, nutrient recommendations, and
maximum rates of nitrogen and
phosphorus application for each crop.
Unlike the linear approach, which
would rely on projections of the
amount, in tons or gallons, of manure,
litter, and process wastewater to be
land-applied, based on prescribed
sources, methods of application, and
timing, in the matrix approach, the
terms of the NMP would include
maximum limitations on the amount of
nitrogen and phosphorus, in pounds,
from manure, litter, and process
wastewater that could be land applied
and the methodology by which these
factors would be used to calculate how
much manure, litter, and process
wastewater would be allowed to be
applied so that the maximum
application rates of nitrogen and
phosphorus would not be exceeded.
This would provide flexibility to the
CAFO in selecting the source of manure,
litter or process wastewater, and the
choice of method of application, all of
which could vary during the period of
permit coverage. This approach would
ensure that the amount of manure, litter,
or process wastewater allowed to be
land-applied would be based on the
results of the most recent annual
manure test (which, for permitted Large
CAFOs, must be done at least annually,
as required by 40 CFR 412.4(c)(3)),
rather than on manure tests and
projections used in the development of
the NMP.
For CAFOs using the matrix
approach, the minimum factors used to
determine the rates of application in the
CAFO’s NMP that would be required to
be included as terms of the NMP would
be:
• The outcome of the field-specific
assessment of the potential for nitrogen
and phosphorus transport from each
field;
• The crop or crops to be planted in
each field or any other uses such as
pasture or fallow fields;
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• The realistic annual yield goal for
each crop or use identified for each
field;
• The nitrogen and phosphorus
recommendations from sources
acceptable to the Director for each crop
or use identified for each field;
• Credits for all nitrogen and
phosphorus in the field that will be
plant available;
• And accounting for all other
supplemental plant available additions
of nitrogen and phosphorus to the field.
In addition, this second approach
would add as a term of the NMP the
methodology by which the NMP
accounts for the following factors when
calculating the amounts of manure,
litter, and process wastewater to be land
applied:
• The form and source of manure,
litter, and process wastewater;
• The timing and method of
application; and
• The values and formulas used to
calculate volatilization of nitrogen and
mineralization of organic nitrogen and
phosphorus, which are necessary for
determining the availability of nitrogen
and phosphorus for crop uptake in
different forms of manure, depending on
method and timing of land application.
Under this approach, none of these
latter factors would itself be a term of
the NMP. Rather, the methodology used
in the NMP, which would be a term,
would allow the Director and the public
to predict how rates of application of
manure, litter, and process wastewater
would be calculated based upon
consistent use of the methodology in
accounting for all of these factors.
Most CAFO operators plan a specific
crop rotation around several crops that
may be planted on a given field.
Although crops are generally planted in
a manner that follows established crop
rotations, an operator may make farming
decisions that result in a different crop
being planted than was scheduled for a
given year in the CAFO’s NMP. A CAFO
may change its rotation for any number
of reasons including but not limited to,
drought, excessive rainfall, or changed
market conditions. The advantage of the
matrix approach is that it would not
lock the CAFO into a single planting
sequence for each field, nor into
applying manure from a particular
source, at a particular time, in a
particular way, thus reducing the need
for CAFOs to seek permit modifications.
A concern associated with the matrix
approach is that, in determining
maximum rates of application when
deviating from the planned rotation, the
levels of crop available nutrients in the
soil used for calculating rates would be
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the baseline levels established when the
NMP is developed and so would not
take into account any changes in crop
available nitrogen and phosphorus on
the field up to that point in the term of
the permit. Instead, the methodology
would need to estimate current levels of
crop available nutrients by estimating
residuals remaining from the prior
year(s) of crops, land application, and
other additions of nutrients since the
beginning of the permit period. Thus, a
CAFO applying at the maximum levels
of nitrogen and phosphorus allowed by
the permit could actually overapply
nitrogen and phosphorus if the amount
of crop available nitrogen or phosphorus
in the field were in fact higher than the
amounts estimated using the soil test
data available when the NMP was
developed. Conversely, if the crop
available nitrogen or phosphorus on the
field was lower than the amount used in
calculating the maximum rates
incorporated into the permit, a CAFO
applying at the maximum rate allowed
by the permit might be applying less
nitrogen and phosphorus from manure,
litter, and process wastewater than the
amount needed for the crop, and would
need to seek a permit modification if
more nutrients from manure, litter, and
process wastewater were needed.
This problem also exists to a lesser
degree for the linear approach, in that
factors not under the control of the
operator (eg, actual crop yields) might
affect the residual nutrients on the field
and thus the appropriate amounts of
manure, litter, and process wastewater
to apply. Where the maximum
application rates, under either
approach, are too high, because residual
nutrients on the field are higher than
projected, the operator may adjust the
application rates downward to reflect
these changes. However, where the
maximum rates are insufficient to
provide for the nutrient needs of the
crops, the operator will need to either
(1) increase the supply of nutrients from
other sources (eg, commercial fertilizer)
or (2) apply for a change to the permit.
EPA expects that operators will
generally use realistic yield assumptions
that will minimize, but not eliminate,
the need for such permit changes. The
third approach for determining permit
terms, discussed below, avoids this
problem by allowing the operator to
recalculate the specific amounts of
manure, litter, and process wastewater
to be applied based on field-specific
conditions in the year of application.
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(c) Narrative Rate Approach—Rates
Derived From Total Amounts of Crop
Available Nitrogen and Phosphorus
EPA is proposing a third approach
that would allow rates of application to
be expressed as a narrative rate that
includes the total amount of crop
available nutrients from all sources
combined with a specific, quantitative
method for calculating the amount, in
tons or gallons, of manure, litter, and
process wastewater to be land applied.
For this quantitative approach, the
terms of the NMP would include the
maximum amounts of total nitrogen and
phosphorus from all sources of nutrients
for each year of permit coverage for each
crop or other field use identified in the
nutrient management plan in chemical
forms determined to be acceptable to the
Director in pounds per acre per year for
each field.
The narrative rate approach would
include as terms the four terms required
under all three approaches:
• The outcome of the field-specific
assessment of the potential for nitrogen
and phosphorus transport from each
field;
• The crop or crops to be planted in
each field or any other uses such as
pasture or fallow fields;
• The realistic annual yield goal for
each crop or use identified for each
field; and
• The nitrogen and phosphorus
recommendations from sources
acceptable to the Director for each crop
or use identified for each field.
In addition, as in the matrix approach,
this second approach would include as
a term of the NMP the methodology by
which the NMP accounts for certain
factors when calculating the amounts of
manure, litter, and process wastewater
to be land applied.
Unlike the linear approach, the
amount of manure, litter, and process
wastewater to be applied as projected in
the NMP submitted with the permit
application or NOI would not be a term
of the NMP. Instead, the rate would be
the amount of manure, litter, and
process wastewater calculated using the
methodology and based on actual
amounts of plant available nitrogen and
phosphorus from all sources at the time
of land application. The amounts of
total nitrogen and phosphorus from all
sources would include the amounts, in
pounds, of plant available nitrogen and
phosphorus already on the field and
applied as commercial fertilizer, as well
as the amounts in the manure, litter, and
process wastewater to be land applied.
This approach would eliminate
certain issues associated with a five-year
planning cycle previously discussed in
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connection with the two approaches
presented above. A key difference of
this proposed approach is that it would
require the use of annual soil tests for
determining actual soil phosphorus
levels. EPA is proposing this approach
to allow CAFOs that may need to adjust
their rates of application of manure,
litter, and process wastewater due to
changes in soil levels of nitrogen and
phosphorus to do so without requiring
the permit to be modified. Therefore, it
is important to ensure that the actual
changes in soil levels of plant available
nitrogen and phosphorus are taken into
account, rather than relying on
projected fluctuations provided in the
NMP. The results of the annual soil test
and manure test data would be used to
calculate, in real time, the amount of
manure, litter and wastewater to be
applied, to supply the remaining
nitrogen and phosphorus needed for the
actual crop being planted on the field.
In addition to accounting for the crop
and field information, the methodology
for making this calculation would be
required to account for a number of
other variables, including the form and
source of the manure, litter, and process
wastewater and the timing and method
of application. In other words, the
maximum application rate for land
application of manure, litter, and
process wastewater would be a
requirement that the operator apply not
more than the maximum amount of
nitrogen and phosphorus calculated
using the methodology.
As stated above, the terms of the NMP
would include the complete
methodology for calculating the amount
of manure, litter, or process wastewater
to be applied. The proposed rule would
require the methodology to account for
the following factors:
• Results of soil tests conducted in
accordance with protocols identified in
the nutrient management plan, as
required by 40 CFR 122.42 (e)(1)(vii);
• Credits for all nitrogen and
phosphorus in the field that will be
plant available;
• The amount of nitrogen and
phosphorus in the manure, litter, and
process wastewater to be applied;
• All other additions of plant
available nitrogen and phosphorus to
the field;
• The form and source of manure,
litter, and process wastewater;
• The timing and method of land
application; and
• The values and formulas used to
calculate volatilization of nitrogen and
mineralization of organic nitrogen and
phosphorus.
The factors listed above would not
themselves be terms in the narrative rate
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approach, but the methodology used to
account for them in the CAFO’s permit
would be. Thus, the terms of the NMP
under this approach would not include
the amount of nitrogen and phosphorus
in the manure, litter, or process
wastewater to be land-applied as set
forth in the NMP. Nor would the terms
of the NMP include the predicted
source, form, timing, and method of
application of manure, litter, or process
wastewater set forth in the NMP. These
factors would be subject to recalculation
during the period of permit coverage,
using the methodology in the NMP for
calculating the amount of manure, litter
or process wastewater allowed to be
applied.
Under this proposed approach, the
NMP would include planned crop
rotations for each field and
corresponding projected amounts, in
tons or gallons, of manure, litter, and
process wastewater to be applied,
including all of the calculations for
determining such projected amounts, for
the period of permit coverage. This
would give the permitting authority and
the public an opportunity to review,
prior to permit issuance, the adequacy
of the CAFO’s methodology and the way
the CAFO would use the methodology
to calculate the appropriate amount of
manure, litter, and process wastewater
to be applied, based on the operator’s
planned crop rotation at the time of
permit issuance.
The narrative rate approach would
require the CAFO to recalculate the
application rates projected in the NMP,
in tons and gallons, of manure, litter,
and process wastewater, using the
methodology in the NMP, at least once
a year, throughout the period of permit
coverage. In recalculating these rates, a
CAFO would be required to use annual
soil tests and concurrent calculations of
credits for all plant available nitrogen
and phosphorus in the field. The CAFO
would then calculate the maximum
amount of nitrogen and phosphorus
from manure, litter, and process
wastewater allowed to be applied, as a
portion of the total amount of nitrogen
and phosphorus from all sources, using
the methodology in the NMP. In order
to ensure that such recalculations are
made available to the Director and the
public, the recalculations and the new
data from which they are derived would
be required to be reported in the CAFO’s
annual report for the previous twelve
months. In other words, the rate of
application would be an objective,
enforceable rate, because the permit
would specify the methodology required
for calculating the rate, certain values or
sources of information required to be
used in the methodology, and would
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limit the total amount of nitrogen and
phosphorus from all sources for each
year of the permit. Failure to comply
with the rate established under the
permit would be a violation of the
permit.
EPA believes that the flexibility of
this proposed approach would reduce
the burden on permitting authorities
and CAFO operators by decreasing the
number of substantial changes to the
permit, which require public notice and
comment, arising from changes to the
CAFO’s crop rotations, while ensuring
that all effluent limitations applicable to
a permitted CAFO are incorporated as
terms of the permit, as required by the
Waterkeeper decision.
As many commenters on the 2006
proposed rule pointed out and EPA
recognizes, there may be changes in
field conditions or practices at a CAFO,
including, for example, those that alter
the projected levels of crop available
nitrogen and phosphorus in the soil, or
in the manure, over the period of permit
coverage. Such changes introduce some
uncertainty in setting application rates
for five years as enforceable terms of the
permit. This third approach is designed
to accommodate these concerns, by
allowing a CAFO to compensate for
changes in soil levels of crop available
nutrients, in manure content, or in the
timing and method of application, by
adjusting the application rates
accordingly without the need for a
permit modification. However, the
operator would be limited to the total
crop-specific amount of nitrogen and
phosphorus from all sources and would
have to adhere to a methodology that
would establish the way in which such
rates could be calculated. Thus, in the
second and later years of the permit
term, this approach would provide an
accurate and verifiable means of
achieving realistic production goals
while minimizing transport of
phosphorus and nitrogen from the field.
This would help CAFOs to avoid the
possibility of over-application of
nitrogen or phosphorus because of
increased levels of nutrients in the soil,
compared to what was projected at the
time of permit issuance, and,
conversely, the possibility of failing to
meet crop agronomic needs due to
under-application of nitrogen or
phosphorus.
4. Changes to Nutrient Management
Plans
It is well understood that agricultural
operations modify their nutrient
management and farming practices
during the normal course of their
operations. Such alterations may require
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changes to a permitted CAFO’s NMP
during the period of permit coverage.
As discussed in the preamble to the
2006 proposed rule, the permit does not
need to be modified for all operating
changes. Because of the way NMPs are
developed, most routine changes at a
facility should not require changes to
the NMP itself. To minimize the need
for revision, nutrient management plans
should anticipate and accommodate
routine variations inherent in
agricultural operations such as
anticipated changes in crop rotation, as
well as changes in numbers of animals
and volume of manure, litter, or process
wastewater resulting from normal
fluctuations or a facility’s planned
expansion. Typically, an NMP is
developed to accommodate, for
example, normal fluctuations in herd or
flock size, capacity for manure, litter,
and process wastewater storage, the
fields available for land application and
their capacity for nutrient applications.
Moreover, as discussed in this
preamble, EPA would encourage
operators to develop an NMP that
includes reasonably predictable
alternatives that a CAFO may
implement during the period of permit
coverage. However, unanticipated
changes to a nutrient management plan
may nevertheless be necessary.
In the 2006 proposed rule, EPA
proposed a process that CAFOs and the
permitting authority would need to
follow when a CAFO makes changes to
its NMP. The proposal also included
criteria for determining when a change
to a CAFO’s NMP should be considered
a substantial change. In this
supplemental notice, the Agency is
soliciting comment on several
modifications to the 2006 proposal.
(a) Changes to a Permitted CAFO’s
Nutrient Management Plan
EPA is proposing to revise the
proposed list of changes to the NMP that
would constitute a substantial change to
the terms of a facility’s NMP, thus
triggering public notice and permit
modification. Substantial changes
would include: (1) Addition of new land
application areas not previously
included in the CAFO’s nutrient
management plan; (2) any changes to
the maximum field-specific land
application rates for nitrogen and
phosphorus, as expressed in accordance
with either the linear approach, the
matrix approach or the narrative rate
approach; (3) addition of any crop not
included in the terms of the CAFO’s
nutrient management plan and
corresponding field-specific rates of
application; and (4) changes to fieldspecific components of the CAFO’s
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nutrient management plan, where such
changes are likely to increase the risk of
nitrogen and phosphorus transport from
the field to waters of the U.S.
EPA is also proposing one exception
to the first type of substantial change (a
land application area being added to the
nutrient management plan), where such
additional land is already included in
the terms of another existing nutrient
management plan incorporated into an
existing NPDES permit. If, under the
revised NMP, the CAFO owner or
operator applies manure, litter, or
process wastewater on such land
application area in accordance with the
existing field-specific terms of the
existing permit, such addition of new
land would not be a substantial change
to the terms of the CAFO owner or
operator’s nutrient management plan.
The Agency believes that these
revised proposed criteria are better
designed to address changes that most
directly affect fundamental components
of the NMP that relate to the land
application of manure, litter, and
process wastewater, which was a
primary focus of the Waterkeeper
decision. First, by proposing the
addition of new land application areas
not originally included in the terms of
the NMP as a substantial change, the
Agency makes clear that the fields to be
used for land application would be
fundamental permit conditions, as all
permitted CAFOs would be required to
land apply manure, litter, and process
wastewater at field-specific agronomic
rates. The identification of land
application areas in the NMP is
essential for determining the effluent
limitations applicable to a particular
CAFO, which the Waterkeeper decision
required be made available for public
review and comment and incorporated
into the permit. Under Waterkeeper, the
public must have such opportunity to
review the fields planned for land
application during both the initial
permit issuance phase and any
subsequent permit modification phase.
The proposed exception for the addition
of new fields already covered by an
existing NPDES permit is consistent
with the Waterkeeper decision because
the rates of application for those land
application areas will have already been
publicly reviewed, approved, and
incorporated into a permit as required
by Waterkeeper.
The second proposed substantial
change is any change to the fieldspecific maximum rates of application.
The Waterkeeper decision makes clear
the importance of these rates as terms of
the NMP.
The third proposed substantial change
is the addition to the NMP of crops not
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previously included in the CAFO’s
NMP, together with the corresponding
maximum field-specific rates of
application for those crops. Because
rates of application are based on the
yield goals for each specific crop, any
crops newly added to the plan will
require corresponding newly calculated
rates of application. Because the
maximum rates of application must be
made available to the public for review
prior to incorporation as terms of the
permit, consistent with Waterkeeper,
the addition of new crops and their
corresponding rates of application
would be considered a substantial
change.
Finally, any change to field-specific
components of the CAFO’s nutrient
management plan that is likely to
increase the risk of nitrogen and
phosphorus transport from the field to
waters of the U.S. would be a
substantial change. The Agency
recognizes a number of changes as
potentially triggering this requirement,
including the following examples: (1)
Alternate timing of land application that
would diminish the potential for plant
nutrient uptake; (2) methods of land
application not provided for in the NMP
calculation of amount of manure, litter,
and process wastewater to be applied;
(3) changes to conservation practices;
and (4) changes in the CAFO’s
procedures for handling, storage, or
treatment of manure, litter, and process
wastewater. The actual crop planted,
timing and method of land application,
crop uptake, and conservation practices
utilized with respect to the land
application areas are all key factors that
affect nitrogen and phosphorus runoff
from the land application area. Changes
to any of the planning considerations
listed above can directly (and
measurably) alter the outcome of the
decisions made in an NMP and the
efficacy of that plan in ensuring
appropriate agricultural utilization of
those nutrients that are land applied.
Such substantial changes would apply
to all permitted CAFOs, regardless of
which of the three proposed approaches
for expressing rates of application was
followed in the CAFO’s NMP. However,
the specific changes that would
constitute substantial changes would
necessarily, to some extent, be
dependent on which of the three
proposed approaches was used. For
example, while a change to the method
or timing of application might be a
substantial change under the linear
approach, if it increased the risk of
nutrient transport to surface waters, it
would not be a substantial change under
the matrix or calculated rate
approaches, provided that the
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methodology (itself a permit term) for
converting maximum amounts of
nutrients into allowable amounts of
manure, litter, or process wastewater
was able to appropriately account for
the change in method or timing.
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(b) Limited Exceptions
Because changes to the NMP could
result in a change to a permit term, the
2006 proposed rule provided that
whenever a CAFO makes any change to
its NMP, the owner or operator would
be required to provide the Director with
the revised NMP and identify the
changes from the previous version
submitted. EPA is proposing a limited
exception for CAFOs following either
the second (‘‘matrix’’) or third
(‘‘quantitative’’) approaches described
above for the terms of the NMP
regarding rates of application. Such
CAFOs would not be required to submit
to the Director any changes in crop
rotations so long as the rates of
application of nitrogen and phosphorus
are in accordance with the outcome of
the field-specific assessment of the
potential for nitrogen and phosphorus
transport, do not exceed the maximum
application rates identified in the
nutrient management plan for the crop
actually planted, and account for any
residual nitrogen and phosphorus in the
field.
5. Annual Reporting Requirements
In the 2006 proposed rule, EPA
discussed the use of annual reports to
balance greater flexibility for CAFO
operators in making cropping decisions
with ensuring appropriate permitting
authority and public oversight of permit
compliance. The preamble solicited
comment as to whether the annual
report requirements should be modified
to require all permitted CAFOs to
submit information in their annual
reports indicating how the CAFO
achieved substantive compliance with
the terms of the NMP as set forth in the
permit. In this supplemental notice, the
Agency is proposing additional annual
reporting requirements for CAFOs that
relate to the proposed provisions in this
notice regarding the terms of the NMP.
This proposal would not affect any of
the annual report requirements
promulgated in the 2003 CAFO rule,
and EPA is not taking comment on any
revisions to the requirements
promulgated in 2003.
The Agency is proposing to require all
permitted CAFOs to include in their
annual reports the actual crop(s) planted
and actual yield(s) for each field, the
actual nitrogen and phosphorus content
of the manure, litter, and process
wastewater, and the amount of manure,
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litter, or process wastewater applied to
each field during the previous 12
months. The Agency believes that it
would be important for the permitting
authority to obtain this information on
an annual basis in order to ensure that
the CAFO has been operating in
compliance with the terms of its permit.
The annual report would inform the
Director and the public how the
operator has operated, given the
flexibility proposed for the terms of the
NMP incorporated into the permit.
The Agency is also proposing to
require CAFOs that follow the third
(‘‘narrative rate’’) approach for
describing rates of application in the
NMP to submit as part of their annual
report the results of all soil testing and
concurrent calculations to account for
residual nitrogen and phosphorus in the
soil, all recalculations, and the new data
from which they are derived. The CAFO
would be required to report the amounts
of manure, litter, process wastewater
and the amount of chemical fertilizer
applied to each field during the
preceding 12 months. Together with the
total amount of crop available nitrogen
and phosphorus from all sources, the
information that would be required to
be included in the annual report would
provide the information necessary to
determine that the CAFO was adhering
to the terms of its permit when
recalculating rates of application. The
Agency seeks comment on these
proposed annual reporting requirements
for each of the approaches to identifying
terms of the NMP for rates of
application.
C. Compliance Deadlines
As discussed in the Background
section of this notice, EPA has twice
extended the compliance dates for
several requirements which were
originally established in the 2003 final
rule. February 27, 2009, is the date by
which the following much occur: (1)
Operations defined as CAFOs as of
April 14, 2003, that were not defined as
CAFOs prior to that date, must seek
NPDES permit coverage; (2) operations
that become defined as CAFOs after
April 14, 2003, due to operational
changes that would not have made them
a CAFO prior to April 14, 2003, and that
are not new sources, must seek NPDES
permit coverage; and (3) permitted
CAFOs are required to develop and
implement nutrient management plans.
As explained in the preamble to the
second compliance date revision,
February 27, 2009, is an appropriate
deadline for these requirements because
it would provide additional time from
the date of the final rule in response to
the Waterkeeper decision for States, the
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regulated community, and other
stakeholders to adjust to the new
regulatory requirements. See 72 FR
40,248 (July 24, 2007).
EPA plans to complete the regulatory
revisions in response to Waterkeeper in
the summer of 2008, since the Agency
has had adequate time to consider the
comments submitted on the 2006
proposed rule and the scope of this
supplemental notice of proposed
rulemaking is narrow relative to the
context of what was proposed in 2006.
This would leave six to eight months
from promulgation of the final rule until
the February 27, 2009, deadline for
AFOs not previously defined as CAFOs
to submit permit applications, for
CAFOs to submit nutrient management
plans to their permitting authorities,
and for permitting authorities to
incorporate the terms of these nutrient
management plans as enforceable
permit conditions in accordance with
the provisions of the final rule. Given
that both operators and permitting
authorities have known for several years
generally what will be required under
the final rule, EPA believes that six to
eight months is sufficient time for these
remaining permitting actions to be
completed, and is thus not intending at
this time to extend those deadlines.
However, the Agency is interested in
taking comment on this issue.
IV. Statutory and Executive Order
Reviews
A. Executive Order 12866: Regulatory
Planning and Review
Under Executive Order (EO) 12866
(58 FR 51,735, October 4, 1993), this
action is not a ‘‘significant regulatory
action.’’
B. Paperwork Reduction Act
The information collection
requirements in this supplemental
notice have been submitted for approval
to the Office of Management and Budget
(OMB) under the Paperwork Reduction
Act (PRA), 44 U.S.C. 3501 et seq. The
Information Collection Request (ICR)
document prepared by EPA has been
assigned EPA ICR number 1989.05.
This SNPRM contains three proposed
regulatory actions that would add to the
paperwork burden associated with the
CAFO NPDES regulations as presented
in the PRA analysis for the 2006
proposed rule. First, today’s notice
proposes supplemental annual reporting
requirements for permitted CAFOs as
part of all three proposed approaches for
specifying terms of the NMP with
respect to rates of application. In
addition, the notice proposes a no
discharge certification option and a new
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narrative rate approach for
incorporating the terms of an NMP into
the permit. The no discharge
certification and the quantitative
approach would both be optional for
CAFOs. Nevertheless, EPA has assessed
the administrative burden associated
with these approaches in order to
characterize the burden likely to be
experienced by facilities that elect to
pursue these options.
This impact analysis covers a three
year period from 2008–2010. Over this
time period, the industry is expected to
experience slight growth from
approximately 20,700 facilities in 2008
to 22,100 facilities in 2010. Projections
for burden hours according to the
various additional requirements in this
supplemental proposal were derived
using these projections, and then
annualized over the three years in
calculating overall results. These
analyses are very complex in that they
also take into account the activities that
are already occurring in the field in
some cases, and rough estimates of the
number of facilities that will be meeting
these requirements, which grows over
the three year period. Therefore, some of
the impact results presented below and
how they match up with the number of
CAFOs and the projected burden hours
will not be immediately apparent. For
example, as described below, due to the
additional annual reporting
requirements, the Agency estimates an
annual burden of 15,800 hours. The
basis for this burden estimate is that for
2008 it is estimated that approximately
15,300 CAFOs would incur an
additional hour of time to meet this
requirement. On the surface, that would
equate to an added annual burden of
15,300 hours. However, because this is
an analysis that is annualized over a 3
year period, the burden is actually
calculated to be 15,800 hours, which
takes into account the growth of the
industry over the 3 years. The Agency
directs the reader to the public docket
to review the draft ICR report which
provides details of all calculations.
Compared to the 2006 proposed rule,
the total administrative burden is
expected to increase by approximately
$1.4 million (52,600 hours) annually
due expressly to the proposed options
in this supplemental notice. This
change derives from annual increases of
$480,000 (15,800 hours) due to the
expanded requirements for annual
reporting, $460,000 (14,500 hours) due
to the added cost of certification, and
$470,000 (22,300 hours) due to the
added cost of the new narrative rate
approach.
For purposes of costing the burden
increment that would arise from the
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additional requirements for annual
reporting, EPA assumed that the new
requirements would add an extra hour
of labor burden to the existing costs per
facility for annual reporting. This new
burden would be incurred by all
permitted CAFOs annually as part of
completing the required annual reports,
with the result that the burden
increment would be experienced by an
estimated 15,300 CAFOs as of 2008.
For purposes of costing the burden
increment due to certification, EPA
assumed that the burden per CAFO for
certification would add 6.5 hours of
labor burden every five years when a
facility submits its certification. EPA’s
burden calculations further assumed
that the certification option would be
chosen by 25 percent of all CAFOs,
yielding an estimate of approximately
5,400 CAFOs that would choose to
certify as of 2008.
To cost the burden for soil sampling
under the narrative rate approach, EPA
assumed that CAFOs would incur an
average of 10 hours of additional labor
burden per facility annually to complete
the sampling. In addition, the burden
estimate is based on an assumption that
one-half of permitted CAFOs that landapply would use the proposed narrative
rate approach for expressing rates of
application. This assumption resulted in
a projection that as of 2008, roughly
5,900 CAFOs would use the narrative
rate approach—approximately 30
percent of the current projection of
20,700 total CAFOs for 2008. Note that
EPA discounted the sampling burden
for CAFOs in states that are already
requiring this practice. EPA’s estimate
of the PRA burden impact due to the
narrative rate approach also took into
account the burden reduction that
permitting authorities could potentially
experience as a result of needing to
process fewer permit modifications due
to changes to NMPs. For this aspect of
the analysis, EPA estimated that
permitting authorities would process
roughly 300 fewer permit modifications
annually, each representing a labor
savings of approximately 12 hours.
These calculations represent a projected
burden reduction compared to the
number of permit modifications
projected for the PRA analysis originally
presented for the 2006 proposed rule.
Burden means the total time, effort, or
financial resources expended by persons
to generate, maintain, retain, or disclose
or provide information to or for a
Federal agency. This includes the time
needed to review instructions; develop,
acquire, install, and utilize technology
and systems for the purposes of
collecting, validating, and verifying
information, processing and
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12337
maintaining information, and disclosing
and providing information; adjust the
existing ways to comply with any
previously applicable instructions and
requirements; train personnel to be able
to respond to a collection of
information; search data sources;
complete and review the collection of
information; and transmit or otherwise
disclose the information.
An agency may not conduct or
sponsor, and a person is not required to
respond to a collection of information
unless it displays a currently valid OMB
control number. The OMB control
numbers for EPA’s regulations in 40
CFR are listed in 40 CFR Part 9.
To comment on the Agency’s need for
this information, the accuracy of the
provided burden estimates, and any
suggested methods for minimizing
respondent burden, including the use of
automated collection techniques, EPA
has established a public docket for this
proposed rule, which includes this ICR,
under Docket ID number EPA–HQ–OW–
2005–0037. Submit any comments
related to the ICR for this proposed rule
to EPA and OMB. See ADDRESSES
section at the beginning of this notice
for where to submit comments to EPA.
Send comments to OMB at the Office of
Information and Regulatory Affairs,
Office of Management and Budget, 725
17th Street, NW., Washington, DC
20503, Attention: Desk Office for EPA.
Since OMB is required to make a
decision concerning the ICR between 30
and 60 days after March 7, 2008, a
comment to OMB is best assured of
having its full effect if OMB receives it
by April 7, 2008. The final rule will
respond to any OMB or public
comments on the information collection
requirements contained in this proposal.
C. Regulatory Flexibility Act
The Regulatory Flexibility Act (RFA)
generally requires an agency to prepare
a regulatory flexibility analysis of any
rule subject to notice and comment
rulemaking requirements under the
Administrative Procedure Act or any
other statute unless the agency certifies
that the rule will not have a significant
economic impact on a substantial
number of small entities. Small entities
include small businesses, small
organizations, and small governmental
jurisdictions.
For purposes of assessing the impacts
of today’s supplemental notice on small
entities, small entity is defined as: (1) A
small business as defined by the Small
Business Administration (SBA) at 13
CFR 121.201 size standards; (2) a small
governmental jurisdiction that is a
government of a city, county, town,
school district or special district with a
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population of less than 50,000; and (3)
a small organization that is any not-forprofit enterprise which is independently
owned and operated and is not
dominant in its field.
After considering the economic
impacts of today’s supplemental notice
of proposed rulemaking on small
entities, I certify that this action will not
have a significant adverse economic
impact on a substantial number of small
entities. The proposed approaches for
incorporating the terms of an NMP into
the permit are generally consistent with
the 2006 proposed rule, but with greater
specificity. Within these approaches,
the expanded annual reporting
requirements for permitted facilities
would not impose a ‘‘significant adverse
economic impact’’ on any small entities.
With the exception of the soil sampling
data, the information that would be
reported is all information that small
entities are required to prepare and
maintain under the 2003 CAFO rule;
only the requirement to include this
information in the annual report to the
Director is new.
The other two revisions proposed in
today’s notice, the no discharge
certification option and the new
narrative rate approach, would be
voluntary, so presumably small entities
will only choose them if they see an
economic advantage from doing so.
This supplemental notice would not
affect small governments, as the
permitting authorities are State or
federal agencies. We continue to be
interested in the potential impacts of the
proposed rule on small entities and
welcome comments on issues related to
such impacts.
D. Unfunded Mandates Reform Act
Title II of the Unfunded Mandates
Reform Act of 1995 (UMRA), Public
Law 104–4, establishes requirements for
Federal agencies to assess the effects of
their regulatory actions on State, local,
and tribal governments and the private
sector. Under section 202 of the UMRA,
EPA generally must prepare a written
statement, including a cost-benefit
analysis, for proposed and final rules
with ‘‘Federal mandates’’ that may
result in expenditures to State, local,
and tribal governments, in the aggregate,
or to the private sector, of $100 million
or more in any one year. Before
promulgating an EPA rule for which a
written statement is needed, section 205
of UMRA generally requires EPA to
identify and consider a reasonable
number of regulatory alternatives and to
adopt the least costly, most costeffective, or least burdensome
alternative that achieves the objectives
of the rule. The provisions of section
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205 do not apply when they are
inconsistent with applicable law.
Moreover, section 205 allows EPA to
adopt an alternative other than the least
costly, most cost-effective or least
burdensome alternative if the
Administrator publishes with the final
rule an explanation why that alternative
was not adopted. Before EPA establishes
any regulatory requirements that may
significantly or uniquely affect small
governments, including tribal
governments, it must have developed
under section 203 of the UMRA a small
government agency plan. The plan must
provide for notifying potentially
affected small governments, enabling
officials of affected small governments
to have meaningful and timely input in
the development of EPA regulatory
proposals with significant Federal
intergovernmental mandates, and
informing, educating, and advising
small governments on compliance with
the regulatory requirements.
EPA has determined that this
supplemental notice would not contain
a Federal mandate that may result in
expenditures of $100 million or more
for State, local, and tribal governments,
in the aggregate, or the private sector in
any one year. Today’s supplemental
notice is in fact anticipated to result in
a net reduction in burden to State
permitting authorities as a consequence
of needing to process fewer permit
modifications due to changes to NMPs.
Specifically, State permitting authorities
are projected to experience a net burden
reduction of approximately $169,000
(4,200 hours) annually. The
supplemental notice would increase the
burden to CAFOs by approximately $1.6
million (56,800 hours) annually due
collectively to activities called for under
the new annual reporting requirements,
the certification option, and the new
quantitative approach. Thus, today’s
supplemental notice is not subject to the
requirements of sections 202 and 205 of
the UMRA. For the same reason, EPA
has determined that this supplemental
notice contains no regulatory
requirements that might significantly or
uniquely affect small governments.
Thus, today’s supplemental notice is not
subject to the requirements of section
203 of UMRA.
E. Executive Order 13132: Federalism
Executive Order 13132, entitled
‘‘Federalism’’ (64 FR 43255, August 10,
1999), requires EPA to develop an
accountable process to ensure
‘‘meaningful and timely input by State
and local officials in the development of
regulatory policies that have federalism
implications.’’ ‘‘Policies that have
federalism implications’’ is defined in
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the Executive Order to include
regulations that have ‘‘substantial direct
effects on the States, on the relationship
between the national government and
the States, or on the distribution of
power and responsibilities among the
various levels of government.’’
Under section 6(b) of Executive Order
13132, EPA may not issue a regulation
that has federalism implications, that
imposes substantial direct compliance
costs, and that is not required by statute,
unless the Federal government provides
the funds necessary to pay the direct
compliance costs incurred by State and
local governments, or EPA consults with
State and local officials early in the
process of developing the proposed
regulation. Under section 6(c) of
Executive Order 13132, EPA may not
issue a regulation that has federalism
implications and that preempts State
law, unless the Agency consults with
State and local officials early in the
process of developing the proposed
regulation.
EPA has concluded that this
supplemental notice does not have
Federalism implications. It will not
have any direct effects on the States, on
the relationship between the national
government and the States, or on the
distribution of power and
responsibilities among the various
levels of government, as specified in
Executive Order 13132. In addition,
EPA does not expect this rule to have
any impact on local governments.
Further, the revised regulations would
not alter the basic State-Federal scheme
established in the Clean Water Act
under which EPA authorizes States to
carry out the NPDES permitting
program. EPA expects the revised
regulations to have little effect on the
relationship between, or the distribution
of power and responsibilities among,
the Federal and State governments.
Thus, Executive Order 13132 does not
apply to this proposed rule.
Consistent with EPA policy, EPA
nonetheless consulted with
representatives of State governments
early in the process of developing the
Agency’s response to the Waterkeeper
court ruling to permit them to have
meaningful and timely input into its
development. Through a variety of
meetings with State associations, States
have been appris2ed of the issues
related to addressing the court’s
decisions. States provided input during
these meetings. State concerns generally
focused on the process for incorporating
NMPs into permits and the related
public review process, and also on
guidance related to what is a discharge
from a CAFO given that the 2006
proposed rule would require only those
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operations that discharge or propose to
discharge to apply for a permit. This
supplemental notice provides additional
guidance addressing both of these
concerns.
In the spirit of Executive Order 13132,
and consistent with EPA policy to
promote communications between EPA
and State and local governments, EPA
specifically solicits comment on this
supplemental notice from State and
local officials.
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F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
Executive Order 13175, entitled,
‘‘Consultation and Coordination with
Indian Tribal Governments’’ (65 FR
67249, November 9, 2000), requires EPA
to develop an accountable process to
ensure ‘‘meaningful and timely input by
tribal officials in the development of
regulatory policies that have tribal
implications.’’
This supplemental notice does not
have tribal implications. It will not have
substantial direct effects on tribal
governments, on the relationship
between the Federal government and
Indian tribes, or on the distribution of
power and responsibilities between the
Federal government and Indian tribes,
as specified in Executive Order 13175.
Thus, Executive Order 13175 does not
apply to this rule.
In the spirit of Executive Order 13175,
and consistent with EPA policy to
promote communications between EPA
and tribal governments, EPA
specifically solicits additional comment
on this supplemental notice from tribal
officials.
G. Executive Order 13045: Protection of
Children From Environmental Health
and Safety Risks
Executive Order 13045: ‘‘Protection of
Children from Environmental Health
Risks and Safety Risks’’ (62 FR 19885,
April 23, 1997) applies to any rule that:
(1) Is determined to be ‘‘economically
significant’’ as defined under E.O.
12866, and (2) concerns an
environmental health or safety risk that
EPA has reason to believe may have a
disproportionate effect on children. If
the regulatory action meets both criteria,
the Agency must evaluate the
environmental health or safety effects of
the planned rule on children, and
explain why the planned regulation is
preferable to other potentially effective
and reasonably feasible alternatives
considered by the Agency.
This supplemental notice is not
subject to Executive Order 13045
because it is not economically
significant as defined under E.O. 12866,
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and because the Agency does not have
reason to believe the environmental
health and safety risks addressed by this
action present a disproportionate risk to
children. The benefits analysis
performed for the 2003 CAFO rule
determined that the rule would result in
certain significant benefits to children’s
health. (Please refer to the Benefits
Analysis in the record for the 2003
CAFO final rule.) Today’s action does
not affect the environmental benefits of
the rule.
H. Executive Order 13211: Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use
This rule is not subject to Executive
Order 13211, ‘‘Actions Concerning
Regulations That Significantly Affect
Energy Supply, Distribution, or Use’’ (66
FR 28355 (May 22, 2001)) because it is
not a significant regulatory action under
Executive Order 12866.
I. National Technology Transfer and
Advancement Act
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (‘‘NTTAA’’), Public Law
104–113, Section 12(d) (15 U.S.C. 272
note) directs EPA to use voluntary
consensus standards in its regulatory
activities unless to do so would be
inconsistent with applicable law or
otherwise impractical. Voluntary
consensus standards are technical
standards (e.g., materials specifications,
test methods, sampling procedures, and
business practices) that are developed or
adopted by voluntary consensus
standard bodies. The NTTAA directs
EPA to provide Congress, through OMB,
explanations when the Agency decides
not to use available and applicable
voluntary consensus standards.
The 2006 proposed rule involved the
use of technical standards for land
application of manure and elimination
of discharges from the production area.
In the 2006 proposal, EPA noted that the
specific standards applicable to a
specific operator are generally
determined by the permitting authority
on a State-wide or site-specific best
professional judgment basis. Today’s
supplemental notice does not pertain to
this aspect of the CAFO rulemaking, and
EPA continues to encourage the use by
permitting authorities of voluntary
consensus standards, such as those
developed by USDA, in establishing the
site-specific technical requirements in
CAFO permits.
List of Subjects in 40 CFR Part 122
Environmental protection,
Administrative practice and procedure,
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12339
Confidential business information,
Hazardous substances, Reporting and
recordkeeping requirements, Water
pollution control.
Dated: March 3, 2008.
Stephen L. Johnson,
Administrator.
For the reasons stated in the
preamble, the Environmental Protection
Agency proposes to amend 40 CFR part
122 as follows:
PART 122—EPA ADMINISTERED
PERMIT PROGRAMS: THE NATIONAL
POLLUTANT DISCHARGE
ELIMINATION SYSTEM
1. The authority citation for part 122
continues to read as follows:
Authority: The Clean Water Act, 33 U.S.C.
1251 et seq.
2. Section 122.23 is amended by
revising paragraph (h) to read as
follows:
§ 122.23 Concentrated animal feeding
operations (applicable to State NPDES
programs, see § 123.25).
*
*
*
*
*
(h) No Discharge Certification Option.
(1) The owner or operator of a CAFO
that meets the eligibility criteria in
paragraph (h)(2) of this section may
certify to the Director that the CAFO
does not discharge or propose to
discharge. A CAFO owner or operator
who certifies that the CAFO does not
discharge or propose to discharge is not
required to seek coverage under an
NPDES permit pursuant to paragraph
(d)(1) of this section, provided that the
CAFO is designed, constructed,
operated, and maintained in accordance
with the documents and certification
required by paragraphs (h)(2) through
(3) of this section, and subject to the
limitations in paragraph (h)(4) of this
section.
(2) Eligibility Criteria. In order to
certify that a CAFO does not discharge
or propose to discharge, the owner or
operator of a CAFO must document,
based on an objective assessment of the
conditions at the CAFO, that the CAFO
is designed, constructed, operated, and
maintained in a manner such that the
CAFO will not discharge, as follows:
(i) The CAFO’s production area is
designed, constructed, operated, and
maintained so as not to discharge. The
CAFO must maintain documentation on
site that demonstrates that:
(A) Any open surface manure storage
structures are designed, constructed,
operated, and maintained to achieve no
discharge based on a technical
evaluation in accordance with the
elements of the technical evaluation set
forth in 40 CFR 412.46(a)(1)(i)–(vii);
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(B) Any part of the CAFO’s
production area that is not addressed by
paragraph (h)(2)(i)(A) of this section is
designed, constructed, operated, and
maintained such that there will be no
discharge of manure, litter, or process
wastewater; and
(C) The CAFO implements the
additional measures set forth in 40 CFR
412.37(a) and (b); and
(ii) The CAFO maintains on site and
implements an up-to-date nutrient
management plan that addresses, at a
minimum, the elements of
§ 122.42(e)(1)(i) through (ix) and 40 CFR
412.37(c), and that includes all land
application areas under the control of
the CAFO where the CAFO will landapply manure, litter, or process
wastewater, and that includes all
operation and maintenance practices
necessary to ensure that the CAFO will
not discharge.
(3) Submission to the Director. In
order to certify that a CAFO does not
discharge or propose to discharge, the
CAFO owner or operator must complete
and submit to the Director, by certified
mail or equivalent method of
documentation, a certification that
includes, at a minimum, the following
information:
(i) The legal name, address and phone
number of the CAFO owner or operator
(see ¶122.21(b));
(ii) The CAFO name and address, the
county name and the latitude and
longitude where the CAFO is located;
(iii) A statement that describes the
manner in which the CAFO satisfies the
eligibility requirements identified in
paragraph (h)(2) of this section; and
(iv) The following certification
statement: ‘‘I certify under penalty of
law that I am the owner or operator of
a concentrated animal feeding operation
(CAFO), identified as [Name of CAFO],
and that said CAFO meets the
requirements of 40 CFR 122.23(h). I
have read and understand the eligibility
requirements of 40 CFR 122.23(h)(2) for
certifying that a CAFO does not
discharge or propose to discharge and
further certify that this CAFO satisfies
the eligibility requirements. As part of
this certification, I am including the
information required by 40 CFR
122.23(h)(3). I also understand the
conditions set forth in 40 CFR
122.23(h)(5) regarding loss of
certification. I certify under penalty of
law that this document and all other
documents required for this certification
were prepared under my direction or
supervision and that qualified personnel
properly gathered and evaluated the
information submitted. Based upon my
inquiry of the person or persons directly
involved in gathering and evaluating the
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information, the information submitted
is to the best of my knowledge and
belief true, accurate and complete. I am
aware there are significant penalties for
submitting false information, including
the possibility of fine and imprisonment
for knowing violations.’’; and
(v) The certification must be signed in
accordance with the signatory
requirements of 40 CFR 122.22.
(4) Term of Certification. Certification
shall be effective for five years from the
date on which it is submitted or until
the certification is no longer valid or is
withdrawn, whichever occurs first. A
certification is no longer valid when a
discharge has occurred or when the
CAFO ceases to meet the eligibility
criteria in paragraph (h)(2) of this
section.
(5) Withdrawal of Certification; Recertification. (i) At any time, a CAFO
may withdraw its certification by
notifying the Director by certified mail
or equivalent method of documentation.
A certification is withdrawn on the date
the notification is submitted to the
Director. The CAFO does not need to
specify any reason for the withdrawal in
its notification to the Director.
(ii) If a certification becomes invalid
in accordance with paragraph (h)(4) of
this section, the CAFO must withdraw
its certification within three days of the
date on which the CAFO’s certification
becomes invalid. Such a CAFO remains
subject to the requirement under
paragraph (d) of this section to seek
permit coverage if it discharges or
proposes to discharge.
(iii) A previously certified CAFO may
re-certify in accordance with paragraph
(h) of this section, provided the
following additional criteria are met if
the previous certification was
invalidated due to an actual discharge
from the CAFO:
(A) The owner or operator modifies
the CAFO’s design, construction,
operation, and/or maintenance as
necessary to permanently address the
cause of the discharge and ensure that
no discharge from this cause occurs in
the future; and
(B) In addition to the certification
submission requirements provided in
paragraph (h)(3) of this section, the
CAFO submits to the Director a
description of the discharge, including
the date, time, cause, duration, and
approximate volume of the discharge,
and a detailed explanation of the steps
taken by the CAFO to permanently
address the cause of the discharge.
[FR Doc. E8–4504 Filed 3–6–08; 8:45 am]
BILLING CODE 6560–50–P
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ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 271
[EPA–R08–RCRA–2006–0127; FRL–8538–2]
Utah: Final Authorization of State
Hazardous Waste Management
Program Revision
Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
AGENCY:
SUMMARY: Utah has applied to EPA for
final authorization of the changes to its
hazardous waste program under the
Resource Conservation and Recovery
Act (RCRA). The EPA proposes to grant
final authorization to the hazardous
waste program changes submitted by
Utah. In the ‘‘Rules and Regulations’’
section of this Federal Register, EPA is
authorizing the State’s program changes
as an immediate final rule. EPA did not
make a proposal prior to the immediate
final rule because we believe these
actions are not controversial and do not
expect comments to oppose them. We
have explained the reasons for this
authorization in the preamble to the
immediate final rule. Unless we get
written comments opposing this
authorization during the comment
period, the immediate final rule will
become effective and the Agency will
not take further action on this proposal.
If we receive comments that oppose
these actions, we will publish a
document in the Federal Register
withdrawing this rule before it takes
effect. EPA will then address public
comments in a later final rule based on
this proposal. Any parties interested in
commenting on these actions must do so
at this time. EPA may not provide
further opportunity for comment.
DATES: Comments must be received on
or before April 7, 2008.
ADDRESSES: Submit your comments,
identified by Docket ID No. EPA–R08–
RCRA–2006–0127, by one of the
following methods:
• Federal eRulemaking Portal: https://
www.regulations.gov.
Follow the on-line instructions for
submitting comments.
• E-mail: daly.carl@epa.gov.
• Fax: (303) 312–6341.
• Mail: Send written comments to
Carl Daly, Solid and Hazardous Waste
Program, EPA Region 8, Mailcode 8P–
HW, 1595 Wynkoop Street, Denver,
Colorado 80202–1129.
• Hand Delivery or Courier: Deliver
your comments to Carl Daly, Solid and
Hazardous Waste Program, EPA Region
8, Mailcode 8P–HW, 1595 Wynkoop
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Agencies
[Federal Register Volume 73, Number 46 (Friday, March 7, 2008)]
[Proposed Rules]
[Pages 12321-12340]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E8-4504]
=======================================================================
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 122
[EPA-HQ-OW-2005-0037; FRL-8539-9]
RIN 2040-AE94
Revised National Pollutant Discharge Elimination System Permit
Regulations for Concentrated Animal Feeding Operations; Supplemental
Notice of Proposed Rulemaking
AGENCY: Environmental Protection Agency (EPA).
ACTION: Supplemental notice of proposed rulemaking.
-----------------------------------------------------------------------
SUMMARY: This action is a supplemental notice of proposed rulemaking
(SNPRM) to EPA's June 30, 2006, notice of proposed rulemaking (NPRM)
revising the National Pollutant Discharge Elimination System (NPDES)
permitting requirements for concentrated animal feeding operations
(CAFOs), in response to the order issued by the U.S. Court of Appeals
for the Second Circuit in Waterkeeper Alliance et al. v. EPA, 399 F.3d
486 (2d Cir. 2005). In the June 2006 NPRM, EPA proposed to require only
CAFOs that discharge or propose to discharge to seek coverage under a
permit. In this SNPRM, EPA is proposing a voluntary option for CAFOs to
certify that the CAFO does not discharge or propose to discharge based
on an objective assessment of the CAFO's design, construction,
operation, and maintenance. The June 2006 proposal also discussed the
terms of the nutrient management plan (NMP) that would need to be
incorporated into NPDES permits. This SNPRM proposes a framework for
identifying the terms of the NMP and three alternative approaches for
addressing rates of application of manure, litter, and process
wastewater when identifying terms of the NMP to be included in the
permit. This supplemental proposal focuses solely on certification and
terms of the NMP and is not opening any other provisions of the June
2006 proposal and existing NPDES regulations or
[[Page 12322]]
Effluent Limitations Guidelines and Standards for public comment.
DATES: Comments must be received on or before April 7, 2008.
ADDRESSES: Submit your comments, identified by Docket ID No. EPA-HQ-OW-
2005-0037 by one of the following methods:
(1) https://www.regulations.gov: Follow the online instructions for
submitting comments.
(2) E-mail: ow-docket@epa.gov, Attention Docket ID No. EPA-HQ-OW-
2005-0037.
(3) Mail: Send the original and three copies of your comments to:
Water Docket, Environmental Protection Agency, Mail Code 2822T, 1200
Pennsylvania Ave., NW., Washington, DC 20460, Attention Docket ID No.
OW-2005-0037.
(4) Hand Delivery: Deliver your comments to: EPA Docket Center, EPA
West, Room B102, 1301 Constitution Avenue, NW., Washington, DC,
Attention Docket ID No. OW-2005-0037. Such deliveries are only accepted
during the Docket's normal hours of operation and special arrangements
should be made for deliveries of boxed information.
Instructions: Direct your comments to Docket ID No. EPA-HQ-OW-2005-
0037. EPA's policy is that all comments received will be included in
the public docket without change and may be made available online at
www.regulations.gov, including any personal information provided,
unless the comment includes information claimed to be Confidential
Business Information (CBI) or other information whose disclosure is
restricted by statute. Do not submit information that you consider to
be CBI or otherwise protected through www.regulations.gov or e-mail.
The www.regulations.gov Web site is an ``anonymous access'' system,
which means EPA will not know your identity or contact information
unless you provide it in the body of your comment. If you send an e-
mail comment directly to EPA without going through www.regulations.gov
your e-mail address will be automatically captured and included as part
of the comment that is placed in the public docket and made available
on the Internet. If you submit an electronic comment, EPA recommends
that you include your name and other contact information in the body of
your comment and with any disk or CD-ROM you submit. If EPA cannot read
your comment due to technical difficulties and cannot contact you for
clarification, EPA may not be able to consider your comment. Electronic
files should avoid the use of special characters, any form of
encryption, and be free of any defects or viruses. For additional
information about EPA's public docket visit the EPA Docket Center
homepage at https://www.epa.gov/epahome/dockets.htm.
Docket: All documents in the docket are listed in the
www.regulations.gov index. Although listed in the index, some
information is not publicly available, e.g., CBI or other information
whose disclosure is restricted by statute. Certain other material, such
as copyrighted material, will be publicly available only in hard copy.
Publicly available docket materials are available either electronically
in www.regulations.gov or in hard copy at the Water Docket, EPA Docket
Center, 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.
FOR FURTHER INFORMATION CONTACT: Rebecca Roose, Water Permits Division,
Office of Wastewater Management (4203M), Environmental Protection
Agency, 1200 Pennsylvania Ave., NW., Washington, DC 20460; telephone
number: (202) 564-0758; e-mail address: roose.rebecca@epa.gov.
SUPPLEMENTARY INFORMATION:
I. General Information
A. Does This Action Apply to Me?
B. What Should I Consider as I Prepare my Comments for EPA?
II. Background
III. This Proposal
A. No Discharge Certification
B. Terms of Nutrient Management Plan
C. Compliance Deadlines
IV. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory Planning and Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation and Coordination With
Indian Tribal Governments
G. Executive Order 13045: Protection of Children From
Environmental Health and Safety Risks
H. Executive Order 13211: Actions Concerning Regulations That
Significantly Affect Energy Supply, Distribution, or Use
I. National Technology Transfer and Advancement Act
I. General Information
A. Does This Action Apply to Me?
This action applies to concentrated animal feeding operations
(CAFOs), included as point sources in section 502(14) of the Clean
Water Act and defined in the NPDES regulations at 40 CFR 122.23. The
following table provides a list of standard industrial codes for
operations covered under this revised rule.
Table 1.--Entities Potentially Regulated by this Rule
----------------------------------------------------------------------------------------------------------------
North Standard
American industrial
Category Examples of regulated entities industry code classification
(NAIC) code
----------------------------------------------------------------------------------------------------------------
Federal, State, and Local Government:
Industry............................... Operators of animal production
operations that meet the
definition of a CAFO:
Beef cattle feedlots (including 112112 0211
veal).
Beef cattle ranching and farming 112111 0212
Hogs............................ 11221 0213
Sheep........................... 11241, 11242 0214
General livestock except dairy 11299 0219
and poultry.
Dairy farms..................... 11212 0241
Broilers, fryers, and roaster 11232 0251
chickens.
Chicken eggs.................... 11231 0252
Turkey and turkey eggs.......... 11233 0253
Poultry hatcheries.............. 11234 0254
Poultry and eggs................ 11239 0259
[[Page 12323]]
Ducks........................... 112390 0259
Horses and other equines........ 11292 0272
----------------------------------------------------------------------------------------------------------------
This table is not intended to be exhaustive, but rather provides a
guide for readers regarding entities likely to be regulated by this
action. This table lists the types of entities that EPA is now aware
could potentially be regulated by this action. Other types of entities
not listed in the table could also be regulated. To determine whether
your facility may be regulated under this rulemaking, you should
carefully examine the applicability criteria in 40 CFR 122.23. If you
have questions regarding the applicability of this action to a
particular entity, consult the person listed in the preceding FOR
FURTHER INFORMATION CONTACT section.
B. What Should I Consider as I Prepare my Comments for EPA?
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. It will be helpful if you
follow these guidelines as you prepare your written comments:
i. Identify the rulemaking by docket number and other identifying
information (subject heading, Federal Register date and page number).
ii. 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.
iii. Explain why you agree or disagree; suggest alternatives and
substitute language for your requested changes.
iv. Describe any assumptions and provide any technical information
and/or data that you used.
v. If you estimate potential costs or burdens, explain how you
arrived at your estimate in sufficient detail to allow for it to be
reproduced.
vi. Provide specific examples to illustrate your concerns, and
suggest alternatives.
vii. Explain your views as clearly as possible.
viii. Make sure to submit your comments by the comment period
deadline identified.
II. Background
Congress enacted the Federal Water Pollution Control Act (1972),
also known as the Clean Water Act (CWA), to ``restore and maintain the
chemical, physical, and biological integrity of the nation's waters''
(CWA section 101(a)). Among the core provisions, the CWA establishes
the NPDES permit program to authorize and regulate the discharge of
pollutants from point sources to waters of the U.S. (CWA section 402).
Section 502(14) of the CWA specifically includes CAFOs in the
definition of the term ``point source.'' Section 502(12) defines the
term ``discharge of a pollutant'' to mean ``any addition of any
pollutant to navigable waters from any point source'' (emphasis added).
EPA has issued comprehensive regulations that implement the NPDES
program at 40 CFR part 122. The Act also provides for the development
of technology-based and water quality-based effluent limitations that
are imposed through NPDES permits to control the discharge of
pollutants from point sources. CWA sections 301(a) and (b).
EPA began regulating wastewater and manure from CAFOs in the 1970s.
EPA initially issued national effluent limitations guidelines and
standards for feedlots on February 14, 1974 (39 FR 5,704), and NPDES
CAFO regulations on March 18, 1976 (41 FR 11,458).
In February 2003, EPA issued revisions to these regulations,
focusing on the 5% of the nation's animal feeding operations (AFOs)
that present the highest risk of impairing water quality and public
health (68 FR 7,176) (``the 2003 CAFO rule''). The 2003 CAFO rule
required the owners or operators of all CAFOs \1\ with a potential to
discharge to apply for an NPDES permit. A number of CAFO industry
organizations (American Farm Bureau Federation, National Pork Producers
Council, National Chicken Council, and National Turkey Federation
(NTF), although NTF later withdrew its petition) and several
environmental groups (Waterkeeper Alliance, Natural Resources Defense
Council, Sierra Club, and American Littoral Society) filed petitions
for judicial review of certain aspects of the 2003 CAFO rule. This case
was brought before the U.S. Court of Appeals for the Second Circuit. On
February 28, 2005, the court ruled on these petitions and upheld most
provisions of the 2003 rule but vacated and remanded others.
Waterkeeper Alliance, et al. v. EPA, 399 F.3d 486 (2d Cir. 2005).
Provisions of the 2003 CAFO rule that were challenged by the
petitioners but upheld by the court include the Agency's land
application regulatory framework and interpretation of ``agricultural
stormwater,'' and the Agency's determination regarding effluent
limitations guidelines pertaining to groundwater controls and best
available technology for waste management. The court vacated the 2003
rule requirement that all CAFOs must apply for permits or demonstrate
that they do not have the potential to discharge. The court also found
that the terms of the nutrient management plan (NMP) are themselves
``effluent limitations'' and, therefore, must be made part of the
permit and be enforceable as required by CWA sections 301 and 402, made
subject to public comment, and reviewed and approved by the permitting
authority. The court also remanded several aspects of the 2003 CAFO
rule for further clarification and analysis.
On June 30, 2006, EPA published a proposed rule to revise several
aspects of the Agency's regulations governing discharges from CAFOs in
response to
[[Page 12324]]
the Waterkeeper decision. 71 FR 37,744. EPA is briefly describing the
proposed revisions to the 2003 CAFO here for context only. The proposed
provisions in response to the Waterkeeper decision are beyond the scope
of this final rule, and EPA is not addressing those provisions in this
final rule.
In summary, EPA proposed to require only owners or operators of
those CAFOs that discharge or propose to discharge to seek
authorization to discharge under a permit. Second, EPA proposed to
require CAFOs seeking authorization to discharge under individual
permits to submit their NMPs with their permit applications or, under
general permits, with their notices of intent. Permitting authorities
would be required to review the NMP and provide the public with an
opportunity for meaningful public review and comment. Permitting
authorities would also be required to incorporate terms of the NMP as
NPDES permit conditions. The proposed rule also addressed the remand of
issues for further clarification and analysis. These issues concern
clarifications regarding the applicability of water quality-based
effluent limitations (WQBELs); new source performance standards for
swine, poultry, and veal CAFOs; and ``best conventional technology''
effluent limitations guidelines for fecal coliform.
In addition to the proposed revisions in the 2006 proposed rule,
EPA has extended certain deadlines in the NPDES permitting requirements
and ELGs in two separate rulemakings in order to allow the Agency
adequate time to complete this rulemaking in response to the
Waterkeeper decision, in advance of those deadlines. The first rule
revised dates established in the 2003 CAFO rule by which facilities
newly defined as CAFOs were required to seek permit coverage and by
which all permitted CAFOs were required to develop and implement
nutrient management plans. 71 FR 6978. Because EPA was unable to
complete this final rule prior to July 31, 2007, EPA again revised the
compliance dates on July 24, 2007, further extending those dates from
July 31, 2007, to February 27, 2009. 72 FR 40248.
III. This Proposal
This notice supplements the 2006 proposed rule by proposing
additional options being considered by EPA for inclusion in the
rulemaking to respond to the Second Circuit's decision in the
Waterkeeper case. EPA is only seeking comment on the issues presented
in this supplemental proposal. No provisions promulgated in the 2003
final rule are affected or reopened by this supplemental proposal, nor
is EPA reopening the comment period on the 2006 proposed rule. In
addition, EPA is taking comment on the compliance deadlines established
in the second date change rule.
---------------------------------------------------------------------------
\1\ The Clean Water Act regulates the conduct of persons, which
includes the owners and operators of CAFOs, rather than the
facilities or their discharges. To improve readability in this
preamble, reference is made to ``CAFOs'' as well as ``owners and
operators of CAFOs.'' No change in meaning is intended.
---------------------------------------------------------------------------
A. No Discharge Certification
In this notice, the Agency is proposing a new provision that would
allow CAFOs to voluntarily certify that the CAFO does not discharge or
propose to discharge. This supplemental proposal seeks comment on this
voluntary certification option, described below.
1. Background
The 2003 CAFO rule required all CAFOs to seek coverage under an
NPDES permit unless the Director determined that the CAFO has no
potential to discharge. 68 FR 7176 (Feb. 12, 2003). This duty to apply
for a permit based on a potential discharge was successfully
challenged. Waterkeeper Alliance et al. v. EPA, 399 F.3d 486 (2nd Cir.
2005). The court found that the duty to apply, which the Agency had
based on a presumption that most CAFOs have at least a potential to
discharge, was invalid because the CWA subjects only actual discharges
to permitting requirements rather than potential discharges.
Waterkeeper, 399 F.3d at 506. The court acknowledged EPA's policy
considerations for seeking to impose a duty to apply solely on the
basis of a CAFO's potential to discharge but found that the Agency
lacked statutory authority to do so.
In June 2006, in response to the Waterkeeper decision, EPA proposed
to amend the duty to apply provision for CAFOs, found at 40 CFR
122.23(d), to require all CAFOs that ``discharge or propose to
discharge'' to seek NPDES permit coverage. 71 FR 37744 (June 30, 2006).
As discussed in the preamble to the 2006 proposed rule, the CAFO
operator would decide whether or not to apply for a permit. 71 FR
37749. EPA received several hundred comments on the 2006 proposed rule
related to how a CAFO operator would decide whether to seek permit
coverage. In particular, many commenters asked EPA to specify
conditions at a CAFO that would clearly trigger the requirement to
apply for a permit, while others stated the position that there is no
``duty to apply'' for CAFOs in advance of any discharge because an
NPDES permit is only required for actual discharges. In response to
these comments EPA has developed an option that would allow a CAFO that
determines it does not need to seek permit coverage to certify to the
Director that the operation does not discharge or propose to discharge.
The proposal would establish clear criteria, described in detail below,
that a CAFO must meet in order to be eligible for the certification.
The certification option proposed in this notice would not change the
duty to apply requirement proposed in 2006 that CAFOs that discharge or
propose to discharge would be required to seek permit coverage. It
would, however, provide a structured process for CAFOs that wish to
certify to establish that they do not discharge or propose to
discharge. EPA believes that such a structured process would be helpful
to CAFOs as they determine whether or not to seek permit coverage.
Furthermore, a CAFO with a valid no discharge certification would not
be subject to liability for violation of the duty to apply at 122.23(d)
in the unlikely event that a discharge should occur, though it would
still be liable for violation of the prohibition on unpermitted
discharges in CWA section 301. EPA wishes to emphasize that submission
of a no discharge certification is voluntary. Only CAFOs that discharge
or propose to discharge would be subject to NPDES permit requirements,
whether or not they submit a certification.
2. Overview of Certification
EPA is proposing a voluntary option for CAFOs to certify to the
Director that the CAFO does not discharge or propose to discharge based
on an objective assessment of the CAFO's design, construction,
operation, and maintenance. This objective assessment would take into
account the CAFO's production area design and construction and its
operating parameters as described in its nutrient management plan
(NMP). The CAFO operator would certify that the CAFO does not discharge
or propose to discharge by signing and submitting a certification
statement to the Director. A CAFO's no discharge certification would
not be subject to approval by the permitting authority and there would
not be an opportunity for the public to comment and request a hearing
regarding the certification. The proposed eligibility requirements,
submission requirements, and conditions for a valid certification are
discussed in detail below.
3. Certification Eligibility Criteria
EPA is proposing to establish specific eligibility criteria for
CAFO certification at 40 CFR 122.23(h)(2). Meeting these criteria would
establish that the CAFO does not ``discharge or propose to discharge''
for purposes of proposed Sec. 122.23(d), for as long as the
certification is valid. The two proposed
[[Page 12325]]
criteria are as follows: (1) An objective evaluation of the production
area design, construction, operation, and maintenance, which shows that
the production area will not discharge, and (2) development,
implementation, and maintenance on-site of a nutrient management plan
(NMP) that addresses the elements set forth in 40 CFR 122.42(e)(1) and
412.37(c), including operation and maintenance practices for the
production area and land application areas under the control of the
CAFO. While a description of how the CAFO meets the eligibility
criteria would be required to be submitted to the Director, this
proposed rule would not require that the documents necessary to meet
the eligibility criteria be submitted to the permitting authority, nor
would they be subject to permitting authority approval. However, during
the certification period a properly certified CAFO would be required to
maintain such documents on site or make them readily available, along
with any associated records created to support the basis for the
certification. Certified CAFOs, like any other permitted or unpermitted
CAFO, would be subject to potential inspection by EPA or State
inspectors, during which they could be required to produce the
documentation showing that the CAFO meets the eligibility criteria,
including that the CAFO has been and is being operated and maintained
in accordance with the NMP.
The first proposed eligibility criterion for valid certification
would cover the design, construction, operation, and maintenance of the
CAFO's production area. Proposed Sec. 122.23(h)(2)(i) would require
the CAFO to maintain documentation on site to demonstrate that the
CAFO's production area is designed, constructed, operated, and
maintained so as not to discharge. This demonstration would be the same
as the demonstration provided for in proposed 40 CFR 412.46 (71 FR
37786), which would allow swine, poultry, and veal calf operations
subject to new source performance standards (NSPS) to demonstrate that
there will be no discharge from their production area. However, the no
discharge certification would be available to all unpermitted CAFOs
that do not discharge or propose to discharge, not just new sources in
the swine, poultry and veal calf sectors with open storage. Due to the
variations in production area design based on the type of containment
system used at the operation, the proposed regulatory text for the
first eligibility criterion has two parts: the first for open manure
storage structures and the second for any part of the production area
not considered to be open containment.
EPA is proposing that any CAFO with an open surface manure storage
structure seeking to certify that it does not discharge or propose to
discharge would be required to perform a technical evaluation. This
evaluation would include the same elements as the technical evaluation
required for open storage new source swine, poultry and veal calf
operations seeking to demonstrate no discharge under 40 CFR
412.46(a)(1). In the 2006 proposed rule, EPA proposed to revise the
provisions at 40 CFR 412.46(a)(1) to allow such new sources with open
containment to meet the no discharge requirement for their NPDES permit
using best management practices based in part on a rigorous site-
specific technical evaluation that includes use of the Soil Plant Air
Water (SPAW) Hydrology Tool or equivalent model. See the 2006 proposed
regulation at 71 FR 37786-87 and corresponding preamble discussion at
71 FR 37760-62. Under this proposed certification, any unpermitted CAFO
with open storage seeking to certify its operation as no discharge, not
just new source swine, poultry, and veal calf operations, would be
required to undertake a technical evaluation in accordance with the
elements of the technical evaluation in Sec. 412.46(a)(1)(i)-(vii) to
demonstrate that it meets the production area requirement for
certification under proposed Sec. 122.23(h)(2)(i)(A). Today's proposed
rule does not reopen for additional comment the 2006 proposed revisions
to section 412.46 relating to NSPS. The comment period on the revised
NSPS requirements is closed. Rather, EPA is now seeking comment on
whether the elements of the technical evaluation set forth in proposed
Sec. 412.46(a)(1)(i)-(vii) provide an appropriate basis for an
unpermitted CAFO to certify, on the basis of its design, construction,
operation, and maintenance, that its open surface manure storage
structure will not discharge.
In order to meet the second part of the first eligibility
criterion, this proposed rule would require, in Sec.
122.23(h)(2)(i)(B), that any certifying CAFO must demonstrate that all
of its production area, as defined at 40 CFR 122.23(b)(8), not just
open surface containment structures, is designed, constructed,
operated, and maintained such that there will be no discharge of
manure, litter, process wastewater, or raw materials, such as feed, to
surface waters. For a CAFO without open containment, this provision
would require a demonstration of no discharge from the entire
production area. For a CAFO that has an open containment structure,
this provision would require a demonstration that the remainder of the
production area (other than the open containment structure subject to
the demonstration in 122.23(h)(2)(i)(A)), also will not discharge.
Because of the special risk of discharge from open manure storage
structures, greater specificity is provided regarding the elements of
the demonstration in 122.23(h)(2)(i)(A); however, the demonstration in
122.23(h)(2)(i)(B) must also be technically sound and must be adequate
to demonstrate that the production area is designed, constructed,
operated and maintained for no discharge. This demonstration must be
based on an evaluation of site-specific characteristics, including,
among others, the amount of manure generated during the storage period,
the size of the storage structure, control measures to ensure diversion
of clean water, and seasonal restrictions on land application. Some
CAFOs may have a combination of open manure storage structures and
covered structures, while others will house all animals and store all
manure, feed and by-products under cover. In either case, all parts of
the production area will need to be covered by the demonstrations
required under Sec. 122.23(h)(2)(i)(A) and (B). In addition, like
permitted new source swine, poultry, and veal calf operations, any
unpermitted CAFO seeking to certify no discharge would be required to
implement the measures set forth in 40 CFR 412.37(a) and (b) for the
production area. These additional measures pertain to operation and
maintenance and include provisions for visual inspections, depth
markers for all open surface liquid impoundments, corrective action,
mortality handling and recordkeeping. Since both these permitted new
source operations and unpermitted certified CAFOs would need to ensure
no discharge from the production area under the permit and
certification requirements, respectively, EPA believes it is
appropriate to rely, in part, on those provisions to establish
eligibility criteria for no discharge certification. The documents that
would be necessary to satisfy this eligibility requirement would
include design documentation and all recordkeeping and operation and
maintenance planning necessary to address the elements of proposed
Sec. 122.23(h)(2)(i), which includes the measures set forth in Sec.
412.37(a) and (b). EPA is considering developing a recordkeeping
checklist for use by certified CAFOs. Such a checklist would be made
available to all CAFO
[[Page 12326]]
operators through EPA guidance published subsequent to issuance of the
final CAFO rule. EPA requests comment on whether such a checklist would
be useful.
The second eligibility criterion would require the CAFO to develop,
implement, and maintain on site an NMP that addresses, at a minimum,
the elements set forth in 40 CFR 122.42(e)(1) and 40 CFR 412.37(c), and
addresses all operation and maintenance practices necessary to ensure
that the CAFO will not discharge. The NMP would include provisions
regarding nutrient management in the production area as well as in all
land application areas under the control of the CAFO where the CAFO
will land-apply manure. EPA believes that implementation of an NMP is
an essential component of any CAFO's efforts to ensure that it will not
discharge from its production or land application areas. EPA notes that
a comprehensive nutrient management plan (CNMP), developed in
accordance with Natural Resources Conservation Service (NRCS) technical
guidance for CNMPs,\2\ would be sufficient to meet this eligibility
criterion as long as the CNMP addresses the minimum elements set forth
in 40 CFR 122.42(e)(1) and Sec. 412.37(c), and the CAFO addresses all
the necessary operation and maintenance protocols either in the CNMP or
one or more operation and maintenance plans. It is common for an
operation to have one or more operation and maintenance plans in order
to properly implement a number of NRCS conservation practice standards
simultaneously. Also, to the extent that the necessary operation and
maintenance requirements to implement any provision of the NMP are not
included in the NMP itself, those requirements would need to be
included in an operation and maintenance plan to be implemented and
maintained on site.
---------------------------------------------------------------------------
\2\ Technical Guidance for Developing Comprehensive Nutrient
Management Plans, USDA Natural Resources Conservation Service
(2003), available at https://policy.nrcs.usda.gov/
viewerFS.aspx?id=3073.
---------------------------------------------------------------------------
Proper certification would require the CAFO to revise its NMP if
any of the design specifications, practices or other NMP provisions
changed over time. For example, if the CAFO decided to land-apply
manure on a field that was not included in the NMP, the CAFO would need
to calculate rates of application in accordance with the protocols
required by Sec. 122.42(e)(1)(viii) and revise the NMP to include the
new field and the corresponding application rates. Because valid
certification would require the CAFO to at all times be designed,
constructed, operated, and maintained such that it meets the
eligibility criteria to establish that the operation does not discharge
or propose to discharge (see proposed Sec. 122.23(h)(4), discussed
below), to maintain a valid certification, a CAFO should make the
adjustments necessary to accommodate a change in circumstances, before
the circumstances change. For example, if an increase in animals would
cause the operation to exceed the existing storage capacity for
precipitation, manure and process wastewater required for no discharge,
to remain certified the CAFO would need to remedy the storage capacity
problem prior to bringing the additional animals to the operation.
EPA would encourage a CAFO preparing the documents necessary for
the proposed certification to consult with a professional engineer and
an NRCS-certified technical service provider (TSP) or other qualified
nutrient management planner. Any professional consulted by the CAFO
should have the requisite training, experience and expertise to conduct
and/or substantively review the required analyses, and to advise the
owner or operator as to whether the CAFO is, in fact, designed,
constructed, operated, and maintained such that it will not discharge.
4. Submitting the Certification
Under the proposed certification option, a CAFO seeking to certify
that it does not discharge or propose to discharge would be required to
submit the certification to the permitting authority. Under proposed
Sec. 122.23(h)(3), the submission to the Director would include: (1)
The CAFO owner or operator's name, address and phone number; (2)
information regarding the CAFO's location, including latitude and
longitude; (3) a description of the manner in which the CAFO satisfies
the eligibility requirements of Sec. 122.23(h)(2); (4) the
certification statement set forth in proposed Sec. 122.23(h)(3)(iv);
and (5) an official signature that meets the signatory requirements of
40 CFR 122.22. The signed certification would make the CAFO legally
responsible for its representations to the Director regarding the
design, construction, operation, and maintenance of the CAFO. The
language regarding legal liability for making a false statement under
the proposed option is consistent with language in 40 CFR 122.26(g)
which applies to facilities seeking to obtain a ``no exposure''
exclusion for industrial storm water.
Today's proposed rule would make no changes to the existing
regulations concerning how CAFOs may make Confidential Business
Information (CBI) claims with respect to information they must submit
to the permitting authority and how those claims will be evaluated. A
facility may make a claim of confidentiality under the existing
regulations at 40 CFR part 2, subpart B.
The third item the Agency is proposing for submission to the
Director, as listed above, is a statement describing the manner in
which the CAFO satisfies the certification eligibility criteria. EPA
believes that, at a minimum, the description to be submitted to the
Director should include: (1) The type and number of animals; (2) the
type and capacity of manure and wastewater storage and/or containment;
(3) storm size used as basis for containment design; (4) whether the
CAFO consulted with a professional engineer or TSP; (5) identification
of the documents maintained on site in accordance with the eligibility
criteria; and (6) any technical standards, tools (e.g., RUSLE and
Phosphorus Index) and formulas used to calculate application rates of
manure, litter, and process wastewater. EPA seeks comment on whether
this is the scope and type of information that should be submitted, as
well as suggestions of other information that should be included in the
eligibility description submitted for certification.
The authority given to the permitting authority under section 308
of the CWA to conduct inspections at point source operations would not
be affected by this proposed rule. Therefore, any CAFO, whether it is
certified, permitted, or neither, may be subject to an information
gathering request or inspection, at the Director's discretion and for
any of the reasons provided by section 308 of the Clean Water Act. 33
U.S.C. 1318.
Under the proposal, the certification would become effective upon
submission to the Director. The proposed rule would require the use of
certified mail or equivalent method of documentation for identifying
the date of submission.
5. Limitations on Certification
This proposed rule also includes several limitations on
certification related to the term of a valid certification, reporting,
and re-certification when a certification becomes invalid. EPA proposes
that the certification would be valid for five years from the date of
certification or would terminate when the CAFO has either discharged or
ceases to be
[[Page 12327]]
designed, constructed, operated and maintained in accordance with the
documentation supporting the certification (i.e., its production area
design documentation and nutrient management plan), whichever is
sooner. See proposed Sec. 122.23(h)(4). EPA is proposing that a valid
certification would need to be renewed, if desired by the CAFO, every
five years. This is the maximum statutory term of an NPDES permit. The
permit renewal process provides the opportunity for operations of a
permitted CAFO to be reviewed to ensure that they still meet the
requirements of the Clean Water Act and for new conditions to be
imposed as necessary. EPA believes that a five-year term for no
discharge certifications will similarly prompt the CAFO to periodically
reevaluate whether it is designed, constructed, operated, and
maintained so as not to discharge and make adjustments to operations
where necessary. EPA seeks comment on whether five years is an
appropriate length of time for a no discharge certification.
In the unlikely event of a discharge from a certified CAFO, the
CAFO operator, although subject to liability for the discharge itself,
would not be liable for a violation of the duty to apply in Sec.
122.23(d), but the certification would cease to be valid. Similarly,
should a CAFO fail to continue to meet any of the eligibility criteria,
the CAFO's certification would no longer be valid. Circumstances that
could result in the certification becoming invalid would include, for
example, an increase in animals that exceeds the capacity of the
production area for manure storage and handling, a loss of land
application areas such that the assumptions in the NMP concerning land
application would no longer be appropriate, and a discharge of
pollutants to waters of the United States (other than discharges of
agricultural stormwater from the land application area, which is exempt
from permitting requirements).
Once a certification ceased to be valid, the operator would not be
able to rely on it if an enforcement action were brought for a
subsequent violation of the duty to apply for a permit. In sum, a
discharge by the CAFO or failure of a certified CAFO to continue to be
designed, constructed, operated, and maintained in accordance with the
eligibility criteria and certification statement would render the
certification invalid and put the CAFO in the same position as any
other unpermitted and uncertified CAFO.
Failure to continue to meet the eligibility requirements for
certification in proposed Sec. 122.23(h)(2) would not, in and of
itself, be a violation of any regulatory requirement, since
certification would be strictly voluntary. For example, failure to
implement the measures set forth in Sec. 412.37(a)-(b), which would be
required for no discharge certification eligibility under proposed
Sec. 122.23(h)(2)(i), would not be a violation of Sec. 412.37(a)-(b)
but would render the certification invalid.
Under proposed Sec. 122.23(h)(5) a CAFO could withdraw its
certification at anytime by notifying the Director, by certified mail
or equivalent method of documentation, that it was withdrawing its
certification. The certification would be withdrawn on the date the
notification was submitted to the Director. If a CAFO certification
becomes invalid, proposed Sec. 122.23(h)(5) would require the CAFO
operator to withdraw its certification within three days of the date on
which the CAFO's no discharge certification became invalid.
The CAFO operator would not be required to notify the Director of
the reason for withdrawing the certification, or even if it was
withdrawn because some change in circumstances had rendered it invalid
or merely because the operator no longer chooses to maintain it. For
example, an operator might decide that particular recordkeeping
requirements needed for certification were more burdensome than the
certification was worth, and choose to withdraw the certification so as
not to have to keep such records. While EPA believes it is important
for permitting authorities to have an accurate and up-to-date record of
which unpermitted CAFOs have a valid no discharge certification, and
thus to require operators to withdraw any certification which ceases to
be valid, EPA also wishes to emphasize that certification is strictly
voluntary, and can be withdrawn by the operator without explanation at
any time.
If a certification is withdrawn because it ceases to be valid, the
operator could seek to re-certify that the CAFO does not discharge or
propose to discharge by revising its operations to address the
deficiency and submitting a new certification statement. If the
certification was rendered invalid by a discharge, under proposed Sec.
122.23(h)(5), in order to re-certify, a CAFO would have to submit to
the Director the information required under Sec. 122.23(h)(3) and
additional information describing the discharge, including the time,
date, cause, and approximate volume of the discharge, and the steps
taken by the CAFO to permanently address the cause of the discharge,
i.e., to ensure that no discharge from this cause occurs in the future.
While review and approval of the technical basis for certification by
the permitting authority is not generally required, EPA believes it is
appropriate in situations where a certified CAFO has in fact discharged
and still believes that it can certify that it does not discharge or
propose to discharge, for the operator to provide sufficient
information to assure the Director that the cause of the discharge has
been adequately addressed to ensure that there will not be future such
discharges. EPA would generally consider a recurring discharge as
evidence that a CAFO is not eligible for certification or re-
certification and would need to seek permit coverage.
6. Additional Rationale
As stated above, under the 2006 proposed revisions to 40 CFR
122.23(d)(1), a CAFO that does not discharge or propose to discharge
would not be subject to the duty to apply for an NPDES permit. However,
as discussed in the preamble to the 2006 proposed rule, if an
unpermitted CAFO discharges, the CAFO would be in violation of section
301(a) of the CWA due to the unpermitted discharge and could be in
violation of the duty to apply if the CAFO could have reasonably
foreseen that the discharge would occur and did not seek permit
coverage prior to discharge. A valid certification, however, would
document the CAFO operator's basis for making an informed decision not
to seek permit coverage because the CAFO does not discharge or propose
to discharge, and would protect the CAFO from being held liable for not
applying for the permit prior to discharge. In the unlikely event that
a properly certified CAFO discharges, the CAFO would not be subject to
liability for failure to seek permit coverage prior to discharge in
violation of 40 CFR 122.23(d) and section 308 of the CWA. However, any
discharge even from a properly certified CAFO would be an unpermitted
discharge in violation of CWA section 301 subject to applicable
injunctive relief and penalties.
EPA believes that providing protection from liability for violation
of 40 CFR 122.23(d) and section 308 for a properly certified CAFO is
reasonable and justified. Certification would require a CAFO owner or
operator to undertake and document a rigorous analysis of the
operation's structure and design, and to be committed to operation and
maintenance protocols designed to ensure no discharge. As stated above,
certification is entirely voluntary for a CAFO that does not discharge
or propose to discharge. EPA
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believes that a CAFO owner or operator that would make the effort and
take the steps needed to certify no discharge should be afforded
protection from enforcement for failure to have applied for a permit
prior to discharge if, in the future, there is an unanticipated
discharge from the CAFO, so long as there has been no lapse in the
CAFO's eligibility for certification. The operator of an unpermitted
CAFO choosing not to make and document this certification in accordance
with each element listed in 40 CFR 122.23(h)(2)-(3) would not receive
the liability protection provided by a no discharge certification.
Unlike the 2003 rule that required all CAFOs to seek permit
coverage in order to operate unless they obtained a determination of
``no potential to discharge,'' the certification provision proposed
here would be entirely voluntary. The purpose of the certification
would be to provide a mechanism by which a CAFO can document that it
does not discharge or propose to discharge and be assured that even if
the CAFO does discharge in the future, it would not face an enforcement
action for failure to apply for a permit. The certification process
would not, in and of itself, establish whether the CAFO must apply for
a permit. As proposed in 2006, the requirement for a CAFO to apply for
a permit would be triggered only when a CAFO discharges or proposes to
discharge. 71 FR 37,784. The decision to seek permit coverage or no
discharge certification would be made by the operator based on an
objective assessment of conditions at the facility, in contrast to the
2003 rule, which required the operator either to seek permit coverage
or prove to the satisfaction of the Director that the CAFO had no
potential to discharge. Therefore, under this proposed rule and Sec.
122.23(d)(1), the operator would decide whether (1) to obtain permit
coverage; (2) to certify under the provisions at 122.23(h); or (3) to
operate without either a permit or certification. EPA notes that a CAFO
that chooses to operate without a permit implicitly faces more
stringent requirements than permitted CAFOs because discharges in any
size storm event are prohibited from unpermitted CAFOs, while certain
exceptions may be applicable to permitted CAFOs. NPDES permit coverage
reduces CAFO operator risk and provides certainty to CAFO operators
regarding activities and actions that are necessary to comply with the
Clean Water Act.
B. Terms of the Nutrient Management Plan
In this notice, the Agency is proposing a framework for identifying
the terms of the nutrient management plan (NMP) that must be
enforceable requirements of a CAFO's NPDES permit. The proposed
framework includes three alternative approaches for specifying terms of
the NMP with respect to rates of application, which are needed to
satisfy the requirement that the NMP include ``protocols to land apply
manure, litter or process wastewater * * * that ensure appropriate
agricultural utilization of the nutrients.'' 40 CFR 122.42(e)(1)(viii).
For Large CAFOs, these proposed alternatives would also satisfy the
requirements set forth in 40 CFR 412.4. The proposed framework would
include supplemental annual reporting requirements for permitted CAFOs
to accompany these proposed alternative approaches. In addition, this
supplemental proposal includes two revisions to the 2006 proposed rule
with respect to changes to a CAFO's NMP, including revisions to the
proposed conditions that would constitute substantial change to the
terms of the NMP. This supplemental proposal seeks comment on the
proposed framework for specifying terms of the NMP to be included in an
NPDES permit, and on the proposals for changes to the NMP included in
this notice. No NMP provisions promulgated in the 2003 final rule are
affected or reopened by this supplemental proposal, nor is EPA
reopening the comment period on the 2006 proposed rule.
1. Background
As discussed in the June 2006 proposed rule, the Waterkeeper court
held that the ``terms of the NMP'' are effluent limitations that must
be included in the permit. Waterkeeper Alliance v. EPA, 399 F.3d 486,
502 (2d Cir. 2005). In the preamble to the proposed rule, EPA discussed
how the ``terms'' of a CAFO's NMP could be identified and included in
the permit. As stated in the June 2006 proposed rule, the terms of the
NMP would need to address the nine minimum required elements in 40 CFR
122.42(e)(1)(i)-(ix) and 412.4(c) (for Large CAFOs, as applicable). 71
FR 37753.
The 2006 proposed rule preamble identified a number of factors that
are necessary to the development of an NMP, including: The maximum
amount of manure that the CAFO may apply to land application areas
under its control; an inventory of the fields for land application and
the associated acreage, soil types, soil tests and testing protocols;
setbacks and other conservation measures; and a list of all of the
crops the CAFO may wish to grow on each of those fields with a matrix
of the associated realistic yield expectations and land application
rates consistent with the various field conditions. 71 FR 37755. The
Agency also stated that the NMP should include calculations necessary
to determine rates of application for the array of crops most likely to
be planted in accordance with the cropping system utilized by the CAFO
operator and could include likely alternative scenarios for other crops
that could be planted. In the Agency's view, listing alternative
cropping plans would allow a CAFO some flexibility in utilizing
different combinations of crops and crop rotations for land
application. However, the Agency added that the NMP should reasonably
forecast the practices most likely to be utilized by the CAFO. In the
proposed rule preamble, EPA solicited comment on the degree of
flexibility that should be allowed in NMPs, particularly regarding the
terms of the NMP included as permit conditions, and highlighted the
advantages and disadvantages of allowing some flexibility to the CAFO
operator. 71 FR 37753-55.
With respect to portions of the NMP that would be incorporated as
permit terms, the Agency also proposed regulatory language for
accommodating changes to the NMP that involve changes to the terms
during the permit period. The proposed rule identified changes to the
terms of the NMP that would be considered substantial changes and those
that would be considered nonsubstantial changes. The items listed as
constituting a substantial change to the terms of the NMP included
changes that could result in an increase in runoff of manure, litter,
or process wastewater from the facility and changes that could result
in an increase in the rate of nutrients from manure, litter, or process
wastewater applied to the land application area that is significant in
relation to technical standards established by the Director. 71 FR
37,756.
EPA received many comments on the NMP issues highlighted in the
proposed rule preamble. Commenters stressed the complexity associated
with nutrient management planning, particularly with respect to land
application, and the need to address changes in operation as well as
changes due to circumstances beyond the CAFO's control arising during
the permit term, especially where such changes would lead to different
rates of application of manure, litter, and process wastewater. Many
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commenters wanted clarification of the terms associated with land
application, and a number of commenters suggested factors that should
be included as terms of the NMP.
In reviewing these comments, the Agency has determined that a
provision specifically identifying the terms of the NMP required to be
included in the permit would address a number of these concerns. In
particular, the comments indicated a need to clarify what constitutes
the terms of the NMP regarding rates of application, given the
complexity of factors used to determine rates of application and the
dynamics associated with such factors. This clarification would
facilitate a common understanding of the terms of the NMP required in a
CAFO's permit, and thereby reduce the likelihood of confusion and
promote better awareness of what the permitting authority must do to
ensure that the permit complies with the Clean Water Act and these
regulations and of what a CAFO must do to comply with its permit.
Moreover, specifically identifying the terms that must be included for
each CAFO would enhance the public's ability to participate
meaningfully in the development, revision, and enforcement of the terms
of the NMP as called for by the Second Circuit in the Waterkeeper
decision.
2. Supplemental Proposal for Terms of the NMP To Be Included in the
Permit
In light of these concerns, EPA is supplementing the June 2006
proposed rule with a proposal to specify in the regulation what
elements of the NMP would be terms of the NMP that would be required to
be included as enforceable terms of a CAFO's NPDES permit. The rule
would require that the terms of the NMP must include the information,
protocols, best management practices, and other conditions identified
in a CAFO's nutrient management plan and determined by the permitting
authority to be necessary to meet the requirements of 40 CFR
122.42(e)(1). For Large CAFOs subject to the land application
requirements of the effluent limitations guideline, the terms would
include the best management practices in 40 CFR 412.4(c) in addition to
the requirements of part 122.
The ``information, protocols, best management practices, and other
conditions'' that would constitute the terms of the NMP would include
what the CAFO operator would be required to do to properly implement
its NMP and determinative conditions upon which such actions are based.
For example, both the structural design capacity necessary to satisfy
the storage requirement of Sec. (e)(1)(i) and the associated
operational and maintenance conditions necessary to ensure adequate
storage, would be considered terms of the NMP. Likewise, the terms of
the NMP would need to ensure, for example, proper management of
mortalities and diversion of clean water. However, the number of
animals confined would not necessarily need to be a term of the NMP
because a CAFO operator would be required to properly operate and
maintain the CAFO's storage facilities regardless of the number of
animals or the volume of manure, litter, or process wastewater
generated. On the other hand, the Director could, for example, include
an upper limit on the number of animals as a term.
For CAFOs that land apply manure, litter, and process wastewater,
the fields the CAFO plans to use for land application would be a term
of the NMP. Similarly, as discussed in greater detail below, field-
specific, crop-specific application rates would be terms of the NMP, as
would certain factors needed to determine the rates. However,
background information that is fixed and unchangeable, such as actual
historic yields used in the development of an NMP, while important for
determining rates of application, would not need to be terms of the
NMP.
3. Rates of Application
40 CFR 122.42(e)(1)(viii) requires the nutrient management plan to
include ``protocols to land apply manure, litter or process wastewater
in accordance with site specific nutrient management practices that
ensure appropriate agricultural utilization of the nutrients in the
manure, litter or process wastewater.'' As EPA noted in the June 2006
proposed rule, the Waterkeeper court focused on rates of application as
perhaps the most important term of the NMP, in particular the
provisions of the effluent limitations guidelines in 40 CFR 412.4(c),
and emphasized their site-specific nature. 71 FR 37753. In considering
the elements of an NMP that should be identified as the minimum terms
with respect to land application rates, in light of comments received
on the 2006 proposed rule, two general principles emerged. First, rates
of application depend on the information on which they are based, such
as information about the field, crops, and nutrient content of the
manure. Second, this information can change, and in order to address
changing circumstances during the period of a permit (ordinarily five
years), there is a need for some flexibility in establishing rates of
application. The Agency proposes three alternative approaches,
discussed below, which vary in the degree of flexibility with respect
to expressing rates of application and factors to be included in the
permit as terms of the NMP. However, all three approaches would ensure
that legally-enforceable field- and crop-specific application rates are
included in the permit.
Rates of application are field-specific and are designed to ensure
that crops receive sufficient nutrients to meet yield goals, while
minimizing the amounts of nutrients that could be transported from the
field. The total amount of plant available nutrients necessary to meet
yield goals includes residual nutrients already in the field and the
nutrients added for a particular crop. Residual nutrients are those in
the soil or on the field remaining from prior applications of manure,
litter, process wastewater, or chemical fertilizer, or from other
sources such as crop residues and nitrogen fixing legumes. The addition
of nutrients to a field includes application of chemical fertilizer, as
well as application of manure, litter, or process wastewater.
The NMP must consider the capacity of the field for manure, litter,
or process wastewater application, generally depending on the capacity
of the soil to retain phosphorus. State technical standards generally
require the use of the phosphorus index or a similar tool for assessing
the potential for nutrient transport from a field and for determining
the limiting nutrient (phosphorus or nitrogen) for application of
manure, litter, or process wastewater. The outcome of the assessment of
the potential for phosphorus transport does not typically change from
year to year. However, because soil phosphorus levels tend to change
incrementally depending upon the buffering capacity of the soil, this
assessment may limit the amount of phosphorus, and thus the amount of
manure, litter, and process wastewater, that may be added to a field.
Once the residual nutrients and potential for nutrient transport
from the fields has been determined, the next step is to identify the
crops to be planted, or other uses, for each field where land
application will occur and the nitrogen and phosphorus needs of these
crops or other uses. The NMP also must identify the realistic yield
expected from the crop or crops planted in the field, in order to
calculate the proper amount of nutrients to apply. A crop's nutrient
needs are generally determined in accordance with the
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nutrient recommendations for a given crop (or other planting, such as
forage or pasture) and the per acre realistic yield goal for such crop,
both of which are typically set by the State land grant university or
based on equations provided by the land grant university. The realistic
yield rate can also be based on historic field-specific yield data.
Finally, the amount of manure, litter, or process wastewater, in
tons or gallons, to be land applied in order to meet, but not exceed,
crop nutrient needs (after considering residual nutrients and potential
for nutrient transport from fields) depends on the nutrient content of
the manure, litter, and process wastewater, as well as the source and
form of nutrients to be land applied and the method and timing of land
application. Whereas one CAFO operator may wish to follow the planned
sequence of steps for planting crops and applying manure, litter, and
process wastewater described in the NMP submitted to the Director,
another operator may want or need to vary from that linear sequence of
events, due to choices made in the course of normal operations, or in
response to events or circumstances beyond the CAFO's control, such as
weather, crop failure, or market conditions. EPA addressed these
concerns in the preamble to the 2006 proposed rule, and stated that the
proposed approach could accommodate such changes.
In the proposed rule preamble discussion concerning changes to the
terms of the nutrient management plan, EPA encouraged CAFO operators to
develop NMPs that anticipate contingencies and changes in operations
that may occur over the term of the permit. Such contingencies may
include other potential crops that could be planted, or possible crop
rotations or other alterations in cropping patterns with accompanying
field-specific calculations for manure, litter, and process wastewater
application rates based on realistic crop yield goals, soil
characteristics, typical weather patterns, and other site-specific
field conditions. The Agency noted that the public would then have the
opportunity to review all anticipated operational scenarios and
associated field-specific manure, litter, and process wastewater
application rates, including the calculations on which these rates were
based. The Agency viewed this approach as allowing an NMP to address
most year-to-year changes in nutrient management practices anticipated
during the period of permit coverage and greatly reduce the need for
NMP and associated permit modifications, as the NMP would have already
accounted for a range of potential operational scenarios.
With respect to identifying annual rates of application as terms of
the NMP, a number of commenters stated that it was unrealistic for EPA
to expect all CAFOs to be able to establish rates of ap