National Pollutant Discharge Elimination System (NPDES) Water Transfers Rule, 33697-33708 [E8-13360]
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Federal Register / Vol. 73, No. 115 / Friday, June 13, 2008 / Rules and Regulations
parts 51 and 52. See, 72 FR 72607,
December 21, 2007.
EPA is now correcting the entirety of
that first full paragraph at 73 FR 23958
by replacing it with the following
paragraph:
‘‘The ‘reasonable possibility’ standard
identifies, for sources and reviewing
authorities, the circumstances under
which a major stationary source
undergoing a modification that does not
trigger major NSR must keep records.
EPA’s December 2007 action clarified
the meaning of the term ‘reasonable
possibility’ through changes to the
federal rule language in 40 CFR parts 51
and 52. In the present case, although
Alabama’s rules include the term
‘reasonable possibility,’ Alabama’s rules
require recordkeeping for facilities for
which there is a reasonable possibility
as well as those for which there is not.
Therefore, Alabama’s SIP revisions are
approvable.’’
Authority: 42 U.S.C. 7401 et seq.
Dated: June 4, 2008.
Russell L. Wright, Jr.,
Acting Regional Administrator, Region 4.
[FR Doc. E8–13348 Filed 6–12–08; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 122
[EPA–HQ–OW–2006–0141; FRL–8579–3]
RIN 2040–AE86
National Pollutant Discharge
Elimination System (NPDES) Water
Transfers Rule
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
SUMMARY: EPA is issuing a regulation to
clarify that water transfers are not
subject to regulation under the National
Pollutant Discharge Elimination System
(NPDES) permitting program. This rule
defines water transfers as an activity
that conveys or connects waters of the
United States without subjecting the
transferred water to intervening
industrial, municipal, or commercial
use. This rule focuses exclusively on
water transfers and does not affect any
other activity that may be subject to
NPDES permitting requirements.
This rule is consistent with EPA’s
June 7, 2006, proposed rule, which was
based on an August 5, 2005, interpretive
memorandum entitled ‘‘Agency
Interpretation on Applicability of
Section 402 of the Clean Water Act to
Water Transfers.’’
DATES: This final rule is effective on
August 12, 2008. For judicial review
purposes, this action is considered
issued as of 1 p.m. eastern daylight time
(e.d.t.) on June 27, 2008, as provided in
40 CFR 23.2. Under section 509(b)(1) of
the Clean Water Act, judicial review of
the Administrator’s action can only be
had by filing a petition for review in the
United States Court of Appeals within
120 days after the decision is considered
issued for purposes of judicial review.
ADDRESSES: The administrative record is
available for inspection and copying at
the Water Docket, located at the EPA
Docket Center (EPA/DC), EPA West
1301 Constitution Ave., Room 3334,
NW., Washington DC 20460. The
administrative record is also available
via EPA Dockets (Edocket) at https://
www.regulations.gov under docket
number EPA–HQ–OW–2006–0141. The
rule and key supporting documents are
also electronically available on the
Internet at https://www.epa.gov/npdes/
agriculture.
FOR FURTHER INFORMATION CONTACT: For
additional information contact Virginia
Garelick, Water Permits Division, Office
of Wastewater Management (4203M),
Environmental Protection Agency, 1200
Pennsylvania Ave., NW., Washington,
33697
DC 20460; telephone number: 202–564–
2316; fax: 202–564–6384; e-mail
address: garelick.virginia@epa.gov.
SUPPLEMENTARY INFORMATION:
I. General Information
A. Does This Action Apply to Me?
B. How Can I Get Copies of This Document
and Other Related Information?
C. Under What Legal Authority Is This
Final Rule Issued?
D. What is the Comment Response
Document?
II. Background and Definition of Water
Transfers
III. Rationale for the Final Rule
A. Legal Framework
B. Statutory Language and Structure
C. Legislative History
IV. Public Comment
V. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory
Planning and Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
G. Executive Order 13045: Protection of
Children From Environmental Health
and Safety Risks
H. Executive Order 13211: Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use
I. National Technology Transfer and
Advancement Act
J. Executive Order 12898: Actions To
Address Environmental Justice in
Minority Populations and Low-Income
Populations
K. Congressional Review Act
I. General Information
A. Does This Action Apply to Me?
This action applies to those involved
in the transfer of waters of the United
States. The following table provides a
list of standard industrial codes for
operations potentially covered under
this rule.
TABLE 1.—ENTITIES POTENTIALLY REGULATED BY THIS RULE
NAICS
Examples of potentially affected entities
Resource management parties (includes state departments of fish
and wildlife, state departments of
pesticide regulation, state environmental agencies, and universities).
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Category
924110 Administration of Air and
Water Resource and Solid
Waste Management Programs.
Government establishments primarily engaged in the administration,
regulation, and enforcement of water resource programs; the administration and regulation of water pollution control and prevention
programs; the administration and regulation of flood control programs; the administration and regulation of drainage development
and water resource consumption programs; and coordination of
these activities at intergovernmental levels.
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TABLE 1.—ENTITIES POTENTIALLY REGULATED BY THIS RULE—Continued
Category
NAICS
924120 Administration
servation Programs.
Examples of potentially affected entities
of
Con-
237110 Water and Sewer Line
and Related Structures Construction.
237990 Other Heavy and Civil Engineering Construction.
Public Water Supply ........................
221310 Water Supply ....................
Government establishments primarily engaged in the administration,
regulation, supervision and control of land use, including recreational areas; conservation and preservation of natural resources; erosion control; geological survey program administration;
weather forecasting program administration; and the administration
and protection of publicly and privately owned forest lands. Government establishments responsible for planning, management,
regulation and conservation of game, fish, and wildlife populations,
including wildlife management areas and field stations; and other
administrative matters relating to the protection of fish, game, and
wildlife are included in this industry.
This category includes entities primarily engaged in the construction
of water and sewer lines, mains, pumping stations, treatment
plants and storage tanks.
This category includes dam Construction and management, flood
control structure construction, drainage canal and ditch construction, flood control project construction, and spillway, floodwater,
construction.
This category includes entities engaged in operating water treatment
plants and/or operating water supply systems. The water supply
system may include pumping stations, aqueducts, and/or distribution mains. The water may be used for drinking, irrigation, or other
uses.
number for the Public Reading Room is
(202) 566–1744, and the telephone
number for the Water Docket is (202)
566–2426.
2. Electronic Access. You may access
this Federal Register document
electronically through the EPA Web site
under the Federal Register listings at
https://www.regulations.gov.
B. How Can I Get Copies of This
Document and Other Related
Information?
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This table is not intended to be
exhaustive, but rather provides a guide
for readers regarding entities likely to be
affected by this action. This table lists
the types of entities that EPA is now
aware could potentially be affected by
this action. Other types of entities not
listed in the table could also be affected.
To determine whether your facility is
affected by this action, you should
carefully examine the applicability
criteria in 40 CFR 122.3. 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.
D. What Is the Comment Response
Document?
EPA received a large number of
comments on the proposed rule,
including thousands of form letters.
EPA evaluated all of the comments
submitted and prepared a Comment
Response Document containing both the
comments received and the Agency’s
responses to those comments. The
Comment Response Document
complements and supplements this
preamble by providing more detailed
explanations of EPA’s final action. The
Comment Response Document is
available at the Water Docket.
1. Docket. EPA has established an
official public docket for this action
under Docket ID No. EPA–HQ–OW–
2006–0041. The official public docket
consists of the documents specifically
referenced in this action, any public
comments received, and other
information related to this action.
Although listed in the index, some
information, such as copyrighted
material, will be publicly available only
in hard copy. Publicly available docket
materials are available either
electronically in https://
www.regulations.gov or in hard copy at
the Water Docket in the EPA Docket
Center, EPA West, 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
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C. Under What Legal Authority Is This
Final Rule Issued?
This final rule is issued under the
authority of sections 402 and 501 of the
Clean Water Act., 33 U.S.C. 1342 and
1361.
II. Background and Definition of Water
Transfers
Water transfers occur routinely and in
many different contexts across the
United States. Typically, water transfers
route water through tunnels, channels,
and/or natural stream water features,
and either pump or passively direct it
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for uses such as providing public water
supply, irrigation, power generation,
flood control, and environmental
restoration. Water transfers can be
relatively simple, moving a small
quantity of water a short distance, or
very complex, transporting substantial
quantities of water over long distances,
across both State and basin boundaries.
Water transfers may be of varying
complexities and sizes; there may be
multiple reservoirs, canals, or pumps
over the course of the transfer, or the
route may be a more direct connection
between the donor and the receiving
waterbody. There are thousands of
water transfers currently in place in the
United States, including sixteen major
diversion projects in the western States
alone. Examples include the ColoradoBig Thompson Project in Colorado and
the Central Valley Project in California.
Water transfers are administered by
various federal, State, and local agencies
and other entities. The Bureau of
Reclamation administers significant
transfers in western States to provide
approximately 140,000 farmers with
irrigation water. With the use of water
transfers, the Army Corps of Engineers
keeps thousands of acres of agricultural
and urban land in southern Florida from
flooding in former areas of Everglades
wetlands. Many large cities in the west
and the east would not have adequate
sources of water for their citizens were
it not for the continuous redirection of
water from outside basins. For example,
both the cities of New York and Los
Angeles depend on water transfers from
distant watersheds to meet their
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municipal demand. In short, numerous
States, localities, and residents are
dependent upon water transfers, and
these transfers are an integral
component of U.S. infrastructure.
The question of whether or not an
NPDES permit is required for water
transfers arises because activities that
result in the movement of waters of the
U.S., such as trans-basin transfers of
water to serve municipal, agricultural,
and commercial needs, typically move
pollutants from one waterbody (donor
water) to another (receiving water).
Although there have been a few isolated
instances where entities responsible for
water transfers have been issued NPDES
permits, Pennsylvania is the only
NPDES permitting authority that
regularly issues NPDES permits for
water transfers. Pennsylvania began
issuing permits for water transfers in
1986, in response to a State court
decision mandating the issuance of such
permits. See DELAWARE Unlimited v.
DER, 508 A.2d 348 (Pa. Cmwlth, 1986).
In addition, some Courts of Appeals
have required NPDES permits for
specific water transfers associated with
the expansion of a ski resort and the
supply of drinking water. See, e.g.,
Dubois v. U.S. Dep’t of Agriculture, 102
F.3d 1273 (1st Cir. 1996); Catskill
Mountains Chapter of Trout Unlimited,
Inc. v. City of New York, 273 F.3d 481
(2nd Cir 2001), aff’d, Catskill Mountains
Chapter of Trout Unlimited, Inc. v. City
of New York, 451 F.3d 77 (2nd Cir
2006). Otherwise, however, water
transfers have not been regulated under
section 402 of the Clean Water Act
(CWA or the Act).
The Supreme Court recently
addressed the issue of whether an
NPDES permit is necessary for the mere
transfer of water in South Fla. Water
Mgmt. Dist. v. Miccosukee Tribe of
Indians, 541 U.S. 95 (2004). The
Supreme Court in Miccosukee vacated a
decision by the 11th Circuit, which had
held that a Clean Water Act permit was
required for transferring water from one
navigable water into another, a Water
Conservation Area in the Florida
Everglades. The Court remanded the
case for further fact-finding as to
whether the two waters in question
were ‘‘meaningfully distinct.’’ 1 If they
were not, an NPDES permit would not
be required. The Court declined to
resolve the question of whether water
transfers require NPDES permits when
the waterbodies at issue are
meaningfully distinct. The Court noted
1 At the time of this rulemaking, the District Court
has stayed its proceedings until resolution of a
similar case in the same District Court, Friends of
the Everglades v. South Florida Water Management
District.
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that some legal arguments made by the
parties regarding this question had not
been raised in the lower court
proceedings and noted that these
arguments would be open to the parties
on remand. Id. at 109.
On August 5, 2005, EPA issued a legal
memorandum entitled ‘‘Agency
Interpretation on Applicability of
section 402 of the Clean Water Act to
Water Transfers’’ (‘‘interpretive
memorandum’’). The principal legal
question addressed in the interpretive
memorandum was whether the
movement of pollutants from one water
of the U.S. to another by a water transfer
is the ‘‘addition’’ of a pollutant
potentially subjecting the activity to the
permitting requirement under section
402 of the Act. Based on the statute as
a whole and consistent with the
Agency’s longstanding practice, the
interpretive memorandum concluded
that Congress generally expected water
transfers would be subject to oversight
by water resource management agencies
and State non-NPDES authorities, rather
than the permitting program under
section 402 of the CWA.
On June 7, 2006, EPA proposed
regulations based on the analysis
contained in the interpretive
memorandum to expressly state that
water transfers are not subject to
regulation under section 402 of the
CWA. The Agency proposed to define
water transfers as ‘‘an activity that
conveys waters of the United States to
another water of the United States
without subjecting the water to
intervening industrial, municipal, or
commercial use.’’ The Act reserves the
ability of States to regulate water
transfers under State law and this
proposed rulemaking was not intended
to interfere with this State prerogative.
See CWA section 510.
EPA is issuing a final regulation that
is nearly identical to the proposed rule.
(Minor changes have been made for
clarity.) Through today’s rule, the
Agency concludes that water transfers,
as defined by the rule, do not require
NPDES permits because they do not
result in the ‘‘addition’’ of a pollutant.
Consistent with the proposed rule, EPA
defines water transfers in the following
manner: ‘‘Water transfer means an
activity that conveys or connects waters
of the United States without subjecting
the transferred water to intervening
industrial, municipal, or commercial
use.’’ In order to constitute a ‘‘water
transfer’’ under this rule, and, therefore,
be exempt from the requirement to
obtain an NPDES permit, the water
being conveyed must be a water of the
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33699
U.S.2 prior to being discharged to the
receiving waterbody. If the water that is
being conveyed is not a water of the
U.S. prior to being discharged to the
receiving body, then that activity does
not constitute a water transfer under
today’s rule. Additionally, the water
must be conveyed from one water of the
U.S. to another water of the U.S.
Conveyances that remain within the
same water of the U.S., therefore, do not
constitute water transfers under this
rule, although movements of water
within a single water body are also not
subject to NPDES permitting
requirements. As the rule makes clear,
in order to be a water transfer under the
rule, the water must be conveyed
without being subjected to an
intervening industrial, municipal, or
commercial use.
Consider water that is being moved
from Reservoir A to Reservoir B in a
different watershed. In order to get from
Reservoir A to Reservoir B, the water
must first be released through a dam.
The water then travels down River A,
which is considered a water of the U.S.
Next, the water is conveyed from River
A to River B through a tunnel. Finally,
the water travels down River B, also a
water of the U.S., and flows into
Reservoir B. There are several points in
this example where water is conveyed
from one body to another, but not all of
those points would themselves
constitute a ‘‘water transfer’’ because
they are not the conveyance of ‘‘waters
of the United States to another water of
the United States.’’ The first example is
the release from Reservoir A to River A.
This does not constitute a water transfer
under EPA’s definition because the
water on both sides of the dam is part
of the same water of the U.S.3 The next
movement is the release from River A
into River B, through a tunnel. This
release constitutes a water transfer
under the scope of this rule because it
conveys water from one water of the
U.S. to another water of the U.S.
without subjecting the water to an
intervening industrial, municipal or
2 Waters of the U.S. are defined for purposes of
the NPDES program in 40 CFR 122.2 and this
rulemaking does not seek to address what is within
the scope of that term.
3 It should be noted, however, that this release
would still not require an NPDES permit because
EPA and the Federal courts have determined that
a discharge from a dam does not result in an
‘‘addition’’ of a pollutant unless the dam itself
discharges a pollutant such as grease into the water
passing through the dam. See National Wildlife
Fed’n v. Gorsuch, 693 F.2d 156 (D.C. Cir. 1982);
National Wildlife Fed’n v. Consumers Power
Company, 862 F.2d 580 (6th Cir. 1988). Cf. S.D.
Warren Co. v. Maine Board of Environmental
Protection, 126 S.Ct. 1843 (2006) (Certification
under CWA section 401 may be needed in some
instances).
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commercial use. Therefore, unless this
conveyance itself introduces pollutants
into the water being conveyed, the
release will not require an NPDES
permit under today’s rule. River B’s
subsequent flow into Reservoir B, which
is formed by a dam on Reservoir B, does
not constitute a water transfer because
it is merely movement within the same
water of the U.S., and, as discussed
above, would not require an NPDES
permit for such movement.
The remainder of the preamble to this
final rule is organized as follows.
Section III discusses the rationale for the
final rule based on the language,
structure, and legislative history of the
Clean Water Act. Section IV summarizes
and responds to the major comments
received in response to the scope of the
proposed rule. Section V reviews
statutory provisions and various
executive orders.
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III. Rationale for the Final Rule
On June 7, 2006, EPA published a
proposed rule that would exclude from
NPDES permit requirements discharges
from water transfers that do not subject
the water to an intervening industrial,
municipal, or commercial use, so long
as pollutants are not introduced by the
water transfer activity itself. This
proposal, like EPA’s August 5, 2005,
interpretive memorandum, explained
that no one provision of the Act
expressly addresses whether water
transfers are subject to the NPDES
program but described the indicia of
Congressional intent that water transfers
not be so regulated. Therefore, today’s
rule appropriately defers to
congressional concerns that the statute
not unnecessarily burden water quantity
management activities and excludes
water transfers from the NPDES
program. This section will review the
legal framework for evaluating EPA’s
interpretation of the CWA, explain the
Agency’s interpretation of the CWA,
including a brief survey of prior
litigation over the relevant statutory
terms, and outline the relevant
legislative history.
A. Legal Framework
Under what is traditionally viewed as
Chevron analysis, a court examining the
legality of an agency’s interpretation of
a statute is to first ask whether the
statute speaks clearly to the precise
question at issue and must give effect to
the unambiguously expressed intent of
Congress if such unambiguous intent
can be discerned. Chevron U.S.A. Inc. v.
NRDC, 467 U.S. 837, 842–843
(Chevron); National Ass. of
Homebuilders, et al. v. Defenders of
Wildlife, et al., 127 S.Ct. 2518, 2534
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(2007) (NAHB). To the extent that a
statute does not speak clearly to the
specific issue, the Agency interpretation
must be upheld if it is based on a
permissible construction of the statute.
Chevron, 467 U.S. at 843; NAHB, 127
S.Ct. at 2534. Courts are required to
accept an agency’s reasonable
interpretation of a statute, even if this
interpretation differs from what the
court believes is the ‘‘best’’ statutory
interpretation. National Cable and
Telecommunications Ass’n, et. al. v.
Brand X, et al., 545 U.S. 967, 980 (2005)
(Brand X).
Deference to an agency interpretation
of a statute under Chevron is
appropriate where Congress has
authorized an agency to make rules
carrying the force of law, and such
authorization is apparent where the
agency is empowered to make rules or
adjudicate issues or there are other
indications of comparable congressional
intent. United States v. Mead Corp., 533
U.S. 218 (2001). Congress has expressly
authorized EPA to prescribe regulations
as are necessary to administer the CWA,
and today’s rule has been promulgated
to address the question whether water
transfers require NPDES permits. CWA
section 501(a); 33 U.S.C. 1361(a); 71 FR
32887 (June 7, 2006).
As discussed below, EPA has
reviewed the language, structure and
legislative history of the CWA and
concludes that today’s rule, which
clarifies that NPDES permits are not
required for transfers of waters of the
United States from one water body to
another, is a permissible construction of
the statute. Taken as a whole, the
statutory language and scheme support
the conclusion that permits are not
required for water transfers.
B. Statutory Language and Structure
The Clean Water Act prohibits the
discharge of a pollutant by any person
except in compliance with specified
statutory sections, including section
402. CWA section 301(a). The term
‘‘discharge of a pollutant’’ is defined as
‘‘any addition of any pollutant to
navigable waters from any point
source.’’ CWA section 502(12). The legal
question addressed by today’s rule is
whether a water transfer as defined in
the new regulation constitutes an
‘‘addition’’ within the meaning of
section 502(12).
The term ‘‘addition’’ has been
interpreted by courts in a variety of
contexts that are relevant here. Several
courts of appeals have determined that
water flowing through dams and
hydroelectric facilities does not
constitute an addition of a pollutant
under the CWA. Specifically, the Court
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of Appeals for the D.C. Circuit agreed
with EPA that the term ‘‘addition’’ may
reasonably be limited to situations in
which ‘‘the point source itself
physically introduces a pollutant into a
water from the outside world.’’ National
Wildlife Fed’n v. Gorsuch, 693 F.2d 156,
175 (D.C. Cir. 1982) (Gorsuch)
(accepting EPA’s view that the
requirement for an NPDES permit ‘‘is
established when the pollutant first
enters the navigable water, and does not
change when the polluted water later
passes through the dam from one body
of navigable water (the reservoir) to
another (the downstream river).’’) The
Court of Appeals for the Sixth Circuit
reached the same conclusion with
regard to a hydropower facilities
operating on Lake Michigan. National
Wildlife Fed’n v. Consumers Power Co.
862 F.2d 580, 584 (6th Cir. 1988)
(Consumers Power) (agreeing with the
Gorsuch Court’s conclusion that EPA’s
construction of ‘‘addition’’ is a
permissible one). Both the Gorsuch and
Consumers Power courts accorded
deference to EPA’s interpretation of the
CWA, and specifically to its
interpretation of the term ‘‘addition.’’
Gorsuch, 693 F.2d at 166–167;
Consumers Power, 862 F.2d at 584.
Three other Courts of Appeals,
however, have concluded that where a
water transfer involves distinct waters
of the United States, the transfer
constitutes an ‘‘addition’’ of pollutants.
Dubois v. U.S. Dept. of Agriculture, et
al., 102 F.3d 1273, 1298–1300 (1st Cir.
1996); Catskill Mountains Chapter of
Trout Unlimited, Inc. v. City of New
York, 273 F.3d 481, 491–93 (2nd Cir.
2001) (Catskill I); Miccosukee Tribe of
Indians v. South Florida Water
Management District, 280 F.3d 1364
(11th Cir. 2002), vacated by Miccosukee,
541 U.S. at 112.4 These three Courts of
Appeals construed the term ‘‘addition’’
4 EPA recognizes that the approach adopted by
these three courts is at odds with today’s rule. None
of these three courts, however, viewed the question
of statutory interpretation through the lens of
Chevron deference. DuBois, 102 F.3d at 1285, n. 15
(Chevron does not apply because the court ‘‘was not
reviewing an agency’s interpretation of the statute
that it was directed to enforce.’’); Catskill
Mountains Chapter of Trout Unlimited, Inc. v. City
of New York, 451 F.3d 77, 82 (2nd Cir. 2006)
(Catskill II) (‘‘The City concedes that this EPA
interpretation is not entitled to Chevron
deference.’’); Catskill I, 273 F.3d at 490 (Declining
to apply Chevron deference, but acknowledging that
‘‘[i]f the EPA’s position had been adopted in a
rulemaking or other formal proceeding, deference of
the sort applied by the Gorsuch and Consumers
Power courts might be appropriate.’’); Miccosukee,
280 F.3d at 1367, n. 4 (‘‘The EPA is no party to this
case; we can ascertain no EPA position applicable
to [the water transfer at issue) to which to give any
deference, much less Chevron deference.’’).
Moreover, the approaches adopted by the Gorsuch
and Consumers Power courts is compatible with
today’s rule.
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so as to include transfers of water from
one body to another distinct body
(Catskill I, 273 F.3d at 491 (‘‘EPA’s
position * * * is that for there to be an
‘addition,’ a ‘point source must
introduce the pollutant into navigable
water from the outside world.’ We agree
with this view provided that ‘outside
world’ is construed as any place outside
the particular water body to which
pollutants are introduced.’’) (internal
citations omitted, emphasis added);
Catskill II, 451 F.3d at 82–85) or
transfers that cause water to move in a
direction it would not ordinarily flow
(DuBois, 102 F.3d at 1297; Catskill I, 273
at 493–94 (explaining DuBois);
Miccosukee, 280 F.3d at 1368–69).
In pending litigation, on the other
hand, the United States has taken the
position that the Clean Water Act
generally does not subject water
transfers to the NPDES program:
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The statute defines ‘‘‘discharge of a
pollutant’’’ as ‘‘any addition of any pollutant
to navigable waters from any point source.’’
33 U.S.C. 1362(12). When the statutory
definition of ‘‘‘navigable waters’’’—i.e., ‘‘the
waters of the United States,’’ 33 U.S.C.
1362(7)—is inserted in place of ‘‘navigable
waters,’’ the statute provides that NPDES
applies only to the ‘‘addition of any pollutant
to the waters of the United States.’’ Given the
broad definition of ‘‘pollutant,’’ transferred
(and receiving) water will always contain
intrinsic pollutants, but the pollutants in
transferred water are already in ‘‘the waters
of the United States’’ before, during, and after
the water transfer. Thus, there is no
‘‘addition’’; nothing is being added ‘‘to’’ ‘‘the
waters of the United States’’ by virtue of the
water transfer, because the pollutant at issue
is already part of ‘‘the waters of the United
States’’ to begin with. Stated differently,
when a pollutant is conveyed along with, and
already subsumed entirely within, navigable
waters and the water is not diverted for an
intervening use, the water never loses its
status as ‘‘waters of the United States,’’ and
thus nothing is added to those waters from
the outside world.
Brief for the United States in Friends
of the Everglades v. South Florida Water
Management Dist., No. 07–13829–H
(11th Cir.).
The Agency has concluded that, taken
as a whole, the statutory language and
structure of the Clean Water Act
indicate that Congress generally did not
intend to subject water transfers to the
NPDES program. Interpreting the term
‘‘addition’’ in that context, EPA
concludes that water transfers, as
defined by today’s rule, do not
constitute an ‘‘addition’’ to navigable
waters to be regulated under the NPDES
program. Instead, Congress intended to
leave primary oversight of water
transfers to state authorities in
cooperation with Federal authorities.
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In interpreting the term ‘‘addition’’ in
section 502(12) of the statute, EPA is
guided by several principles.
‘‘Addition’’ is a general term, undefined
by the statute. Partly for this reason, the
courts have accorded substantial
discretion to EPA in interpreting the
term in the context of the ‘‘dams’’ cases.
Gorsuch, 693 F.2d at 175 (finding the
statute capable of supporting multiple
interpretations, the legislative history
unhelpful, and concluding that
Congress would have given EPA
discretion to define ‘‘addition’’ had it
expected the meaning of the term to be
disputed); Consumers Power, 862 F.2d
at 584–85 (agreeing with the analysis in
Gorsuch). Moreover, several alternative
ways of interpreting the term ‘‘addition’’
have been proposed in the context of
water transfers. As noted above, EPA’s
longstanding position is that an NPDES
pollutant is ‘‘added’’ when it is
introduced into a water from the
‘‘outside world’’ by a point source.
Gorsuch, 693 F.2d at 174–175. Under
one interpretation, advanced by the 2nd
Circuit in Catskill Mountain, ‘‘the
outside world’’ means anywhere outside
the particular waterbody receiving the
pollutant, and so a permit in that case
was required for movement of
pollutants between distinct waterbodies.
Catskill I, 273 F.3d at 491. EPA does not
agree with this understanding of the
term ‘‘outside world’’ as evinced by its
long-standing practice of generally not
requiring NPDES permits for transfers
between water bodies, which it has
defended against court challenges
asserting that such transfers do require
such permits. Rather, EPA believes that
an addition of a pollutant under the Act
occurs when pollutants are introduced
from outside the waters being
transferred.
As noted above, various courts have
reached different conclusions in
determining when movement of waters
of the United States containing
pollutants constitutes an ‘‘addition’’ of a
pollutant. To resolve the confusion
created by these conflicting approaches,
the Agency has looked to the statute as
a whole for textual and structural
indices of Congressional intent on the
question whether water transfers that do
not themselves introduce new
pollutants require an NPDES permit.
Statutory construction principles
instruct that the Clean Water Act should
be interpreted by analyzing the statute
as a whole. United States v. Boisdore’s
Heirs, 49 U.S. 113, 122 (1850). The
Supreme Court has long explained ‘‘in
expounding a statute, we must not be
guided by a single sentence or member
of a sentence, but look to the provisions
of the whole law, and its object and
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33701
policy.’’ Id. See also, Gustafond v.
Alloyd Co., Inc., 513 U.S. 561, 570
(1995), Smith v. United States, 508 U.S.
223, 233 (1993), United States Nat’l
Bank of Or. v. Independent Ins. Agents
of Am., Inc., 508 U.S. 439, 455 (1993).
In general, the ‘‘whole statute’’
interpretation analysis means that ‘‘a
statute is passed as a whole and not in
parts or sections and is animated by one
general purpose and intent.
Consequently, each part or section
should be construed in connection with
every other part or section so as to
produce a harmonious whole.’’ Norman
J. Singer, Statutes and Statutory
Construction vol. 2A § 46:05, 154 (6th
ed., West Group 2000). As the Second
Circuit has explained with regard to the
CWA:
Although the canons of statutory
interpretation provide a court with numerous
avenues for supplementing and narrowing
the possible meaning of ambiguous text, most
helpful to our interpretation of the CWA in
this case are two rules. First, when
determining which reasonable meaning
should prevail, the text should be placed in
the context of the entire statutory structure
[quoting United States v. Dauray, 215 F.3d
257, 262 (2d Cir. 2000)]. Second, ‘‘absurd
results are to be avoided and internal
inconsistencies in the statute must be dealt
with.’’ United States v. Turkette, 452 U.S.
576, 580 (1981).
Natural Res. Def. Council v. Muszynski,
268 F.3d 91, 98 (2d Cir. 2001). See also,
Singer, vol. 3B § 77:4, at 256–258.
A holistic approach to the text of the
CWA is needed here in particular
because the heart of this matter is the
balance Congress created between
federal and State oversight of activities
affecting the nation’s waters. The
purpose of the CWA is to protect water
quality. Congress nonetheless
recognized that programs already
existed at the State and local levels for
managing water quantity, and it
recognized the delicate relationship
between the CWA and State and local
programs. Looking at the statute as a
whole is necessary to ensure that the
analysis herein is consonant with
Congress’s overall policies and
objectives in the management and
regulation of the nation’s water
resources.
While the statute does not define
‘‘addition,’’ sections 101(g), 102(b),
304(f), and 510(2) provide a strong
indication that the term ‘‘addition’’
should be interpreted in accordance
with the text of the more specific
sections of the statute. In light of
Congress’ clearly expressed policy not
to unnecessarily interfere with water
resource allocation and its discussion of
changes in the movement, flow or
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circulation of any navigable waters as
sources of pollutants that would not be
subject to regulation under section 402,
it is reasonable to interpret ‘‘addition’’
as not including the mere transfer of
navigable waters.
The specific statutory provisions
addressing the management of water
resources—coupled with the overall
statutory structure—provide textual
support for the conclusion that Congress
generally did not intend for water
transfers to be regulated under section
402. The Act establishes a variety of
programs and regulatory initiatives in
addition to the NPDES permitting
program. It also recognizes that the
States have primary responsibilities
with respect to the ‘‘development and
use (including restoration, preservation,
and enhancement) of land and water
resources.’’ CWA section 101(b).
Congress also made clear that the
Clean Water Act is to be construed in a
manner that does not unduly interfere
with the ability of States to allocate
water within their boundaries, stating:
It is the policy of Congress that the
authority of each State to allocate quantities
of water within its jurisdiction shall not be
superseded, abrogated or otherwise impaired
by [the Act]. It is the further policy of
Congress that nothing in this chapter shall be
construed to supersede or abrogate rights to
quantities of water which have been
established by any State. Federal agencies
shall co-operate with State and local agencies
to develop comprehensive solutions to
prevent, reduce and eliminate pollution in
concert with programs for managing water
sources.
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CWA section 101(g). While section
101(g) does not prohibit EPA from
taking actions under the CWA that it
determines are needed to protect water
quality,5 it nonetheless establishes in
the text of the Act Congress’s general
direction against unnecessary Federal
interference with State allocations of
water rights.
Water transfers are an essential
component of the nation’s infrastructure
for delivering water that users are
entitled to receive under State law.
Because subjecting water transfers to a
federal permitting scheme could
unnecessarily interfere with State
decisions on allocations of water rights,
this section provides additional support
for the Agency’s interpretation that,
absent a clear Congressional intent to
the contrary, it is reasonable to read the
No. 1 of Jefferson County. v. Wash. State
Dep’t. of Ecology, 511 U.S. 700, 720 (1994)
(‘‘Sections 101(g) and 510(2) preserve the authority
of each State to allocate water quantity as between
users; they do not limit the scope of water pollution
controls that may be imposed on users who have
obtained, pursuant to state law, a water
allocation.’’).
statute as not requiring NPDES permits
for water transfers. See United States v.
Bass, 404 U.S. 336, 349 (1971) (‘‘unless
Congress conveys its purpose clearly, it
will not be deemed to have significantly
changed the federal-state balance.’’)
An additional statutory provision,
section 510(2), similarly provides:
Except as expressly provided in this Act,
nothing in this Act shall * * * be construed
as impairing or in any manner affecting any
right or jurisdiction of the States with respect
to the waters (including boundary waters) of
such States.
Like section 101(g), this provision
supports the notion that Congress did
not intend administration of the CWA to
unduly interfere with water resource
allocation.
Finally, one section of the Act—
304(f)—expressly addresses water
management activities. Mere mention of
an activity in section 304(f) does not
mean it is exclusively nonpoint source
in nature. See Miccosukee 541 U.S. at
106 (noting that section 304(f)(2)(F) does
not explicitly exempt nonpoint sources
if they also fall within the definition of
point source). Nonetheless, section
304(f) is focused primarily on
addressing pollution sources outside the
scope of the NPDES program. See H.R.
Rep. No. 92–911, at 109 (1972),
reprinted in Legislative History of the
Water Pollution Control Act
Amendments of 1972, Vol. 1 at 796
(Comm. Print 1973) (‘‘[t]his section
* * * on * * * nonpoint sources is
among the most important in the 1972
Amendments’’) (emphasis added)). This
section directed EPA to issue guidelines
for identifying and evaluating the nature
and extent of nonpoint sources of
pollution,6 as well as processes,
procedures and methods to control
pollution from, among other things,
‘‘changes in the movement, flow or
circulation of any navigable waters or
ground waters, including changes
caused by the construction of dams,
levees, channels, causeways, or flow
diversion facilities.’’ CWA 304(f)(2)(F)
(emphasis added).
While section 304(f) does not
exclusively address nonpoint sources of
pollution, it nonetheless ‘‘concerns
nonpoint sources’’ (Miccosukee, 541
U.S. at 106) and reflects an
understanding by Congress that water
movement could result in pollution, and
that such pollution would be managed
by States under their nonpoint source
5 PUD
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6 Sources not regulated under sections 402 or 404
are generically referred to as ‘‘nonpoint sources.’’
See Consumers Power, 862 F.2d at 582 (‘‘‘nonpoint
source’ is shorthand for and ‘includes all water
quality problems not subject to section 402’’’)
(quoting Gorsuch, 693 F.2d at,166) (internal
quotation marks omitted).
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program authorities, rather than the
NPDES program. Today’s rule accords
with the direction to EPA and other
federal agencies in section 101(g) to
work with State and local agencies to
develop ‘‘comprehensive solutions’’ to
water pollution problems ‘‘in concert
with programs for managing water
resources.’’
The text of these sections of the Act
together demonstrate that Congress was
aware that there might be pollution
associated with water management
activities, but chose to defer to
comprehensive solutions developed by
State and local agencies for controlling
such pollution. Because the NPDES
program focuses on discharges from
point sources of pollutants, it is not the
kind of comprehensive program that
Congress believed was best suited to
addressing pollution, which is the term
used for the nonpoint source program.
It is this type of non-point source
pollution that may be associated with
water transfers.
In several important ways, water
transfers are unlike the types of
discharges that were the primary focus
of Congressional attention in 1972.
Discharges of pollutants covered by
section 402 are subject to ‘‘effluent’’
limitations. Water transfers, however,
are not like effluent from an industrial,
commercial or municipal operation.
Rather than discharge effluent, water
transfers convey one water of the U.S.
into another. Additionally, the operators
of water control facilities are generally
not responsible for the presence of
pollutants in the waters they transport.
Rather, those pollutants often enter ‘‘the
waters of the United States’’ through
point and nonpoint sources
unassociated with those facilities and
beyond control of the project operators.
Congress generally intended that
pollutants be controlled at the source
whenever possible. See S. Rep. No. 92–
414, p. 77 (1972) (justifying the broad
definition of navigable waters because it
is ‘‘essential that discharge of pollutants
be controlled at the source’’).7 The
pollution from transferred waters is
more sensibly addressed through water
resource planning and land use
regulations, which attack the problem at
its source. See, e.g., CWA section 102(b)
(reservoir planning); CWA section
208(b)(2)(F) (land use planning to
7 Recognition of a general intent to control
pollutants at the source does not mean that
dischargers are responsible only for pollutants that
they generate; rather, point sources need only
convey pollutants into navigable waters to be
subject to the Act. See Miccosukee at 105.
Municipal separate storm sewer systems, for
example, are clearly subject to regulation under the
Act. CWA section 402(p).
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reduce agricultural nonpoint sources of
pollution); CWA section 319 (nonpoint
source management programs); and
CWA section 401 (state certification of
federally licensed projects). Congress
acknowledged this when it directed
Federal agencies to co-operate with
State and local agencies to develop
comprehensive solutions to prevent,
reduce, and eliminate pollution in
concert with programs for managing
water sources.
The Agency, therefore, concludes
that, taken as a whole, the statutory
language and structure of the Clean
Water Act indicate that Congress
generally did not intend to subject water
transfers to the NPDES program.
Interpreting the term ‘‘addition’’ in that
context, EPA concludes that water
transfers, as defined by today’s rule, do
not constitute an ‘‘addition’’ to
navigable waters to be regulated under
the NPDES program. Rather, Congress
intended to leave primary oversight of
water transfers to state authorities in
cooperation with Federal authorities.
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C. Legislative History
The legislative history of the Clean
Water Act also supports the conclusion
that Congress generally did not intend
to subject water transfers to the NPDES
program. First, the legislative history of
section 101(g) reveals that ‘‘[i]t is the
purpose of this [provision] to insure that
State [water] allocation systems are not
subverted.’’ 3 Congressional Research
Serv., U.S. Library of Congress, Serial
No. 95–14, A Legislative History of the
Clean Water Act of 1977, at 532 (1978);
see PUD No. 1 of Jefferson County v.
Washington Dep’t of Ecology, 511 U.S.
700, 721 (1994).
Notably, the legislative history of the
Act discusses water flow management
activities in the context of the nonpoint
source program only. In discussing
section 304(f), the House Committee
Report specifically mentioned water
flow management as an area where EPA
would provide technical guidance to
States for their nonpoint source
programs, rather than an area to be
regulated under section 402.
This section and the information on such
nonpoint sources is among the most
important in the 1972 Amendments. * * *
The Committee, therefore, expects the
Administrator to be most diligent in
gathering and distribution of the guidelines
for the identification of nonpoint sources and
the information on processes, procedures,
and methods for control of pollution from
such nonpoint sources as * * * natural and
manmade changes in the normal flow of
surface and ground waters.
H.R. Rep. No. 92–911, at 109 (1972)
(emphasis added).
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In the legislative history of section
208 of the Act, the House Committee
report noted that in some States, water
resource management agencies
allocating stream flows are required to
consider water quality impacts. The
Report stated:
[I]n some States water resource
development agencies are responsible for
allocation of stream flow and are required to
give full consideration to the effects on water
quality. To avoid duplication, the Committee
believes that a State which has an approved
program for the handling of permits under
section 402, and which has a program for
water resource allocation should continue to
exercise the primary responsibility in both of
these areas and thus provide a balanced
management control system.
H.R. Rep. No. 92–911, at 96 (1972).
Thus, Congress recognized that the
new section 402 permitting program
was not the only viable approach for
addressing water quality issues
associated with State water resource
management. The legislative history
makes clear that Congress generally did
not intend a wholesale transfer of
responsibility for water quality away
from water resource agencies to the
NPDES authority. Rather, Congress
encouraged States to obtain approval of
authority to administer the NPDES
program under section 402(b) so that the
NPDES program could work in concert
with water resource agencies’ oversight
of water management activities to
ensure a ‘‘balanced management control
system.’’ Id.
In sum, the language, structure, and
legislative history of the statute all
support the conclusion that Congress
generally did not intend to subject water
transfers to the NPDES program. Water
transfers are an integral part of water
resource management; they embody
how States and resource agencies
manage the nation’s water resources and
balance competing needs for water.
Water transfers also physically
implement State regimes for allocating
water rights, many of which existed
long before enactment of the Clean
Water Act. Congress was aware of those
regimes, and did not want to impair the
ability of these agencies to carry them
out. EPA’s conclusion that the NPDES
program does not apply to water
transfers respects Congressional intent,
comports with the structure of the Clean
Water Act, and gives meaning to
sections 101(g) and 304(f) of the Act.
Based on these reasons, today’s rule is
within EPA’s authority and consistent
with the CWA.
IV. Public Comment
EPA received many comments from
the public and a number of states stating
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33703
that the Agency does not have authority
to exclude from the requirement to
obtain NPDES permits, a specific class
of dischargers (in this case, water
transfers). These commenters were
concerned that the proposed rule could
jeopardize the NPDES and water quality
standards (WQS) programs. In
particular, they feared that point source
regulation of discharges from
impoundments used to settle mining
wastes might fall outside the scope of
section 402 if the proposed rule were
finalized. In response to these
comments, the Agency believes that
impoundments used to settle mining
process water or waste water would
generally constitute ‘‘waste treatment
systems’’ designed to meet the
requirements of the CWA and would be
excluded from the definition of ‘‘waters
of the United States.’’ See 40 CFR 122.2
(definition of ‘‘Waters of the United
States’’). The addition of pollutants from
a waste treatment system to a water of
the United States triggers the permitting
requirement, and today’s rule therefore
does not affect the permitting of such
facilities.
Some commenters argued that the
proposed rule is inconsistent with
section 404 of the CWA (permits for
dredged or fill material). They stated
that dredged material is listed as a
pollutant under section 502 of the CWA
and that the proposed rule implies that
dredged material never requires a
permit unless the dredged material
originates from a waterbody that is not
a water of the U.S. EPA believes that
today’s final rule will not have an effect
on the 404 program. The statutory
definition of ‘‘pollutant’’ includes
‘‘dredged spoil,’’ which by its very
nature comes from a waterbody. 33
U.S.C. 1362(6); 40 CFR 232.2; United
States v. Hubenka, 438 F.3d 1026, 1035
(10th Cir. 2006); United States v.
Deaton, 209 F.3d 331, 335–336 (4th Cir.
2000); Borden Ranch Partnership v.
United States, 261 F.3d 810, 814 (9th
Cir. 2001). Because Congress explicitly
forbade discharges of dredged material
except as in compliance with the
provisions cited in CWA section 301,
today’s rule has no effect on the 404
permit program, under which
discharges of dredged or fill material
may be authorized by a permit. 33
U.S.C. 1344.
As explained above, EPA disagrees
that Congress generally intended water
transfers to obtain NPDES permits. EPA
believes that this action will add clarity
to an area in which judicial decisions
have created uncertainty, and for
reasons previously described in section
III of this preamble, concludes that
Congress generally intended to leave the
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oversight of water transfers to
authorities other than the NPDES
program. Congress made clear that the
CWA is to be construed in a manner that
does not unduly interfere with the
ability of States to allocate water within
their boundaries. Specific statutory
provisions in the CWA addressing the
management of water resources denote
that Congress generally did not intend
for water transfers to be regulated under
section 402 of the CWA. Rather, sections
101(b), 208, and 304(f), in particular,
establish a variety of programs and
regulatory initiatives that more
appropriately address water transfers.
EPA’s conclusion that the NPDES
program does not apply to water
transfers respects Congressional intent
and comports with the structure of the
CWA.
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Definition of a Water Transfer
In the proposed rule, EPA specifically
requested comment on whether the
proposed definition of a water transfer
properly achieves the Agency’s
objective. Many commenters supported
the Agency’s proposed definition, either
generally or explicitly. On the other
hand, some commenters found the
proposed definition too narrow and
suggested that the Agency defer to state
law. Others found the definition overly
broad and suggested that it may
encompass too many activities. These
concerns, among others, are addressed
in the following discussions.
In response to the comment
suggesting that the proposed definition
of a water transfer is too narrow and
should also include transfers between
waterbodies defined as waters of the
State, even where they do not constitute
waters of the United States under the
CWA, EPA believes that making such a
change would not be appropriate
because the NPDES program only
applies to waters of the U.S. The same
commenter also suggested that EPA
defer to state law in defining a water
transfer. In response, the Agency finds
that a definition applicable nationwide
is important to provide consistency in
the application of this rule. However,
nothing in this rule precludes a State,
under State law, from regulating water
transfers that are not subject to section
402 of the Clean Water Act. States may
not exclude from NPDES permit
requirements sources that are point
sources under Federal law, including
those that do not meet the definition of
a water transfer in today’s rule. For
example, a point source that subjects
waters of the United States to an
intervening industrial, municipal or
commercial use could not be exempted
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from NPDES permitting requirements
under State law.
This rule expressly states that
‘‘discharges from a water transfer’’ are
not subject to NPDES permitting. The
Agency defines a water transfer as ‘‘an
activity that conveys or connects waters
of the United States without subjecting
the transferred water to intervening
industrial, municipal, or commercial
use.’’ A water transfer is an engineered
activity that diverts a water of the U.S.
to a second water of the U.S. Thus,
commenters who read the natural
convergence of two rivers as being a
water transfer are incorrect, though such
natural convergences also do not require
NPDES permits.
Some commenters sought clarification
of certain elements of the term ‘‘water
transfer’’ while others suggested
changes they believed would either
clarify or improve the scope of the term.
Commenters suggested that EPA change
the use of the term ‘‘activity’’ to either
‘‘occasion,’’ ‘‘instance,’’ or
‘‘occurrence,’’ such that the definition
would read: ‘‘water transfer means an
instance in which waters of the U.S. are
conveyed * * *.’’ The commenters’
concern is that the term ‘‘activities’’
narrows the rule to only human directed
or controlled events rather than any
instance in which water supplies are
moved. The Agency disagrees that the
change is necessary. By ‘‘activity,’’ the
Agency means any system of pumping
stations, canals, aqueducts, tunnels,
pipes, or other such conveyances
constructed to transport water from one
water of the U.S. to another water of the
U.S. Such a system may consist of a
single tunnel or pumping station or it
may require the use of multiple facilities
along the course of the transfer to reach
the second water of the U.S.
Intervening Industrial, Municipal, or
Commercial Use
A discharge of a pollutant associated
with a water transfer resulting from an
intervening commercial, municipal, or
industrial use, or otherwise introduced
to the water by a water transfer facility
itself would require an NPDES permit as
any discharge of a pollutant from a
point source into a water of the U.S.
would. The most frequent comment on
the proposed definition was that the
phrase ‘‘intervening industrial,
municipal, or commercial use’’ was
unclear or overbroad.8 EPA disagrees
8 EPA’s discussion of intervening uses is not
intended to address or exclude any other activity
that is currently subject to NPDES permitting. For
example, this rule does not affect EPA’s
longstanding position that, if water is withdrawn
from waters of the U.S. for an intervening
industrial, municipal or commercial use, the
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that this phrase is unclear or overbroad,
and provides clarification and examples
of intervening uses below.
For example, if the water is
withdrawn to be used as cooling water,
drinking water, irrigation, or any other
use such that it is no longer a water of
the U.S. before being returned to a water
of the U.S., the water has been subjected
to an intervening use.9 In contrast, a
water pumping station, pipe, canal, or
other structure used solely to facilitate
the transfer of the water is not an
intervening use.
The reintroduction of the intake water
and associated pollutants from an
intervening use through a point source
is an ‘‘addition’’ and has long been
subject to NPDES permitting
requirements. See, e.g., 40 CFR 122.2
(definition of process wastewater); 40
CFR 125.80 through 125.89 (regulation
of cooling towers); 40 CFR 122.45(g)
(regulations governing intake pollutants
for technology-based permitting); 40
CFR Part 132, Appendix F, Procedure 5–
D (containing regulations governing
water quality-based permitting for
intake pollutants in the Great Lakes).
Moreover, a discharge from a waste
treatment system, for example, to a
water of the United States, would not
constitute a water transfer and would
require an NPDES permit. See 40 CFR
122.2. In these situations, the
reintroduction of water and that water’s
associated pollutants physically
introduces pollutants from the outside
world and, therefore, is an ‘‘addition’’
subject to NPDES permitting
requirements. The fact that some of the
pollutants in the discharge from an
intervening use may have been present
in the source water does not remove the
need for a permit, although, under some
circumstances, permittees may receive
‘‘credit’’ in their effluent limitations for
such pollutants. See 40 CFR 122.45(g)
(regulations governing intake pollutants
for technology-based permitting); 40
CFR Part 132, Appendix F, Procedure 5–
reintroduction of the intake water and associated
pollutants is an ‘‘addition’’ subject to NPDES
permitting requirements. Nor does this rule change
EPA’s position, upheld by the Supreme Court in
Miccosukee, that the definition of ‘‘discharge of a
pollutant’’ in the CWA includes coverage of point
sources that do not themselves generate pollutants.
The Supreme Court stated, ‘‘A point source is, by
definition, a ‘discernible, confined, and discrete
conveyance’ section 1362(14) (emphasis added).
That definition makes plain that a point source
need not be the original source of the pollutant; it
need only convey the pollutant to ‘navigable
waters,’ which are, in turn, defined as ‘the waters
of the United States.’ Section 1362(7).’’ Miccosukee,
541 U.S. at 105.
9 Note that return flows from irrigated agriculture
are exempt from the requirement to obtain a NPDES
permit under both the Act itself and 40 CFR 122.3.
Today’s rule does not affect that exemption.
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D (containing regulations governing
water quality-based permitting for
intake pollutants in the Great Lakes).
Similarly, an NPDES permit is
normally required if a facility
withdraws water from a water of the
U.S., removes preexisting pollutants to
purify the water, and then discharges
the removed pollutants (perhaps in
concentrated form) back into the water
of the U.S. while retaining the purified
water for use in the facility. An example
of this situation is a drinking water
treatment facility which withdraws
water from streams, rivers, and lakes.
The withdrawn water typically contains
suspended solids, which are removed to
make the water potable. The removed
solids are a waste material from the
treatment process and, if discharged
into waters of the U.S., are subject to
NPDES permitting requirements, even
though that waste material originated in
the withdrawn water. See, e.g., In re City
of Phoenix, Arizona Squaw Peak & Deer
Valley Water Treatment Plants, 9 E.A.D.
515, 2000 WL 1664964 (EPA Envtl. App.
Bd. Nov. 1, 2000) (rejecting, on
procedural grounds, challenges to
NPDES permits for two drinking water
treatment plants that draw raw water
from the Arizona Canal, remove
suspended solids to purify the water,
and discharge the solids back into the
Canal); Final NPDES General Permits for
Water Treatment Facility Discharges in
the State of Massachusetts and New
Hampshire, 65 FR 69,000 (2000)
(NPDES permits for discharges of
process wastewaters from drinking
water treatment plants).
The Clean Water Act also clearly
imposes permitting requirements on
publicly owned treatment works, and
large and medium municipal separate
storm sewer systems. See CWA sections
402(a), 402(p)(1)–(4). Congress amended
the Clean Water Act in 1987 specifically
to add new section 402(p) to better
regulate stormwater discharges from
point sources. Water Quality Act of
1987, Public Law 100–4, 101 Stat. 7
(1987). Again, this interpretation
regarding water transfers does not affect
EPA’s longstanding regulation of such
discharges. These examples are
mentioned to illustrate what is meant by
‘‘intervening industrial, municipal, or
commercial use,’’ and are situations not
associated with water transfers.
Hydroelectric Operations
Some commenters, including State
agencies with hydroelectric resources,
utilities, and water districts expressed
concern that if hydroelectric operations
incidental to a water transfer were
considered an intervening use, the water
transfer would be disqualified from the
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exemption. Utilities often take
advantage of the change in elevation
over the course of a water transfer by
installing hydroelectric facilities. The
California State Water Resources
Control Board highlighted in their
comment that the Central Valley Project
includes eleven power plants and that
the State Water Project, the Los Angeles
Aqueduct, and the All American Canal
also contain hydroelectric power plants.
Today’s rule does not affect the
longstanding position of EPA and the
Courts that hydroelectric dams do not
generally require NPDES permits. See
Gorsuch, 693 F.2d 156; Consumers
Power 862 F.2d 580. EPA agrees that the
transfers described in California are
excluded from NPDES permitting
requirements unless, as discussed
below, the hydroelectric facility itself
introduces a pollutant such as grease
into the water passing though the dam.
When Water Transfers Introduce
Pollutants
Comments were also submitted
regarding pollutants that were added by
the water transfer. Commenters
expressed concern that water transfers
may have significant impacts on the
environment, including (1) the
introduction of invasive species, toxic
blue-green algae, chemical pollutants,
and excess nutrients; (2) increased
turbidity; and (3) alteration of habitat
(e.g., warm water into cold water or salt
water into fresh water). In response to
these comments, EPA notes that today’s
rule does not interfere with any of the
states’ rights or authorities to regulate
the movement of waters within their
borders. Rather, this rule merely
clarifies that NPDES permits are not
required for water transfers. States
currently have the ability to address
potential in-stream and/or downstream
effects of water transfers through their
WQS and TMDL programs. Nothing in
today’s rule affects the ability for states
to establish WQS appropriate to
individual waterbodies or waterbody
segments.
The final rule, consistent with the
proposed rule, would require NPDES
permits for ‘‘pollutants introduced by
the water transfer activity itself to the
water being transferred.’’ Water transfers
should be able to be operated and
maintained in a manner that ensures
they do not themselves add pollutants
to the water being transferred. However,
where water transfers introduce
pollutants to water passing through the
structure into the receiving water,
NPDES permits are required. Consumers
Power, 862 F.2d at 588; Gorsuch, 693
F.2d at 165, n. 22.
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In those instances where a water
transfer facility does itself introduce
pollutants into the water being
transferred, the scope of the required
NPDES permit would only be for those
added pollutants. Such a permit would
not require the water transfer facility to
address pollutants that may have been
in the donor waterbody and are being
transferred.10 Furthermore, EPA expects
these additions will probably be rare.
EPA considers the likelihood of such
additions to be similar to the frequency
of additions of leaks of oil from the
turbines at hydroelectric dams. In a
review of the NPDES permits issued to
dams, EPA was able to identify only a
minimal number of permits issued to
address this concern.
Pollutants Incidental to Water Transfers
Many utilities and water districts
commented that it was unclear whether
naturally occurring changes to the water
would require a permit. For example, as
water moves through dams or sits in
reservoirs along the transfer, chemical
and physical factors such as water
temperature, pH, BOD, and dissolved
oxygen may change. The Agency views
these changes the same way it views
changes to water quality caused by
water moving through dams (National
Wildlife Fed’n v. Gorsuch, 693 F.2d 156
(D.C. Cir. 1982)); they do not constitute
an ‘‘addition’’ of pollutant subject to the
permitting requirements of section 402
of the Act.
EPA would also like to make clear
that this rule does not change the
Agency’s position regarding the
application of pesticides directly to
waters of the United States. See 71 FR
68483; 40 CFR 122.3(h). Ditches and
canals are commonly treated with
pesticides to control pest species such
10 Because water transfers simply change the
flow, direction or circulation of navigable waters,
they would not themselves cause the waters being
moved to lose their status as waters of the United
States. See Consumers Power, 862 F.2d at 589.
Hence, pollutants moved from the donor water into
the receiving water, which are contained in
navigable waters throughout the transfer, would not
be ‘‘added’’ by the facility and would therefore not
be subject to NPDES permitting requirements. This
differs from a situation in which, for example, an
industrial facility takes in water for the purpose of
cooling some part of the facility itself. In such cases,
the water used for cooling loses its status as a water
of the United States when subjected to an
intervening industrial use and, therefore, is subject
to NPDES permit requirements for all the pollutants
it contains when it is discharged back into a
navigable water, generally including those that were
in the source water originally. See Consumers
Power, 862 F.2d at 589. Likewise, discharges from
a concentrated aquatic animal production facility,
such as excess food provided to animals in net pens
(e.g., food that was added to water but not eaten by
the fish) would require a NPDES permit because the
uneaten, waste food would be considered an
‘‘addition’’ of a pollutant from the facility.
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as algae to facilitate flow, and today’s
rule has no effect on the exclusion
provided to such activities from NPDES
permit requirements set forth in 40
CFR.122.3(h).
Designation Authority
In the preamble to the proposed water
transfers rule, EPA solicited public
comment on an option that would
provide an additional provision
allowing the NPDES authority to
designate particular water transfers as
subject to NPDES permit requirements
on a case-by-case basis. EPA received
nearly sixty comments from states,
municipalities, environmental groups,
water districts, industry and others
regarding EPA’s consideration of this
‘‘designation authority’’ approach.
Comments addressing EPA’s discussion
of such designation authority were
mixed regarding their opposition to, or
agreement with, this approach. The
following paragraphs provide additional
details regarding comments the Agency
received on this option.
Commenters who opposed the
designation option generally believed
that this provision would be legally
unsupportable and practically
unworkable. The most frequently cited
reason for opposing this approach was
a belief that the Clean Water Act
provides no authority to regulate water
transfers on a case-by-case basis. Other
commenters were concerned that
designating some water transfers, but
not others, as subject to NPDES permit
requirements would result in states
treating water transfers in an
inconsistent manner. Several
commenters stated that the existence of
an impairment is not an appropriate or
relevant test for determining whether or
not an activity should be subject to the
NPDES program. Some commenters also
stated that EPA already has regulations
in place with regard to use impairments,
at 40 CFR 131.10, which afford
flexibility in responding to unique
factual circumstances where uses may
be impacted by pollutants not subject to
NPDES permitting under section 402.
Other commenters supported
inclusion of the designation authority
provision in the final rule. Some of
these commenters thought this approach
would be helpful in instances where the
transfer involves interstate waters
because NPDES permits would provide
a tool to protect receiving water
quality—especially in situations in
which water quality standards differed
in the two relevant states. In addition,
several states indicated that being
allowed the option of designating water
transfers as requiring an NPDES permit
on a case-by-case basis was important to
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them and cited the following three
reasons for supporting this approach: (1)
The designation option is consistent
with Congress’s general direction
against unnecessary federal interference
with state allocation of water rights and
states’ flexibility on handling water
transfers; (2) states would be unable to
require NPDES permits for water
transfers on a case-by-case basis in the
absence of the designation option; and
(3) some water transfers should be
considered discharges of pollutants, so
it is important to retain NPDES
authority in these cases.
Some commenters suggested
additional programs and authorities that
states can use as an alternative to
NPDES permitting such as the 401 water
quality certification program or a
memorandum of understanding or
agreement.
After considering these comments,
EPA has decided not to include a
mechanism in 123.3 for the permitting
authority to designate water transfers on
a case-by-case basis as needing an
NPDES permit. This conclusion is
consistent with EPA’s interpretation of
the CWA as not subjecting water
transfers to the permitting requirements
of section 402. Moreover, as discussed
elsewhere in this preamble, states
currently have the ability to address
potential in-stream and/or downstream
effects of water transfers through their
WQS and TMDL programs and pursuant
to state authorities preserved by section
510, and today’s final rule does not have
an effect on these state programs and
authorities.
V. Statutory and Executive Order
Reviews
A. Executive Order 12866: Regulatory
Planning and Review
Under Executive Order (EO) 12866
(58 FR 51735, October 4, 1993), this
action is a ‘‘significant regulatory
action.’’ Accordingly, EPA submitted
this action to the Office of Management
and Budget (OMB) for review under EO
12866 and any changes made in
response to OMB recommendations
have been documented in the docket for
this action.
B. Paperwork Reduction Act
This action does not impose any new
information collection burden because
this final rule generally excludes water
transfers from requiring an NPDES
permit. The Office of Management and
Budget (OMB) has previously approved
the information collection requirements
contained in the existing regulations 40
CFR 122.21 and 123.25 under the
provisions of the Paperwork Reduction
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Act, 44 U.S.C. 3501 et seq. and has
assigned OMB control number 2040–
0086, EPA ICR number 0226.18.
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
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.
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 final rule on small entities,
small entity is defined as: (1) A small
business as defined by the Small
Business Administration’s (SBA)
regulations at 13 CFR 121.201; (2) a
small governmental jurisdiction that is a
government of a city, county, town,
school district or special district with a
population of less than 50,000; and (3)
a small organization that is any not-forprofit enterprise which is independently
owned and operated and is not
dominant in its field.
After considering the economic
impacts of today’s final rule on small
entities, I certify that this action will not
have a significant adverse economic
impact on a substantial number of small
entities. Because EPA is simply
codifying the Agency’s longtime
position that Congress did not generally
intend for the NPDES program to
regulate the transfer of one water of the
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United States into another water of the
United States, this action will not
impose any requirement on small
entities.
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
adopt the least costly, most costeffective, or least burdensome
alternative that achieves the objectives
of the rule. The provisions of section
205 do not apply when they are
inconsistent with applicable law.
Moreover, section 205 allows EPA to
adopt an alternative other than the least
costly, most cost-effective, or least
burdensome alternative if the
Administrator publishes with the final
rule an explanation why that alternative
was not adopted. Before EPA establishes
any regulatory requirements that may
significantly or uniquely affect small
governments, including tribal
governments, it must have developed
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 rule
does not contain a Federal mandate that
may result in expenditures of $100
million or more for State, local, and
tribal governments, in the aggregate, or
the private sector in any one year. EPA
is simply codifying the Agency’s
longtime position that Congress did not
generally intend for the NPDES program
to regulate the transfer of a water of the
United States into another water of the
United States. Thus, today’s rule is not
subject to the requirements of sections
202 and 205 of the UMRA. For the same
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reason, EPA has determined that this
rule contains no regulatory
requirements that might significantly or
uniquely affect small governments.
Thus, today’s rule 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
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.
This final rule does not have
Federalism implications. It will not
have substantial direct effects on the
States, on the relationship between the
national government and the States, or
on the distribution of power and
responsibilities among the various
levels of government, as specified in
Executive Order 13132. Today’s rule
does not change the relationship
between the government and the States
or change their roles and
responsibilities. Rather, this rule
confirms EPA’s longstanding practice
consistent with the Agency’s
understanding that Congress generally
intended for water transfers to be
subject to oversight by water resource
management agencies and State nonNPDES authorities, rather than the
permitting program under section 402 of
the CWA. 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
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33707
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 rule.
In the spirit of Executive Order 13132,
and consistent with EPA policy to
promote communications between EPA
and State and local governments, EPA
specifically solicited comment on the
proposed rule from State and local
officials. EPA received comments from
States that favored and opposed the
rule. States that favored the rule were
primarily drier, Western states. These
States argued that their State laws
provide adequate and appropriate
authority to address the impacts from
water transfers and that permitting
would negatively impact State water
rights allocations. This latter point was
also raised by water districts, which are
quasi-governmental entities, and by
local governments. States that were
opposed to the rule argued that they had
an interest in using their NPDES
authority to prevent potential water
quality impairments caused by water
transfers and disagreed with EPA’s
analysis of the Clean Water Act.
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 final rule does not have tribal
implications, as specified in Executive
Order 13175. It will neither impose
substantial direct compliance costs on
tribal governments, nor preempt Tribal
law. Today’s rule clarifies that Congress
did not generally intend for the NPDES
program to regulate the transfer of
waters of the United States into another
water of the United States. Nothing in
this rule prevents an Indian Tribe from
exercising its own authority to deal with
such matters. 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 solicited additional
comments on the proposed rule from
tribal officials. Comments from tribal
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governments were considered in the
development of this final rule. Since the
issues identified by tribal governments
were not unique to their concerns, EPA
has addressed these issues generally in
its response to comments.
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 regulation is not subject to
Executive Order 13045 because it is not
economically significant as defined
under E.O. 12866, and because the
Agency does not have reason to believe
that it addresses environmental health
and safety risks that present a
disproportionate risk to children.
Today’s rule would simply clarify
Congress’ intent that water transfers
generally be subject to oversight by
water resource management agencies
and State non-NPDES authorities, rather
than the permitting program under
section 402 of the CWA.
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H. Executive Order 13211: Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use
This rule is not a ‘‘significant energy
action’’ as defined in Executive Order
13211, ‘‘Actions Concerning Regulations
That Significantly Affect Energy Supply,
Distribution, or Use’’ (66 FR 28355 (May
22, 2001)) because it is not likely to
have a significant adverse effect on the
supply, distribution, or use of energy.
Further, EPA has concluded that this
rule is not likely to have any adverse
energy effects.
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
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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. This
rule does not involve technical
standards. Therefore, EPA did not
consider the use of any voluntary
consensus standards.
J. Executive Order 12898: Federal
Actions To Address Environmental
Justice in Minority Populations and
Low-Income Populations.
Executive Order (EO) 12898 (59 FR
7629 (Feb. 16, 1994)) establishes federal
executive policy on environmental
justice. Its main provision directs
federal agencies, to the greatest extent
practicable and permitted by law, to
make environmental justice part of their
mission by identifying and addressing,
as appropriate, disproportionately high
and adverse human health or
environmental effects of their programs,
policies, and activities on minority
populations and low-income
populations in the United States.
EPA has determined that this final
rule will not have disproportionately
high and adverse human health or
environmental effects on minority or
low-income populations. Today’s rule
would simply clarify Congress’ intent
that water transfers generally be subject
to oversight by water resource
management agencies and State nonNPDES authorities, rather than the
permitting program under section 402 of
the CWA.
K. Congressional Review Act
The Congressional Review Act, 5
U.S.C. section 801 et seq., as added by
the Small Business Regulatory
Enforcement Fairness Act of 1996,
generally provides that before a rule
may take effect, the agency
promulgating the rule must submit a
rule report, which includes a copy of
the rule, to each House of the Congress
and to the Comptroller General of the
United States. EPA will submit a report
containing this rule and other required
information to the U.S. Senate, the U.S.
House of Representatives, and the
Comptroller General of the United
States prior to publication of the rule in
the Federal Register. A major rule
cannot take effect until 60 days after it
is published in the Federal Register.
This action is not a ‘‘major rule’’ as
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defined by 5 U.S.C. 804(2). This rule
will be effective August 12, 2008.
List of Subjects in 40 CFR Part 122
Environmental protection,
Administrative practice and procedure,
Confidential business information,
Hazardous substances, Reporting and
recordkeeping requirements, Water
pollution control.
Dated: June 9, 2008.
Stephen L. Johnson,
Administrator.
For the reasons set forth in the
preamble, chapter I of title 40 of the
Code of Federal Regulations is amended
as follows:
I
PART 122—EPA ADMINISTERED
PERMIT PROGRAMS: THE NATIONAL
POLLUTANT DISCHARGE
ELIMINATION SYSTEM
1. The authority citation for part 122
continues to read as follows:
I
Authority: The Clean Water Act, 33 U.S.C.
1251 et seq.
2. Section 122.3 is amended by adding
paragraph (i) to read as follows:
I
§ 122.3
Exclusions.
*
*
*
*
*
(i) Discharges from a water transfer.
Water transfer means an activity that
conveys or connects waters of the
United States without subjecting the
transferred water to intervening
industrial, municipal, or commercial
use. This exclusion does not apply to
pollutants introduced by the water
transfer activity itself to the water being
transferred.
[FR Doc. E8–13360 Filed 6–12–08; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 180
[EPA–HQ–OPP–2007–0596; FRL–8367–7]
(Z)-7,8-epoxy-2-methyloctadecane
(Disparlure); Exemption from the
Requirement of a Tolerance
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
SUMMARY: This regulation establishes an
exemption from the requirement of a
tolerance for residues of the (Z)-7,8epoxy-2-methyloctadecane on all food
and feed crops when used to treat trees,
shrubs, and pastures resulting in
unintentional spray and drift from
application as well as unintentional
E:\FR\FM\13JNR1.SGM
13JNR1
Agencies
[Federal Register Volume 73, Number 115 (Friday, June 13, 2008)]
[Rules and Regulations]
[Pages 33697-33708]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E8-13360]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 122
[EPA-HQ-OW-2006-0141; FRL-8579-3]
RIN 2040-AE86
National Pollutant Discharge Elimination System (NPDES) Water
Transfers Rule
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: EPA is issuing a regulation to clarify that water transfers
are not subject to regulation under the National Pollutant Discharge
Elimination System (NPDES) permitting program. This rule defines water
transfers as an activity that conveys or connects waters of the United
States without subjecting the transferred water to intervening
industrial, municipal, or commercial use. This rule focuses exclusively
on water transfers and does not affect any other activity that may be
subject to NPDES permitting requirements.
This rule is consistent with EPA's June 7, 2006, proposed rule,
which was based on an August 5, 2005, interpretive memorandum entitled
``Agency Interpretation on Applicability of Section 402 of the Clean
Water Act to Water Transfers.''
DATES: This final rule is effective on August 12, 2008. For judicial
review purposes, this action is considered issued as of 1 p.m. eastern
daylight time (e.d.t.) on June 27, 2008, as provided in 40 CFR 23.2.
Under section 509(b)(1) of the Clean Water Act, judicial review of the
Administrator's action can only be had by filing a petition for review
in the United States Court of Appeals within 120 days after the
decision is considered issued for purposes of judicial review.
ADDRESSES: The administrative record is available for inspection and
copying at the Water Docket, located at the EPA Docket Center (EPA/DC),
EPA West 1301 Constitution Ave., Room 3334, NW., Washington DC 20460.
The administrative record is also available via EPA Dockets (Edocket)
at https://www.regulations.gov under docket number EPA-HQ-OW-2006-0141.
The rule and key supporting documents are also electronically available
on the Internet at https://www.epa.gov/npdes/agriculture.
FOR FURTHER INFORMATION CONTACT: For additional information contact
Virginia Garelick, Water Permits Division, Office of Wastewater
Management (4203M), Environmental Protection Agency, 1200 Pennsylvania
Ave., NW., Washington, DC 20460; telephone number: 202-564-2316; fax:
202-564-6384; e-mail address: garelick.virginia@epa.gov.
SUPPLEMENTARY INFORMATION:
I. General Information
A. Does This Action Apply to Me?
B. How Can I Get Copies of This Document and Other Related
Information?
C. Under What Legal Authority Is This Final Rule Issued?
D. What is the Comment Response Document?
II. Background and Definition of Water Transfers
III. Rationale for the Final Rule
A. Legal Framework
B. Statutory Language and Structure
C. Legislative History
IV. Public Comment
V. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory Planning and Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation and Coordination With
Indian Tribal Governments
G. Executive Order 13045: Protection of Children From
Environmental Health and Safety Risks
H. Executive Order 13211: Actions Concerning Regulations That
Significantly Affect Energy Supply, Distribution, or Use
I. National Technology Transfer and Advancement Act
J. Executive Order 12898: Actions To Address Environmental
Justice in Minority Populations and Low-Income Populations
K. Congressional Review Act
I. General Information
A. Does This Action Apply to Me?
This action applies to those involved in the transfer of waters of
the United States. The following table provides a list of standard
industrial codes for operations potentially covered under this rule.
Table 1.--Entities Potentially Regulated by This Rule
------------------------------------------------------------------------
Examples of
Category NAICS potentially affected
entities
------------------------------------------------------------------------
Resource management parties 924110 Government
(includes state departments Administration establishments
of fish and wildlife, state of Air and Water primarily engaged in
departments of pesticide Resource and the administration,
regulation, state Solid Waste regulation, and
environmental agencies, and Management enforcement of water
universities). Programs. resource programs;
the administration
and regulation of
water pollution
control and
prevention programs;
the administration
and regulation of
flood control
programs; the
administration and
regulation of
drainage development
and water resource
consumption
programs; and
coordination of
these activities at
intergovernmental
levels.
[[Page 33698]]
924120 Government
Administration establishments
of Conservation primarily engaged in
Programs. the administration,
regulation,
supervision and
control of land use,
including
recreational areas;
conservation and
preservation of
natural resources;
erosion control;
geological survey
program
administration;
weather forecasting
program
administration; and
the administration
and protection of
publicly and
privately owned
forest lands.
Government
establishments
responsible for
planning,
management,
regulation and
conservation of
game, fish, and
wildlife
populations,
including wildlife
management areas and
field stations; and
other administrative
matters relating to
the protection of
fish, game, and
wildlife are
included in this
industry.
237110 Water and This category
Sewer Line and includes entities
Related primarily engaged in
Structures the construction of
Construction. water and sewer
237990 Other lines, mains,
Heavy and Civil pumping stations,
Engineering treatment plants and
Construction. storage tanks.
This category
includes dam
Construction and
management, flood
control structure
construction,
drainage canal and
ditch construction,
flood control
project
construction, and
spillway,
floodwater,
construction.
Public Water Supply........... 221310 Water This category
Supply. includes entities
engaged in operating
water treatment
plants and/or
operating water
supply systems. The
water supply system
may include pumping
stations, aqueducts,
and/or distribution
mains. The water may
be used for
drinking,
irrigation, or other
uses.
------------------------------------------------------------------------
This table is not intended to be exhaustive, but rather provides a
guide for readers regarding entities likely to be affected by this
action. This table lists the types of entities that EPA is now aware
could potentially be affected by this action. Other types of entities
not listed in the table could also be affected. To determine whether
your facility is affected by this action, you should carefully examine
the applicability criteria in 40 CFR 122.3. 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. How Can I Get Copies of This Document and Other Related Information?
1. Docket. EPA has established an official public docket for this
action under Docket ID No. EPA-HQ-OW-2006-0041. The official public
docket consists of the documents specifically referenced in this
action, any public comments received, and other information related to
this action. Although listed in the index, some information, such as
copyrighted material, will be publicly available only in hard copy.
Publicly available docket materials are available either electronically
in https://www.regulations.gov or in hard copy at the Water Docket in
the EPA Docket Center, EPA West, 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.
2. Electronic Access. You may access this Federal Register document
electronically through the EPA Web site under the Federal Register
listings at https://www.regulations.gov.
C. Under What Legal Authority Is This Final Rule Issued?
This final rule is issued under the authority of sections 402 and
501 of the Clean Water Act., 33 U.S.C. 1342 and 1361.
D. What Is the Comment Response Document?
EPA received a large number of comments on the proposed rule,
including thousands of form letters. EPA evaluated all of the comments
submitted and prepared a Comment Response Document containing both the
comments received and the Agency's responses to those comments. The
Comment Response Document complements and supplements this preamble by
providing more detailed explanations of EPA's final action. The Comment
Response Document is available at the Water Docket.
II. Background and Definition of Water Transfers
Water transfers occur routinely and in many different contexts
across the United States. Typically, water transfers route water
through tunnels, channels, and/or natural stream water features, and
either pump or passively direct it for uses such as providing public
water supply, irrigation, power generation, flood control, and
environmental restoration. Water transfers can be relatively simple,
moving a small quantity of water a short distance, or very complex,
transporting substantial quantities of water over long distances,
across both State and basin boundaries. Water transfers may be of
varying complexities and sizes; there may be multiple reservoirs,
canals, or pumps over the course of the transfer, or the route may be a
more direct connection between the donor and the receiving waterbody.
There are thousands of water transfers currently in place in the United
States, including sixteen major diversion projects in the western
States alone. Examples include the Colorado-Big Thompson Project in
Colorado and the Central Valley Project in California.
Water transfers are administered by various federal, State, and
local agencies and other entities. The Bureau of Reclamation
administers significant transfers in western States to provide
approximately 140,000 farmers with irrigation water. With the use of
water transfers, the Army Corps of Engineers keeps thousands of acres
of agricultural and urban land in southern Florida from flooding in
former areas of Everglades wetlands. Many large cities in the west and
the east would not have adequate sources of water for their citizens
were it not for the continuous redirection of water from outside
basins. For example, both the cities of New York and Los Angeles depend
on water transfers from distant watersheds to meet their
[[Page 33699]]
municipal demand. In short, numerous States, localities, and residents
are dependent upon water transfers, and these transfers are an integral
component of U.S. infrastructure.
The question of whether or not an NPDES permit is required for
water transfers arises because activities that result in the movement
of waters of the U.S., such as trans-basin transfers of water to serve
municipal, agricultural, and commercial needs, typically move
pollutants from one waterbody (donor water) to another (receiving
water). Although there have been a few isolated instances where
entities responsible for water transfers have been issued NPDES
permits, Pennsylvania is the only NPDES permitting authority that
regularly issues NPDES permits for water transfers. Pennsylvania began
issuing permits for water transfers in 1986, in response to a State
court decision mandating the issuance of such permits. See DELAWARE
Unlimited v. DER, 508 A.2d 348 (Pa. Cmwlth, 1986). In addition, some
Courts of Appeals have required NPDES permits for specific water
transfers associated with the expansion of a ski resort and the supply
of drinking water. See, e.g., Dubois v. U.S. Dep't of Agriculture, 102
F.3d 1273 (1st Cir. 1996); Catskill Mountains Chapter of Trout
Unlimited, Inc. v. City of New York, 273 F.3d 481 (2nd Cir 2001),
aff'd, Catskill Mountains Chapter of Trout Unlimited, Inc. v. City of
New York, 451 F.3d 77 (2nd Cir 2006). Otherwise, however, water
transfers have not been regulated under section 402 of the Clean Water
Act (CWA or the Act).
The Supreme Court recently addressed the issue of whether an NPDES
permit is necessary for the mere transfer of water in South Fla. Water
Mgmt. Dist. v. Miccosukee Tribe of Indians, 541 U.S. 95 (2004). The
Supreme Court in Miccosukee vacated a decision by the 11th Circuit,
which had held that a Clean Water Act permit was required for
transferring water from one navigable water into another, a Water
Conservation Area in the Florida Everglades. The Court remanded the
case for further fact-finding as to whether the two waters in question
were ``meaningfully distinct.'' \1\ If they were not, an NPDES permit
would not be required. The Court declined to resolve the question of
whether water transfers require NPDES permits when the waterbodies at
issue are meaningfully distinct. The Court noted that some legal
arguments made by the parties regarding this question had not been
raised in the lower court proceedings and noted that these arguments
would be open to the parties on remand. Id. at 109.
---------------------------------------------------------------------------
\1\ At the time of this rulemaking, the District Court has
stayed its proceedings until resolution of a similar case in the
same District Court, Friends of the Everglades v. South Florida
Water Management District.
---------------------------------------------------------------------------
On August 5, 2005, EPA issued a legal memorandum entitled ``Agency
Interpretation on Applicability of section 402 of the Clean Water Act
to Water Transfers'' (``interpretive memorandum''). The principal legal
question addressed in the interpretive memorandum was whether the
movement of pollutants from one water of the U.S. to another by a water
transfer is the ``addition'' of a pollutant potentially subjecting the
activity to the permitting requirement under section 402 of the Act.
Based on the statute as a whole and consistent with the Agency's
longstanding practice, the interpretive memorandum concluded that
Congress generally expected water transfers would be subject to
oversight by water resource management agencies and State non-NPDES
authorities, rather than the permitting program under section 402 of
the CWA.
On June 7, 2006, EPA proposed regulations based on the analysis
contained in the interpretive memorandum to expressly state that water
transfers are not subject to regulation under section 402 of the CWA.
The Agency proposed to define water transfers as ``an activity that
conveys waters of the United States to another water of the United
States without subjecting the water to intervening industrial,
municipal, or commercial use.'' The Act reserves the ability of States
to regulate water transfers under State law and this proposed
rulemaking was not intended to interfere with this State prerogative.
See CWA section 510.
EPA is issuing a final regulation that is nearly identical to the
proposed rule. (Minor changes have been made for clarity.) Through
today's rule, the Agency concludes that water transfers, as defined by
the rule, do not require NPDES permits because they do not result in
the ``addition'' of a pollutant. Consistent with the proposed rule, EPA
defines water transfers in the following manner: ``Water transfer means
an activity that conveys or connects waters of the United States
without subjecting the transferred water to intervening industrial,
municipal, or commercial use.'' In order to constitute a ``water
transfer'' under this rule, and, therefore, be exempt from the
requirement to obtain an NPDES permit, the water being conveyed must be
a water of the U.S.\2\ prior to being discharged to the receiving
waterbody. If the water that is being conveyed is not a water of the
U.S. prior to being discharged to the receiving body, then that
activity does not constitute a water transfer under today's rule.
Additionally, the water must be conveyed from one water of the U.S. to
another water of the U.S. Conveyances that remain within the same water
of the U.S., therefore, do not constitute water transfers under this
rule, although movements of water within a single water body are also
not subject to NPDES permitting requirements. As the rule makes clear,
in order to be a water transfer under the rule, the water must be
conveyed without being subjected to an intervening industrial,
municipal, or commercial use.
---------------------------------------------------------------------------
\2\ Waters of the U.S. are defined for purposes of the NPDES
program in 40 CFR 122.2 and this rulemaking does not seek to address
what is within the scope of that term.
---------------------------------------------------------------------------
Consider water that is being moved from Reservoir A to Reservoir B
in a different watershed. In order to get from Reservoir A to Reservoir
B, the water must first be released through a dam. The water then
travels down River A, which is considered a water of the U.S. Next, the
water is conveyed from River A to River B through a tunnel. Finally,
the water travels down River B, also a water of the U.S., and flows
into Reservoir B. There are several points in this example where water
is conveyed from one body to another, but not all of those points would
themselves constitute a ``water transfer'' because they are not the
conveyance of ``waters of the United States to another water of the
United States.'' The first example is the release from Reservoir A to
River A. This does not constitute a water transfer under EPA's
definition because the water on both sides of the dam is part of the
same water of the U.S.\3\ The next movement is the release from River A
into River B, through a tunnel. This release constitutes a water
transfer under the scope of this rule because it conveys water from one
water of the U.S. to another water of the U.S. without subjecting the
water to an intervening industrial, municipal or
[[Page 33700]]
commercial use. Therefore, unless this conveyance itself introduces
pollutants into the water being conveyed, the release will not require
an NPDES permit under today's rule. River B's subsequent flow into
Reservoir B, which is formed by a dam on Reservoir B, does not
constitute a water transfer because it is merely movement within the
same water of the U.S., and, as discussed above, would not require an
NPDES permit for such movement.
---------------------------------------------------------------------------
\3\ It should be noted, however, that this release would still
not require an NPDES permit because EPA and the Federal courts have
determined that a discharge from a dam does not result in an
``addition'' of a pollutant unless the dam itself discharges a
pollutant such as grease into the water passing through the dam. See
National Wildlife Fed'n v. Gorsuch, 693 F.2d 156 (D.C. Cir. 1982);
National Wildlife Fed'n v. Consumers Power Company, 862 F.2d 580
(6th Cir. 1988). Cf. S.D. Warren Co. v. Maine Board of Environmental
Protection, 126 S.Ct. 1843 (2006) (Certification under CWA section
401 may be needed in some instances).
---------------------------------------------------------------------------
The remainder of the preamble to this final rule is organized as
follows. Section III discusses the rationale for the final rule based
on the language, structure, and legislative history of the Clean Water
Act. Section IV summarizes and responds to the major comments received
in response to the scope of the proposed rule. Section V reviews
statutory provisions and various executive orders.
III. Rationale for the Final Rule
On June 7, 2006, EPA published a proposed rule that would exclude
from NPDES permit requirements discharges from water transfers that do
not subject the water to an intervening industrial, municipal, or
commercial use, so long as pollutants are not introduced by the water
transfer activity itself. This proposal, like EPA's August 5, 2005,
interpretive memorandum, explained that no one provision of the Act
expressly addresses whether water transfers are subject to the NPDES
program but described the indicia of Congressional intent that water
transfers not be so regulated. Therefore, today's rule appropriately
defers to congressional concerns that the statute not unnecessarily
burden water quantity management activities and excludes water
transfers from the NPDES program. This section will review the legal
framework for evaluating EPA's interpretation of the CWA, explain the
Agency's interpretation of the CWA, including a brief survey of prior
litigation over the relevant statutory terms, and outline the relevant
legislative history.
A. Legal Framework
Under what is traditionally viewed as Chevron analysis, a court
examining the legality of an agency's interpretation of a statute is to
first ask whether the statute speaks clearly to the precise question at
issue and must give effect to the unambiguously expressed intent of
Congress if such unambiguous intent can be discerned. Chevron U.S.A.
Inc. v. NRDC, 467 U.S. 837, 842-843 (Chevron); National Ass. of
Homebuilders, et al. v. Defenders of Wildlife, et al., 127 S.Ct. 2518,
2534 (2007) (NAHB). To the extent that a statute does not speak clearly
to the specific issue, the Agency interpretation must be upheld if it
is based on a permissible construction of the statute. Chevron, 467
U.S. at 843; NAHB, 127 S.Ct. at 2534. Courts are required to accept an
agency's reasonable interpretation of a statute, even if this
interpretation differs from what the court believes is the ``best''
statutory interpretation. National Cable and Telecommunications Ass'n,
et. al. v. Brand X, et al., 545 U.S. 967, 980 (2005) (Brand X).
Deference to an agency interpretation of a statute under Chevron is
appropriate where Congress has authorized an agency to make rules
carrying the force of law, and such authorization is apparent where the
agency is empowered to make rules or adjudicate issues or there are
other indications of comparable congressional intent. United States v.
Mead Corp., 533 U.S. 218 (2001). Congress has expressly authorized EPA
to prescribe regulations as are necessary to administer the CWA, and
today's rule has been promulgated to address the question whether water
transfers require NPDES permits. CWA section 501(a); 33 U.S.C. 1361(a);
71 FR 32887 (June 7, 2006).
As discussed below, EPA has reviewed the language, structure and
legislative history of the CWA and concludes that today's rule, which
clarifies that NPDES permits are not required for transfers of waters
of the United States from one water body to another, is a permissible
construction of the statute. Taken as a whole, the statutory language
and scheme support the conclusion that permits are not required for
water transfers.
B. Statutory Language and Structure
The Clean Water Act prohibits the discharge of a pollutant by any
person except in compliance with specified statutory sections,
including section 402. CWA section 301(a). The term ``discharge of a
pollutant'' is defined as ``any addition of any pollutant to navigable
waters from any point source.'' CWA section 502(12). The legal question
addressed by today's rule is whether a water transfer as defined in the
new regulation constitutes an ``addition'' within the meaning of
section 502(12).
The term ``addition'' has been interpreted by courts in a variety
of contexts that are relevant here. Several courts of appeals have
determined that water flowing through dams and hydroelectric facilities
does not constitute an addition of a pollutant under the CWA.
Specifically, the Court of Appeals for the D.C. Circuit agreed with EPA
that the term ``addition'' may reasonably be limited to situations in
which ``the point source itself physically introduces a pollutant into
a water from the outside world.'' National Wildlife Fed'n v. Gorsuch,
693 F.2d 156, 175 (D.C. Cir. 1982) (Gorsuch) (accepting EPA's view that
the requirement for an NPDES permit ``is established when the pollutant
first enters the navigable water, and does not change when the polluted
water later passes through the dam from one body of navigable water
(the reservoir) to another (the downstream river).'') The Court of
Appeals for the Sixth Circuit reached the same conclusion with regard
to a hydropower facilities operating on Lake Michigan. National
Wildlife Fed'n v. Consumers Power Co. 862 F.2d 580, 584 (6th Cir. 1988)
(Consumers Power) (agreeing with the Gorsuch Court's conclusion that
EPA's construction of ``addition'' is a permissible one). Both the
Gorsuch and Consumers Power courts accorded deference to EPA's
interpretation of the CWA, and specifically to its interpretation of
the term ``addition.'' Gorsuch, 693 F.2d at 166-167; Consumers Power,
862 F.2d at 584.
Three other Courts of Appeals, however, have concluded that where a
water transfer involves distinct waters of the United States, the
transfer constitutes an ``addition'' of pollutants. Dubois v. U.S.
Dept. of Agriculture, et al., 102 F.3d 1273, 1298-1300 (1st Cir. 1996);
Catskill Mountains Chapter of Trout Unlimited, Inc. v. City of New
York, 273 F.3d 481, 491-93 (2nd Cir. 2001) (Catskill I); Miccosukee
Tribe of Indians v. South Florida Water Management District, 280 F.3d
1364 (11th Cir. 2002), vacated by Miccosukee, 541 U.S. at 112.\4\ These
three Courts of Appeals construed the term ``addition''
[[Page 33701]]
so as to include transfers of water from one body to another distinct
body (Catskill I, 273 F.3d at 491 (``EPA's position * * * is that for
there to be an `addition,' a `point source must introduce the pollutant
into navigable water from the outside world.' We agree with this view
provided that `outside world' is construed as any place outside the
particular water body to which pollutants are introduced.'') (internal
citations omitted, emphasis added); Catskill II, 451 F.3d at 82-85) or
transfers that cause water to move in a direction it would not
ordinarily flow (DuBois, 102 F.3d at 1297; Catskill I, 273 at 493-94
(explaining DuBois); Miccosukee, 280 F.3d at 1368-69).
---------------------------------------------------------------------------
\4\ EPA recognizes that the approach adopted by these three
courts is at odds with today's rule. None of these three courts,
however, viewed the question of statutory interpretation through the
lens of Chevron deference. DuBois, 102 F.3d at 1285, n. 15 (Chevron
does not apply because the court ``was not reviewing an agency's
interpretation of the statute that it was directed to enforce.'');
Catskill Mountains Chapter of Trout Unlimited, Inc. v. City of New
York, 451 F.3d 77, 82 (2nd Cir. 2006) (Catskill II) (``The City
concedes that this EPA interpretation is not entitled to Chevron
deference.''); Catskill I, 273 F.3d at 490 (Declining to apply
Chevron deference, but acknowledging that ``[i]f the EPA's position
had been adopted in a rulemaking or other formal proceeding,
deference of the sort applied by the Gorsuch and Consumers Power
courts might be appropriate.''); Miccosukee, 280 F.3d at 1367, n. 4
(``The EPA is no party to this case; we can ascertain no EPA
position applicable to [the water transfer at issue) to which to
give any deference, much less Chevron deference.''). Moreover, the
approaches adopted by the Gorsuch and Consumers Power courts is
compatible with today's rule.
---------------------------------------------------------------------------
In pending litigation, on the other hand, the United States has
taken the position that the Clean Water Act generally does not subject
water transfers to the NPDES program:
The statute defines ```discharge of a pollutant''' as ``any
addition of any pollutant to navigable waters from any point
source.'' 33 U.S.C. 1362(12). When the statutory definition of
```navigable waters'''--i.e., ``the waters of the United States,''
33 U.S.C. 1362(7)--is inserted in place of ``navigable waters,'' the
statute provides that NPDES applies only to the ``addition of any
pollutant to the waters of the United States.'' Given the broad
definition of ``pollutant,'' transferred (and receiving) water will
always contain intrinsic pollutants, but the pollutants in
transferred water are already in ``the waters of the United States''
before, during, and after the water transfer. Thus, there is no
``addition''; nothing is being added ``to'' ``the waters of the
United States'' by virtue of the water transfer, because the
pollutant at issue is already part of ``the waters of the United
States'' to begin with. Stated differently, when a pollutant is
conveyed along with, and already subsumed entirely within, navigable
waters and the water is not diverted for an intervening use, the
water never loses its status as ``waters of the United States,'' and
thus nothing is added to those waters from the outside world.
Brief for the United States in Friends of the Everglades v. South
Florida Water Management Dist., No. 07-13829-H (11th Cir.).
The Agency has concluded that, taken as a whole, the statutory
language and structure of the Clean Water Act indicate that Congress
generally did not intend to subject water transfers to the NPDES
program. Interpreting the term ``addition'' in that context, EPA
concludes that water transfers, as defined by today's rule, do not
constitute an ``addition'' to navigable waters to be regulated under
the NPDES program. Instead, Congress intended to leave primary
oversight of water transfers to state authorities in cooperation with
Federal authorities.
In interpreting the term ``addition'' in section 502(12) of the
statute, EPA is guided by several principles. ``Addition'' is a general
term, undefined by the statute. Partly for this reason, the courts have
accorded substantial discretion to EPA in interpreting the term in the
context of the ``dams'' cases. Gorsuch, 693 F.2d at 175 (finding the
statute capable of supporting multiple interpretations, the legislative
history unhelpful, and concluding that Congress would have given EPA
discretion to define ``addition'' had it expected the meaning of the
term to be disputed); Consumers Power, 862 F.2d at 584-85 (agreeing
with the analysis in Gorsuch). Moreover, several alternative ways of
interpreting the term ``addition'' have been proposed in the context of
water transfers. As noted above, EPA's longstanding position is that an
NPDES pollutant is ``added'' when it is introduced into a water from
the ``outside world'' by a point source. Gorsuch, 693 F.2d at 174-175.
Under one interpretation, advanced by the 2nd Circuit in Catskill
Mountain, ``the outside world'' means anywhere outside the particular
waterbody receiving the pollutant, and so a permit in that case was
required for movement of pollutants between distinct waterbodies.
Catskill I, 273 F.3d at 491. EPA does not agree with this understanding
of the term ``outside world'' as evinced by its long-standing practice
of generally not requiring NPDES permits for transfers between water
bodies, which it has defended against court challenges asserting that
such transfers do require such permits. Rather, EPA believes that an
addition of a pollutant under the Act occurs when pollutants are
introduced from outside the waters being transferred.
As noted above, various courts have reached different conclusions
in determining when movement of waters of the United States containing
pollutants constitutes an ``addition'' of a pollutant. To resolve the
confusion created by these conflicting approaches, the Agency has
looked to the statute as a whole for textual and structural indices of
Congressional intent on the question whether water transfers that do
not themselves introduce new pollutants require an NPDES permit.
Statutory construction principles instruct that the Clean Water Act
should be interpreted by analyzing the statute as a whole. United
States v. Boisdore's Heirs, 49 U.S. 113, 122 (1850). The Supreme Court
has long explained ``in expounding a statute, we must not be guided by
a single sentence or member of a sentence, but look to the provisions
of the whole law, and its object and policy.'' Id. See also, Gustafond
v. Alloyd Co., Inc., 513 U.S. 561, 570 (1995), Smith v. United States,
508 U.S. 223, 233 (1993), United States Nat'l Bank of Or. v.
Independent Ins. Agents of Am., Inc., 508 U.S. 439, 455 (1993). In
general, the ``whole statute'' interpretation analysis means that ``a
statute is passed as a whole and not in parts or sections and is
animated by one general purpose and intent. Consequently, each part or
section should be construed in connection with every other part or
section so as to produce a harmonious whole.'' Norman J. Singer,
Statutes and Statutory Construction vol. 2A Sec. 46:05, 154 (6th ed.,
West Group 2000). As the Second Circuit has explained with regard to
the CWA:
Although the canons of statutory interpretation provide a court
with numerous avenues for supplementing and narrowing the possible
meaning of ambiguous text, most helpful to our interpretation of the
CWA in this case are two rules. First, when determining which
reasonable meaning should prevail, the text should be placed in the
context of the entire statutory structure [quoting United States v.
Dauray, 215 F.3d 257, 262 (2d Cir. 2000)]. Second, ``absurd results
are to be avoided and internal inconsistencies in the statute must
be dealt with.'' United States v. Turkette, 452 U.S. 576, 580
(1981).
Natural Res. Def. Council v. Muszynski, 268 F.3d 91, 98 (2d Cir. 2001).
See also, Singer, vol. 3B Sec. 77:4, at 256-258.
A holistic approach to the text of the CWA is needed here in
particular because the heart of this matter is the balance Congress
created between federal and State oversight of activities affecting the
nation's waters. The purpose of the CWA is to protect water quality.
Congress nonetheless recognized that programs already existed at the
State and local levels for managing water quantity, and it recognized
the delicate relationship between the CWA and State and local programs.
Looking at the statute as a whole is necessary to ensure that the
analysis herein is consonant with Congress's overall policies and
objectives in the management and regulation of the nation's water
resources.
While the statute does not define ``addition,'' sections 101(g),
102(b), 304(f), and 510(2) provide a strong indication that the term
``addition'' should be interpreted in accordance with the text of the
more specific sections of the statute. In light of Congress' clearly
expressed policy not to unnecessarily interfere with water resource
allocation and its discussion of changes in the movement, flow or
[[Page 33702]]
circulation of any navigable waters as sources of pollutants that would
not be subject to regulation under section 402, it is reasonable to
interpret ``addition'' as not including the mere transfer of navigable
waters.
The specific statutory provisions addressing the management of
water resources--coupled with the overall statutory structure--provide
textual support for the conclusion that Congress generally did not
intend for water transfers to be regulated under section 402. The Act
establishes a variety of programs and regulatory initiatives in
addition to the NPDES permitting program. It also recognizes that the
States have primary responsibilities with respect to the ``development
and use (including restoration, preservation, and enhancement) of land
and water resources.'' CWA section 101(b).
Congress also made clear that the Clean Water Act is to be
construed in a manner that does not unduly interfere with the ability
of States to allocate water within their boundaries, stating:
It is the policy of Congress that the authority of each State to
allocate quantities of water within its jurisdiction shall not be
superseded, abrogated or otherwise impaired by [the Act]. It is the
further policy of Congress that nothing in this chapter shall be
construed to supersede or abrogate rights to quantities of water
which have been established by any State. Federal agencies shall co-
operate with State and local agencies to develop comprehensive
solutions to prevent, reduce and eliminate pollution in concert with
programs for managing water sources.
CWA section 101(g). While section 101(g) does not prohibit EPA from
taking actions under the CWA that it determines are needed to protect
water quality,\5\ it nonetheless establishes in the text of the Act
Congress's general direction against unnecessary Federal interference
with State allocations of water rights.
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\5\ PUD No. 1 of Jefferson County. v. Wash. State Dep't. of
Ecology, 511 U.S. 700, 720 (1994) (``Sections 101(g) and 510(2)
preserve the authority of each State to allocate water quantity as
between users; they do not limit the scope of water pollution
controls that may be imposed on users who have obtained, pursuant to
state law, a water allocation.'').
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Water transfers are an essential component of the nation's
infrastructure for delivering water that users are entitled to receive
under State law. Because subjecting water transfers to a federal
permitting scheme could unnecessarily interfere with State decisions on
allocations of water rights, this section provides additional support
for the Agency's interpretation that, absent a clear Congressional
intent to the contrary, it is reasonable to read the statute as not
requiring NPDES permits for water transfers. See United States v. Bass,
404 U.S. 336, 349 (1971) (``unless Congress conveys its purpose
clearly, it will not be deemed to have significantly changed the
federal-state balance.'')
An additional statutory provision, section 510(2), similarly
provides:
Except as expressly provided in this Act, nothing in this Act
shall * * * be construed as impairing or in any manner affecting any
right or jurisdiction of the States with respect to the waters
(including boundary waters) of such States.
Like section 101(g), this provision supports the notion that Congress
did not intend administration of the CWA to unduly interfere with water
resource allocation.
Finally, one section of the Act--304(f)--expressly addresses water
management activities. Mere mention of an activity in section 304(f)
does not mean it is exclusively nonpoint source in nature. See
Miccosukee 541 U.S. at 106 (noting that section 304(f)(2)(F) does not
explicitly exempt nonpoint sources if they also fall within the
definition of point source). Nonetheless, section 304(f) is focused
primarily on addressing pollution sources outside the scope of the
NPDES program. See H.R. Rep. No. 92-911, at 109 (1972), reprinted in
Legislative History of the Water Pollution Control Act Amendments of
1972, Vol. 1 at 796 (Comm. Print 1973) (``[t]his section * * * on * * *
nonpoint sources is among the most important in the 1972 Amendments'')
(emphasis added)). This section directed EPA to issue guidelines for
identifying and evaluating the nature and extent of nonpoint sources of
pollution,\6\ as well as processes, procedures and methods to control
pollution from, among other things, ``changes in the movement, flow or
circulation of any navigable waters or ground waters, including changes
caused by the construction of dams, levees, channels, causeways, or
flow diversion facilities.'' CWA 304(f)(2)(F) (emphasis added).
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\6\ Sources not regulated under sections 402 or 404 are
generically referred to as ``nonpoint sources.'' See Consumers
Power, 862 F.2d at 582 (```nonpoint source' is shorthand for and
`includes all water quality problems not subject to section 402''')
(quoting Gorsuch, 693 F.2d at,166) (internal quotation marks
omitted).
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While section 304(f) does not exclusively address nonpoint sources
of pollution, it nonetheless ``concerns nonpoint sources'' (Miccosukee,
541 U.S. at 106) and reflects an understanding by Congress that water
movement could result in pollution, and that such pollution would be
managed by States under their nonpoint source program authorities,
rather than the NPDES program. Today's rule accords with the direction
to EPA and other federal agencies in section 101(g) to work with State
and local agencies to develop ``comprehensive solutions'' to water
pollution problems ``in concert with programs for managing water
resources.''
The text of these sections of the Act together demonstrate that
Congress was aware that there might be pollution associated with water
management activities, but chose to defer to comprehensive solutions
developed by State and local agencies for controlling such pollution.
Because the NPDES program focuses on discharges from point sources of
pollutants, it is not the kind of comprehensive program that Congress
believed was best suited to addressing pollution, which is the term
used for the nonpoint source program. It is this type of non-point
source pollution that may be associated with water transfers.
In several important ways, water transfers are unlike the types of
discharges that were the primary focus of Congressional attention in
1972. Discharges of pollutants covered by section 402 are subject to
``effluent'' limitations. Water transfers, however, are not like
effluent from an industrial, commercial or municipal operation. Rather
than discharge effluent, water transfers convey one water of the U.S.
into another. Additionally, the operators of water control facilities
are generally not responsible for the presence of pollutants in the
waters they transport. Rather, those pollutants often enter ``the
waters of the United States'' through point and nonpoint sources
unassociated with those facilities and beyond control of the project
operators. Congress generally intended that pollutants be controlled at
the source whenever possible. See S. Rep. No. 92-414, p. 77 (1972)
(justifying the broad definition of navigable waters because it is
``essential that discharge of pollutants be controlled at the
source'').\7\ The pollution from transferred waters is more sensibly
addressed through water resource planning and land use regulations,
which attack the problem at its source. See, e.g., CWA section 102(b)
(reservoir planning); CWA section 208(b)(2)(F) (land use planning to
[[Page 33703]]
reduce agricultural nonpoint sources of pollution); CWA section 319
(nonpoint source management programs); and CWA section 401 (state
certification of federally licensed projects). Congress acknowledged
this when it directed Federal agencies to co-operate with State and
local agencies to develop comprehensive solutions to prevent, reduce,
and eliminate pollution in concert with programs for managing water
sources.
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\7\ Recognition of a general intent to control pollutants at the
source does not mean that dischargers are responsible only for
pollutants that they generate; rather, point sources need only
convey pollutants into navigable waters to be subject to the Act.
See Miccosukee at 105. Municipal separate storm sewer systems, for
example, are clearly subject to regulation under the Act. CWA
section 402(p).
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The Agency, therefore, concludes that, taken as a whole, the
statutory language and structure of the Clean Water Act indicate that
Congress generally did not intend to subject water transfers to the
NPDES program. Interpreting the term ``addition'' in that context, EPA
concludes that water transfers, as defined by today's rule, do not
constitute an ``addition'' to navigable waters to be regulated under
the NPDES program. Rather, Congress intended to leave primary oversight
of water transfers to state authorities in cooperation with Federal
authorities.
C. Legislative History
The legislative history of the Clean Water Act also supports the
conclusion that Congress generally did not intend to subject water
transfers to the NPDES program. First, the legislative history of
section 101(g) reveals that ``[i]t is the purpose of this [provision]
to insure that State [water] allocation systems are not subverted.'' 3
Congressional Research Serv., U.S. Library of Congress, Serial No. 95-
14, A Legislative History of the Clean Water Act of 1977, at 532
(1978); see PUD No. 1 of Jefferson County v. Washington Dep't of
Ecology, 511 U.S. 700, 721 (1994).
Notably, the legislative history of the Act discusses water flow
management activities in the context of the nonpoint source program
only. In discussing section 304(f), the House Committee Report
specifically mentioned water flow management as an area where EPA would
provide technical guidance to States for their nonpoint source
programs, rather than an area to be regulated under section 402.
This section and the information on such nonpoint sources is
among the most important in the 1972 Amendments. * * * The
Committee, therefore, expects the Administrator to be most diligent
in gathering and distribution of the guidelines for the
identification of nonpoint sources and the information on processes,
procedures, and methods for control of pollution from such nonpoint
sources as * * * natural and manmade changes in the normal flow of
surface and ground waters.
H.R. Rep. No. 92-911, at 109 (1972) (emphasis added).
In the legislative history of section 208 of the Act, the House
Committee report noted that in some States, water resource management
agencies allocating stream flows are required to consider water quality
impacts. The Report stated:
[I]n some States water resource development agencies are
responsible for allocation of stream flow and are required to give
full consideration to the effects on water quality. To avoid
duplication, the Committee believes that a State which has an
approved program for the handling of permits under section 402, and
which has a program for water resource allocation should continue to
exercise the primary responsibility in both of these areas and thus
provide a balanced management control system.
H.R. Rep. No. 92-911, at 96 (1972).
Thus, Congress recognized that the new section 402 permitting
program was not the only viable approach for addressing water quality
issues associated with State water resource management. The legislative
history makes clear that Congress generally did not intend a wholesale
transfer of responsibility for water quality away from water resource
agencies to the NPDES authority. Rather, Congress encouraged States to
obtain approval of authority to administer the NPDES program under
section 402(b) so that the NPDES program could work in concert with
water resource agencies' oversight of water management activities to
ensure a ``balanced management control system.'' Id.
In sum, the language, structure, and legislative history of the
statute all support the conclusion that Congress generally did not
intend to subject water transfers to the NPDES program. Water transfers
are an integral part of water resource management; they embody how
States and resource agencies manage the nation's water resources and
balance competing needs for water. Water transfers also physically
implement State regimes for allocating water rights, many of which
existed long before enactment of the Clean Water Act. Congress was
aware of those regimes, and did not want to impair the ability of these
agencies to carry them out. EPA's conclusion that the NPDES program
does not apply to water transfers respects Congressional intent,
comports with the structure of the Clean Water Act, and gives meaning
to sections 101(g) and 304(f) of the Act.
Based on these reasons, today's rule is within EPA's authority and
consistent with the CWA.
IV. Public Comment
EPA received many comments from the public and a number of states
stating that the Agency does not have authority to exclude from the
requirement to obtain NPDES permits, a specific class of dischargers
(in this case, water transfers). These commenters were concerned that
the proposed rule could jeopardize the NPDES and water quality
standards (WQS) programs. In particular, they feared that point source
regulation of discharges from impoundments used to settle mining wastes
might fall outside the scope of section 402 if the proposed rule were
finalized. In response to these comments, the Agency believes that
impoundments used to settle mining process water or waste water would
generally constitute ``waste treatment systems'' designed to meet the
requirements of the CWA and would be excluded from the definition of
``waters of the United States.'' See 40 CFR 122.2 (definition of
``Waters of the United States''). The addition of pollutants from a
waste treatment system to a water of the United States triggers the
permitting requirement, and today's rule therefore does not affect the
permitting of such facilities.
Some commenters argued that the proposed rule is inconsistent with
section 404 of the CWA (permits for dredged or fill material). They
stated that dredged material is listed as a pollutant under section 502
of the CWA and that the proposed rule implies that dredged material
never requires a permit unless the dredged material originates from a
waterbody that is not a water of the U.S. EPA believes that today's
final rule will not have an effect on the 404 program. The statutory
definition of ``pollutant'' includes ``dredged spoil,'' which by its
very nature comes from a waterbody. 33 U.S.C. 1362(6); 40 CFR 232.2;
United States v. Hubenka, 438 F.3d 1026, 1035 (10th Cir. 2006); United
States v. Deaton, 209 F.3d 331, 335-336 (4th Cir. 2000); Borden Ranch
Partnership v. United States, 261 F.3d 810, 814 (9th Cir. 2001).
Because Congress explicitly forbade discharges of dredged material
except as in compliance with the provisions cited in CWA section 301,
today's rule has no effect on the 404 permit program, under which
discharges of dredged or fill material may be authorized by a permit.
33 U.S.C. 1344.
As explained above, EPA disagrees that Congress generally intended
water transfers to obtain NPDES permits. EPA believes that this action
will add clarity to an area in which judicial decisions have created
uncertainty, and for reasons previously described in section III of
this preamble, concludes that Congress generally intended to leave the
[[Page 33704]]
oversight of water transfers to authorities other than the NPDES
program. Congress made clear that the CWA is to be construed in a
manner that does not unduly interfere with the ability of States to
allocate water within their boundaries. Specific statutory provisions
in the CWA addressing the management of water resources denote that
Congress generally did not intend for water transfers to be regulated
under section 402 of the CWA. Rather, sections 101(b), 208, and 304(f),
in particular, establish a variety of programs and regulatory
initiatives that more appropriately address water transfers. EPA's
conclusion that the NPDES program does not apply to water transfers
respects Congressional intent and comports with the structure of the
CWA.
Definition of a Water Transfer
In the proposed rule, EPA specifically requested comment on whether
the proposed definition of a water transfer properly achieves the
Agency's objective. Many commenters supported the Agency's proposed
definition, either generally or explicitly. On the other hand, some
commenters found the proposed definition too narrow and suggested that
the Agency defer to state law. Others found the definition overly broad
and suggested that it may encompass too many activities. These
concerns, among others, are addressed in the following discussions.
In response to the comment suggesting that the proposed definition
of a water transfer is too narrow and should also include transfers
between waterbodies defined as waters of the State, even where they do
not constitute waters of the United States under the CWA, EPA believes
that making such a change would not be appropriate because the NPDES
program only applies to waters of the U.S. The same commenter also
suggested that EPA defer to state law in defining a water transfer. In
response, the Agency finds that a definition applicable nationwide is
important to provide consistency in the application of this rule.
However, nothing in this rule precludes a State, under State law, from
regulating water transfers that are not subject to section 402 of the
Clean Water Act. States may not exclude from NPDES permit requirements
sources that are point sources under Federal law, including those that
do not meet the definition of a water transfer in today's rule. For
example, a point source that subjects waters of the United States to an
intervening industrial, municipal or commercial use could not be
exempted from NPDES permitting requirements under State law.
This rule expressly states that ``discharges from a water
transfer'' are not subject to NPDES permitting. The Agency defines a
water transfer as ``an activity that conveys or connects waters of the
United States without subjecting the transferred water to intervening
industrial, municipal, or commercial use.'' A water transfer is an
engineered activity that diverts a water of the U.S. to a second water
of the U.S. Thus, commenters who read the natural convergence of two
rivers as being a water transfer are incorrect, though such natural
convergences also do not require NPDES permits.
Some commenters sought clarification of certain elements of the
term ``water transfer'' while others suggested changes they believed
would either clarify or improve the scope of the term. Commenters
suggested that EPA change the use of the term ``activity'' to either
``occasion,'' ``instance,'' or ``occurrence,'' such that the definition
would read: ``water transfer means an instance in which waters of the
U.S. are conveyed * * *.'' The commenters' concern is that the term
``activities'' narrows the rule to only human directed or controlled
events rather than any instance in which water supplies are moved. The
Agency disagrees that the change is necessary. By ``activity,'' the
Agency means any system of pumping stations, canals, aqueducts,
tunnels, pipes, or other such conveyances constructed to transport
water from one water of the U.S. to another water of the U.S. Such a
system may consist of a single tunnel or pumping station or it may
require the use of multiple facilities along the course of the transfer
to reach the second water of the U.S.
Intervening Industrial, Municipal, or Commercial Use
A discharge of a pollutant associated with a water transfer
resulting from an intervening commercial, municipal, or industrial use,
or otherwise introduced to the water by a water transfer facility
itself would require an NPDES permit as any discharge of a pollutant
from a point source into a water of the U.S. would. The most frequent
comment on the proposed definition was that the phrase ``intervening
industrial, municipal, or commercial use'' was unclear or overbroad.\8\
EPA disagrees that this phrase is unclear or overbroad, and provides
clarification and examples of intervening uses below.
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\8\ EPA's discussion of intervening uses is not intended to
address or exclude any other activity that is currently subject to
NPDES permitting. For example, this rule does not affect EPA's
longstanding position that, if water is withdrawn from waters of the
U.S. for an intervening industrial, municipal or commercial use, the
reintroduction of the intake water and associated pollutants is an
``addition'' subject to NPDES permitting requirements. Nor does this
rule change EPA's position, upheld by the Supreme Court in
Miccosukee, that the definition of ``discharge of a pollutant'' in
the CWA includes coverage of point sources that do not themselves
generate pollutants. The Supreme Court stated, ``A point source is,
by definition, a `discernible, confined, and discrete conveyance'
section 1362(14) (emphasis added). That definition makes plain that
a point source need not be the original source of the pollutant; it
need only convey the pollutant to `navigable waters,' which are, in
turn, defined as `the waters of the United States.' Section
1362(7).'' Miccosukee, 541 U.S. at 105.
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For example, if the water is withdrawn to be used as cooling water,
drinking water, irrigation, or any other use such that it is no longer
a water of the U.S. before being returned to a water of the U.S., the
water has been subjected to an intervening use.\9\ In contrast, a water
pumping station, pipe, canal, or other structure used solely to
facilitate the transfer of the water is not an intervening use.
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\9\ Note that return flows from irrigated agriculture are exempt
from the requirement to obtain a NPDES permit under both the Act
itself and 40 CFR 122.3. Today's rule does not affect that
exemption.
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The reintroduction of the intake water and associated pollutants
from an intervening use through a point source is an ``addition'' and
has long been subject to NPDES permitting requirements. See, e.g., 40
CFR 122.2 (definition of process wastewater); 40 CFR 125.80 through
125.89 (regulation of cooling towers); 40 CFR 122.45(g) (regulations
governing intake pollutants for technology-based permitting); 40 CFR
Part 132, Appendix F, Procedure 5-D (containing regulations governing
water quality-based permitting for intake pollutants in the Great
Lakes). Moreover, a discharge from a waste treatment system, for
example, to a water of the United States, would not constitute a water
transfer and would require an NPDES permit. See 40 CFR 122.2. In these
situations, the reintroduction of water and that water's associated
pollutants physically introduces polluta