# Vol. 79 Monday,

No. 76 April 21, 2014

Part II



# Department of Defense

Department of the Army, Corps of Engineers

33 CFR Part 328



# Environmental Protection Agency

40 CFR Parts 110, 112, 116, et al.
Definition of ‘‘Waters of the United States’’ Under the Clean Water Act;
Proposed Rule


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1 ‘‘Interstate waters’’ in this preamble refers to all interstate waters including interstate wetlands. 

### DEPARTMENT OF DEFENSE

**Department of the Army, Corps of Engineers** 

**33 CFR Part 328**

**ENVIRONMENTAL PROTECTION**

**AGENCY**

**40 CFR Parts 110, 112, 116, 117, 122, 230, 232, 300, 302, and 401** 

**[EPA–HQ–OW- 2011–0880; FRL–9901–47– OW]** 

**RIN 2040–AF30**



### Definition of ‘‘Waters of the United

**States’’ Under the Clean Water Act**

**AGENCY**

### : U.S. Army Corps of Engineers, Department of the Army, Department of Defense; and Environmental Protection Agency (EPA).

**ACTION**

### : Proposed rule.

**SUMMARY**

### : The Environmental Protection Agency (EPA) and the U.S. Army Corps of Engineers (Corps) are publishing for public comment a proposed rule defining the scope of waters protected under the Clean Water Act (CWA), in light of the U.S. Supreme Court cases in

U.S. v. Riverside Bayview, Rapanos v. United States, and Solid Waste Agency of Northern Cook Countyv. U.S. Army Corps of Engineers (SWANCC), and Rapanos v. United States (Rapanos). This proposal would enhance protection for the nation’s public health and aquatic resources, and increase CWA program predictability and consistency by increasing clarity as to the scope of ‘‘waters of the United States’’ protected

under the Act.

**DATES**

### : Submit comments on or before July 21, 2014.

**ADDRESSES**

### : Submit your comments, identified by Docket ID No. EPA–HQ– OW–2011–0880 by one of the following

methods:

• Federal eRulemaking Portal: http:// www.regulations.gov. Follow the instructions for submitting comments.

• Email: ow-docket@epa.gov. Include EPA–HQ–OW–2011–0880 in the subject line of the message.

• Mail: Send the original and three copies of your comments to: Water Docket, Environmental Protection Agency, Mail Code 2822T, 1200 Pennsylvania Avenue NW., Washington, DC 20460, Attention: Docket ID No. EPA–HQ–OW–2011–0880.

• Hand Delivery/Courier: Deliver your comments to EPA Docket Center,

EPA West, Room 3334, 1301 Constitution Avenue NW., Washington, DC 20460, Attention Docket ID No. EPA–HQ–OW–2011–0880. Such deliveries are accepted only during the Docket’s normal hours of operation, which are 8:30 a.m. to 4:30 p.m., Monday through Friday, excluding legal holidays. Special arrangements should

be made for deliveries of boxed information. The telephone number for

the Water Docket is 202–566–2426.

Instructions: Direct your comments to Docket ID No. EPA–HQ–OW–2011– 0880. EPA’s policy is that all comments received will be included in the public docket without change and may be

made available on-line at http:// www.regulations.gov, including any personal information provided, unless

the comment includes information

claimed to be Confidential Business Information (CBI) or other information whose disclosure is restricted by statute. Do not submit information that you consider to be CBI, or otherwise protected, through http:// www.regulations.gov or email. The http://www.regulations.govWeb site is an ‘‘anonymous access’’ system, which means EPA will not know your identity or contact information unless you provide it in the body of your comment. If you send an email directly to EPA without going through http:// www.regulations.gov, your email address will be automatically captured and included as part of the comment that is placed in the public docket and made available on the Internet. If you submit an electronic comment, EPA recommends that you include your

name and other contact information in the body of your comment and with any disk or CD–ROM you submit. If EPA cannot read your comment due to

technical difficulties and cannot contact you for clarification, EPA might not be able to consider your comment. Avoid the use of special characters and any form of encryption, and ensure that electronic files are free of any defects or

viruses. For additional information about EPA’s public docket, visit the EPA Docket Center homepage at http:// www.epa.gov/epahome/dockets.htm.

Docket: All documents in the docket

are listed in the http:// www.regulations.gov index. Some information, however, is not publicly available, e.g., CBI or other information whose disclosure is restricted by statute. Certain other material, such as copyrighted material, is publicly available only in hard copy. Publicly

available docket materials are available electronically at http:// www.regulations.gov or in hard copy at the Water Docket, EPA Docket Center,

EPA West, Room 3334, 1301 Constitution Avenue NW., Washington, DC. The Public Reading Room is open from 8:30 a.m. to 4:30 p.m., Monday through Friday, excluding legal holidays. The telephone number for the Public Reading Room is 202–566–1744, and the telephone number for the Water

Docket is 202–566–2426.

**FOR FURTHER INFORMATION CONTACT**

### : Ms. Donna Downing, Office of Water (4502– T), Environmental Protection Agency, 1200 Pennsylvania Avenue NW., Washington, DC 20460; telephone number 202–566–2428; email address: CWAwaters@epa.gov. Ms. Stacey Jensen, Regulatory Community of Practice (CECW–CO–R), U.S. Army Corps of Engineers, 441 G Street NW., Washington, DC 20314; telephone number 202–761–5856; email address:

USACE

_CWA

_Rule@usace.army.mil.

**SUPPLEMENTARY INFORMATION**

### : The

SWANCC and Rapanos decisions resulted in the agencies evaluating the jurisdiction of waters on a case-specific basis far more frequently than is best for clear and efficient implementation of the CWA. This approach results in confusion and uncertainty to the regulated public and results in significant resources being allocated to these determinations by Federal and State regulators. The agencies are proposing this rule to fully carry out their responsibilities under the Clean Water Act. The agencies are providing clarity to regulated entities as to

whether individual water bodies are jurisdictional and discharges are subject to permitting, and whether individual water bodies are not jurisdictional and discharges are not subject to permitting.

Developing a final rule to provide the intended level of certainty and predictability, and minimizing the number of case-specific determinations, will require significant public involvement and engagement. Such involvement and engagement will allow the agencies to make categorical determinations of jurisdiction, in a

manner that is consistent with the scientific body of information before the agencies—particularly on the category

of waters known as ‘‘other waters.’’

The agencies propose to define

‘‘waters of the United States’’ in section (a) of the proposed rule for all sections

of the CWA to mean: Traditional navigable waters; interstate waters, including interstate wetlands; the territorial seas; impoundments of traditional navigable waters, interstate waters, including interstate wetlands, the territorial seas, and tributaries, as defined, of such waters; tributaries, as defined, of traditional navigable waters,
interstate waters,1 

### or the territorial seas;


## 22189 Federal Register/ Vol. 79, No. 76 / Monday, April 21, 2014 / Proposed Rules

2 The term ‘‘waters of the United States’’ does not include prior converted cropland, which is currently defined by the U.S. Department of Agriculture (USDA) for purposes of the Agriculture Act of 2014 at 7 CFR 122.2. EPA and the Corps use the USDA definition of prior converted cropland for purposes of determining jurisdiction under the

CWA. 

### and adjacent waters, including adjacent wetlands. Waters in these categories would be jurisdictional ‘‘waters of the United States’’ by rule—no additional analysis would be required. The agencies emphasize that the categorical finding of jurisdiction for tributaries and adjacent waters was not based on the mere connection of a water body to downstream waters, but rather a determination that the nexus, alone or in combination with similarly situated waters in the region, is significant based on data, science, the CWA, and caselaw.

In addition, the agencies propose that ‘‘other waters’’ (those not fitting in any of the above categories) could be

determined to be ‘‘waters of the United States’’ through a case-specific showing that, either alone or in combination with similarly situated ‘‘other waters’’ in the region, they have a ‘‘significant nexus’’ to a traditional navigable water, interstate water, or the territorial seas.

The rule would also offer a definition of significant nexus and explain how similarly situated ‘‘other waters’’ in the region should be identified.

The agencies acknowledge that there may be more than one way to determine which waters are jurisdictional as ‘‘other waters.’’ To best meet their goals and responsibilities, the agencies request comment on alternate approaches to determining whether ‘‘other waters’’ are similarly situated and have a ‘‘significant nexus’’ to a traditional navigable water, interstate water, or the territorial seas. In the

discussion of ‘‘other waters’’ later in the preamble, the agencies seek comment on these other approaches and whether they could better meet the goals of greater predictability and consistency through increased clarity, while simultaneously fulfilling the agencies’ responsibility to the CWA’s objectives and policies to protect water quality, public health, and the environment. Commenters will specifically be asked

to comment on whether and how these alternate approaches may be more consistent with the goal of clarity, and the CWA, the best available science, and

the caselaw.

In particular, the agencies are interested in comments, scientific and technical data, caselaw, and other information that would further clarify

which ‘‘other waters’’ should be considered similarly situated for purposes of a case-specific significant nexus determination. The agencies seek

comment on a number of alternative approaches. These alternatives include potentially determining waters in identified ecological regions (ecoregions) or hydrologic-landscape regions are similarly situated for purposes of evaluating a significant nexus, as well as the basis for determining which ecoregions or hydrologic-landscape regions should be so identified. The agencies also solicit comment on whether the legal,

technical and scientific record would support determining limited specific subcategories of waters are similarly situated, or as having a significant nexus sufficient to establish jurisdiction.

Just as the agencies are seeking comment on a variety of approaches, or combination of approaches, as to which waters are jurisdictional, the agencies also request comment on determining

which waters should be determined non-jurisdictional. The agencies seek

comment on how inconclusiveness of

the science relates to the use of casespecific determinations. As the science develops, the agencies could determine that additional categories of ‘‘other waters’’ are similarly situated and have a significant nexus and are jurisdictional by rule, or that as a class they do not have such a significant nexus and might not be jurisdictional.

The agencies pose the questions because of the strong intent to provide as much certainty to the regulated public and the regulators as to which waters are and are not subject to CWA jurisdiction. These comments on alternate approaches will inform the agencies in addition to the comments on the case-specific determination proposed in the rule.

The agencies’ decision on how best to address jurisdiction over ‘‘other waters’’ in the final rule will be informed by the

final version of the EPA’s Office of Research and Development synthesis of published peer-reviewed scientific literature discussing the nature of connectivity and effects of streams and wetlands on downstream waters (U.S. Environmental Protection Agency, Connectivity of Streams and Wetlands

to Downstream Waters: A Review and Synthesis of the Scientific Evidence, (Washington, DC: U.S. Environmental Protection Agency, 2013)) (‘‘Report’’)

and other available scientific

information.

The agencies also propose to exclude specified waters from the definition of

‘‘waters of the United States’’ in section (b) of the proposed rule. The agencies propose no change to the exclusion for waste treatment systems designed consistent with the requirements of the CWA, no change to the exclusion for prior converted cropland,2 

### and no change to the regulatory status of water transfers. The agencies propose, for the first time, to exclude by regulation

certain waters and features over which the agencies have as a policy matter generally not asserted CWA jurisdiction. Codifying these longstanding practices supports the agencies’ goals of providing greater clarity, certainty, and predictability for the regulated public and the regulators. Waters and features

that are determined to be excluded under section (b) of the proposed rule will not be jurisdictional under any of the categories in the proposed rule under section (a). There is no recapture provision for these excluded waters in the proposal.

In light of the Supreme Court

decisions in SWANCC and Rapanos, the scope of regulatory jurisdiction in this proposed rule is narrower than that under the existing regulations. See 40 CFR 122.2 (defining ‘‘waters of the United States’’).

The rule does not affect longstanding permitting exemptions in the CWA for farming, silviculture, ranching and other specified activities. Where waters would be determined jurisdictional under the proposed rule, applicable exemptions in the CWA would continue to preclude application of CWA permitting requirements.

Finally, the agencies retain the existing regulatory definitions for the terms ‘‘adjacent’’ and ‘‘wetlands.’’ The agencies propose for the first time to define the terms ‘‘neighboring,’’ ‘‘riparian area,’’ ‘‘floodplain,’’ ‘‘tributary,’’ and ‘‘significant nexus.’’

This proposal does not affect Congressional policy to preserve the primary responsibilities and rights of states to prevent, reduce, and eliminate pollution, to plan the development and use of land and water resources, and to

consult with the Administrator with respect to the exercise of the Administrator’s authority under the CWA. CWA section 101(b).

This proposal also does not affect Congressional policy not to supersede, abrogate or otherwise impair the authority of each State to allocate quantities of water within its jurisdiction and neither does it affect the policy of Congress that nothing in

the CWA shall be construed to supersede or abrogate rights to quantities of water which have been established by any state. CWA section 101(g).

This proposal requests public

comment on issues associated with the


## 22190 Federal Register/ Vol. 79, No. 76 / Monday, April 21, 2014 / Proposed Rules

agencies’ proposed regulatory definition

of ‘‘waters of the United States.’’ Because the agencies do not address the

exclusions from the definition of

‘‘waters of the United States’’ for waste treatment systems and prior converted cropland or the existing definition of ‘‘wetlands’’ in this proposed rule the agencies do not seek comment on these existing regulatory provisions. This

notice also solicits information and data from the general public, the scientific community, and tribal, state and local resource agencies on the aquatic resource, implementation, and economic implications of a definition of

‘‘waters of the United States’’ as described in the proposal. The goal of the agencies is to ensure the regulatory definition is consistent with the CWA, as interpreted by the Supreme Court, and as supported by science, and to provide maximum clarity to the public, as the agencies work to fulfill the CWA’s objectives and policy to protect water quality, public health, and the

environment.

Table of Contents

I. General Information A. How can I get copies of this document and

related information? B. Under what legal authority is this proposed rule issued? II. Background A. Executive Summary B. The Clean Water Act and Regulatory

Definition of Waters of the United States C. Background on Scientific Review and Significant Nexus Analysis 1. Scientific Synthesis 2. Summary of Significant Nexus

Conclusions III. Proposed Definition of Waters of the

United States A. Summary of Proposed Rule B. Traditional Navigable Waters

C. Interstate Waters

D. Territorial Seas E. Impoundments

F. Tributaries G. Adjacent Waters

H. Other Waters

I. Waters That Are Not Waters of the United

States IV. Related Acts of Congress, Executive

Orders, and Agency Initiatives 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: Federal Actions To
Address Environmental Justice in Minority Populations and Low-Income Populations

K. Environmental Documentation Appendix A. Scientific Evidence Appendix B. Legal Analysis



### I. General Information

A. How can I get copies of this document and related information?

1. Docket. EPA and the Corps of Engineers have established an official public docket for this action under Docket Id. No. EPA–HQ–OW–2011– 0880. The official public docket consists of the document specifically referenced in this action, any public comments received, and other information related to this action. Although a part of the official docket, the public docket does

not include Confidential Business Information (CBI) or other information whose disclosure is restricted by statute. The official public docket is the

collection of materials that is available for public viewing at the OW Docket,

EPA West, Room 3334, 1301 Constitution Ave. NW., Washington, DC 20004. This Docket Facility is open from 8:30 a.m. to 4:30 p.m., Monday through Friday, excluding legal holidays. The OW Docket telephone number is 202–

566–2426. A reasonable fee will be charged for copies.

2. Electronic Access. You may access

this Federal Register document electronically through the EPA Internet

under the ‘‘Federal Register’’ listings at http://www.regulations.gov. An electronic version of the public docket is available through EPA’s electronic public docket and comment system, EPA Dockets. You may use EPA Dockets

at http://www.regulations.govto view public comments, access the index listing of the contents of the official public docket, and to access those documents in the public docket that are available electronically. For additional information about EPA’s public docket, visit the EPA Docket Center homepage

at http://www.epa.gov/epahome/

dockets.htm. Although not all docket materials may be available electronically, you may still access any of the publicly available docket materials through the Docket Facility

identified earlier.

B. Under what legal authority is this proposed rule issued?

The authority for this proposed rule is the Federal Water Pollution Control Act,
33 U.S.C. 1251, et seq. II. Background

A. Executive Summary

The U.S. Environmental Protection Agency (EPA) and the U.S. Army Corps of Engineers (Corps) publish for public comment a proposed rule defining the scope of waters protected under the Clean Water Act (CWA), in light of the U.S. Supreme Court cases in U.S. v. Riverside Bayview Homes, Solid Waste Agency of Northern Cook Countyv. U.S. Army Corps of Engineers (SWANCC),

and Rapanos v. United States (Rapanos). The purposes of the proposed rule are to ensure protection of our nation’s aquatic resources and make the process of identifying ‘‘waters of the United States’’ less complicated

and more efficient. The rule achieves these goals by increasing CWA program transparency, predictability, and consistency. This rule will result in more effective and efficient CWA permit evaluations with increased certainty and less litigation. This rule provides increased clarity regarding the CWA regulatory definition of ‘‘waters of the

United States’’ and associated definitions and concepts.

EPA’s Office of Research andDevelopment prepared a draft peerreviewed synthesis of published peerreviewed scientific literature discussing the nature of connectivity and effects of

streams and wetlands on downstream waters (U.S. Environmental Protection Agency, Connectivity of Streams and

Wetlands to Downstream Waters: A Review and Synthesis of the Scientific Evidence, (Washington, DC: U.S. Environmental Protection Agency, 2013)) (‘‘Report’’). The Report is under review by EPA’s Science Advisory Board, and the rule will not be finalized until that review and the final Report are complete. This proposal is also supported by a body of peer-reviewed scientific literature on the connectivity of tributaries, wetlands, adjacent open waters, and other open waters to downstream waters and the important

effects of these connections on the chemical, physical, and biological integrity of those downstream waters.

Appendix A of this preamble summarizes currently available scientific literature and the Report that are part of the administrative record for this proposal and explains how this scientific information supports the proposed rule. Additional data and information likely will become available during the rulemaking process, including that provided during the public comment process, and by additional research, studies, and investigations that take place before the rulemaking process is concluded. The


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3 The agencies use the term ‘‘water’’ and ‘‘waters’’ in the proposed rule in categorical reference to rivers, streams, ditches, wetlands, ponds, lakes, playas, and other types of natural or man-made aquatic systems. The agencies use the terms ‘‘waters’’ and ‘‘water bodies’’ interchangeably in this preamble. The terms do not refer solely to the water contained in these aquatic systems, but to the system as a whole including associated chemical, physical, and biological features. 4While section 311 uses the phrase ‘‘navigable waters of the United States,’’ EPA has interpreted it to have the same breadth as the phrase ‘‘navigable
waters’’ used elsewhere in section 311, and in other

sections of the CWA. See United States v. Texas Pipe Line Co., 611 F.2d 345, 347 (10th Cir. 1979);

United States v. Ashland Oil & Transp. Co., 504 F.2d 1317, 1324–25 (6th Cir. 1974). In 2002, EPA revised its regulatory definition of ‘‘waters of the United States’’ in 40 CFR part 112 to ensure that the actual language of the rule was consistent with the regulatory language of other CWA programs. Oil Pollution & Response; Non-Transportation-Related Onshore & Offshore Facilities, 67 FR 47042, July 17,

2002. A district court vacated the rule for failure to comply with the Administrative Procedure Act, and reinstated the prior regulatory language. American

Petroleum Ins. v. Johnson, 541 F.Supp. 2d 165 (D. DC 2008). However, EPA interprets ‘‘navigable waters of the United States’’ in CWA section 311(b), in the pre-2002 regulations, and in the 2002 rule to have the same meaning as ‘‘navigable waters’’ in CWA section 502(7).

5 For example, the CWA section 402 (33 U.S.C. § 1342) program regulates discharges of pollutants from ‘‘point sources’’ to ‘‘waters of the United States,’’ whether these pollutants reach jurisdictional waters directly or indirectly. The plurality opinion in Rapanos noted that ‘‘there is no reason to suppose that our construction today significantly affects the enforcement of § 1342. . . . The Act does not forbid the ‘addition of any pollutant directlyto navigable waters from any point source,’ but rather the ‘addition of any pollutant to navigable waters.’ ’’ 547 U.S. at 743. Clean Water Act section 311(b)(1) provides: ‘‘[I]t is the policy of the United States that there should be no discharges of oil or hazardous substances into or upon the navigable waters of the United States [or] adjoining shorelines . . . or which may affect natural resources belonging to, appertaining to, or under the exclusive management authority of the United States.’’ (Emphasis added.) ‘‘Discharge’’ is broadly defined in CWA section 311(a)(2) to include ‘‘any spilling, leaking, pumping, pouring, emitting, emptying or dumping,’’ with certain enumerated exceptions, and is not limited to point source discharges. 

### agencies are specifically requesting

information that would inform the

decision on how best to address ‘‘other

waters.’’ At the conclusion of the rulemaking process, the agencies will review the entirety of the completed

administrative record and determine at that time what, if any, adjustments are appropriate for the final rule.

‘‘Waters of the United States,’’ which include wetlands, rivers, streams, lakes, ponds and the territorial seas, provide many functions and services critical for

our nation’s economic and

environmental health.3 

### In addition to providing habitat, rivers, lakes, ponds and wetlands cleanse our drinking water, ameliorate storm surges, provide invaluable storage capacity for some flood waters, and enhance our quality of life by providing myriad recreational opportunities, as well as important water supply and power generation benefits. A desire to protect these vital resources led Congress to pass the CWA

in 1972 in order to restore and maintain the chemical, physical, and biological integrity of our nation’s waters while recognizing, preserving, and protecting the primary responsibilities and rights of states to prevent, reduce, and eliminate pollution within their borders. Decades of experience implementing the CWA’s programs and existing science provide strong support for the regulatory and policy underpinnings of the proposed rule. The proposed rule was developed with an enhanced understanding of the importance of all aspects of tributary, wetland, and lake and pond systems and the ecological functions and services they provide.

The proposed rule will reduce documentation requirements and the time currently required for making jurisdictional determinations. It will provide needed clarity for regulators, stakeholders and the regulated public for identifying waters as ‘‘waters of the United States,’’ and reduce time and resource demanding case-specific analyses prior to determining jurisdiction and any need for permit or

enforcement actions.

The modern Clean Water Act was established by the Federal Water

Pollution Control Act Amendments of 1972, which was substantially amended in 1977 and 1987. (The 1972

amendments were to the Federal Water Pollution Control Act originally enacted in 1948.) As stated in section 101(a), the objective of the CWA is to restore and maintain the chemical, physical, and biological integrity of the Nation’s waters. Prior to the CWA, the Rivers and Harbors Appropriations Act of 1899 protected navigation and protected some waters from discharges of pollution.

The 1899 Act continues in force and applies primarily to the ‘‘navigable

waters of the United States.’’ The 1948

Federal Water Pollution Control Act called for programs eliminating or reducing the pollution of interstate waters and tributaries thereof, and improving the sanitary condition of surface and underground waters. The jurisdictional scope of the CWA is ‘‘navigable waters,’’ defined in section 502(7) of the statute as ‘‘waters of the United States, including the territorial seas.’’ Both the legislative history and

the caselaw confirm that ‘‘waters of the

United States’’ in the CWA are not limited to the traditional navigable

waters. It is the CWA definition that is the subject of this proposed rule.

The term ‘‘navigable waters’’ is used in a number of provisions of the CWA, including the section 402 National Pollutant Discharge Elimination System (NPDES) permit program, the section 404 permit program, the section 311 oil spill prevention and response program,4 

### the water quality standards and total maximum daily load programs under section 303, and the section 401 state water quality certification process. However, while there is only one CWA

definition of ‘‘waters of the United States,’’ there may be other statutory

factors that define the reach of a particular CWA program or provision.5 

### The CWA leaves it to EPA and the Corps to define the term ‘‘waters of the United States.’’ Existing regulations (last codified in 1986) define ‘‘waters of the United States’’ as traditional navigable waters, interstate waters, all other

waters that could affect interstate or foreign commerce, impoundments of waters of the United States, tributaries, the territorial seas, and adjacent wetlands. 33 CFR 328.3; 40 CFR 122.2.

The U.S. Supreme Court addressed the scope of ‘‘waters of the United States’’ protected by the CWA in United

States v. Riverside Bayview Homes, 474 U.S. 121 (1985), which involved wetlands adjacent to a traditional navigable water in Michigan. In a unanimous opinion, the Court deferred to the Corps’ judgment that adjacent wetlands are ‘‘inseparably bound up’’ with the waters to which they are adjacent, and upheld the inclusion of adjacent wetlands in the regulatory

definition of ‘‘waters of the United

States.’’ The Court observed that the broad objective of the CWA to restore the integrity of the nation’s waters ‘‘incorporated a broad, systemic view of the goal of maintaining and improving water quality

. . . . Protection of aquatic ecosystems, Congress recognized, demanded broad federal authority to control pollution, for ‘[w]ater moves in hydrologic cycles and it is essential that discharge of pollutants be controlled at the source.’ In keeping with these views, Congress chose to define the waters covered by the Act broadly.’’ Id. at 133 (citing Senate Report 92–414).

The issue of CWA regulatory jurisdiction over ‘‘waters of the United States’’ was addressed again by the Supreme Court in Solid Waste Agency of Northern Cook Countyv. U.S. Army Corps of Engineers, 531 U.S. 159 (2001).

In SWANCC, the Court (in a 5–4 opinion) held that the use of ‘‘isolated’’ nonnavigable intrastate ponds by migratory birds was not by itself a

sufficient basis for the exercise of Federal regulatory authority under the


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CWA. The Court noted that in the

Riverside case it had ‘‘found that Congress’ concern for the protection of water quality and aquatic ecosystems indicated its intent to regulate wetlands ‘inseparably bound up with the

‘‘waters’’ of the United States’ ’’ and that ‘‘[i]t was the significant nexus between the wetlands and ‘navigable waters’ that informed our reading of the CWA’’ in

that case. Id. at 167.

Five years after SWANCC, the Court again addressed the CWA term ‘‘waters

of the United States’’ in Rapanos v. United States, 547 U.S. 715 (2006). Rapanos involved two consolidated

cases in which the CWA had been applied to wetlands adjacent to nonnavigable tributaries of traditional navigable waters. All Members of the Court agreed that the term ‘‘waters of the United States’’ encompasses some waters that are not navigable in the traditional sense. A four-Justice plurality in Rapanos interpreted the

term ‘‘waters of the United States’’ as covering ‘‘relatively permanent, standing or continuously flowing bodies

of water. . .’’ id. at 739, that are connected to traditional navigable

waters, id. at 742, as well as wetlands

with a continuous surface connection to such relatively permanent water bodies,

id. The Rapanos plurality noted that its reference to ‘‘relatively permanent’’ waters did ‘‘not necessarily exclude streams, rivers, or lakes that might dry up in extraordinary circumstances, such as drought,’’ or ‘‘seasonal rivers, which contain continuous flow during some months of the year but no flow during dry months. . . .’’ Id. at 732 n.5 (emphasis in original).

Justice Kennedy’s concurring opinion took a different approach than the plurality’s. Justice Kennedy concluded

that the term ‘‘waters of the United States’’ encompasses wetlands that ‘‘possess a ‘significant nexus’ to waters that are or were navigable in fact or that could reasonably be so made.’’ Id. at 759 (Kennedy, J., concurring in the judgment) (quoting SWANCC, 531 U.S. at 167). He stated that wetlands possess the requisite significant nexus if the wetlands, ‘‘either alone or in combination with similarly situated [wet]lands in the region, significantly affect the chemical, physical, and biological integrity of other covered waters more readily understood as ‘navigable.’ ’’ 547 U.S. at 780. Kennedy’s opinion notes that such a relationship with navigable waters must be more than ‘‘speculative or insubstantial.’’ Id. Because Justice Kennedy identified ‘‘significant nexus’’ as the touchstone for CWA jurisdiction, the agencies

determined that it is reasonable and appropriate to apply the ‘‘significant nexus’’ standard for CWA jurisdiction that Justice Kennedy’s opinion applied to adjacent wetlands to other categories of water bodies as well (such as to tributaries of traditional navigable waters or interstate waters, and to ‘‘other waters’’) to determine whether they are subject to CWA jurisdiction, either by rule or on a case-specific basis.

The four dissenting Justices in Rapanos would have affirmed the court of appeals’ application of the pertinent regulatory provisions, concluding that

the term ‘‘waters of the United States’’ encompasses, inter alia, all tributaries and wetlands that satisfy either the plurality’s standard or that of Justice Kennedy. Id. at 810 & n.14 (Stevens, J., dissenting). Neither the plurality nor the Kennedy opinion invalidated any of the regulatory provisions defining ‘‘waters

of the United States.’’

The proposed rule would revise the existing definition of ‘‘waters of the

United States’’ consistent with the science and the above Supreme Court cases. The proposed rule retains much of the structure of the agencies’ longstanding definition of ‘‘waters of the United States,’’ and many of the existing provisions of that definition where revisions are not required in light of Supreme Court decisions or other bases for revision. As a result of the Supreme

Court decisions in SWANCC and Rapanos, the scope of regulatory jurisdiction of the CWA in this proposed rule is narrower than that under the existing regulations.

The most substantial change is the proposed deletion of the existing regulatory provision that defines

‘‘waters of the ‘‘United States’’ as all other waters such as intrastate lakes, rivers, streams (including intermittent streams), mudflats, sandflats, wetlands, sloughs, prairie potholes, wet meadows, playa lakes, or natural ponds, the use, degradation or destruction of which could affect interstate or foreign commerce including any such waters: Which are or could be used by interstate or foreign travelers for recreational or other purposes; from which fish or

shellfish are or could be taken and sold in interstate or foreign commerce; or

which are used or could be used for industrial purposes by industries in interstate commerce. 33 CFR 328.3(a)(3); 40 CFR 122.2. Under the proposed rule, these ‘‘other waters’’ (those which do not fit within the proposed categories of waters jurisdictional by rule) wouldonly be jurisdictional upon a casespecific determination that they have a significant nexus as defined by the proposed rule. Waters in a watershed in

which there is no connection to a traditional navigable water, interstate

water or the territorial seas would not be

‘‘waters of the United States.’’ In addition, the proposed rule would for the first time explicitly exclude some

features and waters over which the agencies have not generally asserted jurisdiction and in so doing would eliminate the authority of the agencies to determine in case specific

circumstances that some such waters are jurisdictional ‘‘waters of the United

States.’’

The agencies propose a rule that is

clear and understandable and that protects the nation’s waters, consistent with the law and currently available scientific and technical expertise. Continuity with the existing regulations, where possible, will reduce confusion

and will reduce transaction costs for the regulated community and the agencies. To that same end, the agencies also propose, where consistent with the law

and their scientific and technical expertise, categories of waters that are and are not jurisdictional, as well as categories of waters and wetlands that require a case-specific significant nexus evaluation to determine whether they

are ‘‘waters of the United States’’ and protected by the CWA. Finally, the agencies propose definitions for some of the terms used in the proposed regulation.

This preamble also presents several alternative options for determining the jurisdictional status of certain ‘‘other waters’’ that would rely less, or not at all, on case-specific significant nexus evaluations. The agencies may adopt one or a combination of these options for the final rule, after considering public comment and the evolving scientific literature on connectivity of waters. This preamble also seeks comment on a number of other ways that the agencies might provide even greater clarity, certainty, and predictability in determining which ‘‘other waters’’ are and are not subject to CWA jurisdiction. The agencies evaluated extensive peer reviewed science in making their determination in the proposed rule. However, the agencies also seek additional

information that would enhance the predictability and accuracy of its jurisdictional determinations. The agencies request the type of information on the evolving scientific literature on connectivity of waters that could allow the agencies to rely less on case-specific significant nexus evaluations.

Under the proposed first section of the regulation, section (a), the agencies propose to define the ‘‘waters of the

United States’’ for all sections


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(including sections 301, 311, 401, 402, 404) of the CWA to mean:

• All waters which are currently used, were used in the past, or may be susceptible to use in interstate or foreign commerce, including all waters which are subject to the ebb and flow of the tide;

• All interstate waters, including interstate wetlands;

• The territorial seas;

• All impoundments of a traditional navigable water, interstate water, the territorial seas or a tributary;

• All tributaries of a traditional navigable water, interstate water, the territorial seas or impoundment;

• All waters, including wetlands, adjacent to a traditional navigable water, interstate water, the territorial seas, impoundment or tributary; and

• On a case-specific basis, other waters, including wetlands, provided that those waters alone, or in combination with other similarly situated waters, including wetlands, located in the same region, have a significant nexus to a traditional navigable water, interstate water or the

territorial seas.

As discussed in further detail below, the rule would not change the following provisions of the existing rule (although some provisions have been renumbered): Traditional navigable waters; interstate waters; the territorial seas; and impoundments of ‘‘waters of the United States.’’ In paragraph (a)(5) of the proposed rule, the agencies propose

that all tributaries as defined in the proposed rule are ‘‘waters of the United

States.’’ While tributaries are ‘‘waters of the United States’’ under the existing regulation, the rule would for the first time include a regulatory definition of ‘‘tributary.’’

With this proposed rule, the agencies conclude, based on existing science and the law, that a significant nexus exists between tributaries (as defined in the proposed rule) and the traditional navigable waters, interstate waters, and the territorial seas into which they flow; and between adjacent water bodies (as defined in the proposed rule) and traditional navigable waters, interstate waters, and the territorial seas, respectively. Consequently, this rule

establishes as ‘‘waters of the United States,’’ all tributaries (as defined in the proposal), of the traditional navigable waters, interstate waters, and the territorial seas, as well as all adjacent waters (including wetlands). This will

eliminate the need to make a casespecific significant nexus determination for tributaries or for their adjacent

waters because it has been determined that as a category, these waters have a significant nexus and thus are ‘‘waters

of the United States.’’

In paragraph (a)(6) of the proposed rule, the rule would clarify that adjacent waters, rather than simply adjacent wetlands, are ‘‘waters of the United States.’’ The rule would further clarify the meaning of ‘‘adjacent’’ by defining one of its elements, ‘‘neighboring.’’ The related terms of ‘‘riparian area’’ and ‘‘floodplain’’ are also defined in the proposed rule.

The rule states that on a case-specific

basis ‘‘other waters’’ that have a significant nexus to a traditional navigable water, interstate water or the

territorial seas are ‘‘waters of the United States.’’ Unlike the categories of waters in paragraphs (a)(1) through (6), which would be jurisdictional by definition,

these ‘‘other waters’’ would not be ‘‘waters of the United States’’ by definition; rather, these ‘‘other waters’’ would only be jurisdictional provided that they have been determined on a case-specific basis to have a significant nexus to a paragraph (a)(1) through (a)(3) water. Therefore, the rule also includes a definition of ‘‘significant

nexus.’’

‘‘Significant nexus’’ is not itself a scientific term. The relationship that

waters can have to each other and

connections downstream that affect the chemical, physical, or biological integrity of traditional navigable waters, interstate waters, or the territorial seas is not an all or nothing situation. The existence of a connection, a nexus, does not by itself establish that it is a ‘‘significant nexus.’’ There is a gradient in the relation of waters to each other, and this is documented in the Report. The agencies propose a case-specific analysis in establishing jurisdiction over

these ‘‘other waters’’ as consistent with the current science, the CWA, and the caselaw. A case-specific analysis allows for a determination of jurisdiction at the point on the gradient in the relationship that constitutes a ‘‘significant nexus.’’ In the proposed regulation the rule defines the following terms: adjacent, neighboring, riparian area, floodplain, tributary, wetlands, and significant nexus. However, the agencies also recognize that relying on a case-specific analysis provides less certainty to the regulated public on the jurisdictional status of other waters and is considering other approaches, as discussed later in this preamble.

The proposed section (b) excludes specified waters and features from the

definition of ‘‘waters of the United

States.’’ Waters and features that are

determined to be excluded under section (b) of the proposed rule will not be jurisdictional under any of the categories in the proposed rule under section (a), even if they would otherwise satisfy the regulatory definition. Those

waters and features that would not be

‘‘waters of the United States’’ are:

• Waste treatment systems, including treatment ponds or lagoons, designed to meet the requirements of the Clean

Water Act.

• Prior converted cropland. Notwithstanding the determination of an area’s status as prior converted cropland by any other Federal agency, for the purposes of the Clean Water Act the final authority regarding Clean Water Act jurisdiction remains with

EPA.

• Ditches that are excavated wholly in uplands, drain only uplands, and have less than perennial flow.

• Ditches that do not contribute flow, either directly or through another water, to a traditional navigable water, interstate water, the territorial seas or an impoundment of a jurisdictional water.

• The following features:

Æ Artificially irrigated areas that would revert to upland should application of irrigation water to that

area cease;

Æ artificial lakes or ponds created by excavating and/or diking dry land and used exclusively for such purposes as stock watering, irrigation, settling basins, or rice growing;

Æ artificial reflecting pools or swimming pools created by excavating and/or diking dry land;

Æ small ornamental waters created by excavating and/or diking dry land for primarily aesthetic reasons;

Æ water-filled depressions created incidental to construction activity;

Æ groundwater, including groundwater drained through subsurface drainage systems; and

Æ gullies and rills and non-wetland

swales.

The rule does not affect longstanding exemptions in the CWA for farming, silviculture, ranching and other activities, does not change regulatory exclusions for waste treatment systems and prior converted cropland, and does not change the regulatory status of water

transfers. Where waters would be determined jurisdictional under the proposed rule, applicable exemptions of the CWA would continue to preclude application of CWA permitting requirements. For example, if ‘‘other waters’’ are aggregated as similarly situated in the region and determined to be jurisdictional, any exempt activities that include a discharge to those waters would remain outside the regulatory requirements of the CWA. Exempted discharges are established under CWA sections 402, 502, and 404 and include:


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Agricultural stormwater discharges; return flows from irrigated agriculture; normal farming, silvicultural, and ranching activities; upland soil and water conservation practices;

construction or maintenance of farm or stock ponds or irrigation ditches; maintenance of drainage ditches; and construction or maintenance of farm, forest, and temporary mining roads.

To provide additional clarity to farmers, the agencies are today also issuing an interpretive rule clarifying the applicability of the permitting exemption provided under section 404(f)(1)(A) of the CWA to discharges of dredged or fill material associated with certain agricultural conservation practices based on the Natural

Resources Conservation Service conservation practice standards and that are designed and implemented to protect and enhance water quality. This interpretive rule was developed in coordination with the U.S. Department of Agriculture, was signed by EPA and the Army, and became effective immediately. The agencies recognize, however, the value of receiving public comment on the interpretive rule and are publishing it by separate notice in

the Federal Register. The public is encouraged to provide their comments on the interpretive rule to the docket on the interpretive rule, Docket Id. No. EPA–HQ–OW–2013–0820, and not to this docket. The interpretive rule and the request for comments can be found

at http://water.epa.gov/lawsregs/ guidance/wetlands/agriculture.cfm and

at http://www.regulations.govvia Docket Id. No. EPA–HQ–OW–2013–

0820.

The proposed rule is expected to reduce documentation requirements and the time it takes to make approved jurisdictional determinations by decreasing the number of jurisdictional determinations that require case-specific significant nexus analysis evaluations. It will improve clarity for regulators, stakeholders and the regulated public by defining certain categories of waters as

‘‘waters of the United States’’ that previously required case-specific analyses prior to establishing CWA jurisdiction through the approved jurisdictional determination procedures. A comprehensive review of a growing body of scientific literature, as well as the agencies’ growing body of scientific and technical knowledge and field expertise, led the agencies to conclude

that it is reasonable to establish certain categories of waters that are jurisdictional by rule as they have a significant nexus to an (a)(1) through (a)(3) water, specifically tributaries to traditional navigable waters, interstate waters, or the territorial seas, and theiradjacent waters and wetlands. Casespecific jurisdictional determinations would still be required for the ‘‘other waters’’ category in paragraph (a)(7) of the proposed rule. Under the alternate approaches affecting ‘‘other waters’’ described later in the preamble, theagencies request comment on the casespecific analysis.

A review of the scientific literature,including the Report of the peerreviewed science, shows that tributaries and adjacent waters play an important role in maintaining the chemical, physical, and biological integrity of traditional navigable waters, interstate waters, and the territorial seas—and of other jurisdictional waters—because of their hydrological and ecological

connections to and interactions with those waters. Therefore, it is appropriate to protect all tributaries and adjacent waters, because the tributaries, adjacent waters, and the downstream traditional navigable waters, interstate waters, and

the territorial seas function as an integrated system. Water flows through

tributaries to downstream traditional navigable waters, interstate waters, and the territorial seas, and that water carries pollutants that affect the chemical, physical, and biological integrity of the (a)(1) through (a)(3) waters, including water quality, fisheries, recreation, and other ecological services.

In discussing the significant nexus standard, Justice Kennedy stated: ‘‘The required nexus must be assessed in terms of the statute’s goals and purposes. Congress enacted the [CWA] to ‘restore and maintain the chemical, physical, and biological integrity of the

Nation’s waters. . . .’ ’’ 547 U.S. at 779. To protect the integrity of the waters subject to the CWA, the significant nexus standard must be implemented in

a manner that restores and maintains any of these three attributes of traditional navigable waters, interstate waters, or the territorial seas. Waters adjacent to tributaries also provide ecological functions that, in conjunction with the functions provided by the tributaries they are adjacent to, have a significant influence on the chemical, physical, and biological integrity of downstream traditional navigable waters, interstate waters, and the

territorial seas.

Examples of the important functions provided by adjacent waters are the sequestering or transformation of pollutants to reduce inputs to tributaries and subsequently to downstream (a)(1) through (a)(3) waters, water storage, and sediment trapping. Thus, in some instances, the significance of adjacent waters is to prevent or delay a hydrological connection with

downstream waters and store water and/ or pollutants. Given the large scale systematic interactions that occur, and the substantial effects that result, among tributaries, adjacent waters, and the downstream traditional navigable waters, interstate waters, or the territorial seas, a significant nexus exists that warrants making those categories of waters jurisdictional by rule.

States and tribes play a vital role in the implementation and enforcement of the CWA. Section 101(b) of the CWA states that it is Congressional policy to preserve the primary responsibilities and rights of states to prevent, reduce, and eliminate pollution, to plan the development and use of land and water resources, and to consult with the Administrator with respect to the exercise of the Administrator’s authority

under the CWA.

Of particular importance, states and tribes may be authorized by the EPA to administer the permitting programs of sections 402 and 404. Forty-six states and the Virgin Islands are authorized to administer the NPDES program under section 402, while two states administer the section 404 program. Additional CWA programs that utilize the

definition of ‘‘waters of the United States’’ and are of importance to the

states and tribes include the section 311 oil spill prevention and response program, the water quality standards and total maximum daily load programs under section 303, and the section 401 state water quality certification process.

States and tribes, consistent with the CWA, retain full authority to implement their own programs to more broadly or more fully protect the waters in their state. Under section 510 of the Act, unless expressly stated in the CWA, nothing in the Act precludes or denies the right of any state or tribe to establish more protective standards or limits than the Federal CWA. Many states and tribes, for example, protect groundwater, and some others protect

wetlands that are vital to their environment and economy but which are outside the regulatory jurisdiction of the CWA. Nothing in this proposed rule would limit or impede any existing or

future state or tribal efforts to further protect their waters. In fact, providing greater clarity regarding what waters are subject to CWA jurisdiction will reduce the need for permitting authorities, including the states and tribes that have

authorized section 402 and 404 CWA permitting programs, to makejurisdictional determinations on a casespecific basis, leaving them with more resources to protect their waters.


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This proposal also recognizes the unique role of states related to water quantity and as stated in the CWA. The proposal does not affect Congressional policy not to supersede, abrogate or otherwise impair the authority of each state to allocate quantities of water within its jurisdiction and neither does it affect the policy of Congress that nothing in the CWA shall be construed to supersede or abrogate rights to quantities of water which have been established by any state. CWA section 101(g).

While a principal goal of this rulemaking is to improve clarity for determining jurisdiction under the CWA in light of the two most recent Supreme

Court cases with the dual benefits of improving certainty and greater efficiency for determining whether waters are covered, there are other tools and approaches underway to increase efficiency as well. For example, to improve efficiencies, the EPA and the Corps are working in partnership with states to develop new tools and resources that have the potential to improve precision of desk based jurisdictional determinations at lower cost and improved speed than the existing primarily field-based approaches. In the normal course of making jurisdictional determinations,

information derived from field observation is not always required in cases where a ‘‘desktop’’ analysis

furnishes sufficient information to make the requisite findings. However, for more complex or difficult jurisdictional determinations, it may be helpful to supplement such information with field

observation.

EPA and the Corps are very interested in identifying other emerging technologies or approaches that would save time and money and improve efficiency for regulators and the regulated community in determining which waters are subject to CWA jurisdiction. The agencies specifically invite comment on this topic.

The proposed rule will benefit the nation by helping to protect the services and functions these important water bodies provide consistent with the overarching objective of the CWA.

B. The Clean Water Act and Regulatory Definition of ‘‘Waters of the United

States’’

The Federal Water Pollution Control Act Amendments, now known as the Clean Water Act, were enacted in 1972. The objective of the CWA is to restore and maintain the chemical, physical, and biological integrity of the Nation’s waters. CWA section 101(a). Its specific provisions were designed to improve the protection of the nation’s waters provided under earlier statutory

schemes such as certain sections of the Rivers and Harbors Appropriations Act of 1899 (‘‘RHA’’) (33 U.S.C. 03, 407, 411) and the Federal Water Pollution Control Act of 1948 (62 Stat. 1155) and its subsequent amendments through 1970. The jurisdictional scope of the CWA is ‘‘navigable waters,’’ defined in

the statute as ‘‘waters of the United States, including the territorial seas.’’ CWA section 502(7). The CWA leaves it to the agencies to define the term ‘‘waters of the United States.’’ Existing agency regulations define ‘‘waters of the United States’’ as traditional navigable waters, interstate waters, all other

waters that could affect interstate or foreign commerce, impoundments of waters of the United States, tributaries, the territorial seas, and adjacent wetlands. 33 CFR 328.3; 40 CFR 230.3(s). Counterpart and substantively similar regulatory definitions appear at
40 CFR 110.1, 112.2, 116.3, 117.1, 122.2, 232.2, 300.5, part 300 App. E, 302.3 and

401.11.

The current regulatory definition of ‘‘waters of the United States’’ provides two specific exclusions from ‘‘waters of

the United States.’’ Waste treatment systems designed to meet the requirements of the CWA and prior converted cropland are not ‘‘waters of the United States’’ under the agencies’ current regulations. Under the regulations for prior converted cropland, notwithstanding the determination of an area’s status as prior converted cropland by any other Federal agency, for the purposes of the Clean Water Act, the final authority regarding Clean Water Act jurisdiction remains with EPA. 33 CFR 328.3(a)(8).

C. Background on Scientific Review and Significant Nexus Analysis

1. Scientific Synthesis

EPA’s Office of Research andDevelopment prepared a draft peerreviewed synthesis of published peerreviewed scientific literature discussing the nature of connectivity and effects of

streams and wetlands on downstream waters (U.S. Environmental Protection Agency, Connectivity of Streams and

Wetlands to Downstream Waters: A Review and Synthesis of the Scientific Evidence, (Washington, DC: U.S. Environmental Protection Agency, 2013), (the ‘‘Report’’)). The draft Report provides a review and synthesis of the scientific information pertaining to chemical, physical, and biological connections from streams, wetlands, and open waters such as oxbow lakes, to downstream larger water bodies such as rivers, lakes, and estuaries in

watersheds across the United States and the strength of those connections. While

the scientific literature does not use the term ‘‘significant nexus,’’ there is a substantial body of scientific literature on the chemical, physical, and biological connections between tributaries and adjacent waters and

‘‘other waters’’ and the downstream larger waters, and on the strength and

the effect of these connections.

Connectivity is a foundational concept in hydrology and freshwater ecology. Connectivity is the degree to which components of a system are joined, or connected, by various transport mechanisms and is determined by the characteristics of both the physical landscape and the biota of the specific system. The

structure and function of downstream waters are highly dependent on the constituent materials contributed by and transported through waters located

elsewhere in the watershed. Connectivity for purposes of interpreting the scope of ‘‘waters of the

United States’’ under the CWA serves to

demonstrate the ‘‘nexus’’ between upstream water bodies and the downstream traditional navigable water, interstate water, or the territorial sea. Based on the literature, the Office of Research and Development was able to assess the types of connections between the tributaries and adjacent waters and the chemical, physical, and biological integrity of downstream traditional navigable waters, interstate waters, and

the territorial seas.

However, as Justice Kennedy found in Rapanos, a mere hydrologic connection may not suffice in all cases to establish CWA jurisdiction and there needs to be ‘‘some measure of the significance of the

connection for downstream water quality.’’ 547 U.S. at 784–785 (‘‘mere hydrologic connection should not suffice in all cases; the connection may be too insubstantial for the hydrologic linkage to establish the required nexus with navigable waters as traditionally understood’’). The literature does not use the term ‘‘significant’’ but does provide information on the strength of the effects on the chemical, physical, and biological functioning of the

downstream water bodies from the connections among tributaries and adjacent waters and ‘‘other waters’’ and

those downstream waters.

While ‘‘strength’’ of connections to and effects on the integrity of

downstream waters and the ‘‘significance’’ of the nexus to the integrity of downstream waters are clearly related inquiries, ‘‘significant’’ is

not a scientific term but rather a


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determination of the agencies in light of

the law and science. The relative strength of downstream effects informs the agencies’ conclusions about the significance of those effects for purposes of interpreting the CWA. The data and conclusions in the Report concerning the strength of the relevant connections and effects of certain types of waters on downstream waters provide a foundation for the agencies’

determinations that certain waters have effects on the chemical, physical, and biological integrity of traditional navigable waters, interstate waters, or the territorial seas that are ‘‘significant’’ and thus constitute a significant nexus. As clarified in the proposed definition of ‘‘significant nexus’’ and consistent with Justice Kennedy’s guidance, for an effect to be significant it must be more than speculative or insubstantial.

The Office of Research and Development’s review and synthesis of more than a thousand publications from peer-reviewed scientific literature

focuses on evidence of those connections from various categories of waters, evaluated singly or in aggregate,

which affect downstream waters and the strength of that effect. Much of the

scientific literature relied on does not use the terms traditional navigable waters, interstate waters, or the territorial seas. However, evidence of strong chemical, physical, and biological connections to larger rivers, estuaries and lakes applies to that subset of rivers, estuaries and lakes that are traditional navigable waters, interstate waters, or the territorial seas. The objectives of the Report are (1) to provide a context for considering the

evidence of connections between downstream waters and their tributary waters, and (2) to summarize current understanding about these connections, the factors that influence them, and the mechanisms by which the connections

affect the function or condition of

downstream waters. The connections

and mechanisms discussed in the Report include transport of physical materials and chemicals such as water, wood, sediment, nutrients, pesticides, and mercury; functions that adjacent waters perform, such as storing and cleansing water; movement of organisms or their seeds and eggs; and hydrologic and biogeochemical interactions occurring in and among surface and groundwater flows, including hyporheic zones and alluvial aquifers.

The Report concludes that the scientific literature clearly demonstrates that streams, regardless of their size or how frequently they flow, strongly

influence how downstream waters function. Streams supply most of the water in rivers, transport sediment and organic matter, provide habitat for many species, and take up or change nutrients that could otherwise impair downstream waters. The Report also concludes that wetlands and open waters in floodplains of streams and rivers and in riparian areas (transition areas between terrestrial and aquatic ecosystems) have a strong influence on

downstream waters. Such waters act as the most effective buffer to protect downstream waters from nonpoint source pollution (such as nitrogen and phosphorus), provide habitat for breeding fish and aquatic insects that also live in streams, and retain floodwaters, sediment, nutrients, and

contaminants that could otherwise negatively impact the condition or

function of downstream waters.

Regarding wetlands and open waters located outside of floodplains and riparian areas, the Report finds that they provide many benefits to rivers, lakes,

and other downstream waters. If the wetland or open water has a surface or

shallow subsurface water connection to the river network, it affects the

condition of downstream waters. Where the wetland or open water is not connected to the river network through surface or shallow subsurface water, the type and degree of connectivity varies geographically, topographically, and ecologically, such that the significance

of the connection is difficult to generalize across the entire group of

waters.

Lastly, the Report concludes that to understand the health, behavior, and sustainability of downstream waters, the

effects of small water bodies in a

watershed need to be considered in aggregate. The contribution of material by, or an important water-retention function of, a particular stream, other open water, or wetland might be small, but the aggregate contribution by an entire class of streams, other open waters, and wetlands (e.g., all ephemeral streams in the river network)

can be substantial.

In the proposed rule, the agencies interpreted the scope of ‘‘waters of the

United States’’ in the CWA based on the

information and conclusions in the Report, other relevant scientific literature, the agencies’ technical expertise, and the objectives and requirements of the Clean Water Act. In light of this information, the agencies made judgments about the nexus

between the relevant waters and the significance of that nexus and concluded that tributaries and adjacent waters, each as defined by the proposed rule, have a significant nexus such that they are appropriately jurisdictional by

rule.

The Report is currently undergoing peer review by EPA’s Scientific Advisory Board (SAB) and is available

at http://yosemite.epa.gov/sab/ sabproduct.nsf/fedrgstr

_activites/ Watershed%20Connectivity%20Report? OpenDocument. A previous version of the Report dated October 11, 2011 underwent an independent peer review organized by the Eastern Research Group, Inc. (ERG). The purpose of the ERG-organized peer review was to

determine whether the review and interpretation of the scientific literature was complete and correct, and if the conclusions in the Report were supported by the evidence. ERG was responsible for identifying and selecting the expert reviewers, managing the review, organizing and facilitating a one-day peer review meeting, and preparing the peer review summary report. ERG provided the reviewers with

a letter of instruction and the technical charge, which asked for their comments on the various aspects of the draft
report.

ERG convened the one-day meeting on January 31, 2012, in Washington, DC. The meeting was closed to the public

and considered an internal EPA deliberative process. Observers from EPA and the Corps attended to listen to

the discussions. At the close of the meeting, the reviewers developed some brief highlights of their discussions,which were provided with written postmeeting comments from individual reviewers in a report from ERG titled

‘‘Peer Review Meeting of EPA’s Draft Report: Connectivity of Streams and

Wetlands to Downstream Waters—A Review and Synthesis of the Scientific Evidence, Post-Meeting Comments,’’ dated February 16, 2012. The Office of Research and Development revised its Report in response to the peer review comments and submitted the Report to the SAB for peer review and a public process. This peer review report is available in the docket for the proposed

rule.

The agencies have identified key aspects of the Report throughout this preamble and in Appendix A. The Report summarizes and assesses much of the currently available scientific literature that is part of the administrative record for this proposal, and informs the agencies during this rulemaking. Additional data and

information will become available during the rulemaking process, including that provided during the public comment process, and by additional research, studies, and investigations that take place before the


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rulemaking process is concluded. The agencies have relied on the best

available scientific data and information—peer-reviewed literature— and would find, to the extent possible, additional peer-reviewed literature to be

the most useful submissions. At the conclusion of the rulemaking process, the agencies will review the entirety of the completed administrative record, including the final Report reflecting SAB review, and make any adjustments to the final rule that are appropriate based on this record. As noted below, the agencies particularly intend to review the rule provisions related to ‘‘other waters’’ in light of this record, and are soliciting comment on several alternative approaches to applying the science and the law for determining whether ‘‘other waters’’ are similarly situated and have a ‘‘significant nexus’’ to a traditional navigable water, interstate water, or the territorial seas.

2. Summary of Significant Nexus

Conclusions

As the agencies developed this proposed definition of ‘‘waters of the United States,’’ the agencies carefully

considered available scientific literature and propose a rule consistent with their conclusions that a particular category of

waters either alone or in combination with similarly situated waters in the region, significantly affects the chemical, physical, or biological integrity of traditional navigable waters, interstate waters, or the territorial seas.

As discussed in this preamble and Appendix A, tributaries as proposed to be defined perform the requisite

functions for them to be considered ‘‘waters of the United States’’ by rule. Tributary streams exert a strong

influence on the character and functioning of downstream traditional navigable waters, interstate waters, and the territorial seas, either individually or cumulatively. All tributary streams, including perennial, intermittent, and ephemeral streams, are physically and chemically connected to downstream traditional navigable waters, interstate waters, and the territorial seas via

channels and associated alluvial deposits where water and other materials are concentrated, mixed, transformed, and transported. Headwater streams (which can be ephemeral, intermittent or perennial), in particular, supply most of the water to downstream traditional navigable waters, interstate waters, and the

territorial seas and are the most abundant stream-type in most river networks. In addition to water, tributary streams supply sediment, wood, organic matter, nutrients, chemical contaminants, and many of the organisms found in downstream traditional navigable waters, interstate waters, and the territorial seas. Tributary streams are biologically

connected to downstream traditional navigable waters, interstate waters, and the territorial seas by dispersal and migration of aquatic and semi-aquatic organisms, including fish, amphibians, plants, and invertebrates, that use both upstream and downstream habitats during one or more stages of their life cycles, or provide food resources to downstream communities. Chemical, physical, and biological connections between tributary streams and downstream traditional navigable waters, interstate waters, and the territorial seas interact via processes such as nutrient spiraling, in which tributary stream communities assimilate and chemically transform large quantities of nitrogen that would otherwise increase nutrient loading

downstream.

As discussed in this preamble and Appendix A, adjacent waters, as defined in this proposal, perform the requisite

functions for them to be considered ‘‘waters of the United States’’ by rule. Adjacent waters are either directly chemically, physically, or biologically connected with traditional navigable waters, interstate waters, and the territorial seas they are adjacent to, or they are connected to such waters through tributaries. These chemical, physical, and biological connections affect the integrity of downstream traditional navigable waters, interstate waters, and the territorial seas through the export of channel-forming sediment and woody debris, storage of local groundwater sources of baseflow for downstream waters and their tributaries, and transport of organic matter. Wetlands and open waters located in riparian and floodplain areas remove and transform nutrients such as nitrogen and phosphorus. They provide nursery habitat for fish, and colonization opportunities for stream invertebrates. Adjacent waters, including those located in riparian and floodplain areas, serve an important role in the integrity of traditional navigable waters, interstate waters, and the territorial seas because they also act as sinks for water, sediment, nutrients, and contaminants that could otherwise negatively impact traditional navigable waters, interstate waters, and the territorial seas.

Finally, some non-adjacent waters may have, in certain circumstances, a significant nexus to traditional navigable waters, interstate waters, and the territorial seas, but at this time the agencies are not proposing that a category of such ‘‘other waters’’ is jurisdictional by rule. These ‘‘other waters’’ may provide numerous functions of potential benefit to traditional navigable waters, interstate waters, and the territorial seas, including storage of floodwater; retention of nutrients, metals, and pesticides; and re-charge of groundwater

sources of river baseflow. The functions of these ‘‘other waters’’ may affect downstream traditional navigable waters, interstate waters, and the territorial seas, depending on the

characteristics of the connection to the river network. For ‘‘other waters,’’ connectivity varies within a watershed and over time, making it difficult to generalize about their connections to, or isolation from, traditional navigable waters, interstate waters, and the

territorial seas. These ‘‘other waters’’ would be evaluated on a case-specific basis under the proposed rule.

Under the existing regulations, ‘‘other waters’’ (such as intrastate rivers, lakes

and wetlands that are not otherwise jurisdictional under other sections of the rule) could be determined to be jurisdictional if the use, degradation or

destruction of the water could affect interstate or foreign commerce. Jurisdictional decisions for these waters are being made on a case-specific basis. As a practical matter in the past, the agencies generally relied on the presence of migratory birds to indicate

an effect on interstate commerce. In 2001, the Supreme Court in SWANCC rejected the use of migratory birds as a sole basis to establish jurisdiction over such ‘‘isolated’’ intrastate nonnavigable

waters.

The proposed rule provides that ‘‘other waters’’ can be jurisdictional where there is a case-specific showing of a significant nexus to traditional navigable waters, interstate waters, or the territorial seas. ‘‘Significant nexus’’

is not itself a scientific term. The

science of connections and effects on the chemical, physical, or biological integrity of traditional navigable waters, interstate waters, or the territorial seas informs an analysis of the facts and circumstances of the waters being considered under a ‘‘significant nexus’’ analysis.

Scientific literature establishes that ‘‘other waters’’ can have a relationship

to each other and connections downstream that affect the chemical, physical, or biological integrity of traditional navigable waters, interstate waters, or the territorial seas. This relationship is not an all or nothing situation. The existence of a connection, a nexus, does not by itself establish that it is a ‘‘significant nexus.’’ There is a


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gradient in the relation of waters to each other, and this is documented in theReport. The agencies propose a casespecific analysis in establishing jurisdiction over these ‘‘other waters’’ as consistent with the current science, the CWA, and the caselaw. A case-specific analysis allows for a determination of jurisdiction at the point on the gradient in the relationship that constitutes a ‘‘significant nexus.’’

The support for a determination that the nexus is significant will be based on

a record that documents the scientific basis for concluding which functions are provided by the waters and why their effects on a traditional navigable water, interstate water, or the territorial seas are significant, including that they are more than speculative or insubstantial. The agencies considered multiple options for determining how

best to balance the science and the policy options available to address ‘‘other waters.’’ Those options ranged from establishing jurisdiction over all

‘‘other waters’’ with a nexus to traditionally navigable waters, interstate waters, or the territorial seas, with the agencies determining categorically the nexus to be significant, to declining to assert jurisdiction over any ‘‘other

waters.’’

The agencies did not adopt the all in or the all out approach to ‘‘other

waters.’’ Based on the information currently available in the scientific literature, applicable caselaw, and the agencies’ policy judgment about how best to provide clarity and certainty to the public regarding the jurisdictional status of ‘‘other waters’’ the agencies today propose the case-specific significant nexus analysis presented in this rule and explained in the preamble.

In addition to the proposed ‘‘other waters’’ approach in this rule, the agencies are requesting comment on a range of alternate approaches to inform

their decision on how best to address ‘‘other waters.’’ The agencies will consider the full administrative record, including comments requested and received, and the final Report, as revised in response to the SAB review, when developing the final rule, and may adopt one of the alternative approaches or combination of approaches and the proposal.

The agencies solicit comment on identifying subcategories of ‘‘other waters’’ that have a significant nexus to traditional navigable waters, interstate waters, and the territorial seas and could be jurisdictional by rule, and subcategories of ‘‘other waters’’ where a significant nexus or its absence could

not be determined as a class and could be subject to a case-specific analysis under the rule. The Report indicates that there is evidence of very strong connections in some subcategories that are not included as jurisdictional by rule. The agencies solicit comment on making such subcategories of waters with very strong connections jurisdictional by rule as well as on making subcategories of waters that do not have such connections subject to a case-specific analysis or categorically non-jurisdictional under the rule. Such comment should explain with supporting documentation why a particular subcategory of ‘‘other waters’’ might or might not have a significant nexus to traditional navigable waters, interstate waters, or the territorial seas.

The agencies do not propose absolute standards such as flow rates, surface acres, or a minimum number of

functions for ‘‘other waters’’ to establish a significant nexus. A determination of the relationship of ‘‘other waters’’ to traditional navigable waters, interstate waters, and the territorial seas, and consequently the significance to these waters, requires sufficient flexibility to account for the variability of conditions across the country and the varied functions that different waters provide. The case-specific analysis called for in the proposed rule recognizes geographic and hydrologic variability in determining whether an ‘‘other water’’ or group of ‘‘other waters’’ possesses a ‘‘significant nexus’’ with traditional navigable waters, interstate waters, or

the territorial seas.

III. Proposed Definition of ‘‘Waters of

the United States’’

A. Summary of Proposed Rule

This proposed rule retains much of the structure of the agencies’ longstanding definition of ‘‘waters of the United States,’’ and many of the existing provisions of that definition where

revisions are not warranted. The agencies’ goal is to promulgate a rule

that is clear and understandable and protects the nation’s waters, supported by science and consistent with the law. Continuity with the existing regulations, where possible, will minimize

confusion and will reduce transaction costs for the regulated community and the agencies. To that same end, the agencies also propose, where supported by scientific literature and consistent with the law, bright line categories of

waters that are and are not jurisdictional. Waters in the ‘‘other waters’’ category are not a per se jurisdictional category. While the agencies considered multiple options for addressing jurisdiction over ‘‘other waters,’’ the agencies concluded that they could not determine that all ‘‘other waters’’ were jurisdictional, or that all ‘‘other waters’’ were not jurisdictional. Therefore, the proposed rule requires a case-specific significant nexus

evaluation to determine if such ‘‘other waters’’ are subject to CWA jurisdiction and the agencies are requesting

comment on several alternate approaches, including approaches that would not include case-specific analysis, to inform the final rule. Finally, the agencies are for the first time proposing definitions for some of the terms used in the proposed regulation.

Under section (a) the agencies propose to define the ‘‘waters of the

United States’’ for all sections of the

CWA to mean:

• All waters which are currently used, were used in the past, or may be susceptible to use in interstate or foreign commerce, including all waters which are subject to the ebb and flow of the tide;

• All interstate waters, including interstate wetlands;

• The territorial seas;

• All impoundments of a traditional navigable water, interstate water, the territorial seas or a tributary;

• All tributaries of a traditional navigable water, interstate water, the territorial seas or impoundment;

• All waters, including wetlands, adjacent to a traditional navigable water, interstate water, the territorial seas, impoundment or tributary; and

• On a case-specific basis, other waters, including wetlands, provided that those waters alone, or in combination with other similarly situated waters, including wetlands, located in the same region, have a significant nexus to a traditional navigable water, interstate water or the

territorial seas.

As discussed in further detail below, the agencies do not propose to change the following provisions (although some provisions have been renumbered): Traditional navigable waters ((a)(1), see Section III.B of this preamble); interstate waters ((a)(2), see Section III.C of this preamble); the territorial seas ((a)(3), see Section III.D of this preamble); and impoundments of ‘‘waters of the United States’’ ((a)(4), see Section III.E of this preamble). In paragraph (a)(5), the agencies are proposing that tributaries to waters identified in paragraphs (a)(1) through (a)(4) are ‘‘waters of the United

States.’’ While tributaries are ‘‘waters of the United States’’ under the existing regulation, the agencies propose for the first time a regulatory definition of ‘‘tributary’’ and propose that only those

waters that meet the definition and flow


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6 The terms ‘‘in the region’’ and ‘‘watershed’’ are used interchangeably in this document. The agencies have interpreted ‘‘in the region’’ to mean

the watershed that drains to the nearest water identified in paragraphs (a)(1) through (a)(3), which we refer to as the single point of entry watershed. 

### directly or indirectly to an (a)(1) through (a)(3) water are ‘‘waters of the United States’’ (see Section III.F of this preamble). In paragraph (a)(6), the agencies propose that adjacent waters, rather than simply adjacent wetlands,

are ‘‘waters of the United States.’’ The agencies also propose for the first time to define an aspect of adjacency— ‘‘neighboring’’—and related terms (see Section III.G of this preamble). Finally, the agencies propose to define ‘‘waters

of the United States’’ to include on a case-specific basis, other waters, including wetlands, provided that those waters alone, or in combination with other similarly situated waters, including wetlands, located in the same region, have a significant nexus to a water identified in paragraphs (a)(1) through (3). Unlike the per se jurisdictional categories in paragraphs (a)(1) through (6) of this section, such

‘‘other waters’’ are not per se jurisdictional under (a)(7); rather, these ‘‘other waters’’ are only jurisdictional provided that they have a significant nexus to (a)(1) through (a)(3) waters. Therefore, the agencies are providing a definition of ‘‘significant nexus’’ (see Section III.H of this preamble).

The second section of the proposed regulation, section (b), excludes specified waters from the definition of

‘‘waters of the United States.’’ Those

waters and features would not be

‘‘waters of the United States’’ even if they would otherwise be included within the categories in (a)(1) through (a)(7) above. They are:

• Waste treatment systems, including treatment ponds or lagoons, designed to meet the requirements of the Clean

Water Act.

• Prior converted cropland. Notwithstanding the determination of an area’s status as prior converted cropland by any other Federal agency, for the purposes of the Clean Water Act the final authority regarding Clean Water Act jurisdiction remains with

EPA.

• Ditches that are excavated wholly in uplands, drain only uplands, and have less than perennial flow.

• Ditches that do not contribute flow, either directly or through another water, to a traditional navigable water, interstate water, the territorial seas or a jurisdictional impoundment.

• The following features:

Æ artificially irrigated areas that would revert to upland should application of irrigation water to that

area cease;

Æ artificial lakes or ponds created by excavating and/or diking dry land and used exclusively for such purposes as stock watering, irrigation, settling basins, or rice growing;

Æ artificial reflecting pools or swimming pools created by excavating and/or diking dry land;

Æ small ornamental waters created by excavating and/or diking dry land for primarily aesthetic reasons;

Æ water-filled depressions created incidental to construction activity;

Æ groundwater, including groundwater drained through subsurface drainage systems; and

Æ gullies and rills and non-wetland

swales.

The agencies do not propose any changes to the existing exclusions for waste treatment systems designed consistent with the requirements of the CWA and for prior converted cropland. The CWA and current regulations also provide a number of exemptions from permitting for discharges associated with specific activities. The rule does not affect any of the exemptions from CWA section 404 permitting requirements provided by CWA section 404(f), including those for normal farming, silviculture, and ranching activities. CWA section 404(f); 40 CFR 232.3; 33 CFR 323.4. The rule also does not affect either the existing statutory and regulatory exemptions from NPDES permitting requirements, such as for agricultural stormwater discharges and return flows from irrigated agriculture,

or the status of water transfers. CWA section 402(l)(1); CWA section 402(l)(2); CWA section 502(14); 40 CFR 122.3(f); 40 CFR 122.2. The agencies propose for the first time to exclude by rule in section (b) certain waters and features over which the agencies have as a policy matter generally not asserted jurisdiction (see Section III.I of this preamble).

Finally, in section (c) of the proposed rule the agencies define a number of terms, of which ‘‘adjacent’’ and ‘‘wetlands’’ are unchanged from existing

definitions The term adjacent means bordering, contiguous or neighboring. Waters, including wetlands, separated

from other waters of the United States by man-made dikes or barriers, natural river berms, beach dunes and the like are ‘‘adjacent waters.’’ The term neighboring, for purposes of the term ‘‘adjacent’’ in this section, includes waters located within the riparian area or floodplain of a water identified in paragraphs (a)(1) through (5) of this section, or waters with a shallow subsurface hydrologic connection or confined surface hydrologic connection to such a jurisdictional water. The term riparian area means an area bordering a

water where surface or subsurface hydrology directly influence the ecological processes and plant and animal community structure in that area. Riparian areas are transitional areas between aquatic and terrestrial ecosystems that influence the exchange of energy and materials between those ecosystems. The term floodplain means an area bordering inland or coastal waters that was formed by sediment deposition from such water under present climatic conditions and is inundated during periods of moderate to high water flows.

The term tributary means a water physically characterized by the presence of a bed and banks and ordinary high water mark, as defined at 33 CFR 328.3(e), which contributes flow, either directly or through another water, to a water identified in paragraphs (a)(1) through (4). In addition, wetlands, lakes, and ponds are tributaries (even if they lack a bed and banks or ordinary high water mark) if they contribute flow, either directly or through another water to a water identified in paragraphs (a)(1) through (3). A water that otherwise qualifies as a tributary under this

definition does not lose its status as a tributary if, for any length, there are one or more man-made breaks (such as bridges, culverts, pipes, or dams), or one or more natural breaks (such as wetlands at the head of or along the run of a stream, debris piles, boulder fields, or a stream that flows underground) so long as a bed and banks and an ordinary high water mark can be identified upstream of the break. A tributary, including wetlands, can be a natural, man-altered, or man-made water and includes waters such as rivers, streams, lakes, ponds, impoundments, canals, and ditches not excluded in paragraphs (b)(3) or (4).

The term wetlands means those areas that are inundated or saturated by surface or groundwater at a frequency and duration sufficient to support, and

that under normal circumstances do support, a prevalence of vegetation typically adapted for life in saturated soil conditions. Wetlands generally include swamps, marshes, bogs and

similar areas.

The term significant nexus means that a water, including wetlands, either

alone or in combination with other similarly situated waters in the region (i.e., the watershed that drains to the nearest water identified in paragraphs (a)(1) through (3)),6 

### significantly affects


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7 Link to Michigan’s and New Jersey’s Memorandum of Agreement with the Army Corps of Engineers identifying which waters of the US remain under the Corps’ jurisdiction. http://water. epa.gov/type/wetlands/initiative

_index.cfm

. 

### the chemical, physical, or biological integrity of a water identified in paragraphs (a)(1) through (3). For an effect to be significant, it must be more than speculative or insubstantial. Other waters, including wetlands, are similarly situated when they perform

similar functions and are located sufficiently close together or sufficiently

close to a ‘‘water of the United States’’ so that they can be evaluated as a single landscape unit with regard to their effect on the chemical, physical, or biological integrity of a water identified in paragraphs (a)(1) through (3).

B. Traditional Navigable Waters

EPA and the Corps’ existing regulations include within the

definition of ‘‘waters of the United States’’ all waters that are currently used, or were used in the past, or may be susceptible to use in interstate or foreign commerce, including all waters which are subject to the ebb and flow of

the tide. See, e.g., 33 CFR 328.3(a)(1); 40 CFR 230.3(s)(1); 40 CFR 122.2 (‘‘waters of the U.S.’’). This section of the regulation encompasses those waters

that are often referred to as ‘‘traditional navigable waters.’’ The agencies do not propose to make any changes to this section of the regulation. See, Appendix B, Legal Analysis.

For purposes of CWA jurisdiction,

waters will be considered traditional navigable waters, and thus (a)(1) waters under the proposed rule, if:

• They are subject to section 9 or 10

of the Rivers and Harbors Appropriations Act of 1899;

• A Federal court has determined that the water body is navigable-in-fact under Federal law;

• They are waters currently being used for commercial navigation, including commercial waterborne recreation (for example, boat rentals, guided fishing trips, or water ski tournaments);

• They have historically been used for commercial navigation, including commercial waterborne recreation; or

• They are susceptible to being used in the future for commercial navigation, including commercial waterborne recreation. Susceptibility for future use may be determined by examining a number of factors, including the physical characteristics and the capacity

of the water to be used in commercial navigation, including commercial recreational navigation (for example, size, depth, and flow velocity), and the

likelihood of future commercial navigation, including commercial

waterborne recreation. While a traditional navigable water need not be capable of supporting navigation at all times, the frequency, volume, and

duration of flow are relevant considerations for determining if a water body has the physical characteristics suitable for navigation. A

likelihood of future commercial navigation, including commercial waterborne recreation, can be demonstrated by current boating or canoe trips for recreation or other purposes. A determination that a water is susceptible to future commercial navigation, including commercial waterborne recreation, must be supported by evidence.

This proposal does not affect the scope of waters subject to state assumption of the section 404 regulatory program under section 404(g) of the

CWA. See CWA section 404(g). The scope of waters that are subject to state and tribal permitting is a separate inquiry and must be based on the statutory language in CWA section 404. States administer approved CWA section 404 programs for ‘‘waters of the United States’’ within the state, except those waters remaining under Corps jurisdiction pursuant to CWA section 404(g)(1) as identified in a Memorandum of Agreement 7 

### between the state and the Corps. 40 CFR 233.14; 40 CFR 233.70(c)(2); 40 CFR 233.71(d)(2). Clarification of waters that are subject to assumption by states or tribes or retention by the Corps could be made through a separate process under section 404(g).

C. Interstate Waters

The existing EPA and Corps regulations define ‘‘waters of the United States’’ to include interstate waters, including interstate wetlands and the agencies’ proposal today does not change that provision of the regulations.

Interstate waters would continue to be

‘‘waters of the United States’’ even if they are not navigable for purposes of Federal regulation under (a)(1) and do not connect to such waters. Moreover,

because interstate waters are ‘‘waters of the United States’’ under the CWA, the agencies are proposing to continue to include as jurisdictional tributaries to interstate waters, waters adjacent to interstate waters, waters adjacent to tributaries of interstate waters, and ‘‘other waters’’ that have a significant

nexus to interstate waters.

As discussed in more detail in Appendix B to this preamble, the language of the CWA indicates that Congress intended the term ‘‘navigable waters’’ to include interstate waters without imposing a requirement that they be traditional navigable waters

themselves or be connected to traditional navigable waters. The precursor statutes to the CWA always subjected interstate waters and their tributaries to Federal jurisdiction. The text of the CWA, specifically CWA section 303 that establishes ongoing requirements for interstate waters, in conjunction with the definition of navigable waters, provides clear indication of Congress’ intent to protect interstate waters that were previously subject to Federal regulation. Other provisions of the statute provide additional textual evidence of the scope of the primary jurisdictional term of the

CWA.

While congressional intent is clear, the agencies also have a longstanding regulatory interpretation that interstate waters fall within the scope of CWA jurisdiction. The agencies’ interpretation was promulgated contemporaneously with the passage of

the CWA and is consistent with the statutory and legislative history of the CWA. Furthermore, the Supreme Court

has never addressed the CWA’s coverage of interstate waters, and it is

not reasonable to read its decisions in

SWANCC and Rapanos to question the jurisdictional status of interstate waters or to impose additional jurisdictional requirements on interstate waters.

It is reasonable to assert jurisdiction over tributaries, adjacent wetlands and ‘‘other waters’’ that have a significant

nexus to interstate waters consistent with the framework established by Justice Kennedy in Rapanos for establishing jurisdiction over waters with a significant nexus to traditional navigable waters. Justice Kennedy’s

standard seeks to ensure that waters Congress intended to subject to Federal jurisdiction are indeed protected, both by recognizing that waters and wetlands with a significant nexus to traditional navigable waters and interstate waters have important beneficial effects on those waters, and by recognizing that polluting or destroying waters with a significant nexus can harm downstream jurisdictional waters. As Congress intended to protect interstate waters, the agencies propose to also protect interstate waters by defining ‘‘waters of

the United States’’ to include tributaries to interstate waters, waters adjacent to interstate waters, waters adjacent to tributaries of interstate waters, and ‘‘other waters’’ that have a significant

nexus to interstate waters. For additional discussion of the agencies’ interpretation of the CWA with respect


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to interstate waters, see Appendix B to this preamble.

D. Territorial Seas

The CWA and its existing regulations

include ‘‘the territorial seas’’ as a ‘‘water of the United States.’’ The agencies propose to make no changes to that provision of the regulation other than to move the provision to earlier in the regulation. The CWA defines ‘‘navigable

waters’’ to include the territorial seas at section 502(7). The CWA goes on to

define the ‘‘territorial seas’’ as ‘‘the belt

of the seas measured from the line of ordinary low water along that portion of

the coast which is in direct contact with the open sea and the line marking the seaward limit of inland waters, and extending seaward a distance of three

miles.’’ The territorial seas establish the

seaward limit of ‘‘waters of the United

States.’’ As the territorial seas are also clearly protected by the CWA (they are also traditional navigable waters), it is reasonable to use for protecting the territorial seas Justice Kennedy’s significant nexus framework that protects traditional navigable waters. The proposed rule reflects that.

E. Impoundments

The agencies do not propose to make any substantive changes to the existing regulatory language with respect to impoundments of waters otherwise

defined as ‘waters of the United States’ under this definition. The changes proposed are clarifying.

Impoundments are jurisdictional because as a legal matter an impoundment of a ‘‘water of the United

States’’ remains a ‘‘water of the United

States’’ and because scientific literature demonstrates that impoundments continue to significantly affect the chemical, physical, or biological integrity of downstream waters traditional navigable waters, interstate waters, or the territorial seas. The Supreme Court has confirmed that damming or impounding a ‘‘water of the

United States’’ does not make the water non-jurisdictional. See S. D. Warren Co.

v. Maine Bd. of Envtl. Prot., 547 U.S. 370, 379 n.5 (2006) (‘‘[N]or can we agree

that one can denationalize national waters by exerting private control over them.’’). Similarly, when presented with a tributary to the Snake River which flows only about two months per year because of an irrigation diversion structure installed upstream, the Ninth Circuit has opined ‘‘it is doubtful that a

mere man-made diversion would have turned what was part of the waters of the United States into something else and, thus, eliminated it from national

concern.’’ U.S. v. Moses, 496 F.3d 984 (9th Cir. 2007), cert. denied, 554 U.S. 918 (2008). As a matter of policy and law, impoundments do not de-federalize a water, even where there is no longer flow below the impoundment. Where

flow continues below the impoundment, it is straightforward to analyze the stream network, above and below the impoundment, for connection to downstream traditional navigable waters, interstate waters, or the

territorial seas.

The agencies also note that an impoundment of a water that is not a

‘‘water of the United States’’ can become jurisdictional if, for example, theimpounded waters become navigable-infact and covered under paragraph (a)(1)

of the rule.

The existing agency regulations provide that impoundments of ‘‘waters

of the United States’’ remain ‘‘waters of the United States’’ and the agencies do not propose any substantive revisions to that component of the regulation. In addition, tributaries to an impoundment

of a ‘‘water of the United States’’ are

‘‘waters of the United States’’ under this proposed rule. As a matter of law and science, an impoundment does not cut off a connection between upstream tributaries and a downstream (a)(1) through (a)(3) water, so tributaries above the impoundment are still considered tributary to a downstream (a)(1) through (a)(3) water even where the flow of water is impeded due to the impoundment. Scientific literature, as well as the agencies’ scientific and technical expertise, and practical knowledge confirm that impoundments have chemical, physical, and biological effects on downstream waters (see Appendix A, Scientific Evidence).

Appendix A discusses the conclusion

that it is reasonable to maintain jurisdiction over impoundments of ‘‘waters of the United States’’ not only as a legal matter, but because impoundments do not sever the effects the impounded ‘‘waters of the United States’’ have on the chemical, physical, or biological integrity of (a)(1) through (a)(3) waters.

F. Tributaries

Under this proposal, the agencies provide a definition of ‘‘tributary’’ supported by the scientific literature. The agencies also propose that all waters that meet the proposed definition of tributary are ‘‘waters of the United States’’ by rule, unless excluded under section (b), because tributaries and the ecological functions they provide, alone

or in combination with other tributaries in the watershed, significantly affect the chemical, physical, and biological integrity of traditional navigable waters, interstate waters, and the territorial seas.

With today’s proposed regulation, the agencies confirm that these tributary waters have a significant nexus to a traditional navigable water, interstate water, or territorial sea such that they

are ‘‘waters of the United States’’without the need for a separate, casespecific significant nexus analysis. In practice, under this proposal any water that meets the definition of tributary (and is not excluded under section (b) of the proposed rule) is a ‘‘water of the United States,’’ and the agencies would only need to determine that a water meets the definition of ‘‘tributary.’’ See Appendix A, Scientific Evidence (Part I, Discussion of Major Conclusions 2.A; Part II, i); and Appendix B, Legal Analysis.

Tributaries have a significant impact on the chemical, physical, and biological integrity of waters into which they eventually flow—including traditional navigable waters, interstate waters, and the territorial seas—and they have a significant nexus and thus are jurisdictional as a category. The great majority of tributaries are headwater streams, and whether they are perennial, intermittent, or ephemeral, they play an important role in the transport of water, sediments, organic matter, nutrients, and organisms

to downstream environments. Tributaries serve to store water, thereby reducing flooding, provide biogeochemical functions that help maintain water quality, trap and transport sediments, transport, store and modify pollutants, provide habitat for plants and animals, and sustain the biological productivity of downstream rivers, lakes and estuaries.

1. What is a ‘‘tributary’’ for purposes of the proposed regulation?

The proposed rule defines ‘‘tributary’’ as a water physically characterized by the presence of a bed and banks and ordinary high water mark, as defined at 33 CFR 328.3(e), which contributes flow, either directly or through another water, to a water identified in paragraphs (a)(1) through (4). In addition, wetlands, lakes, and ponds are tributaries (even if they lack a bed and banks or ordinary high water mark) if they contribute flow, either directly or through another water to a water identified in paragraphs (a)(1) through (3). A water that otherwise qualifies as a tributary under this definition does not lose its status as a tributary if, forany length, there are one or more manmade breaks (such as bridges, culverts, pipes, or dams), or one or more natural breaks (such as wetlands at the head of


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or along the run of a stream, debris piles, boulder fields, or a stream that flows underground) so long as a bed and banks and an ordinary high water mark can be identified upstream of the break. A tributary, including wetlands, can be a natural, man-altered, or man-made

water and includes waters such as rivers, streams, lakes, ponds, impoundments, canals, and ditches not excluded in paragraph (b)(3) or (4).

While the agencies have not defined tributary in any previous regulation, this proposed definition is consistent with long-standing practice and historical implementation of CWA programs. It is important to note that today’s proposed

definition also is based on best available

science and the intent of the CWA.

To meet this definition, a water need not contribute flow directly to an (a)(1) through (a)(4) water. As the definition makes clear, the water may contribute flow directly or may contribute flow to

another water or waters which eventually flow into an (a)(1) through (a)(4) water. Essentially, the water must be part of a tributary system that drains to an (a)(1) through (a)(4) water. Under the proposed definition, to be a ‘‘tributary,’’ in addition to requiring that

a water contribute flow to a traditional navigable water, interstate water or the territorial sea, the water must also have a bed and banks and ordinary high water mark (except where a wetland is a tributary), because these features generally are physical indicators of flow. The agencies identified these tributary characteristics as indicative that the water is the type of hydrologic feature protected under the CWA because, for example, of a tributary’s ability to transport pollutants to downstream traditional navigable waters, interstate waters, and the territorial seas, and thereby have a significant effect on the chemical, physical, or biological integrity of a water identified in paragraphs (a)(1) through (a)(4).

The flow in the tributary may be ephemeral, intermittent or perennial, but the tributary must drain, or be part of a network of tributaries that drain, into an (a)(1) through (a)(4) water under today’s proposed rule. When considering whether the tributary being evaluated eventually flows to an (a)(1) through (a)(4) water, the tributary connection may be traced using direct observation or U.S. Geological Survey maps, aerial photography or other reliable remote sensing information, or other appropriate information. A bed and banks and ordinary high water mark (OHWM) generally are physical indicators of water flow. These physical indicators can be created by ephemeral, intermittent, and perennial flows.

The agencies’ proposed definition of ‘‘tributary’’ includes waters such as rivers, streams, lakes, impoundments, wetlands, canals, and ditches not excluded in section (b) that, either directly or through other tributaries, convey water to traditional navigable waters, interstate waters, or the territorial seas. A tributary is a longitudinal surface feature that results

from directional surface water movement and sediment dynamics demonstrated by the presence of bed and banks, bottom and lateral boundaries, or other indicators of

OHWM. The movement of water through a tributary can transport pollutants to downstream (a)(1) through (a)(4) waters, as either chemicals dissolved or suspended in the water

column or adsorbed to sediment particles.

The existing Corps regulations define

OHWM as the line on the shore established by the fluctuations of water and indicated by physical characteristics such as a clear, natural line impressed on the banks, shelving, changes in the character of soil, destruction of terrestrial vegetation, the presence of litter and debris, or other appropriate means that consider the characteristics of the surrounding areas. 33 CFR 328.3(e). That definition is not changed by today’s proposed rule. In many tributaries, the bed is that part of the channel below the OHWM, and the

banks often extend above the OHWM. Indicators of an OHWM may vary from region to region across the country.

Under the proposed definition of tributary, the upper limit of a tributary is established where the channel begins. Note that wetlands can be providing flow into a tributary at the upper limit

of the channel and these would also be jurisdictional. The OHWM generally defines the lateral limits of a water, and its absence generally determines whether a tributary’s channel or bed and banks has ended such that the upper limit of the jurisdictional tributary isidentified. However, a natural or manmade break in bed and banks or OHWM does not constitute the upper limit of a tributary where bed and banks or OHWM can be found farther upstream,

as discussed below.

In many tributaries, there are often

natural or man-made breaks in the presence of a bed and banks or ordinary high water mark while hydrologic connectivity remains. For example, in some regions of the country where there is a very low gradient, the banks of a tributary may be very low or may even disappear at times. Also, in many intermittent and ephemeral tributaries, including dry-land systems in the arid and semi-arid west, OHWM indicators

can be discontinuous within an individual tributary due to the variability in hydrologic and climatic influences. The agencies proposed definition of ‘‘tributary’’ addresses these

circumstances and states that waters that meet the definition of tributary

remain tributaries even if such breaks occur. A water that otherwise qualifies as a tributary under the proposed

definition does not lose its status as a tributary if, for any length, there are one or more man-made breaks (such as bridges, culverts, pipes, or dams), or one or more natural breaks (such as debris piles, boulder fields, or a stream segment that flows underground) so long as a bed and banks and an ordinary high water mark can be identified upstream of the break. The presence of a bed and banks and an ordinary high water mark upstream of the break generally demonstrates that the tributary continues upstream of the break.

Waters that meet the definition of tributary under the proposed rule are jurisdictional even if there is an impoundment at some point along the connection from the tributary to the (a)(1) through (a)(3) water.

Longstanding agency practice has identified tributaries as including ‘‘natural, man-altered or manmade’’ water bodies. Natural, man-altered, and manmade tributaries provide many of the same functions, especially as

conduits for the movement of water and pollutants to other tributaries or directly to traditional navigable waters, interstate waters, or the territorial seas. The discharge of a pollutant into a tributary generally has the same effect downstream whether the tributary waterway is natural or manmade (see further discussion below and Appendix A). Given the extensive human

modification of watercourses and hydrologic systems throughout the country, it is often difficult to distinguish between natural

watercourses and watercourses that arewholly or partly manmade or manaltered. For example, tributaries that

have been channelized in concrete or otherwise have been human-altered, may still meet the definition of tributaries under the agencies’ proposed regulation so long as they still contribute flow to an (a)(1) through (a)(4) water. The agencies’ proposeddefinition of tributary provides a nonexclusive list of the types of waters, natural, man-altered and man-made, that may be tributaries: Wetlands, rivers, streams, lakes, ponds, impoundments, canals, and ditches not excluded in


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paragraph (b)(3) or (4) of the proposed

rule.

Under the agencies’ proposal, when a tributary flows through a wetland into another tributary (e.g., a run-of-stream wetland), losing its OHWM through the wetland, it remains a tributary, and the wetland itself is considered a tributary. Wetlands may contribute flow to a stream or river through channelized flow or diffuse flow, and sometimes both. Wetlands may also serve as water sources at the upper limit of headwater streams where the channel begins. In light of their potential to be important

contributors of flow to tributaries to traditional navigable waters, interstate waters, or the territorial seas, the agencies propose a definition of tributary which includes such wetlands. In other instances, wetlands may serve as the connection between a tributary and another tributary or even a traditional navigable water, interstate water, or the territorial seas. For wetland tributaries, water may flow through braided channels that alsoinclude wetlands or through a run-ofstream wetland that does not have a bed

and banks and OHWM.

It is the agencies’ intent that the definitions in this proposed rule provide as much clarity and regulatory certainty as possible. While it is important to include wetlands that connect upstream and downstream portions of a tributary as jurisdictional waters because they have a significant nexus to downstream (a)(1) through (a)(4) waters, the agencies recognize that it may add an element of uncertainty to the definition of tributary to include

features as tributaries which do not have

a bed and bank and OHWM. An alternate approach would be to clarify that wetlands that connect tributary segments are adjacent wetlands, and as such are jurisdictional waters of the United States under (a)(6). In this approach, a tributary would be defined as having a bed and bank and OHWM, and the upper limit of the tributary would be defined by the point where

these features cease to be identifiable. (Note that natural or manmade breaks would still not sever jurisdiction if a tributary segment with a bed and bank

and OHWM could be identified upstream of the break.) Wetlands would not be considered tributaries, but would remain jurisdictional as adjacent waters. Wetlands that contribute flow, for example at the upper reaches of the tributary system, would be considered adjacent waters. The agencies request comment on this alternate approach, as well as any other suggestions commenters may have on how to clarify the definition of tributaries and provide a clear explanation of their lateral and
upstream extent.

Tidal ditches subject to the ebb and

flow of the tide are not evaluated as tributaries, but are jurisdictional under paragraph (a)(1) of the proposed regulation as they are under the current regulation.

The agencies are proposing to clearly

exclude from the definition of ‘‘waters of the United States’’ two types of ditches that might otherwise be

evaluated as tributaries: Ditches that are excavated wholly in uplands, drain only uplands, and have less than perennial flow; and ditches that do not contribute flow, either directly or through another water, to a water identified in paragraphs (a)(1) through (4). The proposed rule for the first time excludes certain ditches by rule rather than simply through preamble and guidance.

Even before the decisions in SWANCC

and Rapanos, the agencies excluded certain ditches from jurisdiction because they either are not part of the tributary system or because they are excavated wholly in uplands, drain only uplands, and are dry for much of the year, i.e. upland ditches. The agencies are proposing to continue this exclusion and, to provide improved consistency and clarity, further define flow characteristics of upland ditches that are and are not jurisdictional. The proposed rule would exclude from jurisdiction upland ditches with less than perennial flow. The scientific concept of perennial flow is a widely accepted and well understood hydrologic characteristic of

tributaries. Perennial flow means that water is present in a tributary year

round when rainfall is normal or above normal. Identifying upland ditches with perennial flow is straightforward and will provide for consistent, predictable, and technically accurate determinations at any time of year. The agencies specifically seek comment on the appropriate flow regime for a ditch excavated wholly in uplands and draining only uplands to be included in the exclusion of paragraph (b)(3). In particular, the agencies seek comment on whether the flow regime in such

ditches should be less than intermittent flow or whether the flow regime in such ditches should be less than perennial flow as proposed.

Only those ditches not excluded by the proposed regulation and that meet the proposed definition of tributary are

‘‘waters of the United States.’’ Ditches

that are excluded from the definition of

‘‘waters of the United States’’ under (b)(3) and (b)(4) cannot be recaptured and considered jurisdictional under any of the jurisdictional categories in section (a) of the proposed rule, such as a ditch that crosses a state line. This is true for

all other features excluded under section (b) as well. Ditches not excluded under paragraphs (b)(3) and (4) of the proposed regulation meet the definition of tributary where they have a bed and banks and ordinary high water mark and they contribute flow directly or indirectly through another water to (a)(1) through (a)(4) waters. Such jurisdictional ditches may include, but are not limited to, the following:

• Natural streams that have been altered (e.g., channelized, straightened or relocated);

• ditches that have been excavated in ‘‘waters of the United States,’’ including jurisdictional wetlands;

• ditches that have perennial flow;

and

• ditches that connect two or more

‘‘waters of the United States.’’

In an effort to distinguish ditches that

are not ‘‘waters of the United States’’

from those that are ‘‘waters of the United States,’’ the proposal states that ditches with less than perennial flow that are excavated in uplands, rather than in wetlands or other types of waters, for their entire length are not

tributaries and are not ‘‘waters of the United States’’ under the proposed rule. Ditches that are perennial generally have water present year round when

rainfall is normal or above normal. Under this exclusion, water that only stands or pools in a ditch is not considered perennial flow and, therefore, any such upland ditch would not be subject to regulation. In addition,

ditches that do not contribute flow to the tributary system of a traditional navigable water, interstate water or the

territorial seas are not ‘‘waters of the United States,’’ even if the ditch has perennial flow.

Historical evidence, such as photographs, prior delineations, or topographic maps, may be used to determine whether a water body was excavated wholly in uplands and drains only uplands, and has less than perennial flow. Site characteristics may also be present to inform the

determination of whether the water body is a ditch, such as shape, sinuosity, flow indications, etc., as

ditches are often created in a linear fashion with little sinuosity and may

not connect to another ‘‘water of the United States.’’ Ditches created by altering natural waters would be

considered ‘‘waters of the United States,’’ so long as they contribute flow to another jurisdictional water. Ditches may have been created for a number of purposes, such as irrigation, water management or treatment, and roadside drains. In order to be excluded,


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8A discharge of dredged or fill material into an existing tributary which converts a ‘‘water of the U.S.’’ into a non-jurisdictional water requires

authorization under section 404 of the CWA. 

### however, the ditch must be excavated wholly in uplands, drain only uplands, and have less than perennial flow. Ditches that do not contribute flow, either directly or through another water, to a water identified in paragraphs (a)(1) through (4) are not ‘‘waters of the

United States.’’

2. What is not a tributary for purposes of this proposal?

Waters that do not contribute flow, either directly or through another water, to a water identified in paragraphs (a)(1) through (4) of the proposed regulation are not considered jurisdictional as tributaries under the CWA. However, even if such waters are not ‘‘tributaries,’’ they may be jurisdictional under other paragraphs of the proposed rule. Note that waters specifically listed under the proposed section (b), including ditches as defined in paragraphs (b)(3) and (b)(4), would not be considered ‘‘waters of the United States’’ in any case. In addition, ephemeral features located on agricultural lands that do not possess a

bed and bank are not tributaries. The defined bed and bank no longer exists due to past normal farming practices such as plowing or discing (see section 404(f)(1)(A)),8 

### and these farming practices often pre-date the CWA. Such

farm field features are not tributaries even though they may contribute flow during some rain events or snowmelt.

Section J below discusses in more detail the agencies’ proposed rule excluding specific waters and features

from the definition of ‘‘waters of the United States.’’ Of importance with respect to tributaries is the exclusion of gullies, rills, non-wetland swales, and

certain ditches. These features are not

considered tributaries under this proposed rule, even though rills and gullies and non-wetland swales (as described in Section J), may contribute flow to a tributary in systems with steep side slopes.

Non-jurisdictional geographic features (e.g., non-wetland swales, ephemeral upland ditches) may still serve as a confined surface hydrologic connection between an adjacent wetland or water and a traditional navigable water, interstate water or the territorial sea, provided there is an actual exchange of water between those waters, and the water is not lost to deep groundwater through infiltration (i.e., transmission losses). In addition, these geographic features may function as ‘‘point sources,’’ such that discharges of pollutants to waters through these features could be subject to other CWA authorities (e.g., CWA section 402 and its implementing regulations).

The agencies request comment on all aspects of the proposed definition of tributaries and in particular on whether

and how this definition can be revised to provide increased clarity as to the distinction between jurisdictionaltributaries, as defined, and nonjurisdictional features such as gullies,

rills and non-wetland swales. The agencies seek comments on how to provide greater regulatory certainty as to which specific aquatic features are jurisdictional tributaries, and which are not. Commenters should explain how any suggestions are consistent with the Clean Water Act, applicable caselaw, and the scientific literature regarding connectivity of aquatic features.

3. Why do the agencies conclude all

tributaries are ‘‘waters of the United

States’’?

Assertion of jurisdiction over tributaries as defined in this proposed rule is appropriate under Rapanos both as a legal matter and as a scientific

matter based on available science and the agencies’ professional judgment and field expertise. The agencies conclude

based on their scientific and technical expertise that tributaries, as defined in the proposed rule, in a watershed are similarly situated and have a significant

nexus alone or in combination with other tributaries because they significantly affect the chemical, physical, or biological integrity of traditional navigable waters, interstate waters, or the territorial seas.

a. Legal Basis for Defining All

Tributaries as ‘‘Waters of the United

States’’

In Rapanos, both the plurality opinion and Justice Kennedy’s opinion discussed the Court’s prior opinion in Riverside Bayviewto begin their analysis of the scope of the CWA. Justice Scalia stated, ‘‘In Riverside Bayview, we stated that the phrase [‘waters of the United States’] in the Act referred primarily to ‘rivers, streams,

and other hydrographic features more conventionally identifiable as ‘‘waters’’’ than the wetlands adjacent to such features. 474 U.S., at 131 (emphasis added).’’ Rapanos, 547 U.S. at 734. Justice Kennedy began, ‘‘As the plurality points out, and as Riverside Bayviewholds, in enacting the Clean Water Act Congress intended to regulate

at least some waters that are not navigable in the traditional sense. Ante

at 12; Riverside Bayview, 474 U.S. at 133; see also SWANCC, supra, at 167.’’ Id at 780. This conclusion is supported by ‘‘the evident breadth of congressional concern for protection of water quality and aquatic ecosystems.’’ Riverside Bayview, supra, at 133; see also

Milwaukee v. Illinois, 451 U.S. 304, 318(1981) (describing the Act as ‘‘an allencompassing program of water pollution regulation’’). In Rapanos, Justice Kennedy established a standard for determining whether wetlands should be considered to possess the requisite nexus in the context of assessing whether wetlands are jurisdictional: ‘‘if the wetlands, either alone or in combination with similarly situated [wet]lands in the region, significantly affect the chemical, physical, and biological integrity of other covered waters more readily understood as ‘navigable.’ ’’ 547 U.S. at 780. While Justice Kennedy focused on adjacent wetlands in light of the facts of the cases before him, it is reasonable to

utilize the same standard for tributaries. As discussed in this preamble, based on

a detailed examination of the scientific literature, the agencies conclude that tributaries as they propose to define them perform the requisite functions identified by Justice Kennedy for them to be considered, as a category, to be

‘‘waters of the United States.’’ Assertion of jurisdiction over tributaries with a

bed and banks and OHWM is also

consistent with Rapanos because five Justices did not reject the current regulations that assert jurisdiction over non-navigable tributaries of traditional navigable waters and interstate waters.

The agencies analyzed the Report and

other scientific literature to determine

whether tributaries to traditional navigable waters, interstate waters, or the territorial seas have a significant

nexus to constitute ‘‘waters of the

United States’’ under the Act such that

it is reasonable to assert CWA jurisdiction over all such tributaries as a category by rule. The agencies’ analysis of the available scientific literature, including the Report, demonstrates through an ecological rationale that tributaries draining to a traditional navigable water, interstate water, or the territorial seas have a significant nexus to such waters, especially because of their ability to transport pollutants to such waters that would impair their chemical, physical, or biological integrity.

One of the primary purposes and functions of the CWA is to prevent the discharge of petroleum wastes and other chemical wastes, biological and medical wastes, sediments, nutrients and all other forms of pollutants into the ‘‘waters of the United States,’’ because such pollutants endanger the nation’s


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public health, drinking water supplies, shellfish, fin fish, recreation areas, etc. Because the entire tributary system of the traditional navigable, interstate

waters or the territorial seas is interconnected, pollutants that are dumped into any part of the tributary system eventually are washed downstream to traditional navigable waters, interstate waters, or the territorial seas where those pollutants endanger public health and the

environment.

The CWA regulates and controls pollution at its source, in part because most pollutants do not remain at the site of the discharge, but instead flow and are washed downstream through the tributary system to endanger drinking water supplies, fisheries, and recreation

areas. These fundamental facts about the movement of pollutants and the interconnected nature of the tributary system demonstrate why all tributaries of traditional navigable waters, interstate waters, and the territorial seas,

alone or in combination with other

tributaries in a watershed have a significant nexus with those downstream waters. The significant nexus relating to pollution transport (or prevention of such transport) from all tributaries of traditional navigable waters, interstate waters, and the

territorial seas to their downstream waters in and of itself justifies the assertion of CWA jurisdiction over all tributaries by rule.

b. The Agencies Conclude That Tributaries, as Defined in the Proposed Rule, Have a Significant Nexus

The finding of significant nexus is based on the chemical, physical, and biological interrelationship between a water, the tributary network, and traditional navigable waters, interstate waters, and the territorial seas. Based on their scientific and technical expertise, the agencies conclude that tributaries, as defined in today’s proposed rule, have a significant nexus and are appropriately identified as jurisdictional by rule. Rapanos, 547 U.S. at 781–82 (J. Kennedy). (For more discussion, see Appendix A).

(1) Tributaries Significantly Affect the Physical Integrity of (a)(1) Through (a)(3) Waters

Physical connections between tributaries and traditional navigable waters, interstate waters, and the

territorial seas result from the hydrologic transport of numerous materials, including water, sediment and organic matter (e.g., leaves, wood)

from tributaries to downstream waters. This transport affects the physical characteristics of downstream waters. Tributaries, even when seasonally dry,

are the dominant source of water in most rivers, rather than direct precipitation or groundwater input to main stem river segments.

One of the primary functions of tributaries is transporting sediment to downstream waters. Tributaries, particularly headwaters, shape and maintain river channels by accumulating and gradually or episodically releasing sediment and large woody debris into river channels. Sediment transport is also provided by ephemeral streams. Effects of the releases of sediment and large woody debris are especially evident at tributary-river confluences, where discontinuities in flow regime and temperature demonstrate physical

alteration of river structure and function by headwater streams.

Tributaries have vitally important effects on the physical integrity of (a)(1) through (a)(3) waters, contributing not only the majority of the flow in these waters but affecting the structure of the

waters. These effects occur even when the tributaries flow infrequently (such as ephemeral tributaries) and even when the tributaries are significant distances from the (a)(1) through (a)(3) water (such as some headwater tributaries). Tributaries provide flow to downstream rivers necessary to support navigation. The agencies conclude that the tributaries alone or together with other

tributaries in a watershed have a significant effect on the physical integrity of downstream waters.

(2) Tributaries Significantly Affect the Chemical Integrity of (a)(1) Through (a)(3) Waters

Tributaries also influence the chemical composition of downstream waters, through the transport and

removal of chemical elements and compounds, such as nutrients, ions, dissolved and particulate organic matter, pollutants, and contaminants. Ecosystem processes in tributaries transform, remove, and transport these

substances to downstream waters. In turn, these chemical compounds can influence water quality, sediment deposition, nutrient availability, and

biotic functions in rivers. Because water flow is the primary mechanism by

which chemical substances are transported downstream, chemical effects are closely related tohydrological connectivity. Longdistance movement of contaminants provides another line of evidence for chemical connectivity between tributaries and traditional navigable waters, interstate waters, and the territorial seas and significantly affects

these waters.

Within tributaries, there are processes that occur that transform and export

nutrients and carbon to downstream waters, serving important source

functions that influence the chemical integrity of downstream waters. Organic carbon, in both dissolved and particulate forms, exported from tributaries is consumed by downstream organisms. The organic carbon that is exported downstream thus supports biological activity (including metabolism) throughout the river

network.

Tributaries have important effects on the chemical integrity of (a)(1) through (a)(3) waters, acting as both sinks and sources of chemical substances. They provide sink functions by trapping chemicals through absorption to sediments in the stream substrate (e.g., phosphorous adsorption to clay particles). They provide source functions by transporting chemicals to downstream (a)(1) through (a)(3) waters

as chemicals dissolved in the waters or as chemicals attached to suspended

sediments. Thus the tributaries of a watershed, alone or in combination, significantly affect the chemical integrity of downstream waters.

(3) Tributaries Significantly Affect the Biological Integrity of (a)(1) Through (a)(3) Waters

Tributaries, including intermittent and ephemeral streams, are critical in the life cycles of many organisms capable of moving throughout river networks. In fact, many organisms, such as anadromous salmon, have complex life cycles which involve migration through the river network, from

headwaters to downstream rivers and oceans and back, over the course of their lives. Anadromous fish spend the majority of their life cycles in saltwater, but migrate upstream to inland freshwater systems in order to spawn and reproduce. More generally, in addition to providing critical habitat for complex life cycle completion, tributaries provide refuge from predators and adverse physical conditions in rivers, and they are reservoirs of genetic- and species-level diversity. These connections between tributaries and (a)(1) through (a)(3) waters significantly influence the biologic integrity of these waters.

Tributaries have important effects on the biological integrity of (a)(1) through (a)(3) waters, contributing materials to

downstream food networks and supporting populations for aquatic species, including economically important species such as salmon, etc.,


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and other essential habitat needs for species that utilize both tributaries and downstream (a)(1) through (a)(3) waters.

These effects occur even when the tributaries flow infrequently (such as ephemeral tributaries) and even when the tributaries are large distances from the (a)(1) through (a)(3) water (such as some headwater tributaries). When all

the tributaries in a watershed are considered together, these effects are significant.

(4) Small, Intermittent, and Ephemeral Tributaries Significantly Affect the Chemical, Physical, and Biological Integrity of (a)(1) Through (a)(3) Waters

As discussed above, the agencies conclude that tributaries, including headwaters, intermittent, and ephemeral streams, and especially when all

tributaries in a watershed are considered in combination, have a significant nexus to traditional navigable waters, interstate waters, or

the territorial seas based on their contribution to the chemical, physical, and biological integrity of (a)(1) through (a)(3) waters. Tributaries, including headwater streams, within a watershed draining to a traditional navigable water, interstate water, or the territorial seas collectively shape the chemical, physical, and biological integrity of (a)(1) through (a)(3) waters.

Tributaries that are small, flow infrequently, or are a substantial distance from the nearest (a)(1) through (a)(3) water (e.g., headwater perennial, intermittent, and ephemeral tributaries) are essential components of the tributary network and have important effects on the chemical, physical, and biological integrity of (a)(1) through (a)(3) waters, contributing many of the same functions downstream as larger

streams. When their functional contributions to the chemical, physical, and biological conditions of

downstream waters are considered at a watershed scale, the scientific evidence supports a legal determination that they meet the ‘‘significant nexus’’ standard articulated by Justice Kennedy in Rapanos.

(5) Tributary Lakes, Ponds, and Wetlands Significantly Affect the Chemical, Physical, and Biological Integrity of (a)(1) Through (a)(3) Waters

Although the above discussion refers primarily to stream tributaries, lake, pond and wetland tributaries also have

the same or similar connections and functions that significantly affect (a)(1) through (a)(3) waters. Lakes and ponds

that contribute surface water to downstream (a)(1) through (a)(3) waters satisfy the agencies’ definition of tributary. They may be at the headwaters of the tributary network (e.g., a lake with no stream inlets that has an outlet to the tributary network) or located outside of the headwaters, or

farther downstream from the headwaters (e.g., a lake with both a stream inlet and a stream outlet to the tributary network). Similarly, wetland tributaries are

wetlands that are located within the

stream channel itself or that form the start of the stream channel, such as channel-origin wetlands that are part of the headwaters of the tributary network.

As noted above, while these wetlands may function as part of the ‘‘tributary network,’’ the agencies are seeking comment on whether it would provide greater regulatory clarity to exclude

such wetlands from the definition of ‘‘tributary’’ because they generally lack a defined bed, bank and OHWM. These features are well understood by the public and agency field staff and have traditionally been the defining characteristics of tributaries. Rather, wetlands in headwaters or connecting tributaries would remain jurisdictional as adjacent waters under the definition of ‘‘adjacent’’ and its supporting terms (e.g., neighboring, floodplain, and riparian area) in this proposal.

Tributary lakes and ponds serve many important functions that affect the chemical, physical, and biological

conditions downstream. Lakes can store floodwaters, sediment, and nutrients, as these materials have the opportunity to settle out, at least temporarily, as water moves through the lake downstream. Lakes, as with other tributaries, can also contribute flow, nutrients, sediment,

and other materials downstream.

(6) Man-Made or Man-Altered Tributaries Significantly Affect the Chemical, Physical, and Biological Integrity of (a)(1) Through (a)(3) Waters

This proposal expressly states that a tributary, including wetlands, can be a natural, man-altered, or man-made water body and includes waters such as rivers, streams, lakes, impoundments, canals, and ditches that meet the definition of tributary and are not

excluded from the definition of ‘‘waters of the United States’’ by paragraphs (b)(3) and (b)(4) of the proposed rule. The agencies’ proposed rule clarifies

that man-made and man-altered

tributaries are ‘‘waters of the United

States’’ because man-made and manaltered tributaries perform many of the same functions as natural tributaries, especially the conveyance of water that carries nutrients, pollutants, and other substances to traditional navigable waters, interstate waters, or the

territorial seas. Man-made and manaltered tributaries also provide corridors for movement of organisms between headwaters and traditional navigable waters, interstate waters, or the territorial seas. The significant nexus between a tributary and a traditional navigable water, interstate water, or the

territorial seas is not broken where the tributary flows through a culvert or

other structure. The scientific literature recognizes that features that conveywater, whether they are natural, manmade, or man-altered, provide the connectivity between streams and

downstream rivers.

Tributary ditches and other manmade or man-altered waters, if they meet the definition of ‘‘tributary,’’ have a significant nexus to (a)(1) through (a)(3) waters due to their effects on the chemical, physical, or biological integrity of those downstream waters. As described above, tributaries of all flow regimes have a significant nexus to downstream (a)(1) through (a)(3) waters. Due to the often straightened and channelized nature of ditches, these tributaries quickly move water downstream to (a)(1) through (a)(3) waters. Ditches and canals, like other tributaries, export sediment, nutrients,

and other materials downstream. Due to their often channelized nature, ditches are very effective at transporting water and these materials, including nitrogen, downstream. It is the agencies’ position

that ditches that meet the definition of tributary (which does not include ditches excluded under paragraphs (b)(3) and (b)(4)) provide the same chemical, physical, and biological

functions as other water bodies defined as tributaries under the proposed rule.

G. Adjacent Waters

The agencies propose to revise the existing jurisdictional category of ‘‘adjacent wetlands,’’ which currently limits consideration to only wetlands, to include ‘‘adjacent waters.’’ The proposed ‘‘adjacent waters’’ category would replace ‘‘adjacent wetlands’’ and

would include wetlands and other waterbodies that meet the proposed definition of adjacent, including ‘‘neighboring.’’ To be jurisdictional, it would be necessary to determine that a wetland or other waterbody meets the definition of ‘‘adjacent’’ water under proposed paragraph (a)(6). Adjacent waters are integrally linked to the chemical, physical, or biological functions of the (a)(1) through (a)(5) waterbodies to which they are adjacent. Waters adjacent to (a)(1) through (a)(3) waters have a significant nexus to those (a)(1) through (a)(3) waters. Waters adjacent to impoundments, (a)(4) and tributaries, (a)(5), are integrally linked to


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the chemical, physical, or biological functions of the impoundments or tributaries and, through those waters, are integrally linked to the chemical, physical or biological functions of traditional navigable waters, interstate
waters or the territorial seas. As such, where waterbodies are adjacent to (a)(4) or (a)(5) waters, they also have a significant nexus to (a)(1) through (a)(3)

waters. See Appendix A, Scientific Evidence (Part I, Discussion of Major Conclusions 2.B–C; Part II, ii) and Appendix B, Legal Analysis.

The proposed rule proposes to change ‘‘adjacent wetlands’’ to ‘‘adjacent

waters’’ so that water bodies such as ponds and oxbow lakes, as well as wetlands, adjacent to jurisdictional

waters are ‘‘waters of the United States’’ by rule. Second, the proposed rule adds a definition of the term ‘‘neighboring,’’ a term which appears in the existing definition of ‘‘adjacent.’’ The agencies propose a definition for ‘‘neighboring’’ to identify those adjacent waters that the agencies concluded have a significant nexus to (a)(1) through (a)(3) waters. To bring greater clarity to the meaning of ‘‘neighboring,’’ the proposed rule adds scientifically-based definitions for the terms ‘‘riparian area’’ and ‘‘floodplain’’

to define the lateral reach of the term ‘‘neighboring.’’ Under the proposed rule, all waters, including wetlands, adjacent to a water identified in paragraphs (a)(1) through (5); would be

‘‘waters of the United States.’’ The term adjacent means bordering, contiguous or neighboring. Waters, including wetlands, separated from other waters of the United States by man-made dikes or barriers, natural river berms, beach dunes and the like are ‘‘adjacent waters.’’ The term neighboring, for purposes of the term ‘‘adjacent,’’

includes waters located within the riparian area or floodplain of a water identified in paragraphs (a)(1) through (5), or waters with a shallow subsurface hydrologic connection or confined surface hydrologic connection to such a jurisdictional water. The term riparian area means an area bordering a water where surface or subsurface hydrology directly influence the ecological processes and plant and animal community structure in that area. Riparian areas are transitional areas between aquatic and terrestrial ecosystems that influence the exchange of energy and materials between those ecosystems. Finally, the term floodplain means an area bordering inland or coastal waters that was formed by sediment deposition from such water under present climatic conditions and is inundated during periods of moderate to high water flows.

1. What are ‘‘adjacent waters’’ under the proposed rule?

‘‘Adjacent waters’’ are wetlands, ponds, lakes and similar water bodies that provide similar functions which have a significant nexus to traditional navigable waters, interstate waters, and

the territorial seas. These include waters and wetlands that are adjacent to traditional navigable waters, interstate waters, and the territorial seas as well as waters and wetlands adjacent to other jurisdictional waters such as tributaries and impoundments. The inclusion of adjacent waters in this category is supported by the Report, the collective body of scientific literature, the agencies’ growing body of scientific and technical knowledge and practical expertise addressing the connectivity and ecological interactions of these waters on (a)(1) through (a)(3) waters, and by the determination made in this rulemaking that all adjacent waters in a watershed have a significant nexus with their traditional navigable waters,

interstate waters or the territorial seas.

Under the existing rule, only wetlands adjacent to ‘‘waters of the United

States’’ are defined as ‘‘waters of the

United States.’’ As noted in San Francisco Baykeeper v. Cargill Salt, 481 F.3d 700 (9th Cir. 2007), this provision of the agencies’ regulations only defines adjacent wetlands, not adjacent ponds,

as ‘‘waters of the United States.’’ Prior

to SWANCC, adjacent non-wetland waters were often jurisdictional under the ‘‘other waters,’’ or ‘‘(a)(3)’’ provision of the existing regulations which the agencies are proposing to eliminate. Waters, including wetlands, that meet the proposed definition of adjacency, including the new proposed definition of neighboring, have a significant nexus to (a)(1) through (a)(3) waters, and this proposed rule would include all adjacent waters, including wetlands, as ‘‘waters of the United States’’ by rule.

The existing definition of ‘‘adjacent’’ would be generally retained under today’s proposal, with a clarification with respect to an existing provision addressing wetlands adjacent to other wetlands. The proposed rule states that the term adjacent means bordering, contiguous or neighboring. Waters, including wetlands, separated from other waters of the United States by man-made dikes or barriers, natural river berms, beach dunes and the like are ‘‘adjacent waters.’’ Within the definition of ‘‘adjacent,’’ the terms bordering and contiguous are well understood, and for continuity and clarity the agencies would continue to interpret and implement those terms consistent with existing policy and practice.

The proposed rule also contains for

the first time a definition of the term ‘‘neighboring.’’ The term ‘‘neighboring’’ has generally been interpreted broadly in practice. The agencies provide a regulatory definition of ‘‘neighboring’’ that captures those waters that in practice the agencies have identified as having a significant effect on the chemical, physical, and biological integrity of traditional navigable waters, interstate waters, or the territorial seas. ‘‘Neighboring’’ is defined as including waters located within the riparian area or floodplain of a water identified in paragraphs (a)(1) through (5), or waters

with a confined surface or shallow subsurface hydrologic connection to such a jurisdictional water.

The terms ‘‘riparian area’’ and ‘‘floodplain’’ are also defined to further clarify how the agencies interpret the term ‘‘neighboring.’’ Those new terms are found at paragraphs (c)(1) through (c)(4) of the proposed rule. The agencies emphasize that these terms help to identify waters, including wetlands, that may be ‘‘adjacent’’ and would, therefore,

be ‘‘waters of the United States’’ under this proposed rule. Absolutely no uplands located in ‘‘riparian areas’’ and ‘‘floodplains’’ can ever be ‘‘waters of the United States’’ subject to jurisdiction of

the CWA.

Most waters, including wetlands, that are neighboring to a water body are found within its riparian zone or floodplain. However, there are some neighboring waters that might be located outside of the riparian zone or floodplain, such as wetlands immediately next to a highly incised and manipulated stream that no longer has a riparian area or a floodplain. Waters, including wetlands, determined to have a shallow subsurface hydrologic

connection or confined surface hydrologic connection to an (a)(1) through (a)(5) water would also be ‘‘waters of the United States’’ by rule as adjacent waters falling within the definition of ‘‘neighboring.’’

In circumstances where a particular water body is outside of the floodplain and riparian area of a tributary, but is connected by a shallow subsurface hydrologic connection or confined surface hydrologic connection with such tributary, the agencies will also

assess the distance between the water body and tributary in determining whether or not the water body is adjacent. ‘‘Adjacent’’ as defined in the agencies’ regulations has always

included an element of reasonable proximity. See Riverside Bayview, 474 at


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133–34 (‘‘Following the lead of the Environmental Protection Agency, see 38 FR 10834 (1973), the Corps has determined that wetlands adjacent to navigable waters do as a general matter play a key role in protecting and enhancing water quality: . . . ‘For this reason, the landward limit of Federal jurisdiction under Section 404 must

include wetlands that are in reasonable proximity to other waters of the United States, as these wetlands are part of this aquatic system.’ ’’ quoting 42 FR 37128, July 19, 1977). Therefore, the determination of whether a particular

water meets the definition of ‘‘neighboring’’ because the water is connected by a shallow subsurface or confined surface hydrologic connection

is made in the context of the terms ‘‘neighboring’’ and ‘‘adjacent’’ as used in the regulation.

The element of reasonable proximity is informed by the scientific literature, supplemented by agency practice, which leads to a recognition of the role of hydrologic connections in supporting a significant chemical, physical, and biological relationship between water bodies, but this relationship can be

reduced as the distance between water bodies increases. The agencies recognize that in specific circumstances, the distance between water bodies may be sufficiently far that even the presence of a hydrologic connection may not support an adjacency determination.

While the agencies’ best professional judgment has always been a factor in determining whether a particular wetland is ‘‘adjacent’’ under the existing definition, the agencies recognize that this may result in some uncertainty as to whether a particular water connected through confined surface or shallow subsurface hydrology is an ‘‘adjacent’’ water. The agencies therefore request

comment on whether there are other reasonable options for providing clarity for jurisdiction over waters with these types of connections.

Options could include asserting jurisdiction over all waters connected through a shallow subsurface hydrologic

connection or confined surface hydrologic connection regardless of distance; asserting jurisdiction over adjacent waters only if they are located in the floodplain or riparian zone of a jurisdictional water; considering only

confined surface connections but not

shallow subsurface connections for purposes of determining adjacency; or establishing specific geographic limits for using shallow subsurface or confined surface hydrological connections as a basis for determining adjacency, including, for example, distance limitations based on ratios compared to the bank-to-bank width of the water to which the water is adjacent. The agencies note that under the proposed rule any waters not fitting within (a)(1) through (a)(6) categories would instead

be treated as ‘‘other waters.’’

Both confined surface and shallow

subsurface connections are forms of direct hydrologic connections between adjacent waters and (a)(1) through (a)(5) waters. For purposes of this rule,

confined surface connections consist of permanent, intermittent or ephemeral surface connections through directional flowpaths, such as (but not limited to) swales, gullies, rills, and ditches. In some cases, these connections will be a result of ‘‘fill and spill’’ hydrology. A directional flowpath is a path where water flows repeatedly from the wetland or open water to the nearby ‘‘water of

the United States’’ that at times contains water originating in the adjacent wetland or open water as opposed to just directly from precipitation.

For the purposes of this rule, ‘‘fill and spill’’ describes situations where wetlands or open waters fill to capacity during intense precipitation events or high cumulative precipitation over time and then spill to the downstream jurisdictional water. Report at 5–62 (citing T.C. Winter and D.O. Rosenberry, ‘‘Hydrology of Prairie Pothole Wetlands during Drought and Deluge: A 17-year Study of the Cottonwood Lake Wetland Complex in North Dakota in the Perspective of Longer Term Measured and Proxy Hydrological Records,’’ Climatic Change 40:189–209 (1998); S.G. Leibowitz, and K.C. Vining, ‘‘Temporal connectivity in a prairie pothole complex,’’ Wetlands 23:13–25 (2003)). Water connected through such flows originates from the adjacent wetland or open water, travels to the downstream jurisdictional water, and is

connected to those downstream waters by swales or other directional flowpaths on the surface. Surface hydrologic connections via physical features or

discrete features described above allow for confined, direct hydrologic flows between an adjacent water and the (a)(1) through (a)(5) water that it neighbors.

A shallow subsurface hydrologic connection is lateral water flow through a shallow subsurface layer, such as can be found, for example, in steeply sloping forested areas with shallow soils, or in soils with a restrictive layer that impedes the vertical flow of water, or in karst systems, especially karst pans. K.J. Devito, et al., ‘‘GroundwaterSurface Water Interactions in Headwater

Forested Wetlands of the Canadian Shield,’’Journal of Hydrology 181:127– 47 (1996); M.A. O’Driscoll, and R.R. Parizek, ‘‘The Hydrologic Catchment Area of a Chain of Karst Wetlands in Central Pennsylvania, USA,’’ Wetlands 23:171–79 (2003); B.J. Cook, and F.R. Hauer, ‘‘Effects of Hydrologic Connectivity on Water Chemistry, Soils, and Vegetation Structure and Function in an Intermontane Depressional Wetland Landscape,’’ Wetlands 27:719– 38 (2007).

A shallow subsurface connection also exists, for example, when the adjacent water and neighboring (a)(1) through (a)(5) water are in contact with the same shallow aquifer. Shallow subsurface connections may be found both within the ordinary root zone and below the ordinary root zone (below 12 inches),

where other wetland delineation factors may not be present. A combination of physical factors may reflect the presence of a shallow subsurface connection, including (but not limited to) stream hydrograph (for example, when the hydrograph indicates an increase in

flow in an area where no tributaries are entering the stream), soil surveys (for example, exhibiting indicators of high transmissivity over an impermeable layer), and information indicating the

water table in the stream is lower than

in the shallow subsurface.

Shallow subsurface connections are distinct from deeper groundwater connections, which do not satisfy the requirement for adjacency, in that the

former exhibit a direct connection to the

water found on the surface in wetlands and open waters. Water does not have to be continuously present in the

confined surface or shallow subsurface hydrologic connection and the flow between the adjacent water and the jurisdictional water may move in one or both directions. While they may provide the connection establishing jurisdiction,

these shallow subsurface flows are not

‘‘waters of the United States.’’

For waters outside of the riparian area or floodplain, confined surface hydrologic connections (as described above) are the only types of surface hydrologic connections that satisfy the requirements for adjacency. Waters outside of the riparian area or floodplain

that lack a shallow subsurface hydrologic connection or a confined surface hydrologic connection would be analyzed as ‘‘other waters’’ under paragraph (a)(7) of the proposed rule.

Application of the terms ‘‘riparian area,’’ ‘‘floodplain,’’ and ‘‘hydrologic connection’’ would be based in part on best professional judgment and experience applied to the definitions

contained in this rule. The new definitions of riparian area and floodplain are designed to provide greater consistency, clarity, and certainty in determining the


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circumstances under which a particular

water meets the definition of the term adjacent. The addition of these two terms to the definition of ‘‘neighboring’’

is based on the scientific literature and agencies’ knowledge of and expertise on river systems, which shows that water bodies such as wetlands, ponds, and oxbow lakes located within the riparian areas and floodplains of (a)(1) through (a)(5) waters generally have substantial hydrologic and ecologic connections with the waters that they neighbor.

These proposed definitions are adapted from scientific definitions using the concepts that are most relevant and

useful in the context of the CWA. Use of the floodplain in characterizing the term ‘‘neighboring’’ is intended to provide greater clarity and predictability

in the determination of when waters are adjacent. The scientific literature clearly demonstrates the enhanced hydrologic connectivity that is present between a tributary and waters within the floodplain of that tributary. There is, however, variability in the size of the floodplain, which is dependent on factors such as the flooding frequency being considered, size of the tributary, and topography. As a general matter, large tributaries in low gradient topography will generally have large floodplains (e.g., the lower Mississippi Delta) whereas small headwater streams located in steep gradients will have the smallest floodplains. It may thus be appropriate for the agencies to consider a floodplain associated with a lower frequency flood when determining adjacency for a smaller stream, and to consider a floodplain associated with a higher frequency flood when determining adjacency for a larger stream. When determining whether a water is located in a floodplain, the agencies will use best professional judgment to determine which flood interval to use (for example, 10 to 20 year flood interval zone). The agencies request comment on whether the rule text should provide greater specificity with regard to how the agencies will

determine if a water is located in the floodplain of a jurisdictional water.

As noted above, the agencies retain the general existing definition of adjacency and have never interpreted

the term to include wetlands that are a great distance from a jurisdictional water. The agencies intend to similarly interpret the new definition of ‘‘neighboring.’’ This new definition is designed to provide greater clarity by identifying specific areas and characteristics for jurisdictional adjacent waters, but the agencies request

comment for additional clarification. Commenters should support where possible from scientific literature any suggestions for additional clarification of current explicit limits on adjacency, such as a specific distance or a specific floodplain interval.

The agencies seek comment on specific options for establishing additional precision in the definition of ‘‘neighboring’’ through: explicit language in the definition that waters connected by shallow subsurface hydrologic or confined surface hydrologic connections to an (a)(1) through (a)(5) water must be geographically proximate to the adjacent water; circumstances under which waters outside the floodplain or riparian zone are jurisdictional if they are reasonably proximate; support for or against placing geographic limits on what waters outside the floodplain or riparian zone are jurisdictional; determining that only waters within the floodplain, only waters within the riparian area, or only waters within the floodplain and riparian area (but not

waters outside these areas with a

shallow subsurface or confined surface hydrologic connection) are adjacent; identification of particular floodplain

intervals within which waters would be considered adjacent; and any other scientifically valid criteria, guidelines or parameters that would increase clarity with respect to neighboring waters.

Finally, the agencies are also proposing to delete the parenthetical from the existing ‘‘adjacent wetlands’’ regulatory provision The phrase ‘‘other

than waters that are themselves wetlands’’ was intended to preclude asserting CWA jurisdiction over wetlands that were simply adjacent to another wetland (such as an ‘‘isolated’’ wetland, as opposed to a wetland adjacent to a tributary). However, in practice some wetlands that were indeed adjacent to a tributary were

found to not meet the definition of ‘‘adjacent’’ simply because another adjacent wetland was located between the adjacent wetland and the tributary. With this proposed change, the agencies

intend to ensure that all waters that meet the proposed definition of ‘‘adjacent’’ are ‘‘waters of the United States,’’ regardless of whether or not another adjacent water is located between those waters and the tributary.

If, for example, one wetland is in the riparian area of a ‘‘tributary’’ as defined in today’s proposed rule, and a different wetland is in the floodplain of that tributary, both wetlands would meet the definition of ‘‘adjacent’’ and be ‘‘waters of the United States,’’ even if the riparian wetland is located between the floodplain wetland and the tributary. Waters located near an adjacent water but which are not themselves (independently) adjacent to an (a)(1) through (a)(5) water would, under the proposed rule, not be regulated under (a)(6). However, waters, including wetlands, that are adjacent to a wetland that meets the definition of a tributary would be considered adjacent waters.

2. Why do the agencies conclude that adjacent waters are ‘‘waters of the

United States?’’

a. Legal Basis for Defining All Adjacent

Waters as ‘‘Waters of the United States’’

For those wetlands adjacent to traditional navigable waters, Justice Kennedy stated in Rapanos that the agencies’ existing regulation ‘‘rests upon a reasonable inference of ecologic interconnection, and the assertion of jurisdiction for those wetlands is sustainable under the Act by showing adjacency alone.’’ 547 U.S. at 780. For all other adjacent waters, including adjacent wetlands, Justice Kennedy has provided a framework for establishing categories of waters which are per se ‘‘waters of the United States.’’ First, he provided that wetlands are jurisdictional if they ‘‘either alone or in combination with similarly situated [wet]lands in the region, significantly affect the chemical, physical, and biological integrity of other covered waters more readily understood as ‘navigable.’ ’’ 547 U.S. at 780. While the issue was not before the Supreme Court,

it is reasonable to also assess whether non-wetland waters have a significant nexus, as Justice Kennedy’s opinion makes clear that a significant nexus is the touchstone for CWA jurisdiction. Justice Kennedy also stated that the agencies could through regulation or adjudication identify categories of waters that ‘‘are likely, in the majority of cases, to perform important functions for an aquatic system incorporating navigable waters.’’ 547 U.S. at 780–81.

Adjacent waters as defined in today’s proposed rule, alone or in combination with other adjacent waters in a

watershed that drain to a traditional navigable water, interstate water or the territorial seas, significantly affect the chemical, physical, or biological integrity of those waters. Waters that are adjacent to (a)(1) through (a)(5) waters, including wetlands, oxbow lakes and adjacent ponds, are integral parts of

stream networks because of their ecological functions and how they interact with each other, and with downstream traditional navigable waters, interstate waters, or the territorial seas. In other words, tributaries and their adjacent waters, and the traditional navigable waters,


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interstate waters, and territorial seas to which those waters flow, are an integrated ecological system, and discharges of pollutants, including discharges of dredged or fill material, into these components of that ecological system, must be regulated under the

CWA to restore and maintain the chemical, physical, and biological integrity of these waters.

The agencies’ proposed rule is consistent with the statute, the Supreme Court’s decisions, the best available science, and scientific and technical expertise. See both Appendices A and

B.

b. Adjacent Waters Under This Proposed Rule Have a Significant Nexus to (a)(1) Through (a)(3) Waters

The agencies’ proposal to determine ‘‘adjacent waters’’ to be jurisdictional by rule is supported by the substantial chemical, physical, and biological relationship between adjacent waters, alone or in combination with similarly situated waters, and (a)(1) through (a)(5) waters. Adjacent wetlands and other adjacent waters such as ponds and oxbow lakes perform important functions for the nearby streams and lakes, and these functions are significant for the chemical, physical, and biological integrity of adjacent and

downstream waters. See Appendix A.

One reason why the agencies propose in this rulemaking that all adjacent waters have a significant nexus with their traditional navigable waters, interstate waters, or the territorial seas is closely related to a primary reason (explained above) why all tributaries of navigable and interstate waters have a significant nexus with those waters. That is, all adjacent waters should be jurisdictional by rule because the discharge of many pollutants (such as nutrients, petroleum wastes and other toxic pollutants) into adjacent waters often flow into and thereby pollute the traditional navigable waters, interstate waters, and the territorial seas.

Based on science and agency expertise, the agencies conclude that adjacent waters, as defined in the proposed rule, ‘‘are likely, in the majority of cases, to perform important functions for an aquatic system incorporating navigable waters.’’ Rapanos, 547 U.S. at 781–82. The agencies identified the characteristics of adjacent waters that as a class have a significant nexus to (a)(1) through (a)(3) waters: They are waters that are bordering to or are contiguous with (a)(1) through (a)(5) waters, including wetlands; they are waters that lie within the riparian area or floodplain of (a)(1) through (a)(5) waters; or they are waters that have a shallow subsurface or confined surface hydrologic connection with (a)(1) through (a)(5) waters. These characteristics ensure that the adjacent waters are part of ‘‘an aquatic system incorporating navigable waters,’’ 547 U.S. at 781–82; and that they perform important functions to maintain the chemical, physical, or biological integrity of (a)(1) through (a)(3) waters.

In showing chemical, physical, and biological connections between adjacent waters and other jurisdictional waters, adjacent waters, including wetlands, may be separated by land or other features not regulated under the CWA, but those intervening uplands do not eliminate or impede the functional interactions between (a)(1) through (a)(5) waters and the waters, including wetlands, that are adjacent to them. For instance, two waters may be separated by upland but be connected through

surface or shallow subsurface

connections with water and chemicals readily exchanging between them. Similarly, uplands separating two waters may not act as a barrier to species that rely on and that regularly

move between the two waters. Therefore, the proposed rule reflects an understanding that adjacent waters affect the chemical, physical, and biological integrity of waters to which they are adjacent and to (a)(1) through (a)(3) waters even where the two waters may be separated by features that are not jurisdictional, such as uplands, berms, roads, levees, and similar features. The presence of these features does not extinguish jurisdiction, a conclusion contained in the agencies’ existing regulation at 33 CFR 328.3(c).

(1) Riparian and Floodplain Waters Significantly Affect the Chemical, Physical, and Biological Integrity of (a)(1) Through (a)(3) Waters

Riparian and floodplain waters, including wetlands, that are adjacent to (a)(1) through (a)(3) waters play an integral role in maintaining the chemical, physical, and biological integrity of those waters. In addition, riparian and floodplain waters, including wetlands, that are adjacent to (a)(4) and (a)(5) waters provide an important role in maintaining the chemical, physical, and biological integrity of traditional navigable waters, interstate waters, and the territorial seas. Among the ways in which riparian and floodplain waters, including wetlands, that are adjacent to (a)(4) and (a)(5) waters significantly affect the chemical, physical, or biological integrity of traditional navigable waters, interstate waters, and the territorial seas is by significantly affecting the chemical, physical, and biological integrity of the (a)(4) and (a)(5) waters to which they are adjacent, and those waters in turn significantly affect the chemical, physical, or biological integrity of traditional navigable waters, interstate waters, and the territorial seas.

(2) Waters, Including Wetlands,

Determined To Have a Confined Surface or a Shallow Subsurface Hydrologic Connection Significantly Affect the Chemical, Physical, and Biological Integrity of (a)(1) Through (a)(3) Waters.

The proposed rule includes as adjacent those waters that are ‘‘neighboring’’ because they possess a

shallow subsurface or confined surface hydrologic connection to a jurisdictional water, and therefore can exchange water, along with chemicals and organisms within that water, with an (a)(1) through (a)(5) water, and subsequently have a significant effect, particularly in combination with other adjacent waters in the watershed, on the chemical, physical, or biological integrity of a downstream traditional navigable water, interstate water, and

the territorial seas.

Confined surface connections that provide a discrete pathway for water to be exchanged between the potentially adjacent wetland or water and an (a)(1) through (a)(5) water present the clearest evidence of a hydrologic connection.

Shallow subsurface connections are also relevant, yet are more difficult to identify and document. Evidence shows that waters, including wetlands, located outside of the riparian area or floodplain, but which still have a

shallow subsurface or confined surface hydrologic connection to an (a)(1) through (a)(5) water, will have a significant nexus to downstream (a)(1) through (a)(3) waters. Note that nothing under the proposed rule would cause

the shallow subsurface connections themselves to become jurisdictional.

Examples of confined surface water hydrologic connections that demonstrate adjacency are swales, gullies, and rills. The frequency, duration, and volume of flow associated

with these confined surface connections can vary greatly depending largely on factors such as precipitation, snowmelt, landforms, soil types, and water table elevation. It is the presence of this hydrologic connection which provides the opportunity for neighboring waters to influence the chemical, physical, or biological integrity of (a)(1) through (a)(5) waters.

In circumstances where a particular water is outside of the floodplain and riparian area of a jurisdictional water, a connection can be established by

confined surface or shallow subsurface


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hydrology that makes the water neighboring, and thus adjacent. The scientific literature recognizes the role of hydrologic connections in supporting a substantial chemical, physical, or biological relationship between water bodies, but this relationship can be

reduced as the distance between water

bodies increases because of various factors, such as soil characteristics, geology, climate, precipitation patterns,

etc. The distance between water bodies may be sufficiently great that even the presence of an apparent hydrologic connection may not support an adjacency determination. The greater the distance, the less likelihood that

there is an actual shallow subsurface or confined surface hydrologic connection, because of the greater potential for the water to infiltrate the soil to deeper groundwater, or for transmission losses in any gully or swale (for example) that may appear to be hydrologic connections. Within a watershed, wetlands and open waters that are closer to tributaries will have a higher probability of being hydrologically connected and of being determined adjacent than more distant waters, assuming that conditions governing type and quantity of flows (e.g., slope, soil, and aquifer permeability) are similar. Report at 5–2. A determination of adjacency based on shallow subsurface or confined surface hydrologic connection outside the riparian area or floodplain requires clear

documentation.

H. ‘‘Other Waters’’

The ‘‘other waters’’ paragraph of the proposed rule is at (a)(7). To be clear,

these ‘‘other waters’’ are not jurisdictional as a single category; rather, as the proposed rule language states, ‘‘other waters’’ are jurisdictionalprovided that they are found, on a casespecific basis, to have a significant nexus to an (a)(1) through (a)(3) water. Thus, the introductory phrase ‘‘on a case-specific basis’’ is designed to signal clearly that this provision of the

definition of ‘‘waters of the United

States’’ does not mean ‘‘other waters’’ are ‘‘waters of the United States’’ by definition in the same way as those defined as jurisdictional in proposed paragraphs (a)(1) through (a)(6).

‘‘Other waters’’ will be evaluated either individually, or as a group of waters where they are determined to be similarly situated in the region. Waters are similarly situated where they perform similar functions and are located sufficiently close together or when they are sufficiently close to a jurisdictional water. How these ‘‘otherwaters’’ are aggregated for a casespecific significant nexus analysis depends on the functions they perform and their spatial arrangement within the ‘‘region’’ or watershed. For other waters that perform similar functions, their landscape position within the watershed (i.e., the ‘‘region’’) relative to each other or to a jurisdictional water is generally the determinative factor for aggregating waters in a significant nexus analysis, which will focus on the degree to which the functions provided by

those ‘‘other waters’’ affect the chemical, physical, or biological integrity of (a)(1) through (a)(3) waters and whether such effects are significant.

See Appendix A, Scientific Evidence (Part I, Discussion of Major Conclusions 2.C; Part II, iii) and Appendix B, Legal Analysis.

Significant nexus is proposed to be defined to mean that a water, including wetlands, either alone or in combination with other similarly situated waters in the region (i.e., the watershed that

drains to the nearest water identified in paragraphs (a)(1) through (a)(3) of this section), significantly affects the chemical, physical, or biological integrity of a water identified in paragraphs (a)(1) through (a)(3) of this section. For an effect to be significant, it must be more than speculative or insubstantial. Other waters, including wetlands, are similarly situated when they perform similar functions and are located sufficiently close together or sufficiently close to a ’’water of the United States’’ so that they can be evaluated as a single landscape unit with regard to their effect on the chemical, physical, or biological integrity of a water identified in paragraphs (a)(1) through (a)(3).

Other waters with a significant nexus can be found to be jurisdictional on a case-specific basis where these waters

do not fit within the definition of another of the proposed categories of

‘‘waters of the United States’’ under paragraphs (a)(1) through (a)(6) and are

not excluded from the definition of

‘‘waters of the United States’’ under proposed section (b).

A significant nexus analysis may be based on a particular water alone or

based on the effect that the water has in combination with other similarly situated waters in the region. Where effects will be analyzed in combination, the agencies will aggregate those effects. The agencies propose to interpret the ‘‘region’’ within which similarly situated waters would be aggregated as

the watershed that drains to the nearest traditional navigable water, interstate water, or the territorial seas.

For purposes of analyzing whether an ‘‘other water’’ has a significant nexus, the agencies are proposing that ‘‘other waters’’ are similarly situated if they perform similar functions and they are either (1) located sufficiently close together so that they can be evaluated as a single landscape unit with regard to their effect on the chemical, physical, or biological integrity of a water identified in paragraphs (a)(1) through (a)(3), or (2) located sufficiently close to a ‘‘water of

the United States’’ for such an

evaluation of their effect. These criteria are explained in a subsequent section.

Consistent with Justice Kennedy’s opinion in Rapanos, the agencies propose today and are soliciting comment on establishing a case-specific analysis of whether ‘‘other waters,’’ including wetlands, that do not meet the criteria for any of the proposed jurisdictional categories in (a)(1) through (a)(6) and are not proposed to be excluded by rule under section (b), are susceptible to a case-specific analysis of whether they alone, or in combination with other similarly situated waters, have a significant nexus to a traditional navigable water, an interstate water, or the territorial seas,

and therefore are ‘‘waters of the United

States.’’

1. Significant Nexus Analysis for ‘‘Other

Waters’’

a. ‘‘Other Waters’’

‘‘Other waters’’ are those waters, including wetlands, that are subject to a case-specific significant nexus determination, and do not meet the criteria of any of the categories of waters in (a)(1) through (a)(6), and also are not

one of the waters and features excluded

from the definition of ‘‘waters of the United States’’ in section (b). In theexisting regulation, there is a nonexclusive list of the types of ‘‘other waters’’ which may be found to be

‘‘waters of the United States.’’ Theagencies do not propose to repromulgate this list of ‘‘other waters’’ because it is unnecessary and has led to confusion where it has been incorrectly

read as an exclusive list.

Of additional concern was that the existing descriptive list of types of

‘‘other waters’’ includes some waters that would be jurisdictional under one of the proposed categories of ‘‘waters of

the United States’’ that would be jurisdictional by rule, such as tributary streams. The agencies want to avoid questions of whether an intermittent

stream that meets the definition of tributary also needs a separate significant nexus analysis. Under the proposed rule, that tributary stream does not require the significant nexus analysis. Removing the list of water


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types does not imply that any of the waters listed in the existing regulation are never jurisdictional under the proposed rule. When one of the waters

on the current enumerated list does not fall under a proposed category for jurisdiction (for example, adjacent waters under (a)(6) or tributaries under (a)(5)), those waters would be jurisdictional if found to have a significant nexus under proposed paragraph (a)(7) on a case-specific

basis.

b. Significant Nexus

The agencies recognize that Supreme

Court decisions in SWANCC and Rapanos placed limits on the scope of ‘‘other waters’’ that may be determined to be jurisdictional. Therefore, the agencies’ proposal today provides that

waters not determined to be jurisdictional as a category are jurisdictional only if they are determined on a case-specific basis to have a significant nexus to a traditional navigable water, an interstate water, or the territorial seas. The agencies also request comment and information below on how the science could support other approaches that could provide greater regulatory certainty regarding the jurisdictional status of ‘‘other waters’’, including expanding the list of waters jurisdictional by rule, expanding the list of waters not jurisdictional by rule, and narrowing the ‘‘other waters’’ subject to a case-specific analysis, including eliminating the case-specific analysis where the science does not support it. The agencies will review the administrative record, including comments received, the scientific literature, and the final Report, in determining how to address ‘‘other

waters’’ in the final rule.

Justice Kennedy explained the

SWANCC decision in his concurring opinion in Rapanos: ‘‘In Solid Waste Agency of Northern Cook Cty. v. Army Corps of Engineers, 531 U.S. 159 (2001) (SWANCC ), the Court held, under the circumstances presented there, that to constitute ‘navigable waters’ under the Act, a water or wetland must possess a ‘significant nexus’ to waters that are or were navigable in fact or that could reasonably be so made.’’ 547 U.S. at 759. The agencies interpret the significant nexus standard to apply to the ‘‘other waters’’ portion of the existing regulation since the Court in SWANCC was considering the validity of the Corps’ assertion of jurisdiction over ponds and mudflats under (a)(3) of the Corps’ regulations (33 CFR 328.3).

To comport with the SWANCC and Rapanos decisions, the agencies propose to delete the requirement that an ‘‘other water’’ be one the use, degradation or destruction of which could affect interstate or foreign commerce and to replace it with the requirement that the ‘‘other water’’ meet Justice Kennedy’s significant nexus standard. The current regulations assert jurisdiction more broadly than what is proposed today. With this proposed regulation, the agencies would limit jurisdiction over ‘‘other waters’’ to only

those that are determined on a casespecific basis to have a significant nexus to an (a)(1) through (a)(3) water.

For purposes of assessing whether a particular water is a ‘‘water of the United States’’ because it, alone or in combination with other similarly situated waters, has a significant nexus to an (a)(1) through (a)(3) water, the agencies are proposing to define ‘‘significant nexus’’ plus each of the key

elements used in the definition of ‘‘significant nexus.’’

i. In the Region

The agencies propose to interpret the phrase ‘‘in the region’’ to mean the

watershed that drains to the nearest traditional navigable water, interstate water, or the territorial seas through a single point of entry. That concept is reflected in the definition of ‘‘significant nexus’’ at (c)(7). Since Justice Kennedy did not define the ‘‘region,’’ the agencies

determined that because the movement of water from watershed drainage basins to river networks and lakes shapes the development and function of these systems in a way that is critical to their long term health, the watershed is a reasonable and technically appropriate extent on which to identify waters that together may have an effect on the chemical, physical, or biological integrity of a particular (a)(1), through (a)(3) water. See Appendix A, Scientific Evidence (Part I, Background; Part II, 4, iii, A).

The agencies choose to use the single point of entry watershed as the appropriate scale for the region. A single point of entry watershed is the drainage

basin within whose boundaries all precipitation ultimately flows to the nearest single traditional navigable water, interstate water, or the territorial sea. There will likely be other traditional navigable waters, interstate waters, and ultimately the territorial

seas further downstream from the ‘‘nearest’’ such water, and these further downstream waters would likely have larger watersheds, but the agencies

determined that a reasonable interpretation of ‘‘in the region’’ is the watershed that drains to the nearest (i.e. first downstream) such water. Any

nexus between other waters and an (a)(1) through (a)(3) water will be strongest with this nearest such water, and its drainage area is likely to be of a size commonly understood as a ‘‘region.’’

The agencies generally use available mapping tools that are based on the National Hydrography Dataset (NHD) to demarcate boundaries of the single point of entry watershed. This point of entry approach identifies a group of waters that flow to a single location and represents the scientifically appropriate sized area for conducting a significant

nexus evaluation in most cases. In the arid West, the agencies recognize there may be situations where the single point of entry watershed is very large, and it may be resource intensive to demarcate

watershed boundaries and all relevant

waters in the watershed. Under those circumstances, for practical administrative purposes the agencies could use the NHD mapping tool to demarcate catchments surrounding the water to be evaluated that, in combination, are roughly the size of the typical nearby 10-digit hydrologic unit code (HUC–10) watershed. This

combination of catchments would be used for conducting a significant nexus evaluation. Such an approach can help resolve some practical concerns about using available mapping tools on very large single point of entry watersheds in

the arid West.

The watershed includes all lands, streams, wetlands, lakes, and other waters within its boundaries. Only

waters within the watershed that meet standards set out in (a)(1) through (a)(7) of the proposed rule would be

considered ‘‘waters of the United States.’’ In light of the scientific literature, the longstanding approach of the agencies to implementation of the CWA, and the statutory goals underpinning Justice Kennedy’s significant nexus framework, the watershed draining to the nearest (a)(1) through (a)(3) water is the appropriate ‘‘region’’ for a significant nexus analysis.

ii. Similarly Situated

Justice Kennedy provided guidance to the agencies that establishing a significant nexus requires examining

whether a water ‘‘alone or in combination with similarly situated [wet]lands in the region, significantly affect[s] the chemical, physical, and biological integrity of other covered waters more readily understood as ‘navigable.’ ’’ 547 U.S. at 780. The proposed rule adopts the concept of the ‘‘alone or in combination with similarly

situated waters’’ test.


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The proposed regulation in the definition of ‘‘significant nexus’’ at (c)(7) clarifies that other waters, including wetlands, are similarly situated when they perform similar functions and are located sufficiently close together or sufficiently close to a ‘water of the United States’ so that they can be evaluated as a single landscape unit with regard to their effect on the chemical, physical, or biological integrity of a water identified in paragraphs (a)(1) through (a)(3) This combination of functionality and proximity to each other or to a ‘‘water

of the United States’’ meets the standard provided by Justice Kennedy. Examining both functionality and proximity also limits the ‘‘other waters’’ that can be aggregated for purposes of determining jurisdiction.

It is appropriate to analyze the chemical, physical, or biological effects ‘‘other waters’’ perform individually or together with all similarly situated ‘‘other waters’’ in the region under Justice Kennedy’ s standard. Today, the agencies are proposing to identify factors to apply in the determination of

when ‘‘other waters’’ should be considered either individually or as a single landscape unit for purposes of a significant nexus analysis. The agencies propose that ‘‘similarly situated’’ requires an evaluation of either a single water or group of waters (i.e., a single landscape unit) in the region that can reasonably be expected to function together in their effect on the chemical, physical, or biological integrity of downstream traditional navigable waters, interstate waters, or the

territorial seas.

In addition, the agencies propose that

‘‘other waters’’ located close to a jurisdictional water are more likely to influence such waters and therefore, to affect the integrity of downstream (a)(1) through (a)(3) waters. These ‘‘other waters,’’ which do not meet the proposed definition of adjacent waters, may be assessed together when determining on a case-specific basis whether a significant nexus exists,

because of their similar functions and similar location in the landscape.

Similarly situated waters may be identified as sufficiently close together for purposes of this paragraph of the proposed regulation when they are within a contiguous area of land with relatively homogeneous soils, vegetation and landform (e.g., plain, mountain, valley, etc.). As a general matter, it would be inappropriate, for example, to consider ‘‘other waters’’ as ‘‘similarly

situated’’ if these ‘‘other waters’’ are located in different landforms, have different elevation profiles, or have different soil and vegetation characteristics, unless the ‘‘other waters’’ perform similar functions and are located sufficiently close to a ‘‘water

of the United States’’ to allow them to consistently and collectively function together to affect an (a)(1) through (a)(3) water. In determining whether other waters are sufficiently close to each other or to a water of the United States, the agencies would also consider hydrologic connectivity to each other or a jurisdictional water.

In determining whether groups of other waters perform ‘‘similar functions’’ the agencies would also consider functions such as habitat, water storage, sediment retention, and pollution sequestration. These and other

relevant considerations would be used by the agencies to document the hydrologic, geomorphic and ecological

characteristics and circumstances of the waters. Examples include: documentation of chemical, physical, and biological interactions of the similarly situated ‘‘other waters;’’ aerial photography; topographical or terrain maps and information; other available geographic information systems (GIS) data; National Wetlands Inventory Maps; and state and local information. The evaluation would use any available site information and pertinent field observations where available, relevant scientific studies or data, or other relevant jurisdictional determinations that have been completed in the region.

Under the proposed rule, the agencies

would assess the combined effects of similarly situated ‘‘other waters’’ in the region on the chemical, physical, or biological integrity of (a)(1) through (a)(3) waters in conducting a significant nexus analysis. The factors identified above would be used by the agencies in determining ‘‘other waters’’ in the region that are similarly situated and should, therefore, be considered together in conducting a significant nexus analysis. The agencies recognize

that consideration of these factors will often limit aggregation of ‘‘other waters’’ for purposes of assessing significant nexus or will require that ‘‘other waters’’ be considered individually with no aggregation.

iii. Significant Nexus

The agencies propose to define the term ‘‘significant nexus’’ consistent with language in SWANCC and Rapanos. The proposed definition recognizes that not all waters have this requisite connection to traditional navigable waters, interstate waters, or the territorial seas

sufficient to be determined jurisdictional. Justice Kennedy was clear that waters with a significant nexus must significantly affect the chemical, physical, or biological integrity of a downstream navigable water and that the requisite nexus must be more than ‘‘speculative or insubstantial,’’ Rapanos, at 780, and the agencies propose to define significant nexus in precisely those terms.

It is important to note that in Rapanos, Justice Kennedy did not conclude that the wetlands adjacent to

tributaries in the cases before the Court

were not ‘‘waters of the United States.’’ Rather, Justice Kennedy concluded that the proper inquiry to determine their jurisdictional status—whether or not the wetlands had a ‘‘significant nexus’’— had not been made by the Corps or the courts below. Justice Kennedy stated

that in both the consolidated cases

before the Court the record contained the types of evidence relevant to the determination of a significant nexus according to the principles he identified. Justice Kennedy stated ‘‘[m]uch the same evidence should permit the establishment of a significant nexus with navigable-in-fact waters, particularly if supplemented by further evidence about the significance of the

tributaries to which the wetlands are

connected.’’ Id. Thus, Justice Kennedy

concluded that ‘‘the end result in these cases and many others to be considered by the Corps may be the same as that suggested by the dissent, namely, that the Corps’ assertion of jurisdiction is

valid.’’ See Appendix B, Legal Analysis.

The agencies will determine whether the water they are evaluating, in combination with other similarly situated waters in the region, has a significant nexus to the nearest traditional navigable water, interstate

water or the territorial seas. Functions of waters that might demonstrate a significant nexus include sediment trapping, nutrient recycling, pollutant trapping and filtering, retention or attenuation of flood waters, runoff storage, export of organic matter, export of food resources, and provision of aquatic habitat. A hydrologic connection is not necessary to establish a significant nexus, because, as Justice Kennedy stated, in some cases the lack of a hydrologic connection would be a sign of the water’s function in relationship to the traditional navigable water, interstate water or the territorial seas. These functional relationships

include retention of flood waters or pollutants that would otherwise flow downstream to the traditional navigable water, interstate water or the territorial

seas. See 547 U.S. at 775 (citations omitted) (J. Kennedy) (‘‘it may be the absence of an interchange of waters prior to the dredge and fill activity that


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makes protection of the wetlands critical to the statutory scheme’’). For example, a report that reviewed the results of multiple scientific studies concluded that depressional wetlands lacking a surface outlet functioned together to significantly reduce or attenuate flooding. Report at 5–26 (citing A. Bullock and M. Acreman,

‘‘The Role of Wetlands in the Hydrological Cycle,’’ Hydrology and Earth System Sciences 7:358–389 (2003)).

When evaluating an ‘‘other water’’ individually or cumulatively for the presence of a significant nexus to an (a)(1) through (a)(3) water, there are a variety of factors that can be considered that will influence the chemical, physical, or biological connections the

‘‘other water’’ has with the downstream (a)(1) through (a)(3) water. The likelihood of a significant connection is greater with increasing size and decreasing distance from the identified (a)(1) through (a)(3) water, as well as with increased density of the ‘‘other

waters’’ for ‘‘other waters’’ that can be

considered in combination with similarly situated waters.

Evidence of chemical connectivity and the effect on waters can be found by identifying: Whether the properties of the water in question are similar or dissimilar to an identified (a)(1) through (a)(3) water; signs of retention, release,

or transformation of nutrients or pollutants; and the effect of landscape position on the strength of the

connection to the nearest ‘‘water of the United States,’’ and through it to an (a)(1) through (a)(3) water. In addition, relevant factors influencing chemical connectivity include hydrologic connectivity (see physical factors, below), surrounding land use and land cover, the landscape setting, and deposition of chemical constituents (e.g. acidic deposition).

Evidence of physical connectivity and the effect on (a)(1) through (a)(3) waters can be found by identifying evidence of physical connections, such as flood water or sediment retention (flood prevention). Presence of indicators of hydrologic connections between the other water and jurisdictional water are also indictors of a physical connection. Factors influencing physical connectivity include rain intensity, duration of rain events or wet season, soil permeability, and distance of hydrologic connection between the ‘‘other water’’ and the (a)(1) through (a)(3) water, depth from surface to water table, and any preferential flowpaths.

Evidence of biological connectivity and the effect on waters can be found byidentifying: resident aquatic or semiaquatic species present in the ‘‘other water’’ and the tributary system (e.g., amphibians, aquatic and semi-aquatic reptiles, aquatic birds); whether those species show life-cycle dependency on the identified aquatic resources (foraging, feeding, nesting, breeding, spawning, use as a nursery area, etc.); and whether there is reason to expect presence or dispersal around the ‘‘other water,’’ and if so whether such dispersal extends to the tributary system or beyond or from the tributary system to the ‘‘other water.’’ Factors influencing biological connectivity include species’ life history traits, species’ behavioral traits, dispersal range, population size, timing of dispersal, distance between ‘‘other water’’ and an (a)(1) through (a)(3) water, the presence of habitat corridors or barriers, and the number, area, and spatial distribution of habitats. Non-aquatic species or species such as non-resident migratory birds that are not demonstrating a life cycle dependency on the identified aquatic resources are not evidence of biological connectivity for purposes of this rule.

When making a jurisdictional determination for an ‘‘other water,’’ the

administrative record will include available information supporting the

determination. In addition to location and other descriptive information regarding the water at issue, the record will include a clear explanation of the rationale for the jurisdictional conclusion and a description of the

information used to determine whether the ‘‘other water’’ has a significant nexus. Information relevant to a finding

that an ‘‘other water’’ alone or in combination with similarly situated ‘‘other waters’’ in the region can come from many sources. Such information need not always be specific to the water whose jurisdictional status is being evaluated. Regional and national studies of the same type of water or similarly situated waters can help to inform a significant nexus analysis as long as they are applicable to the water being

evaluated. Information derived from field observation is not required in cases where a ‘‘desktop’’ analysis can provide

sufficient information to make the requisite findings. However, for more complex or difficult jurisdictional determinations, it may be helpful to supplement such information with field

observation.

The agencies solicit comment regarding this approach to ‘‘other waters,’’ recognizing that a case-specificanalysis of significant nexus is resourceintensive for the regulating agencies and the regulated community alike. In addition, the agencies solicit comment

on additional scientific research and data that might further inform decisions about ‘‘other waters.’’ In particular the agencies solicit information about

whether current scientific research and data regarding particular types of waters are sufficient to support the inclusion of subcategories of types of ‘‘other waters,’’

either alone or in combination with similarly situated waters, that can appropriately be identified as always lacking or always having a significant

nexus.

iv. Additional Request for Public

Comment on ‘‘Other Waters’’

As stated above, significant goals of the agencies in developing this proposed rule are to provide greater clarity, certainty, and predictability to the public as to what waters are and are not subject to the jurisdiction of the CWA. The agencies will achieve these goals consistent with the CWA, as interpreted by the Supreme Court, and as supported by the best available science. The agencies also will fulfill their responsibility to the CWA’s objectives and policies to protect water quality, public health, and the

environment.

The agencies acknowledge that there may be more than one way to determine which waters are jurisdictional as ‘‘other waters.’’ This proposal is for a case-specific analysis of whether ‘‘other waters,’’ including wetlands, alone, or in combination with other similarly

situated waters located in the same region, have a significant nexus to a traditional navigable water, interstate water, or the territorial seas. The agencies make this proposal based on an analysis of the current state of the

science available to them. In this proposal, the agencies continue to solicit additional science (peer-reviewed whenever possible) that could lead to greater clarity, certainty, and predictability of which waters are and are not within the jurisdiction of the

CWA.

To best meet their goals and responsibilities, the agencies solicit

comment and information on the state of the science, and its relation to the CWA and the caselaw, to determine if there are opportunities to provide greater clarity, certainty, and predictability for establishing jurisdiction over ‘‘other waters.’’ This includes the possibility of determining

that additional waters should be jurisdictional by rule such as in paragraphs (a)(1) through (a)(6), and the possibility that additional waters should be excluded from jurisdiction by rule such as in section (b). The agencies’

decision on how best to address jurisdiction over ‘‘other waters’’ in the


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final rule will be informed by the final version of the Report and other available

scientific information.

The agencies request public comment on whether these alternative approaches present options for determining the jurisdictional status of ‘‘other waters’’ that could rely less, or not at all, on case-specific analysis of whether waters are similarly situated for conducting a significant nexus analysis. Possible alternative options to the case-specific

determination in the ‘‘other waters’’ proposal are described below. The agencies might adopt any combination of today’s ‘‘other waters’’ proposal and the alternative options for the final rule, after considering public comment and the evolving scientific literature on connectivity of waters.

The agencies solicit comment on how the agencies propose to find ‘‘other waters’’ to be similarly situated in this proposed rule, whether other methods of identifying similarly situated ‘‘other waters’’ would be reasonable, and

whether no ‘‘other waters’’ should be determined to be similarly situated. In each instance, the comments should address how the actions of the agencies would be consistent with the science, including any science not currently before the agencies, the CWA, and the

caselaw.

The agencies considered multiple approaches and options for how best to

address whether ‘‘other waters’’ were jurisdictional under the CWA. In addition to the case-specific analysis in the proposal, the agencies seek comment on the following alternatives:

1. Determine by rule that ‘‘other waters’’ are similarly situated in certain areas of the country.

The case-specific analysis in the proposed rule approaches the question of what ‘‘other waters’’ are similarly situated for purposes of aggregation in the same manner throughout the U.S. The agencies could determine by rule that ‘‘other waters’’ are similarly situated in only certain areas of the country, and not in other areas. Under this option, the agencies would identify ecological regions (ecoregions) which

contain ‘‘other waters’’ that are ‘‘similarly situated’’ as provided in the proposed rule. Where waters are determined to be similarly situated, those waters are aggregated for evaluation of whether they have a significant nexus to a traditional navigable water, interstate water, or the territorial seas. The agencies expect that determining all ‘‘other waters’’ within an ecoregion to be similarly situated

would result in these ‘‘other waters’’ being determined to have a significant nexus and being found jurisdictional. Waters not located in these identified ecoregions or other specified areas would be determined to not be similarly

situated and their effects would not be aggregated for purposes of a significant

nexus determination. The result of not finding waters to be similarly situated would most likely be a finding of no significant nexus and no jurisdiction. The agencies particularly seek comment on whether the science supports differing approaches with respect to which ‘‘other waters’’ are similarly

situated in certain areas of the U.S based on distinguishing factors in those areas.

The agencies also request comment on

factors that could lead ‘‘other waters’’ to be aggregated in some areas but analyzed individually in other areas for purposes of informing a case-specific significant nexus analysis. The agencies request comment on whether some resource types are more or less likely to be similarly situated than others, and if there are ways to identify regions within which aggregation of ‘‘other waters’’ would be routinely applied rather than a case-specific determination. The agencies also request comment about

whether ‘‘other waters’’ that are not found in identifiable mapped regions should be analyzed individually on a case-specific basis for a significant nexus, aggregated in some other way for a significant nexus analysis, or categorically excluded from jurisdiction.

An ecoregion is an area within the United States that includes generally similar ecosystems and that has similar types, qualities, and quantities of environmental resources. (J.M. Omernik, ‘‘Perspectives on the Nature and Definition of Ecological Regions,’’ Environmental Management 34(Supplement 1):S27–S38 (2004)). Ecoregions cover relatively large areas of land or water, and contain characteristic, geographically distinct assemblages of natural communities and species. The biodiversity of flora, fauna and ecosystems that characterize an ecoregion tends to be distinct from that of other ecoregions. (Id.)

Level III ecoregions are the second most detailed level of ecoregions nationally, with 105 Level III ecoregions in the conterminous United States, and have been refined over the years in several state-level projects conducted in

collaboration with the EPA and other Federal and State agencies. U.S. Environmental Protection Agency, ‘‘Level III Ecoregions of the Continental United States,’’ map scale 1:7,500,000 (Corvallis, OR: U.S. EPA—National

Health and Environmental Effects Research Laboratory, 2013), available at http://www.epa.gov/wed/pages/ ecoregions/level

_iii

_iv.htm. For this reason, the agencies consider Level III ecoregions to be the most appropriate level for analysis. The ‘‘other waters’’ in these ecoregions are within a contiguous area of land with relatively homogeneous soils, vegetation and landform (e.g., plain, mountain, valley, etc.), and generally provide similar

functions to the downstream traditional navigable waters, interstate waters, or the territorial seas. A possible list of Level III ecoregions where waters are similarly situated and aggregation could

be used include:

1. Coast Range

4. Cascades

6. Central California Foothills and

Coastal Mountains 7. Central California Valley

8. Southern California Mountains 9. Eastern Cascades Slopes and Foothills

10. Columbia Plateau

27. Central Great Plains

34. Western Gulf Coastal Plain

42. Northwestern Glaciated Plains

44. Nebraska Sand Hills

46. Northern Glaciated Plains

47. Western Corn Belt Plains 48. Lake Agassiz Plain

50. Northern Lakes and Forests

51. North Central Hardwood Forests

59. Northeastern Coastal Zone

63. Middle Atlantic Coastal Plain

65. Southeastern Plains

75. Southern Coastal Plain 78. Klamath Mountains/California High

North Coast Range 81. Sonoran Basin and Range

83. Eastern Great Lakes Lowlands

84. Atlantic Coastal Pine Barrens 85. Southern California/Northern Baja

Coast

See Map A in docket.

The agencies would consider the ‘‘other waters’’ in a single point of entry watershed in these identified ecoregions as similarly situated for purposes of aggregation for a significant nexus analysis. The agencies expect that this approach would lead to all similarly situated other waters within single point of entry watersheds within an ecoregionbeing found jurisdictional through casespecific analysis of significant nexus. Alternately, the agencies could determine that the similarly situated waters within each ecoregion have a significant nexus and are jurisdictional by rule and therefore do not require a case-specific significant nexus analysis.

The agencies request comment on the list of ecoregions above and whether this list is appropriate, and whether there are other ecoregions or distinct

areas that should be included or

excluded from this list. This list does not include regions in Alaska or Hawaii and the agencies request comment on


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appropriate regions to use to analyze

‘‘other waters’’ in those states. The agencies also request comment on whether using Level III ecoregions is appropriate or whether a finer gradation of ecoregions would be more appropriate.

The factors the agencies used in developing the list above are:

a. Density of ‘‘other waters’’ such that there can be periodic surface hydrologic connections among the waters, for example in West Coast vernal pools.

b. Soil permeability and surface or

shallow subsurface flow such that the

‘‘other waters’’ can be considered hydrologically connected, such as many Texas coastal prairie wetlands.

c. Water chemistry which indicates that the ‘‘other waters’’ are part of the same system and influenced by the

same processes.

d. Physical capacity of ‘‘other waters’’ to provide flood and sediment retention;

this is a case where several small wetlands together may have a different effect than a single large wetland providing the same function, for example prairie potholes in the

Missouri Coteau.

e. Co-location of waters to each other or similarly to the tributary system such

that their cumulative and additive effects on pollutant removal through parallel, serial, or sequential processing are apparent, such as the role of pocosins in maintaining water quality in

estuaries.

f. ‘‘Other waters’’ that are sufficiently near each other or the tributary system and thus function as an integrated habitat that can support the life cycle of a species or more broadly provide habitat to a large number of a single species.

The agencies request comment on the

factors above and whether this list of factors is appropriate, and whether there

are other factors that should be included

or excluded from this list. Comments should address the science that supports

each comment.

In addition to ecoregions, another method of mapping boundaries where

waters could be considered to be similarly situated for a significant nexusanalysis would be to rely on hydrologiclandscape regions. Hydrologiclandscape regions are groups of watersheds that are clustered together

on the basis of similarities in landsurface form, geologic texture, and climate characteristics. (D.M. Wolock, et
al. ‘‘Delineation and Evaluation of Hydrologic-Landscape Regions in the United States Using Geographic Information System Tools and Multivariate Statistical Analyses,’’ Environmental Management 34(Supplement 1):S71–S88 (2004)). Hydrologic-landscape regions are based on a concept that reflects fundamental hydrologic processes that are expected to affect water quality and other

environmental characteristics.

The agencies seek comment on the technical bases for using ecoregions and hydrologic-landscape regions under this option. Commenters may also address

whether some other method or combination of methods (certain ecoregions and hydrologic-landscape regions, for example) of mapping geographic boundaries is better supported by the science. Comments

should also address whether and how this option is consistent with the

science and the caselaw.

If the agencies choose to determine by

rule that ‘‘other waters’’ in certain ecoregions or other geographic boundaries are similarly situated, the agencies could also determine that

waters not located in identified ecoregions or otherwise specifically identified areas are not similarly situated for purposes of establishing a significant nexus and jurisdiction. The agencies also request comment on

whether ‘‘other waters’’ that are not found in identifiable mapped ecoregions or other areas should be analyzed individually on a case-specific basis for determining a significant nexus, and on whether or not case-specific analysis of whether there are similarly situated

‘‘other waters’’ in the area is advisable.

2. Determine by rule that certain additional subcategories of waters would be jurisdictional rather than addressed with a case-specific analysis, and that other subcategories of waters would be non-jurisdictional.

The agencies could choose to

determine that there is science available to determine by rule that certain additional subcategories of ‘‘other waters’’ are similarly situated and have a significant nexus and are jurisdictional by rule rather than addressed with a case-specific significant nexus analysis under paragraph (a)(7). Such an approach would lead to certain subcategories of ‘‘other waters’’ being determined jurisdictional in the same way that waters under paragraphs (a)(1) through(a)(6) are jurisdictional without a casespecific significant nexus analysis. Under this option the agencies could determine that waters such as prairie potholes, Carolina and Delmarva bays, pocosins, Texas coastal prairie wetlands, western vernal pools, and perhaps other categories of waters,

either alone or in combination with other waters of the same type in a single point of entry watershed, have a significant nexus and are jurisdictional by rule. See Appendix A, Part II, iii.C(1).These waters would not require a casespecific significant nexus analysis to determine jurisdiction.

In addition, the agencies could determine that other subcategories of waters are not jurisdictional and lack a significant nexus to an (a)(1) through (a)(3) water. Under this option the agencies could conclude that ‘‘other waters’’ such as playa lakes in the Great Plains, even in combination with other playa lakes in a single point of entry watershed, lack a significant nexus and therefore are not jurisdictional. See Appendix A, Part II, iii.C(1).

Under this approach, where a playa lake, or other excluded category of water, would be within a category established by paragraphs (a)(1) through (a)(6) of the proposed rule (e.g., the playa is an interstate water or the playa is adjacent to an (a)(1) through (a)(5) water), the playas would be jurisdictional. (See R.W. Tiner, ‘‘Geographically Isolated Wetlands of the United States,’’ Wetlands 23(3):494– 516 (2003); M.G. Forbes, et al.,

‘‘Nutrient Transformation and Retention by Coastal Prairie Wetlands, Upper Gulf Coast, Texas,’’ Wetlands 32(4): 705–715 (2012)).

The agencies seek comment on how they should categorize the remaining ‘‘other waters.’’ The agencies seek comment on whether these remaining

‘‘other waters’’ should be nonjurisdictional because they would lack a significant nexus to a traditional navigable water, interstate water, or the

territorial seas.

There is substantial value to the regulated public and all other stakeholders in providing increased certainty regarding which ‘‘other waters’’ are jurisdictional and which are not. By expanding the categories of waters determined jurisdictional and expanding the categories of waters not categorized as jurisdictional, the agencies can better address the clarity, certainty, and predictability goals of this rule. However, the agencies acknowledge that the science may not be sufficient today to conclusively determine whether all categories of other waters significantly affect the chemical, physical and biological integrity of (a)(1) through (a)(3) waters. The agencies seek comment on the science used in support of the proposed rule, plus any additional science they should consider when determining jurisdiction. The agencies also seek

comment on how inconclusiveness of

the science relates to the use of casespecific determinations. As the science develops, the agencies could determine


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that additional categories of ‘‘other waters’’ are similarly situated and have a significant nexus and are jurisdictional by rule, or that as a class they do not have such a significant nexus and might not be jurisdictional.

If waters are categorized as nonjurisdictional because of a lack of science available today, the agencies request comment on how to best accommodate evolving science in the future that could indicate a significant

nexus for these ‘‘other waters.’’ Specifically, the agencies request

comment as to whether this should be done through subsequent rulemaking, or through some other approach, such as through a process established in this rulemaking.

The agencies also seek comment on how the science supports retaining the case-specific determination for the remaining ‘‘other waters’’ that are neither specifically included nor excluded from jurisdiction. Retaining the case-specific analysis for these other waters would not enhance clarity of jurisdiction for these other waters, but it would retain the ability for a jurisdictional determination consistent with the objective of the CWA to restore and maintain the chemical, physical, and biological integrity of the nation’s waters. In the alternative, the agencies

seek comment on whether it would be appropriate to categorize remaining ‘‘other waters’’ as not jurisdictional. The agencies specifically seek comment on

how these ‘‘other waters’’ should be

considered.

3. Additional ‘‘other waters’’ approaches.

The agencies request comment on additional ‘‘other waters’’ approaches considered, but not proposed by the agencies.

The agencies could determine that no ‘‘other waters’’ are similarly situated, and all significant nexus analyses would be made on a case-specific basis for each individual ‘‘other water.’’ The agencies expect that this likely would result in few if any other waters being found jurisdictional. The agencies recognize that if they determine there are no similarly situated ‘‘other waters,’’ there are issues about consistency with existing scientific information and studies regarding the functional relationship of ‘‘other waters’’ of the same type, and their contribution to the chemical, physical, or biological integrity of streams, rivers, lakes, and similar waters. There are also questions of how finding no ‘‘other waters’’ to be similarly situated reconciles with the portion of Justice Kennedy’s opinion discussing ‘‘similarly situated’’ waters in the region that ‘‘significantly affect’’ the chemical, physical, or biological integrity of waters more traditionally understood as navigable. While the agencies do not propose to determine that no ‘‘other waters’’ are similarly situated and aggregated, the agencies specifically seek comment on whether and how choosing to find no ‘‘other waters’’ similarly situated would be
consistent with the science, the CWA,

and the caselaw.

The agencies also considered and seek

comment on all ‘‘other waters’’ in a single point of entry watershed being evaluated as a single landscape unit with regard to their effect on traditional navigable waters, interstate waters, and

the territorial seas.

The agencies seek comment that

would inform a decision that these ‘‘other waters’’ in a single point of entry watershed perform similar functions and are located sufficiently close together or to a paragraph (a)(1) through (a)(5) water so that they can be aggregated and evaluated as a single landscape unit with regard to their effects on the nearest (a)(1) through (a)(3) water. Generally, the agencies anticipate that if the other waters in a single point of entry watershed are aggregated as a single unit, these waters

would be determined to have a significant nexus and be jurisdictional.

The agencies recognize that if they choose to aggregate all other waters in a single point of entry watershed, there likely is insufficient existing scientific information to support the

determination that all ‘‘other waters’’ in

watersheds across the nation are similarly situated as provided in this

rule and described in the caselaw. There are also questions of how determining ‘‘other waters’’ in a single point of entry watershed to be similarly situated reconciles with the portion of Justice Kennedy’s opinion discussing ‘‘similarly situated’’ waters in the region that ‘‘significantly affect’’ the chemical, physical, or biological integrity of waters more traditionally understood as navigable. While the agencies do not propose to determine that ‘‘other waters’’ in a single point of entry watershed are similarly situated and aggregated, the agencies seek comment on whether and how choosing to find such ‘‘other waters’’ similarly situated
would be consistent with the science,
the CWA, and the caselaw.

The agencies’ determination will be informed by the final version of the Report and other available scientific

information. I. Waters That Are Not ‘‘Waters of the

United States’’

The agencies’ longstanding regulations exclude waste treatment systems designed to meet the requirements of the CWA and prior converted cropland from the definition

of ‘‘waters of the United States.’’ The agencies propose no changes to these exclusions and therefore they would continue as a part of this rulemaking. The agencies also propose to codify for the first time longstanding practices that have generally considered certain features and types of waters not to be ‘‘waters of the United States.’’ Codifying these longstanding practices supports the agencies’ goals of providing greater clarity, certainty, and predictability for the regulated public and the regulators. Under today’s proposal, the waters identified in section (b) as excluded

would not be ‘‘waters of the United States,’’, even if they would otherwise fall within one of the categories in (a)(1) through (a)(7).

The agencies propose ministerial actions with respect to the placement of the two existing exemptions for waste treatment systems and prior converted cropland. They will be in proposed new section (b). For the waste treatment systems exclusion, the agencies propose

to delete a cross-reference in the current language to an EPA regulation that is no longer in the Code of Federal Regulations. The parenthetical to be deleted states: ‘‘(other than cooling ponds as defined in 40 CFR 423.11(m)

which also meet the criteria of this definition).’’ The agencies do not

consider this deletion to be a substantive change to the waste treatment systems exclusion or how it is applied. In fact, the agencies do not propose to make conforming changes to ensure that each of the existing

definitions of the ‘‘waters of the United States’’ for the various CWA programs have the exact same language with respect to the waste treatment system exclusion. The regulations implementing the various CWA programs were promulgated and

amended at different times and

therefore there are some differences in language. For example, compare EPA’s regulations for the section 402 program, 40 CFR 122.2 with the Corps’ regulations for the 404 program, 33 CFR 328.3. The agencies do not propose to

address the substance of the waste treatment system exclusion and thus will leave each regulation as is with theexception of deleting the crossreference.

In addition, this regulation does not address or change in any way the many


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statutory exemptions from CWA permitting requirements. The proposed rule does not affect any of the exemptions provided by CWA section 404(f), including those for normal farming, silviculture, and ranching activities. CWA section 404(f); 40 CFR 232.3; 33 CFR 323.4. The proposed rule also does not address or change the statutory and regulatory exemptions from NPDES permitting requirements such as those for agricultural stormwater discharges, return flows from irrigated agriculture, or the status of water transfers. CWA section 402(l)(1) (exempting discharges composed entirely of return flows from irrigated agriculture from section 402 permit requirements); CWA section 502(14)(excluding agricultural stormwater discharges and return flows from irrigated agriculture from the term point source.); 40 CFR 122.3(f) (excluding return flows from irrigated agriculture from the NPDES program); 40 CFR 122.2 (excluding return flows from irrigated agriculture or agricultural storm water runoff from the term point source.).

Finally, in new paragraphs (b)(3) through (5), the agencies propose, for the first time by rule, to exclude some waters and features that the agencies have by longstanding practice generally

considered not to be ‘‘waters of the United States.’’ Specifically, the agencies propose that the following are

not ‘‘waters of the United States’’ notwithstanding whether they would otherwise be jurisdictional under section (a):

• Ditches that are excavated wholly in uplands, drain only uplands, and have less than perennial flow.

• Ditches that do not contribute flow, either directly or through another water, to a traditional navigable water, interstate water, the territorial seas or impoundment.

• The following features:

Æ Artificially irrigated areas that would revert to upland should application of irrigation water to that

area cease;

Æ Artificial lakes or ponds created by excavating and/or diking dry land and used exclusively for such purposes as stock watering, irrigation, settling basins, or rice growing;

Æ Artificial reflecting pools or swimming pools created by excavating and/or diking dry land;

Æ Small ornamental waters created by excavating and/or diking dry land for primarily aesthetic reasons;

Æ Water-filled depressions created incidental to construction activity; Æ Groundwater, including groundwater drained through subsurface drainage systems; and

Æ Gullies and rills and non-wetland

swales.

Most of these features and waters have been identified by the agencies as generally not ‘‘waters of the United States’’ in previous preambles or guidance documents. The agencies’ have always preserved the authority to determine in a particular case that any

of these waters are a ‘‘water of the United States.’’ One of the agencies’ goals in this proposed rule is to increase clarity and certainty about the scope of

‘‘waters of the United States.’’ To that end, the agencies propose not simply

that these features and waters are ‘‘generally’’ not ‘‘waters of the United States,’’ but that they are expressly not ‘‘waters of the United States’’ by rule. The agencies would not retain the authority to determine that any of these

waters was a ‘‘water of the United

States’’ because it would otherwise be jurisdictional under section (a). For example, the agencies could not find that a water had a significant nexus and was an ‘‘other waters’’ under paragraph (a)(7), or that it was an interstate water under paragraph (a)(2). These waters would not be jurisdictional by rule.

In determining that these features and

waters are not ‘‘waters of the United States,’’ the agencies are by the decisions of the Supreme Court. In Riverside Bayview, the Supreme Court deferred to the agencies’ regulations and noted the difficulty of drawing lines identifying where waters end. The plurality opinion in Rapanos also noted

that there were certain features that were not primarily the focus of the

CWA. See 547 U.S. at 734. In this section of the proposed rule, the agencies are drawing lines and concluding that certain waters and features are not subject to the jurisdiction of the Clean Water Act.

A similar list of waters and features not generally ‘‘waters of the United States’’ was provided by the Corps in a 1986 preamble to the existing rule defining ‘‘waters of the United States’’ (51 FR 41206, 41217, November 13, 1986) and by the EPA in a 1988 preamble (53 FR 20764, June 6, 1988). In today’s proposed rule, the agencies

have clarified and added to the list in order to provide a full description of the

waters that will not be ‘‘waters of the United States’’ by rule. The agencies have never interpreted ‘‘waters of the United States’’ to include groundwater and the proposed rule explicitly excludes groundwater, including groundwater drained through subsurface drainage systems. In clarifying the list of waters not subject to CWA jurisdiction, the agencies did not include ‘‘puddles’’ from the lists of waters generally not considered jurisdictional in previous preambles or guidance documents. This is not because puddles are considered jurisdictional, it is because ‘‘puddles’’ is not a sufficiently precise hydrologic term or a hydrologic feature capable of being easily understood. Because of the lack of common understanding and precision inherent in the term ‘‘puddles,’’ the agencies determined that adding puddles would be contrary to the agencies’ stated goals of increased clarity, predictability, and certainty. In addition, one commonly understood meaning for the term ‘‘puddle’’ is a relatively small, temporary pool of water that forms on pavement or uplands immediately after a rainstorm, snow melt, or similar event. Such a puddle cannot reasonably be considered a water body or aquatic feature at all, because usually it exists for only a brief period of time before the water in the puddle evaporates or sinks into the ground. Puddles of this sort obviously are not, and have never been thought to be, waters of the United States subject to CWA jurisdiction. Listing puddles

also could have created the misapprehension that anything larger than a puddle was jurisdictional. That is not the agencies’ intent.

Gullies are relatively deep channels that are ordinarily formed on valley

sides and floors where no channel previously existed. They are commonly found in areas with low-density vegetative cover or with soils that are highly erodible. See, e.g., N.C. Brady and R.R. Weil, The Nature and Properties of Soils, 13th Edition (Upper Saddle River, NJ: Prentice Hall, 2002). Rills are formed by overland water flows eroding the soil surface during rain

storms. See, e.g., L.B. Leopold, A View of the River (Cambridge: Harvard University Press, 1994). Rills are less permanent on the landscape than streams and typically lack an OHWM, whereas gullies are younger than streams in geologic age and also typically lack an OHWM; time has shaped streams into geographic features distinct from gullies and rills. See, e.g., American Society of Civil Engineers, Task Committee on Hydrology Handbook, Hydrology Handbook (ASCE Publications, 1996).

The two main processes that result in the formation of gullies are downcutting and headcutting, which are forms of longitudinal (incising) erosion. These actions ordinarily result in erosional cuts that are often deeper than they are wide, with very steep banks, often small


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beds, and typically only carry water during precipitation events. The principal erosional processes that modify streams are also downcutting and headcutting. In streams, however, lateral erosion is also very important. The result is that streams, except on steep slopes or where soils are highly erodible, are characterized by the presence of bed and banks and an OHWM as compared to typical erosional features that are more deeply incised. It should be noted that some ephemeral streams are called ‘‘gullies’’ or the like when they are not ‘‘gullies’’ in the technical sense; such streams where they are tributaries under the proposed

definition would be considered ‘‘waters of the United States,’’ regardless of the name they are given locally. The agencies request comment on how they could provide greater clarity on how to distinguish between erosional features such as gullies, which are excluded from jurisdiction, and ephemeral tributaries, which are categorically jurisdictional.

Non-wetland natural and man-made

swales would not be ‘‘waters of the United States’’ under this proposal. In certain circumstances, however, swales include areas that meet the regulatory

definition of ‘‘wetlands.’’ Swales generally are considered wetlands when they meet the applicable criteria in the Corps of Engineers Wetland Delineation

Manual and the appropriate regional supplement to that Wetland Delineation

Manual. Wetland swales would be evaluated as adjacent waters under proposed (a)(6) or as ‘‘other waters’’ under proposed (a)(7) depending upon whether they meet the proposed definition of adjacent. Swales are distinct from streams in that they are non-channelized, shallow trough-like depressions that carry water mainly during rainstorms or snowmelt. Report at A–19. Swales typically lack the

OHWM that is characteristic of jurisdictional streams. The agencies request comment on how they could provide greater clarity on how to distinguish swales, which are excluded from jurisdiction, and ephemeral tributaries, which are categorically jurisdictional.

Finally, under paragraphs (b)(3) and (b)(4), the agencies propose to clearly exempt from the definition of ‘‘waters of the United States’’ two types of ditches: (1) Ditches that are excavated wholly in uplands, drain only uplands, and have less than perennial flow, and (2) ditches that do not contribute flow, either directly or through another water, to a water identified in paragraphs (a)(1) through (4). The agencies have long distinguished

between ditches that are ‘‘waters of the

United States’’ and ditches that are not

‘‘waters of the United States.’’ In a 1986 Corps preamble and a 1988 EPA preamble, the agencies each stated that they generally do not consider non-tidal drainage and irrigation ditches excavated on dry land to be ‘‘waters of the United States.’’ 51 FR 41217, November 13, 1986, 53 FR 20764, June 6, 1988. More recently, the agencies have stated that they generally would not assert jurisdiction over ‘‘Ditches (including roadside ditches) excavated wholly in and draining only uplands and that do not carry a relatively permanent flow of water.’’ ‘‘Clean Water Act Jurisdiction Following the Supreme

Court’s Decision in Rapanos v. United

States and Carabell v. United States’’ (Dec. 2, 2008) at 1, 12 (2008 Rapanos guidance).

The agencies recognize that there have been inconsistencies in practice implementing agency policy with respect to ditches and this proposed rule is designed to improve clarity, predictability, and consistency. With this proposal, the agencies would no longer rely on ‘‘generally not’’ jurisdictional but would clearly establish that specific types of ditches are not ‘‘waters of the United States’’ by

rule. Other ditches not excluded under paragraphs (b)(3) or (b)(4), if they meet the new proposed definition of ‘‘tributary’’ would continue to be ‘‘waters of the United States,’’ as they have been under the longstanding implementation of the statute and regulations by the agencies.

The first type of ditch that is excluded needs to meet all three criteria: (1) It is excavated wholly in uplands; (2) it drains only uplands, and (3) it has less than perennial flow. Ditches that are excavated wholly in uplands means ditches that at no point along their length are excavated in a jurisdictional wetland (or other water). Members of the public should consider whether a wetland is jurisdictional before constructing a ditch that would drain the wetland and connect either directly or through other waters to an (a)(1) through (a)(3) water. The ditch must also contain less than perennial flow to be excluded under this proposed provision. Perennial flow means that the flow in the ditch occurs year-round under normal circumstances; therefore, excluded ditches must be dug only in uplands, drain only uplands, and have ephemeral or intermittent flow. As noted above, the 2008 Rapanos guidance stated that the agencies generally would not assert jurisdiction over ‘‘ditches (including roadside ditches) excavated wholly in and draining only uplands and that do not carry a relatively permanent flow of water.’’ The agencies recognize that the term ‘‘relatively permanent’’ does not align with more commonly understood technical descriptions of flow regime. The agencies therefore believe it is appropriate to clarify the extent of this exclusion using the flow regime terms that are familiar to the public and agency field personnel. The agencies request comment on this formulation of the ditch exclusion. The agencies specifically seek comment on the appropriate flow regime for a ditch excavated wholly in uplands and draining only uplands to be covered by the exclusion in paragraph (b)(3). In particular, the agencies seek comment on whether the flow regime in such

ditches should be less than intermittent flow or whether the flow regime in such ditches should be less than perennial flow as proposed.

The other type of ditch that would not

be a ‘‘water of the United States’’ is a ditch that does not contribute flow, either directly or through another water, to a water identified in paragraphs (a)(1) through (4). Essentially, ditches that do not contribute flow to the tributary system of a traditional navigable water,

interstate water or territorial sea would

not be ‘‘waters of the United States.’’

It is important to note, however, that even when not jurisdictional waters, these non-wetland swales, gullies, rills and specific types of ditches may still be a surface hydrologic connection for purposes of the proposed definition of adjacent under paragraph (a)(6) or for purposes of a significant nexus analysis under paragraph (a)(7). For example, a wetland may be a ‘‘water of the United States,’’ meeting the proposed definition of ‘‘neighboring’’ because it is connectedto such a tributary by a nonjurisdictional ditch that does not meet the definition of a ‘‘tributary.’’ In addition, these geographic features may function as ‘‘point sources’’ under CWA section 502(14)), such that discharges of pollutants to waters through these features would be subject to other CWA regulations (e.g., CWA section 402).

IV. Related Acts of Congress, Executive Orders, and Agency Initiatives

A. Executive Order 12866: Regulatory Planning and Review and Executive Order 13563: Improving Regulation and Regulatory Review

Under Executive Order 12866 (58 FR 51735, October 4, 1993), this action is a ‘‘significant regulatory action.’’ Accordingly, the EPA and the Corps

submitted this action to the Office of


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Management and Budget (OMB) for

review under Executive Orders 12866 and 13563 (76 FR 3821, January 21, 2011) and any changes made in response to OMB recommendations

have been documented in the docket for

this action.

In addition, the EPA and the Corps of Engineers prepared an analysis of the potential costs and benefits associated with this action. This analysis is contained in ‘‘Economic Analysis of Proposed Revised Definition of Waters of the United States.’’ A copy of the analysis is available in the docket for

this action.

B. Paperwork Reduction Act

This action does not impose any

information collection burden under the provisions of the Paperwork Reduction Act, 44 U.S.C. 3501 et seq. Burden is defined at 5 CFR 1320.3(b). An Agency may not conduct or sponsor, and a person is not required to respond to, a

collection of information unless it displays a currently valid OMB control

number. The OMB control numbers for EPA’s CWA section 402 program may be found at 40 CFR 9.1. (OMB Control No. 2040–0004, EPA ICR No. 0229.19). For the CWA section 404 regulatory program, the current OMB approval number for information requirements is maintained by the Corps of Engineers (OMB approval number 0710–0003). However, there are no new approval or application processes required as a result of this rulemaking that necessitate a new Information Collection Request (ICR).

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 this final action on small entities, ‘‘small entity’’ is defined as: (1) A small business that is a small industrial entity

as defined in the U.S. Small Business Administration’s size standards (see 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; or (3) a small organization that is any not-for-profit enterprise that is independently owned and operated

and is not dominant in its field.

After considering the economic impacts of this proposed rule on small entities, I certify that this proposed rule will not have a significant economic impact on a substantial number of small entities. See, e.g., Cement Kiln Recycling

Coalition v. EPA, 255 F.3d 855 (D.C. Cir. 2001); Michigan v. EPA, 213 F.3d 663 (D.C. Cir. 2000); Am. Trucking Ass’n v. EPA, 175 F.3d 1027 (D.C. Cir. 1999); Mid-Tex Elec. Co-op, Inc. v. FERC, 773 F.2d 327 (D.C. Cir. 1985).

Under the RFA, the impact of concern is any significant adverse economic impact on small entities, because the primary purpose of the initial regulatory flexibility analysis is to identify and address regulatory alternatives ‘‘which minimize any significant economic impact of the rule on small entities.’’ 5 U.S.C. 603. The scope of regulatory jurisdiction in this proposed rule is narrower than that under the existing regulations. See 40 CFR 122.2 (defining ‘‘waters of the United States’’). Because fewer waters will be subject to the CWA under the proposed rule than are subject to regulation under the existing regulations, this action will not affect small entities to a greater degree than the existing regulations. As a consequence, this action if promulgated will not have a significant adverse economic impact on a substantial number of small entities, and therefore no regulatory flexibility analysis is required.

The proposed rule contemplated here is not designed to ‘‘subject’’ any entities of any size to any specific regulatory burden. Rather, it is designed to clarify the statutory scope of ‘‘the waters of the United States, including the territorial seas’’ (33 U.S.C. 1362(7)), consistent with Supreme Court precedent. This question of CWA jurisdiction will be informed by the tools of statutory construction and the geographical and hydrological factors identified in Rapanos v. United States, 547 U.S. 715 (2006), which are not factors readily informed by the RFA.

Nevertheless, the scope of the term

‘‘waters of the United States’’ is a question that has continued to generate substantial interest, particularly within the small business community, because permits must be obtained for many discharges of pollutants into those waters. In light of this interest, the EPA and the Corps determined to seek early and wide input from representatives of small entities while formulating a proposed definition of this term that reflects the intent of Congress consistent with the mandate of the Supreme Court’s decisions. Such outreach, although voluntary, is also consistent with the President’s January 18, 2011 Memorandum on Regulatory Flexibility, Small Business, and Job Creation, which emphasizes the important role small businesses play in the American economy. This process has enabled the agencies to hear directly from these representatives, at a very preliminary stage, about how they should approach this complex question of statutory interpretation, together with related issues that such representatives of small entities may identify for possible consideration in separate proceedings. The agencies have also prepared a report summarizing their small entity outreach to date, the results of this outreach, and how these results have informed the development of this proposed rule. This report is available in the docket for this proposed rule (cite).

D. Unfunded Mandates Reform Act

This proposed rule contains no Federal mandates (under the regulatory provisions of Title II of the Unfunded Mandates Reform Act of 1995 (UMRA), 2 U.S.C. 1531–1538 for state, local, or tribal governments or the private sector. This proposed rule does not directly regulate or affect any entity and, therefore, is not subject to the requirements of sections 202 and 205 of

UMRA.

The agencies determined that this proposed rule contains no regulatory requirements that might significantly or uniquely affect small governments. Moreover, the proposed definition of ‘‘waters of the United States’’ applies broadly to CWA programs and the subsequently affected entities, which are not uniquely applicable to small governments. Thus, this proposed rule is not subject to the requirements of

section 203 of UMRA.

E. Executive Order 13132: Federalism

This proposed rule seeks to clarify the

definition of the extent of CWA jurisdiction established by statute. Stateand local governments have welldefined and long-standing relationships in implementing affected CWA programs and these relationships will not be altered. Forty-six states and the Virgin Islands have been authorized to administer the NPDES program under section 402, while two states administer the section 404 program. This action

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. Thus, Executive Order 13132 (64 FR 43255,


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August 10, 1999) does not apply to this action. Consistent with EPA and Corps policy to promote communications between the agencies and state and local governments, and in recognition of the vital role states play in implementation of the CWA, EPA voluntarily undertook

federalism consultation for this effort

and met the terms of E.O. 13132 and EPA guidance for implementing the Order. EPA held a series of meetings

and outreach calls with state and local governments and their representatives soliciting input on a potential rule to

define ‘‘waters of the United States.’’

As part of this consultation, early in the rulemaking process, EPA held three in-person meetings and two phone calls

in the fall and winter of 2011. Organizations involved include the
National Governors Association, the

National Conference of State Legislatures, the Council of State
Governments, the National Association of Counties, the National League of Cities, the U.S. Conference of Mayors, the County Executives of America, the

National Associations of Towns and Townships, the International City/ County Management Association, and

the Environmental Council of States. In
addition, the National Association of Clean Water Agencies (NACWA) and

the Association of Clean Water
Administrators (ACWA) were invited to participate. As part of the consultation
12 counties, 8 associations and various state agencies and offices from five states (Alaska, Wyoming, Kansas,
Tennessee, and Texas) submitted
written comments. In addition, EPA

held numerous outreach calls with state and local government agencies seeking their technical input. More than 400 people from a variety of state and local agencies and associations, including the
Western Governors’ Association, the

Western States Water Council and the Association of State Wetland Managers participated in various calls and meetings.

The agencies engaged in voluntary

federalism consultation on this rule and we will continue to work closely with the states with respect to development of a final rule. Additionally, EPA and the Corps are specifically soliciting comments on this proposed action from state and local officials. The agencies

will include a detailed narrative of intergovernmental concerns raised during the course of the rule’s development and a description of the agencies’ efforts to address them with

the final rule. F. Executive Order 13175: Consultation

and Coordination With Indian Tribal

Governments

Subject to the Executive Order (E.O.) 13175 (65 FR 67249, November 9, 2000) Agencies may not issue a regulation that has tribal 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 tribal governments, or the Agencies consult with tribal officials early in the process of developing the proposed regulation and develops a tribal summary impact

statement. This action does not have tribal implications as specified in E.O.

13175.

In compliance with the EPA Policy on

Consultation and Coordination with Indian Tribes (May 4, 2011), EPA consulted with tribal officials to gain an understanding of and, where appropriate, to address the tribal implications of the proposed rule. In the

course of this consultation EPA coordinated with the Corps, and the Corps jointly participated in aspects of the consultation process. In the fall of

2011 EPA sent a Tribal ConsultationNotification letter to all federallyrecognized tribal leaders, via mail and email, inviting tribal officials to participate in outreach and consultation events and provide comments to EPA in coordination with the Corps. Close to 200 tribal representatives and more than 40 tribes participated in the consultation process, which included multiple webinars and national

teleconferences and face-to-face meetings. In addition, EPA received written comments from 3 tribes during the consultation period. In the spirit of E.O. 13175, and consistent with EPA and Corps policy to promote communications between the agencies and tribal governments, the agencies specifically solicit additional comment on this proposed action from tribal

officials.

G. Executive Order 13045: Protection of

Children From Environmental Health and Safety Risks

This action is not subject to E.O.

13045 because the environmental health or safety risks addressed by this action do not present a disproportionate risk to

children.

H. Executive Order 13211: Actions Concerning Regulations That Significantly Affect Energy Supply, Distribution, or Use

This action is not a ‘‘significant energy action’’ as defined in Executive Order 13211 (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.

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, 12(d) (15 U.S.C. 272 note) directs Federal agencies to use voluntary consensus standards in its regulatory activities unless to do so would be inconsistent with applicable law or otherwise impractical. Voluntary

consensus standards are technical standards (e.g., materials specifications, test methods, sampling procedures, and business practices) that are developed or adopted by voluntary consensus

standards bodies. NTTAA directs Federal agencies to provide Congress, through OMB, explanations when the Agency decides not to use available and applicable voluntary consensus

standards.

This proposed rulemaking does not involve technical standards. Therefore, the agencies are not considering 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 (E.O.) 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.

The agencies have determined that this proposed rule will not have disproportionately high and adverse

human health or environmental effects on minority or low-income populations. The proposed rule defines the scope of waters protected under the CWA. The increased clarity regarding the

definition of ‘‘waters of the United

States’’ will be of benefit to all regulators, stakeholders, and interested parties. However, in the spirit of Executive Order 12898, we specifically request comment regarding potential environmental justice issues raised by the proposed rule, and will fully

consider those comments when preparing the final rule.


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K. Environmental Documentation

The U.S. Army Corps of Engineers has prepared a draft environmental

assessment in accordance with the National Environmental Policy Act (NEPA). The Corps has made a preliminary determination that the section 404 aspects of today’s proposed rule do not constitute a major Federal action significantly affecting the quality of the human environment, and thus preparation of an Environmental Impact Statement (EIS) will not be required. The proposed rule will increase and make more efficient the protection of the aquatic environment. Additionally, the Corps complies with NEPA programmatically for general permits, and specifically for each and every standard individual permit application before making final permit decisions.

The implementation of the procedures prescribed in this proposed regulation would not authorize anyone (e.g., any landowner or permit applicant) to perform any work involving regulated

activities in ‘‘waters of the United States’’ without first seeking and obtaining an appropriate CWA authorization, which concurrently documents compliance with all applicable environmental laws.

Appendix A

Scientific Evidence

Overview of Scientific Literature on Aquatic Resource Connectivity and Downstream

Effects

In preparation for this proposal, more than a thousand peer-reviewed scientific papers and other data that address connectivity of aquatic resources and effects on downstream

waters were reviewed and considered. EPA’s Office of Research and Development (ORD) has prepared a draft peer-reviewed synthesis of published peer-reviewed scientific literature discussing the nature of connectivity and effects of tributaries and wetlands on downstream waters (U.S. Environmental Protection Agency, Connectivity of Streams and Wetlands to Downstream Waters: A Review and Synthesis of the Scientific Evidence, (Washington, DC: U.S. Environmental Protection Agency, 2013), hereinafter, ‘‘Report’’). This draft Report similarly has been considered in the development of this proposal. The Report is currently undergoing peer review led by EPA’s Scientific Advisory Board (SAB) and is

available at http://yosemite.epa.gov/sab/ sabproduct.nsf/fedrgstr

_activites/Watershed %20Connectivity%20Report? OpenDocument. The Report also underwent an earlier peer review, and the results of this peer review are available in the docket for this proposed rule. The Report summarizes and assesses much of the currently available scientific literature that is part of the administrative record for this proposal. The agencies anticipate that additional data and information will become available during the rulemaking process, including that provided during the public comment process, and by additional research, studies, and investigations that take place before the rulemaking process is concluded. At the conclusion of the rulemaking process, the agencies will review the entirety of the completed administrative record, including the final Report reflecting SAB review, and will make any adjustments to the final rule deemed to be appropriate at that time. The Report is under review by the Science Advisory Board, and the rule will not be

finalized until that review and the final report are complete. Part I of this Appendix provides the conclusions of the review and synthesis. Part II provides additional detail of the scientific literature and the agencies’ reasoning in support of this proposal.

Part I: Synthesis of Peer-Reviewed Scientific

Literature

Background

The draft Report prepared by ORD reviews and synthesizes the peer-reviewed scientific literature on the connectivity or isolation of streams and wetlands relative to large water bodies such as rivers, lakes, estuaries, and oceans. The purpose of the review and synthesis is to summarize current understanding about these connections, the factors that influence them, and the mechanisms by which connected waters, singly or in aggregate, affect the function or

condition of downstream waters. The focus of the Report is on surface and shallow

subsurface connections from small or temporary streams, non-tidal wetlands, and certain open waters. Specific types of connections considered in the Report include transport of physical materials and chemicals such as water, wood, and sediment, nutrients, pesticides, and mercury; movement of organisms or their seeds or eggs; and hydrologic and biogeochemical interactions occurring in surface and groundwater flows, including hyporheic zones and alluvial aquifers.

The draft Report prepared by ORD consists of six chapters. Following an executive summary and an introduction to the Report, chapter 3 presents a conceptual framework describing the hydrologic elements of a watershed, the types of chemical, physical, and biological connections that link them,

and watershed and climatic factors that influence connectivity at various temporal and spatial scales. It also provides background on the structure and function of

streams and wetlands viewed from an integrated watershed perspective. In a discussion of connectivity, the watershed scale is the appropriate context for interpreting technical evidence about individual watershed components, reviewed in subsequent chapters. Chapter 4 surveys the literature on stream networks (lotic systems) in terms of chemical, physical, and biological connections between upstream and

downstream habitats. Two case studies from the literature examine in greater detail longitudinal connectivity and downstream effects in prairie streams and arid streams of the Southwest. Chapter 5 reviews theliterature on connectivity and effects of nontidal wetlands and certain open waters (lentic systems) on downstream waters. This chapter is further subdivided into two broad categories of landscape settings based on directionality of hydrologic flows: Bidirectional settings, in which wetlands and open waters can have two-way hydrologic exchanges with other water bodies (e.g., riparian and floodplain wetlands and open waters), and unidirectional settings, in which water flows only from the wetland or open water towards the downstream water (e.g., most wetlands and open waters outside of riparian areas and floodplains). Directionality of hydrologic flow was selected as an organizational principle for this section

because it has a dominant role in determining the types of connectivity and downstream effects (if any) of wetlands. However, the use of these landscape settings for hydrologic directionality should not be construed as suggesting directionality of geochemical or biological flows. Also, the

terms ‘‘unidirectional’’ and ‘‘bidirectional’’ describe the landscape setting in which wetlands and open waters occur, and do not refer to wetland type or class. Four case

studies from the literature examine evidence pertaining to connectivity and downstream effects of oxbow lakes, Carolina and Delmarva bays, prairie potholes, and vernal pools in greater detail.

Chapter 6 presents and discusses key findings and major conclusions of the review,

which also are included at the end of each

review section and in this executive

summary.

Summary of Major Conclusions

Based on the review and synthesis of morethan a thousand publications from the peerreviewed scientific literature, the available evidence supports three major conclusions:

1. The scientific literature demonstrates that streams, individually and cumulatively, exert a strong influence on the character and functioning of downstream waters. All tributary streams, including perennial, intermittent, and ephemeral streams, are chemically, physically, and biologically

connected to downstream rivers via channels and associated alluvial deposits where water and other materials are concentrated, mixed, transformed, and transported. Headwater streams (headwaters) are the most abundant stream-type in most river networks, and supply most of the water in rivers. In addition to water, streams supply sediment, wood, organic matter, nutrients, chemical contaminants, and many of the organisms found in rivers. Streams are biologically connected to downstream waters by thedispersal and migration of aquatic and semiaquatic organisms, including fish, amphibians, plants, microorganisms, and invertebrates, that use both up- and downstream habitats during one or more stages of their life cycles, or provide food

resources to downstream communities. Chemical, physical, and biological

connections between streams and downstream waters interact via processes such as nutrient spiraling, in which stream communities assimilate and chemically transform large quantities of nitrogen and

other nutrients that would otherwise increase nutrient loading downstream.


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2. Wetlands and open waters in landscape settings that have bidirectional hydrologic exchanges with streams or rivers (e.g., wetlands and open waters in riparian areas and floodplains) are chemically, physically, and biologically connected with rivers via the export of channel-forming sediment and woody debris, temporary storage of local groundwater that supports baseflow in rivers, and transport of stored organic matter. They

remove and transform excess nutrients such as nitrogen and phosphorus. They provide nursery habitat for breeding fish, colonization opportunities for stream
invertebrates, and maturation habitat for
stream insects. Moreover, wetlands in this landscape setting serve an important role in the integrity of downstream waters because they also act as sinks by retaining
floodwaters, sediment, nutrients, and contaminants that could otherwise negatively impact the condition or function of

downstream waters.

3. Wetlands and open waters in landscape settings that lack bidirectional hydrologic exchanges with downstream waters (e.g., many prairie potholes, vernal pools, and playa lakes) provide numerous functions that can benefit downstream water quality and integrity. These functions include storage of
floodwater; retention and transformation ofnutrients, metals, and pesticides; and recharge of groundwater sources of river

baseflow. The functions and effects of this diverse group of wetlands, which the Report
refers to as ‘‘unidirectional wetlands,’’ affect

the condition of downstream waters if there

is a surface or shallow subsurface water

connection to the river network. In

unidirectional wetlands that are not connected to the river network through surface or shallow subsurface water, the type and degree of connectivity varies geographically within a watershed and over

time. Because such wetlands occur on a gradient of connectivity, it is difficult to generalize about their effects on downstream

waters. Generalization for this class is further complicated because, for certain functions (e.g., sediment removal and water storage),

downstream effects are due to wetland isolation, rather than connectivity. The literature reviewed does not provide

sufficient information to evaluate or generalize about the degree of connectivity (absolute or relative) or the downstream

effects of wetlands in unidirectional landscape settings. However, evaluations of individual geographically isolated wetlands or groups of geographically isolated wetlands could be possible through case-by-case analysis. Further, while the review did not specifically address other unidirectional water bodies, the conclusions apply to these water bodies (e.g., ponds and lakes that lack surface water inlets) as well, since the same principles govern hydrologic connectivity

between these water bodies and downstream

waters.

Section 3 below provides an overview of the conceptual framework, with further discussion of the key findings for streams, riparian and floodplain areas, and

unidirectional wetlands. 1. Conceptual Framework Overview

Connectivity is a foundational concept in hydrology and freshwater ecology. The

structure and function of downstream waters are highly dependent on the constituent materials contributed by and transported through water bodies located elsewhere in

the watershed. Most of the materials in a river, including water, sediment, wood, organic matter, nutrients, chemical contaminants, and certain organisms, originate outside of the river, from upstream tributaries, wetlands, or other components of the river system, and are transported to the river by water movement, wind, or other means. Therefore, streams and wetlands fundamentally affect river structure and function by altering transport of various types of materials to the river. This alteration of material transport depends on two key factors: (1) Connectivity (or isolation) between streams, wetlands and rivers that enables (or prevents) the movement of materials between the system components; and (2) functions within streams and wetlands that supply, remove, transform, provide refuge for, or delay transport of

materials.

The ORD Report defines connectivity as the degree to which components of a system are joined, or connected, by various transport mechanisms. Connectivity is determined by the characteristics of both the physical landscape and the biota of the specific system. Isolation is the opposite of connectivity; or the degree to which system components are not joined. Both connectivity and isolation have important effects on downstream waters. For example, stream channels convey water and channel-forming sediment to rivers, whereas wetlands that lack output channels can reduce flooding and store excess sediment. Materials transport connects different ecosystem types, at multiple spatial and temporal scales. For example, streams flowing into and out of

wetlands or between lakes form continuous or seasonal connections across ecosystem boundaries. Similarly, aquatic food webs connect terrestrial ecosystems, streams, wetlands, and downstream waters.

Water movement through the river system is the primary, but certainly not the only, mechanism providing physical connectivity within river networks. It provides a ‘‘hydraulic highway’’ that transports chemical, physical, and biological materials associated with the water (e.g., sediment, woody debris, contaminants, and organisms).

Because the movement of water is fundamental to understanding watershed connectivity, Chapter 3 begins with a review and an explanation of the hydrologic foundation of river systems, and terms and concepts used throughout the Report are

defined.

Numerous factors influence watershed connectivity. Climate, watershed topography, soil and aquifer permeability, the number and types of contributing waters, their spatial distribution in the watershed, interactions among aquatic organisms, and human alteration of watershed features, among other things, can act individually or in concert to influence stream and wetland connectivity to, and effects on, downstream waters. For example, all else being equal, materials traveling shorter distances could enter the
river with less transformation or dilution, thus increasing a beneficial or harmful effect. In other cases, sequential transformations such as nutrient spiraling (defined and discussed below) connect distant water bodies and produce beneficial effects on downstream waters. Infrequent events that temporarily connect nearby or distant

streams or wetlands to rivers also can have large, long-lasting effects. Most of the major changes in sediment load and river channel structure that are critical to maintaining river health—including meanders of rivers in floodplains and creation of oxbow lakes—are a result of large floods that provide infrequent, intense connections with more distant streams and riparian or floodplain

waters.

Based on a review of the peer-reviewed scientific literature, the Report identifies five functions by which streams, wetlands, and open waters influence material transport into

downstream waters:

• Source: The net export of materials, such

as water and food resources

• Sink: The net removal or storage of

materials, such as sediment and

contaminants

• Refuge: The protection of materials,

especially organisms

• Transformation: The transformation of

materials, especially nutrients and
chemical contaminants, into different physical or chemical forms

• Lags: The delayed or regulated release of

materials, such as storm water

These functions are not static or mutually exclusive (e.g., a wetland can be both a source of organic matter and a sink for nitrogen) and can change over time (e.g., one

wetland can be a water sink when evapotranspiration is high and a water source when evapotranspiration is low). Further, some functions work in conjunction with others. For example, a lag function can include transformation of materials prior to their delayed release. In a particular stream, wetland, or open water, the presence or absence of these functions depends upon the biota, hydrology, and environmental

conditions in the watershed.

When considering effects on downstream waters, it is helpful to distinguish between actual function and potential function of a stream, wetland, or open water. For example, a wetland with appropriate conditions for

denitrification is a potential sink for nitrogen,

a nutrient that can be a contaminant when present in high concentrations. This function is conditional; if nitrogen were to enter a wetland (from agricultural runoff, for example), the wetland has the capacity to remove this nitrogen from the water. The
wetland will not serve this function, however, if no nitrogen enters the wetland. Even if a stream or wetland is not currently serving an actual function, it has the potential to provide that function when a
new material enters it, or when environmental conditions change. Thus, potential functions play a critical role in protecting those waters from future impacts.


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2. Discussion of Major Conclusions

A. Streams

The scientific literature demonstrates that streams, individually or cumulatively, exert a strong influence on the character and functioning of downstream waters. All tributary streams, including perennial, intermittent, and ephemeral streams, are chemically, physically, or biologically

connected to downstream rivers via channels and associated alluvial deposits where water and other materials are concentrated, mixed, transformed, and transported. Headwater streams (headwaters) are the most abundant stream type in most river networks, and supply most of the water in rivers. In addition to water, streams supply sediment, wood, organic matter, nutrients, chemical contaminants, and many of the organisms found in rivers. Streams are biologically connected to downstream waters by dispersal and migration of aquatic and semi-aquatic organisms, including fish, amphibians, plants, microorganisms, and invertebrates, that use both up- and downstream habitats during one or more stages of their life cycles, or provide food resources to downstream communities. Chemical, physical, and biological connections between streams and downstream waters interact via processes such as nutrient spiraling, in which stream communities assimilate and chemically transform large quantities of nitrogen and

other nutrients that would otherwise increase nutrient loading downstream.

Key findings: a. Streams are hydrologically connected to downstream waters via channels that convey surface and subsurface water year-round (perennial flow), weekly to seasonally (intermittent flow), or only in direct response to precipitation (ephemeral flow). Streams

are the dominant source of water in most rivers, and the great majority of tributaries are perennial, intermittent, and ephemeral headwater streams. For example, headwater streams, which are the smallest channels where stream flows begin, are the source of approximately 60% of the total mean annual

flow to all northeastern U.S. streams and

rivers.

b. Headwaters convey water into local storage compartments such as ponds, shallow aquifers, or river banks and into regional and alluvial aquifers. These local storage compartments are important sources of water for baseflow in rivers. The ability of streams to keep flowing even during dry periods typically depends on the delayed (lagged) release of local groundwater, also referred to as shallow groundwater, originating from these water sources, especially in areas with shallow groundwater tables and pervious subsurfaces. For example, in the southwestern United States, short-term shallow groundwater storage in alluvial floodplain aquifers, with gradual release into stream channels by intermittent and ephemeral streams, is a major source of

annual flow in rivers.

c. Even infrequent flows through ephemeral or intermittent channels influence fundamental biogeochemical processes by connecting the channel and shallow groundwater with other landscape elements. Infrequent, high-magnitude events are especially important for transmitting

materials from headwater streams in most river networks. For example, headwater streams, including ephemeral and intermittent streams, shape river channels by accumulating and gradually or episodically releasing stored materials such as sediment and large woody debris. These materials provide substrate, habitat for aquatic organisms, and slow the flow of water through channels.

d. Connectivity between streams and rivers provides opportunities for materials, including nutrients and chemical contaminants, to be sequentially altered as they are transported downstream. Although highly efficient at transport of water and other physical materials, streams are not pipes. They are dynamic ecosystems with permeable beds and banks that interact with terrestrial and aquatic ecosystems above and

below the surface. The connections formed by surface and subsurface streamflows act as a series of complex chemical, physical, and biological alterations that occur as materials move through different parts of the river system. The amount and quality of such materials that eventually reach a river are determined by the aggregate effect of these sequential alterations that begin at the source waters, which can be at some distance from the river. The greater the distance a material travels between a particular stream reach and the river, the greater the opportunity for that material to be altered in intervening stream reaches, which can allow for uptake, assimilation, or beneficial transformation. One example of sequential alteration with significant beneficial effects on downstream waters is the process of nutrient spiraling, in which nutrients entering headwater streams are transformed by various aquatic organisms and chemical reactions as they are transported downstream by streamflow.

Nutrients which enter the headwater stream (e.g., via overland flow) are first removed from the water column by streambed algal and microbial populations. Fish or insects feeding on algae and microbes take up some of those nutrients, which are subsequently

released back to the stream via excretion and decomposition, and the cycle is repeated. In each phase of the cycling process—from dissolved inorganic nutrients in the water column, through microbial uptake, subsequent transformations through the food web, and back to dissolved nutrients in the water column—nutrients are subject to downstream transport. Stream and wetland capacities for nutrient cycling have important implications for the form and concentration of nutrients exported to downstream waters.

e. The literature review found strong

evidence that headwater streams function as nitrogen sources (export) and sinks (uptake and transformation) for river networks. One study estimated that rapid nutrient cycling in small streams that were free from agricultural or urban impacts removed 20–40% of the nitrogen that otherwise would be delivered to downstream waters. Nutrients are necessary to support aquatic life, but excess nutrients create conditions leading to eutrophication and hypoxia, in which oxygen concentrations fall below the level necessary to sustain most within and near-bed animal life. Thus, the role of streams in influencing nutrient loads can have significant repercussions for hypoxic areas in downstream waters.

f. Headwaters provide critical habitat during one or more life cycle stages of many organisms capable of moving throughout river networks. This review found strong evidence that headwaters provide habitat for complex life-cycle completion, refuge from predators or adverse physical conditions inrivers, and reservoirs of genetic- and specieslevel diversity. Use of headwater streams as habitat is especially obvious for the many species that migrate between small streams and marine environments during their life cycles (e.g., Pacific and Atlantic salmon, American eels, certain lamprey species), and the presence of these species within river networks provides robust evidence of biological connections between headwaters and larger rivers. In prairie streams, many fishes swim upstream into tributaries to release eggs, which develop as they are transported downstream. Small streams also provide refuge habitat for riverine organisms seeking protection from temperature extremes, flow extremes, low dissolved oxygen, high sediment levels, or the presence of predators, parasites, and competitors.

B. Riparian/Floodplain Waters

Wetlands and open waters in landscape settings that have bidirectional hydrologic exchanges with streams or rivers (e.g., wetlands and open waters in riparian areas and floodplains) are chemically, physically, or biologically connected with rivers via the export of channel-forming sediment and woody debris, temporary storage of local groundwater that supports baseflow in rivers, and transport of stored organic matter. They

remove and transform excess nutrients such as nitrogen and phosphorus. They provide nursery habitat for breeding fish, colonization opportunities for stream invertebrates, and maturation habitat for stream insects. Moreover, wetlands in this landscape setting serve an important role in the integrity of downstream waters because they also act as sinks by retaining floodwaters, sediment, nutrients, and contaminants that could otherwise negatively impact the condition or function of

downstream waters.

Key Findings: a. Riparian areas act as buffers that are among the most effective tools for mitigating nonpoint source pollution. The wetland literature shows that collectively, riparian wetlands improve water quality through assimilation, transformation, or sequestration of nutrients, sediment and other pollutants— such as pesticides and metals—that can affect downstream water quality. These pollutants enter wetlands via various pathways that include various sources such as dry and wet atmospheric deposition, some runoff from upland agricultural and urban areas, spray drift, and subsurface water flows, as well as point sources such as outfalls, pipes, and

ditches.

b. Riparian and floodplain areas connect upland and aquatic environments through both surface and subsurface hydrologic flow paths. These areas are therefore uniquely situated in watersheds to receive and process


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waters that pass over densely vegetated areas and through subsurface zones before reaching

streams and rivers. When contaminants reach a riparian or floodplain area, such materials can be sequestered in sediments, assimilated into the wetland plants and animals,

transformed into less harmful forms or compounds, or lost to the atmosphere. Wetland potential for biogeochemical transformations (e.g., denitrification) that can improve the quality of water entering streams and rivers is influenced by factors present in riparian areas and floodplains, including anoxic conditions, shallow water tables, slow organic matter decomposition, wetland plant communities, permeable soils, and complex topography.

c. Riparian and floodplain areas can reduce flood peaks by storing and desynchronizing floodwaters. They also can contribute to maintenance of flow by recharging alluvial aquifers. Many studies have documented the ability of riparian and floodplain areas to reduce flood pulses by storing excess water

from streams and rivers. One review of wetland studies reported that riparian wetlands reduced or delayed floods in 23 of 28 studies. For example, peak discharges between upstream and downstream gauging

stations on the Cache River in Arkansas were reduced 10–20% primarily due to floodplain

water storage.

d. Riparian and floodplain areas store large amounts of sediment and organic matter from upland areas before those sediments enter the stream. For example, riparian areas have

been shown to filter 80–90% of sediments leaving agricultural fields in North Carolina. (A. Cooper, et al., ‘‘Riparian Areas as Filters for Agricultural Sediment,’’ Soil Science Society of America Proceedings 51:416–420 (1987); R.B. Daniels, and J.G. Gilliam, ‘‘Sediment and Chemical Load Reduction by Grass and Riparian Filters,’’ Soil Science Society of America Journal 60:246–251 (1996); R.J. Naiman, and H. Decamps, ‘‘The Ecology of Interfaces: Riparian Zones,’’ Annual Review of Ecology and Systematics 28:621–658 (1997)).

e. Ecosystem function within a river system is driven by interactions between the physical environment and the diverse biological communities living within the river system. Movements of organisms connect aquatic habitats and populations in different locations through several processes important for the survival of individuals, populations, and species, and for the functioning of the river ecosystem. For example, lateral expansion and contraction of the river in its floodplain results in an exchange of matter and organisms, including fish populations that are adapted to use floodplain habitat for feeding and spawning during high water. Refuge populations of aquatic plants in floodplains can become important seed sources for the river network, especially if catastrophic flooding scours vegetation and seed banks in other parts of the channel. Many invertebrates exploit temporary hydrologic connections between rivers and floodplain wetland habitats, moving into these wetlands to feed, reproduce, or avoid harsh environmental conditions and then returning to the river network. Amphibians and aquatic reptiles in many parts of the country commonly use both streams and wetlands, including wetlands in riparian and floodplain areas, to hunt, forage, overwinter, rest, or hide from predators.

C. Unidirectional Wetlands

Wetlands and open waters in landscape settings that lack bidirectional hydrologic exchanges with downstream waters (e.g., many prairie potholes, vernal pools, and playa lakes) provide numerous functions that can benefit downstream water quality and integrity. These functions include storage of floodwater; retention and transformation ofnutrients, metals, and pesticides; and recharge of groundwater sources of river

baseflow. The functions and effects of this diverse group of wetlands, hereafter referred to as ‘‘unidirectional wetlands,’’ clearly affect

the condition of downstream waters if there

is a surface or shallow subsurface water

connection to the river network. In

unidirectional wetlands that are not connected to the river network through surface or shallow subsurface water, the type and degree of connectivity varies geographically within a watershed and over

time. Because such wetlands occur on a gradient of connectivity, it is difficult to generalize about their effects on downstream

waters. This evaluation is further complicated because, for certain functions (e.g., sediment removal and water storage),

downstream effects arise from wetland isolation, rather than connectivity. The literature reviewed does not provide

sufficient information to evaluate or generalize about the degree of connectivity (absolute or relative) or the downstream

effects of wetlands in unidirectional landscape settings. However, evaluations of connectivity of individual wetlands or groups of wetlands could be possible through case-by-case analysis. Further, while the review did not specifically address other unidirectional water bodies, the conclusions apply to these water bodies (e.g., ponds and lakes that lack surface water inlets) as well, since the same principals govern hydrologic connectivity between these water bodies and

downstream waters.

Key Findings: a. Water storage by wetlands well outside of riparian or floodplain areas can affect streamflow. Hydrologic models of prairie potholes in the Starkweather Coulee subbasin (North Dakota) that drain to Devils Lake indicate that increasing the volume of pothole storage across the sub-basin by approximately 60% caused simulated total annual streamflow to decrease 50% during a series of dry years and 20% during wet years.

Similar simulation studies of watersheds that

feed the Red River of the North in North

Dakota and Minnesota demonstrated qualitatively comparable results, suggesting that the ability of potholes to modulate streamflow may be widespread across portions of the prairie pothole region. This work also indicates that reducing wetland water storage capacity by connecting formerly isolated potholes through ditching or drainage to the Devils Lake and Red River

basins could increase stormflow and contribute to downstream flooding. In many agricultural areas already crisscrossed by extensive drainage systems, total streamflow and baseflow are enhanced by directly connecting potholes to stream networks. The impacts of changing streamflow are numerous, including altered flow regime, stream geomorphology, habitat, and ecology. The presence or absence of an effect of prairie pothole water storage on streamflow depends on many factors, including patterns of precipitation, topography and degree of human alteration. For example, in parts of the prairie pothole region with low precipitation, low stream density, and little human alteration, hydrologic connectivity between prairie potholes and streams or rivers is likely to be low.

b. Unidirectional wetlands act as sinks and transformers for various pollutants, especially nutrients, which pose a serious pollution problem in the United States. In one study, sewage wastewaters were applied

to forested unidirectional wetlands in Florida for a period of 4.5 years. More than 95% of the phosphorus, nitrate, ammonium, and total nitrogen were removed by the wetland during the study period, and 66–86% of the nitrate removed was attributed to the process of denitrification. In another study, sizeable phosphorus retention occurred in unidirectional marshes that comprised only

7% of the lower Lake Okeechobee basin area in Florida. A unidirectional bog in Massachusetts was reported to sequester nearly 80% of nitrogen inputs from various sources, including atmospheric deposition, and prairie pothole wetlands in the upper

Midwest were found to remove >80% of the nitrate load via denitrification. A large unidirectional prairie marsh was found to remove 86% of nitrate, 78% of ammonium, and 20% of phosphate through assimilation and sedimentation, sorption, and other mechanisms. Together, these and other

studies indicate that on-site removal of nutrients by unidirectional wetlands is significant and geographically widespread.

The effects of this removal on rivers are generally not reported in the literature.

c. Biological connectivity can occur

between unidirectional wetlands and downstream waters through movement of amphibians, aquatic seeds, macroinvertebrates, reptiles, and mammals. Many species in those groups that use both stream and wetland habitats are capable of dispersal distances equal to or greater than distances between many unidirectional

wetlands and river networks. Unidirectional wetlands can be hydrologically connected directly to river networks through channels, non-channelized surface flow, or subsurface flows. A wetland surrounded by uplands is defined as ‘‘geographically isolated.’’ Our review found that in some cases, wetland types such as vernal pools and coastal depressional wetlands are collectively, and incorrectly, referred to as geographically isolated. Technically, the term ‘‘geographically isolated’’ should be applied only to the particular wetlands within a type or class that are completely surrounded by uplands. Furthermore, ‘‘geographic isolation’’

should not be confused with functional isolation, because geographically isolated wetlands can still have hydrological and biological connections to downstream waters.


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d. Unidirectional wetlands occur along a gradient of hydrologic connectivity-isolation with respect to river networks, lakes, or marine/estuarine water bodies. This gradient includes, for example, wetlands that serve as origins for stream channels that have permanent surface water connections to the river network; wetlands with outlets to stream channels that discharge to deep groundwater aquifers; geographically isolated wetlands that have local groundwater or

occasional surface water connections to downstream waters; and geographically

isolated wetlands that have minimal hydrologic connection to other water bodies (but which could include surface and subsurface connections to other wetlands). The existence of this gradient among wetlands of the same type or in the same geographic region can make it difficult to determine or generalize, from the literature alone, the degree to which particular wetlands (individually or as classes), including geographically isolated wetlands, are hydrologically connected.

e. A related issue is that spatial scale must be considered when determining geographic

isolation. Individual wetlands that are geographically isolated could be connected to

downstream waters when considered as a complex (a group of interacting wetlands). This principle was demonstrated in a recent study that examined a depressional wetland complex on the Texas coastal plain. These wetlands have been considered as a type of geographically isolated wetlands. Collectively, however, they are geographically and hydrologically connected to downstream waters in the area. During an almost 4-year study period, nearly 20% of the precipitation that fell on the wetland complex flowed as surface runoff through an intermittent stream to a nearby waterway, the Armand Bayou. Thus, wetland complexes

could have connections to downstream waters through stream channels even when the individual wetland components are geographically isolated.

3. Closing Comments

The strong hydrologic connectivity of river networks is apparent in the existence of stream channels that form the physical

structure of the network itself. Given the discussion above, it is clear that streams and rivers are much more than a system of physical channels for conveying water and other materials downstream, but the presence of physical channels is one strong line of

evidence for surface water connections from tributaries, or water bodies of other types, to downstream waters. Physical channels are defined by continuous bed and bank structures, which may include apparent disruptions (such as by bedrock outcrops, braided channels, flow-through wetlands) associated with changes in the material and gradient over and through which water flows.

The continuation of bed and banks down gradient from such disruptions is evidence of

the surface connection with the channel that is up gradient of the perceived disruption.

The structure and function of rivers are highly dependent on the constituent materials that are stored in and transported through them. Most of these materials, broadly defined here as any chemical, physical, or biological entity, including, but not limited to, water, heat energy, sediment, wood, organic matter, nutrients, chemical contaminants, and organisms, originate outside of the river: They originate from either the upstream river network or other components of the river system, and then are transported to the river by water movement or other mechanisms. Thus, the fundamental way in which streams and wetlands affect river structure and function is by altering

fluxes of materials to the river. The control of material fluxes depends on two key factors: (1) Functions within streams and wetlands that affect material fluxes, and (2) connectivity (or isolation) between streams and wetlands and rivers that allows (or prevents) transport of materials between the

systems.

Absence of channels does not, however, mean that a wetland or open water is isolated or only infrequently connected to

downstream waters. Areas that are infrequently flooded by surface water can be connected more regularly through shallow groundwater or through dispersal among biological populations and communities. Such wetlands and open waters also can reduce flood peaks by storing flood waters, filter large amounts of sediment and nutrients from upland areas, influence stream geomorphology by providing woody debris and sediment, and regulate stream temperature. They also serve as sources of food for river biota and sources of genetic diversity for populations of stream

invertebrates.

Unidirectional wetlands can reduce and attenuate floods through water storage, and can recharge groundwater, thereby contributing to stream and river baseflow. These wetlands also affect nutrient delivery and improve water quality by functioning as sources of food and as sinks for metals, pesticides, excess nutrients. Biological connectivity can also occur between

unidirectional wetlands and downstream waters, through movement of amphibians, aquatic insects, aquatic reptiles, migratory birds, and riverine mammals that require or opportunistically use both river and wetland or open water habitats. However, given a geographically isolated wetland for which a surface water connection cannot be observed, it is difficult to assess its degree of connectivity with the river network without site-specific data.

Additionally, caution should be used in interpreting connectivity for wetlands based on their being designated as ‘‘geographically isolated’’ since (a) the term can be mistakenly applied to a heterogeneous group of wetlands

that can include wetlands that are not geographically isolated, (b) wetlands with permanent channels could be miscategorized as geographically isolated if the designation is based on maps or imagery with inadequate spatial resolution, obscured views, etc., and (c) wetland complexes could have connections to downstream waters through

stream channels even if individual wetlands within the complex are geographically isolated. Thus, the term ‘‘geographically isolated’’ should only be applied to groups of wetlands if they fit the technical definition (i.e., they are surrounded by uplands). Further, even geographically isolated

wetlands can be connected to other wetlands and downstream waters through groundwater connections, occasional spillage, or biological connections. Thus, the term ‘‘geographically isolated’’ should not be used to infer lack of hydrologic, chemical, or biological connectivity.

Lastly, to understand the health, behavior, and sustainability of downstream waters,

effects of small water bodies in a watershed need to be considered in aggregate. The contribution of material by a particular stream and wetland might be small, but the aggregate contribution by an entire class of streams and wetlands (e.g., all ephemeral streams in the river network) might be substantial. For example, western vernal pools typically occur within ‘‘vernal pool landscapes’’ or complexes of pools in which swales connect pools to each other and to seasonal streams, and in which the hydrology and ecology are tightly coupled with the local and regional geological processes that formed them. The vernal pool basins, swales, and seasonal streams are part of a single surface water and shallow groundwater system connected to the river network when seasonal precipitation exceeds storage capacity of the wetlands. Since rivers develop and respond over time and are functions of the whole watershed, understanding the integration of

contributions and effects over time is also necessary to have an accurate understanding of the system, taking into account the duration and frequency of material export and delivery to downstream waters. In addition, when considering the effect of an individual stream or wetland, it is important

to include the cumulative effect of all materials that originate from it, rather than each material individually, to understand that water body’s influence on downstream

waters.

Part II: Additional Scientific Support

i. Tributaries

The agencies propose that all waters that meet the proposed definition of tributary are ‘‘waters of the United States’’ because they meet Justice Kennedy’s test for jurisdiction

under Rapanos. In other words, the agencies are asserting that all tributaries have a significant nexus with traditional navigable waters, interstate waters, and/or the territorial seas. EPA and the Corps’ longstanding definition of ‘‘waters of the

United States’’ has included tributaries. That regulation was based on the agencies’ historic view of the scope of the CWA and the general scientific understanding about the ecological and hydrological relationship between

waters.

Tributaries have a substantial impact on the chemical, physical, or biological integrity of waters into which they eventually flow— including traditional navigable waters, interstate waters, and the territorial seas. The great majority of tributaries are headwater streams, and whether they are perennial, intermittent, or ephemeral, they play an important role in the transport of water, sediments, organic matter, pollutants, nutrients, and organisms to downstream

environments. Tributaries serve to store


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water (thereby reducing flooding), provide biogeochemical functions that help maintain water quality, trap and transport sediments, transport, store and modify pollutants, provide habitat for plants and animals, and sustain the biological productivity of downstream rivers, lakes and estuaries. These conclusions are strongly supported in the scientific literature, as discussed below.

Headwater streams are the smallest channels where stream flows begin, and often

occur at the outer rims of a watershed. Typically these are first-order streams (i.e., they do not have any other streams flowing into them). However, headwater streams can include streams with multiple tributaries flowing into them and can be perennial, intermittent or ephemeral, but are still located near the channel origins of the tributary system in a watershed.

Protection of tributaries under the CWA is critically important because they serve many important functions which directly influence the integrity of downstream waters. It is necessary to regulate the entire tributary system to fulfill the objective of the CWA, because discharges of pollutants into the tributary system adversely affect the chemical, physical, or biological integrity of these waters. For example, destruction or

modification of headwater streams has been shown to affect the integrity of downstream waters, in part through changes in hydrology, chemistry and stream biota. M.C. Freeman, et al., ‘‘Hydrologic Connectivity and the

Contribution of Stream Headwaters to Ecological Integrity at Regional Scales,’’ Journal of the American Water Resources

Association 43:5–14. (2007); M.S. Wipfli., et al., ‘‘Ecological Linkages between Headwaters and Downstream Ecosystems: Transport of Organic Matter, Invertebrates, and Wood Down Headwater Channels,’’ Journal of the American Water Resources

Association 43:72–85 (2007). Additionally, activities such as discharging a pollutant intoone part of the tributary system are welldocumented to affect, at times, other parts of the system, even when the point of discharge is far upstream from the navigable water that experiences the effect of the discharge. In order to protect traditional navigable waters, interstate waters, and the territorial seas it is also critically important to protect tributaries as defined in today’s proposal that are upstream from those waters.

A. The Agencies Have Concluded That Tributaries, as Defined in the Proposed Rule, Have a Significant Nexus

The scientific literature documents that tributary streams, including perennial, intermittent, and ephemeral streams, and certain categories of ditches are integral parts of river networks because they are directly connected to rivers via permanent surface features (channels and associated alluvial deposits) that concentrate, mix, transform, and transport water and other materials, including food resources, downstream. Tributaries transport, and often transform, chemical elements and compounds, such as nutrients, ions, dissolved and particulate organic matter and contaminants, influencing water quality, sediment deposition, nutrient availability, and biotic functions in rivers. Streams also are biologically connected to downstream waters by dispersal and migration, processes which have critical implications for aquatic populations of organisms that use both headwater and river or open water habitats to complete their life cycles or maintain viable populations. The scientific literature clearly demonstrates that cumulatively, streams exert strong influence on the character and functioning of rivers. In light of these well documented connections and functions, the agencies concluded that tributaries, as defined, alone or in

combination with other tributaries in a watershed, significantly affect the chemical, physical, or biological integrity of a traditional navigable water, interstate water,

or the territorial seas. The scientific literature supports this conclusion for ephemeral tributaries, as well as for intermittent and perennial tributaries; for tributaries both near

to and far from the downstream traditional navigable water, interstate water, or the territorial seas; and for natural tributaries or man-altered tributaries, which may include

certain ditches and canals.

The discussion below summarizes the key points in the literature regarding the chemical, physical, and biological

connections and functions of tributaries that significantly affect downstream waters. In addition, the evidence regarding headwater streams and non-perennial streams, types of tributaries whose important functional relationships to downstream traditional navigable waters and interstate waters might not be obvious, is summarized. The scientific literature does not use legal terms like ‘‘traditional navigable water,’’ ‘‘interstate water,’’ or ‘‘the territorial seas.’’ Rather, the

literature assesses tributaries in terms of their

connections to and effects on downstream waters in a watershed. While the agencies

define as ‘‘waters of the United States’’ tributaries only in watersheds which drain to a traditional navigable water, interstate water, or the territorial seas, that distinction

does not affect the conclusions of the scientific literature with respect to the effects

of tributaries on downstream waters.

B. Tributaries Significantly Affect the Physical Integrity of (a)(1) Through (a)(3)

Waters

Tributaries, even when seasonally dry, are the dominant source of water in most rivers, rather than direct precipitation or groundwater input to main stem river

segments. See, e.g., Report at 4–3 (citing T.C. Winter, 2007, ‘‘The role of groundwater in generating streamflow in headwater areas and in maintaining base flow,’’ Journal of the

American Water Resources Association 43:15–25; P.A. Bukaveckas, ‘‘Rivers,’’ in G.E. Likens, ed., Encyclopedia of Inland Waters, Vol. 1 (Elsevier: Oxford, 2009)). Distant headwaters with stronger connections to groundwater or consistently higher precipitation levels than downstream reaches

contribute more water to downstream rivers.

In the northeastern United States headwater streams contribute greater than 60% of the water volume in larger tributaries, including navigable rivers. See, e.g., id. (citing R.B. Alexander, et. al., ‘‘The role of headwater streams in downstream water quality,’’ Journal of the American Water Resources

Association 43:41–59 (2007)). The contributions of tributaries to river flows are often readily measured or observed, especially immediately below confluences, where tributary flows increase the flow volume and alter physical conditions, such as water temperature, in the main stream. The physical effects of tributaries are particularly clear after intense rainfall occurs over only the upper tributary reaches of a river network. For example, a study of ephemeral tributaries to the Rio Grande in

New Mexico found that after a storm event

contributions of the stormflow from ephemeral tributaries accounted for 76% of

the flow of the Rio Grande. See, e.g., id. at 4–5 (citing E.R. Vivoni, et. al., ‘‘Analysis of a Monsoon Flood Event in an Ephemeral Tributary and Its Downstream Hydrologic Effects,’’ Water Resources Research 42:W03404 (2006)). A key effect of tributaries on the hydrologic response of river networks to storm events is dispersion, or the spreading of water output from a drainage basin over time. Hydrologic dispersion of connected tributaries influence the timing and volume of water reaching a river network

outlet. See, e.g., id. at 4–5 to 4–6 (citing P. M. Saco and P. Kumar, ‘‘Kinematic dispersion in stream networks coupling hydraulics and network geometry,’’ Water

Resources Research 38:1244 (2002)).

Tributaries also can reduce the amount of

water that reaches downstream rivers and minimize downstream flooding, often through infiltration or seepage through channel beds and banks or through evapotranspiration. See, e.g., id. at 4–8 (citing S.K. Hamilton, et al., ‘‘Persistence of Aquatic Refugia between Flow Pulses in a Dryland River System (Cooper Creek, Australia),’’ Limnology and Oceanography 50:743–754 (2005); J.F. Costelloe, et.al., ‘‘Determining

Loss Characteristics of Arid Zone River Waterbodies,’’ River Research and Applications 23:715–731 (2007)).

One of the primary functions of tributaries is transporting sediment to downstream waters. Tributaries, particularly headwaters, shape and maintain river channels by accumulating and gradually or episodically releasing sediment and large woody debris into river channels. Sediment transport is also clearly provided by ephemeral streams. Effects of the releases of sediment and large woody debris are especially evident at tributary-river confluences, where discontinuities in flow regime and temperature clearly demonstrate physical alteration of river structure and function by headwater streams. Report at 4–10, 4–14.

Sediment movement is critical for maintaining the river network, including

rivers that are considered to be traditional navigable waters, as fluvial (produced by the action of a river or stream) sediments are eroded from some channel segments, and deposited in others downstream to form channel features, stream and riparian habitat which supports the biological communities resident downstream, and influence the river hydrodynamics. See, e.g., J.L. Florsheim, et al., ‘‘Bank Erosion as a Desirable Attribute of

Rivers,’’ Bioscience 58:519–29 (2008); Report at 4–9 (citing M. Church, ‘‘Bed material transport and the morphology of alluvial river channels,’’ Annual Review of Earth and


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Planetary Sciences: 325–354 (2006)). While essential to river systems, too much sediment can impair ecological integrity by filling interstitial spaces, blocking sunlight transmission through the water column, and increasing contaminant and nutrient concentrations. Report at 4–9 (citing P.J. Wood and P.D. Armitage, ‘‘Biological Effects of Fine Sediment in the Lotic Environment,’’ Environmental Management 21:203–217 (1997)). Over sedimentation thus can reduce photosynthesis and primary productivity

within the stream network and otherwise have harmful effects on downstream biota, including on the health and abundance of fish, aquatic macrophytes (plants), and aquatic macroinvertebrates that inhabit

downstream waters. See, e.g., Wood and Armitage 1997. Headwater streams tend to trap and store sediments behind large structures, such as boulders and trees, that are transported downstream only during infrequent large storm events. See Report at 4–10, 4–12 (citing L.E. Benda, and T.W. Cundy, ‘‘Predicting deposition of debris flows in mountain channels,’’ Canadian Geotechnical Journal 27:409–417 (1990); T. Gomi and R.C. Sidle, ‘‘Bed load transport in managed steep-gradient headwater streams of southeastern Alaska,’’ Water Resources

Research 39:1336 (2003); L.E. Benda, et al., ‘‘Geomorphology of steepland headwaters: The transition from hillslopes to channels,’’ Journal of the American Water Resources

Association 41:835–851 (2005); P.E. Bigelow, et al., ‘‘On Debris Flows, River networks, and the Spatial Structure of Channel Morphology,’’ Forest Science 53:220–238 (2007); J.P.R. Gooderham, et al., ‘‘Upstream Heterogeneous Zones: Small Stream Systems Structured by a Lack of Competence?’’ Journal of the North American Benthological Society 26:365–374 (2007)).

Tributaries can greatly influence water temperatures in tributary networks. This is important because water temperature is a critical factor governing the distribution and growth of aquatic life, both directly (through its effects on organisms) and indirectly (through its effects on other physiochemical properties, such as dissolved oxygen and suspended solids). Id. at 4–13 (citing J.D. Allan, Stream Ecology—Structure and Function of Running Waters (New York, NY: Chapman & Hall, 1995)). For instance, water temperature controls metabolism and level of activity in cold-blooded species like fish, amphibians, and aquatic invertebrates. See,

e.g., G.G. Ice, ‘‘Chapter 3: Stream Temperature and Dissolved Oxygen,’’ in J.D. Stednick, ed., Hydrologic and Biological Responses to Forest Practices (Springer, 2008). Temperature can also control the amount of dissolved oxygen in streams, as colder water holds more dissolved oxygen,

which fish and other fauna need to breathe.

Connections between tributaries and

downstream rivers can affect water temperature in river networks. See, e.g., Report at 4–13 (citing S. Knispel, and E. Castella, ‘‘Disruption of a Longitudinal

Pattern in Environmental Factors and Benthic Fauna by a Glacial Tributary,’’ Freshwater Biology48:604–618 (2003); S.P.

Rice, et al., ‘‘The Ecological Importance of Tributaries and Confluences,’’ in S.P. Rice, et al., ed., River Confluences, Tributaries and the Fluvial Network, (Chichester, UK: John Wiley & Sons, 2008), pp. 209–242)). In particular, tributaries provide both cold and warm water refuge habitats that are critical for protecting aquatic life. Id. at 4–32. Because headwater tributaries often depend on groundwater inputs, temperatures in these systems tend to be warmer in the winter (when groundwater is warmer than ambient temperatures) and colder in the summer (when groundwater is colder than ambient temperatures) relative to downstream waters.

Id. (citing G. Power, et al., ‘‘Groundwater and Fish: Insights from Northern North America,’’ Hydrological Processes 13:401–422 (1999)). Thus tributaries provide organisms with both warm water and coldwater refuges at different times of the year. Id. (citing R.A. Curry, et al., ‘‘Use of Small Streams by Young Brook Trout Spawned in a Lake,’’ Transactions of the American Fisheries Society 126:77–83 (1997); C.V. Baxter, and F.R. Hauer, ‘‘Geomorphology, Hyporheic Exchange and Selection of Spawning Habitat by Bull Trout (Salvelinus confluentus),’’ Canadian Journal of Fisheries and Aquatic

Sciences 57: 1470–1481 (2000); T.R. Labbe, and K.D. Fausch, ‘‘Dynamics of Intermittent Stream Habitat Regulate Persistence of a Threatened Fish at Multiple Scales,’’ Ecological Applications 10:1774–1791 (2000); M.J. Bradford, et al., ‘‘Ecology ofJuvenile Chinook Salmon in a Small Nonnatal Stream of the Yukon River Drainage

and the Role of Ice Conditions on Their Distribution and Survival,’’ Canadian Journal of Zoology-Revue Canadienne De Zoologie 79:2043–2054 (2001)). For example, when temperature conditions in downstream waters are adverse, fish can travel upstream and use tributaries as refuge habitat. Id. (citing Curry et al. 1997; M.A. Cairns, et al., ‘‘Influence of Summer Stream Temperatures on Black Spot Infestation of Juvenile Coho Salmon in the Oregon Coast Range,’’ Transactions of the American Fisheries Society 134:1471–1479 (2005)). Tributaries also help buffer temperatures in downstream

waters. Id. at 4–13 to 4–14 (citing D. Caissie, ‘‘The thermal regime of rivers: A review,’’ Freshwater Biology 51:1389–1406 (2006). Temperatures in tributaries affect downstream water temperature many kilometers away. Id. at 4–14 (citing B. Gardner, and P.J. Sullivan, ‘‘Spatial and Temporal Stream Temperature Prediction: Modeling Nonstationary Temporal
Covariance Structures,’’ Water Resources

Research 40:W01102 doi (2004); B.R. Johnson, et al., ‘‘Use of Spatially Explicit Physicochemical Data to Measure Downstream Impacts of Headwater Stream Disturbance,’’ Water Resources Research 46:W09526 (2010)).

C. Tributaries Significantly Affect the Chemical Integrity of (a)(1) Through (a)(3)

Waters

Tributaries transform and export significant amounts of nutrients and carbon to downstream waters, serving important source functions that greatly influence the chemical integrity of downstream waters. Organic carbon, in both dissolved and particulate forms, exported from tributaries is consumed by downstream organisms. The organic carbon that is exported downstream thus supports biological activity (including metabolism) throughout the river network. See, e.g., Report at 4–22 (citing S.G. Fisher and G.E. Likens, ‘‘Energy Flow in Bear Brook, New Hampshire: An Integrative Approach to Stream Ecosystem Metabolism,’’ Ecological Monographs 43: 421–439 (1973); J.L. Meyer, ‘‘The Microbial Loop in Flowing Waters,’’ Microbial Ecology 28:195–199 (1994); J.B. Wallace, et al. ‘‘Multiple Trophic Levels of a

Forest Stream Linked to Terrestrial Litter Inputs,’’ Science 277:102–104 (1997); R.O. Hall and J.L. Meyer, ‘‘The Trophic Significance of Bacteria in a Detritus-Based Stream Food Web,’’ Ecology 79:1995–2012 (1998); R.O. Hall, et al., ‘‘Organic Matter

Flow in Stream Food Webs with Reduced Detrital Resource Base,’’ Ecology 81:3445– 3463 (2000); C. Augspurger, et al., ‘‘Tracking

Carbon Flow in a 2-Week-Old and 6-WeekOld Stream Biofilm Food Web,’’ Limnology and Oceanography 53:642–650 (2008)). Much or most of the organic carbon that is exported from tributaries has been altered either physically or chemically by ecosystem processes within the tributary streams, particularly by headwater streams.

Nutrient export from tributaries has a large effect on downstream water quality, as excess

nutrients from surface runoff from lawns and agricultural fields can cause algal blooms that reduce dissolved oxygen levels and increase turbidity in rivers, lakes, estuaries, and

territorial seas. Water low in dissolved oxygen cannot support aquatic life; it is widely-recognized that this phenomenon has

resulted in the devastation of commercial

and recreational fisheries in the northern

Gulf of Mexico. Committee on Environment and Natural Resources, Integrated Assessment of Hypoxia in the Northern Gulf of Mexico (Washington, DC: National Science and Technology Council, 2000). The amount of nitrogen that is exported downstream varies depending on stream size, and how much nitrogen is present in the system. Nitrogen loss is greater in smaller, shallow streams, most likely because denitrification and settling of nitrogen particles occur at slower rates in deeper channels. Report at 4– 16 (citing R.G. Alexander, et al., ‘‘Effect of Stream Channel Size on the Delivery of Nitrogen to the Gulf of Mexico,’’ Nature 403:758–761 (2000)). At low loading rates, the biotic removal of dissolved nitrogen from water is high and occurs primarily in small tributaries, reducing the loading to larger tributaries and rivers downstream. At high nitrogen loading rates, tributaries become nitrogen saturated and are not effectively able to remove nitrogen, resulting in high nitrogen export to rivers. Id. at 4–18 (citing P.J. Mulholland, et al., ‘‘Stream Denitrification across Biomes and Its Response to Anthropogenic Nitrate Loading,’’ Nature 452:202–205 (2008)). The transport of nitrogen and phosphorus downstream has also been well-documented, particularly in

the cases of the Gulf of Mexico and the Chesapeake Bay. Tributary streams in the uppermost portions of the Gulf and Bay watersheds transport the majority of nutrients to the downstream waters; an estimated 85% of nitrogen arriving at the hypoxic zone in the Gulf originates in the


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upper Mississippi (north of Cairo, Illinois) and the Ohio River Basins. D. Goolsby, et al., Topic Report 3, Flux and Sources of Nutrients in the Mississippi-Atchafalaya

River Basin (Washington, DC: National Science and Technology Council Committee on Environment and Natural Resources, 1999). The export of nutrients from streams in the Mississippi River Basin has an effect on anoxia, or low oxygen levels, in the Gulf. Report at 4–17 (citing N.N. Rabalais, et al., ‘‘Gulf of Mexico Hypoxia, a.k.a. ‘the Dead

Zone,’ ’’ Annual Review of Ecology and Systematics 33:235–263 (2002)). Similarly, nutrient loads from virtually the entire 64,000 square mile watershed affect water quality in the Chesapeake Bay. Simulation

tools have been used to determine the

nutrient and sediment load reductions that must be made at many different points throughout the entire watershed in order to achieve acceptable water quality in the mainstem of the Bay. These reductions included specific annual nitrogen caps on the upper reaches of the Susquehanna River in New York State, more than 400 miles from the mouth of the Chesapeake Bay. See e.g., U.S. Environmental Protection Agency (EPA), Region III, Chesapeake Bay Program Office, Setting and Allocating the Chesapeake Bay

Basin Nutrient and Sediment Loads: The Collaborative Process, Technical Tools and Innovative Approaches, EPA 903–R–03–007 (Washington, DC: EPA, 2003); Rabalais et al.

2002.

Although tributaries export nutrients, carbon, and contaminants downstream, they also transform these substances. Phosphorous and nitrogen arrive at downstream waters having already been cycled, or taken up and transformed by living organisms, many times in headwater and smaller tributaries. Report at 4–19 to 4–20, 6–3 to 6–4 (citing J.R. Webster, and B.C. Patten, ‘‘Effects of watershed perturbation on stream potassium and calcium dynamics,’’ Ecological Monographs 49:51–72 (1979); J.D. Newbold, et al., ‘‘Measuring nutrient spiraling in

streams,’’ Canadian Journal of Fisheries and Aquatic Sciences 38:860–863 (1981); J. Elwood, et al., ‘‘Resource spiraling: An operational paradigm for analyzing lotic ecosystems,’’ in T.D. Fontaine and S.M. Bartell, ed., Dynamics of Lotic Ecosystems (Ann Arbor, MI: Ann Arbor Science, 1983), pp. 3–23; S.H. Ensign, and M.W. Doyle, ‘‘Nutrient Spiraling in Streams and River Networks,’’Journal of Geophysical ResearchBiogeosciences 111:G04009 (2006)). In addition, some of the nutrient that is taken up as readily available inorganic forms is released back to the water as organic forms that are less available for biotic uptake. Id. at 4–20 (citing P.J. Mulholland, et al., ‘‘Production of Soluble, High Molecular Weight Phosphorus and Its Subsequent Uptake by Stream Detritus,’’ Verhandlungen des Internationalen Verein Limnologie 23:1190–1197 (1988); S.P. Seitzinger, et al., ‘‘Bioavailability of DON from Natural and Anthropogenic Sources to Estuarine Plankton,’’ Limnology and Oceanography 47:353–366 (2002)). Similarly, nutrient incorporated into particulates is not entirely regenerated, but accumulates in longitudinally increasing particulate loads (i.e. increases moving downstream). Id. at 4– 20 (citing J.L Merriam, et al., ‘‘Characterizing Nitrogen Dynamics, Retention and Transport in a Tropical Rainforest Stream Using an in situ N–15 Addition,’’ Freshwater Biology 47:143–160 (2002); M.R. Whiles, and W.K. Dodds, ‘‘Relationships between Stream Size, Suspended Particles, and Filter-Feeding Macroinvertebrates in a Great Plains Drainage Network,’’Journal of Environmental Quality 31:1589–1600 (2002); R.O. Hall, et al., ‘‘Hydrologic Control of Nitrogen Removal, Storage, and Export in a Mountain Stream,’’ Limnology and Oceanography 54:2128–2142 (2009)). Headwater streams have seasonal cycles in the concentrations of phosphorous and nitrogen that are delivered downstream by accumulating nutrient derived from temporarily growing streambed biomass. Id. (citing P.J. Mulholland, and W.R. Hill,

‘‘Seasonal Patterns in Streamwater Nutrient and Dissolved Organic Carbon Concentrations: Separating Catchment Flow Path and In-Stream Effects,’’ Water Resources

Research 33:1297–1306 (1997); P.J. Mulholland, ‘‘The Importance of In-stream Uptake for Regulating Stream Concentrations and Outputs of N and P from a Forested Watershed: Evidence from Long-Term Chemistry Records for Walker Branch Watershed,’’ Biogeochemistry 70:403–426 (2004)). Such variations have been

demonstrated to affect downstream productivity. Id. (citing P.J. Mulholland, et al., ‘‘Longitudinal Patterns of Nutrient Cycling and Periphyton Characteristics in Streams: a Test of Upstream-Downstream Linkage,’’Journal of the North American Benthological Society 14:357–370 (1995)). Nitrification, the microbial transformation of ammonium to nitrate, affects the form of downstream nutrient delivery. Nitrification occurs naturally in undisturbed headwater streams, but increases sharply in response to ammonium inputs, thereby reducing potential ammonium toxicity from pollutant inputs. Id. (citing Newbold, et al., ‘‘Phosphorus Dynamics in a Woodland Stream Ecosystem: a Study of Nutrient Spiraling,’’ Ecology 64:1249–1265 (1983); S.C. Chapra, Surface Water Quality Modeling (McGraw-Hill, 1996); E.S. Bernhardt, et al., ‘‘Whole-system Estimates of Nitrification and Nitrate Uptake in Streams of the Hubbard Brook Experimental Forest,’’ Ecosystems 5:419–430 (2002)). Denitrification, the removal of nitrate from streamwater through transformation to atmospheric nitrogen, is widespread among headwater streams; research indicates that small, unimpacted tributaries can reduce up to 40% of downstream nitrogen delivery through

denitrification. Id. at 4–20 to 4–21 (citing P.J. Mulholland, et al., ‘‘Stream Denitrification across Biomes and Its Response to Anthropogenic Nitrate Loading,’’ Nature 452:202–205 (2008)). Small tributaries also affect the downstream delivery of nutrients through abiotic processes. Streams can reduce phosphorus concentrations through sorption (i.e., ‘‘sticking’’) to stream

sediments. Id. at 4–21 (citing J.L. Meyer, ‘‘The Role of Sediments and Bryophytes in Phosphorus Dynamics in a Headwater Stream Ecosystem,’’ Limnology and Oceanography 24:365–375 (1979)). This is particularly beneficial to downstream chemical integrity where phosphorus sorbs to contaminants such as metal hydroxide precipitates. Id. (citing J.A. Simmons, ‘‘Phosphorus Removal by Sediment in Streams Contaminated with Acid Mine Drainage,’’ Water Air and Soil

Pollution 209:123–132 (2010)).

Tributaries also store significant amounts of nutrients and carbon, functioning as important sinks (lags) for river networks so that they do not reach downstream traditional navigable waters, interstate waters, or the territorial seas. Small tributary streams in particular often have the greatest effect on downstream water quality, in terms of storage and reducing inputs to downstream waters. For instance, uptake and transformation of inorganic nitrogen often occurs most rapidly in the smallest

tributaries. See, e.g., id. at 4–18 (citing B.J.

Peterson, et al., ‘‘Control of Nitrogen Export from Watersheds by Headwater Streams,’’

Science 292:86–90 (2001)). Small tributaries affect the downstream delivery of nutrients such as phosphorus through abiotic processes; such streams can reduce phosphorus concentrations by sorption to

stream sediments.

Tributaries can also serve as a temporary or permanent source or sink for contaminants, for instance substances like metals, sodium, and even dead fish carcasses that adversely affect organisms when occurring at excessive or elevated

concentrations to reduce the amounts that reach downstream traditional navigable waters, interstate waters, or the territorial seas. The transport of contaminants to downstream waters can impact water quality downstream, if they are not stored in

tributaries. See, e.g., id. at 4–26 (citing X. Wang, et al., ‘‘Water Quality Changes as a Result of Coalbed Methane Development in a Rocky Mountain Watershed,’’Journal of the

American Water Resources Association 43:1383–1399 (2007)). Tributaries can also serve as at least a temporary sink for contaminants that would otherwise impair downstream water quality. See, e.g., id. at 133–134 (citing W.L. Graf, Plutonium and the Rio Grande: Environmental Change and Contamination in the Nuclear Age (New York: Oxford University Press, 1994)).

The distances and extent of metal contaminant transport was shown in separate studies in the upper Arkansas River in Colorado, and Clark Fork River in Montana, where past mining activities impacted the

headwater tributaries. River bed sediments showed that metals originating from the mining and smelting areas in the headwaters were reaching water bodies up to 550 km

downstream. Id. at 4–26 to 4–27 (citing E.V. Axtmann, and S.N. Luoma, ‘‘Large-scale

Distribution of Metal Contamination in the Fine-grained Sediments of the Clark Fork

River, Montana, USA,’’ Applied Geochemistry 6:75–88 (1991); B.A. Kimball, et al., ‘‘Effects of Colloids on Metal Transport in a River Receiving Acid Mine Drainage, Upper Arkansas River, Colorado, USA,’’ Applied Geochemistry 10:285–306 (1995)).

Military studies of the distribution, transport, and storage of radionuclides (e.g., plutonium, thorium, uranium) have provided convincing evidence for distant chemical


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connectivity in river networks because the

natural occurrence of radionuclides is extremely rare. From 1942 to 1952, prior to the full understanding of the risks of

radionuclides to human health and the environment, plutonium dissolved in acid was discharged untreated into several

intermittent headwater streams that flow into

the Rio Grande at the Los Alamos National Laboratory, New Mexico. Id. at 4–28 (citing W.L. Graf, Plutonium and the Rio Grande: Environmental Change and Contamination in the Nuclear Age (New York: Oxford University Press, 1994); S.L. Reneau, et al., ‘‘Geomorphic Controls on Contaminant Distribution along an Ephemeral Stream,’’ Earth Surface Processes and Landforms 29:1209–1223 (2004)). Also during this time, nuclear weapons testing occurred west of the upper Rio Grande near Socorro, New Mexico (Trinity blast site) and in Nevada, where

fallout occurred on mountainous areas with thin soils that are readily transported to headwater streams in the upper Rio Grande basin. The distribution of plutonium within

the Rio Grande illustrates how headwater streams transport and store contaminated sediment that has entered the basin through fallout and from direct discharge. Los Alamos Canyon, while only representing 0.4% of the drainage area at its confluence with the Rio Grande, had a mean annual bedload contribution of plutonium almost seven

times that of the mainstem. Id. (citing Graf 1994). Much of the bedload contribution occurred sporadically during intense storms that were out of phase with flooding on the upper Rio Grande. Total estimated contributions of plutonium between the two

sources to the Rio Grande were approximately 90% from fallout to the landscape and 10% from direct effluent discharge at Los Alamos National Laboratory.

Id. (citing Graf 1994).

C. Tributaries Significantly Affect the Biological Integrity of (a)(1) Through (a)(3)

Waters

Tributaries are biologically linked to downstream waters through the movement of living organisms or their reproductive propagules, such as eggs or seeds. For organisms that drift with water flow, biological connections depend on hydrological connections. However, many aquatic organisms are capable of active movement with or against water flow, and others disperse actively or passively over land by walking, flying, drifting, or ‘‘hitchhiking.’’ All of these different types of movement form the basis of biological connectivity between headwater tributaries

and downstream waters.

Headwater tributaries increase the amount and quality of habitat available to aquatic organisms. Under adverse conditions, small tributaries provide safe refuge, allowing organisms to persist and recolonize

downstream areas once adverse conditions

have abated. See, e.g., Report at 4–29 (citing J.L. Meyer and J.B. Wallace, ‘‘Lost Linkages and Lotic Ecology: Rediscovering Small Streams,’’ Pages 295–317 in M.C. Press, N. J. Huntly, and S. Levin, editors. Ecology: Achievement and Challenge (Oxford, UK: Blackwell Science, 2001); A. Meyer et al., ‘‘The Effect of Low Flow and Stream Drying on the Distribution and Relative Abundance of the Alien Amphipod, Echinogammarus

berilloni (Catta, 1878) in a Karstic Stream System (Westphalia, Germany),’’ Crustaceana 77:909–922 (2004); A.D. Huryn et al., ‘‘Landscape Heterogeneity and the Biodiversity of Arctic Stream Communities: A Habitat Template Analysis,’’ Canadian Journal of Fisheries and Aquatic Sciences 62:1905–1919 (2005)). Use of tributaries by

salmon and other anadromous fish forspawning is well-documented, but even nonmigratory species can travel great distances within the river and tributary networks. See, e.g., id. at 4–31 (citing O.T. Gorman, ‘‘Assemblage Organization of Stream Fishes:

The Effects of Rivers on Adventitious
Streams,’’ American Naturalist 128(4): 611– 616 (1986); A. L. Sheldon, ‘‘Conservation of Stream Fishes: Patterns of Diversity, Rarity, and Risk,’’ Conservation Biology 2:149–156 (1988); N.P. Hitt and P.L. Angermeier, ‘‘Evidence for Fish Dispersal from Spatial Analysis of Stream Network Topology,’’ Journal of the North American Benthological Society 27:304–320 (2008)). Tributaries also serve as an important source of food for biota in downstream rivers. Tributaries export plankton, vegetation, fish eggs, insects, invertebrates like worms or crayfish, smaller fish that originate in upstream tributaries and

other food sources that drift downstream to be consumed by other animals. See, e.g., id. at 4–29 (citing D.J. Progar and A.R. Modenke, ‘‘Insect Production from Temporary and Perennially Flowing Headwater Streams in Western Oregon,’’ Journal of Freshwater Ecology 17:391–407 (2002)). For example, many fish feed on drifting insects, and

numerous studies document the downstream

drift of stream invertebrates that then are eaten by fish in larger rivers. See, e.g., id. at 4–29 to 4–30 (citing S. Nakano and M. Murakami, ‘‘Reciprocal Subsidies: Dynamic Interdependence between Terrestrial and Aquatic Food Webs,’’ Proceedings of the National Academy of Sciences USA 98:166– 170 (2001); M.S. Wipfli and D.P. Gregovich, ‘‘Export of Invertebrates and Detritus from

Fishless Headwater Streams in Southeastern Alaska: Implications for Downstream Salmonid Production,’’ Freshwater Biology 47:957–969 (2002)).

Biological connectivity also allows gene flow, or genetic connectivity, among tributary and river populations. Gene flow is needed to maintain genetic diversity in a species, a basic requirement for that species to be able to adapt to environmental change. Populations connected by gene flow have a larger breeding population size, making them less prone to the deleterious effects of inbreeding and local extinction. Id. at 4–33 (citing R. Lande and S. Shannon, ‘‘The role of genetic variation in adaptation and population persistence in a changing

environment,’’ Evolution 50:434–437 (1996)). Genetic connectivity exists at multiple scales and can extend beyond one a single river catchment, and for species capable of long distance movement (such as salmon), reveals complex interactions among spatially distant populations of aquatic organisms Id. (citing J.M. Hughes, et al., ‘‘Genes in Streams: Using

DNA to Understand the Movement of

Freshwater Fauna and Their Riverine Habitat,’’ Bioscience 59:573–583 (2009); C.D. Anderson, ‘‘Considering spatial and temporal scale in landscape-genetic studies of gene flow,’’ Molecular Ecology 19:3565–3575 (2010)).

D. Headwater Tributaries Significantly Affect the Chemical, Physical, or Biological Integrity of (a)(1) Through (a)(3) Waters

As discussed above, the scientific literature supports the conclusion that tributaries, including headwater streams, have a significant nexus to downstream waters based on their contribution to the chemical, physical, or biological integrity of (a)(1) through (a)(3) waters. Headwater tributaries, the small streams at the uppermost reaches of the tributary network, are the most

abundant streams in the United States. See, e.g., id. at 4–2 (citing T.L. Nadeau and M.C. Rains, ‘‘Hydrological connectivity between

headwater streams and downstream waters: How science can inform policy,’’Journal of

the American Water Resources Association 43:118–133 (2007)). Collectively, they help shape the chemical, physical, and biological integrity of downstream waters, and providemany of the same functions as nonheadwater streams. See, e.g., id. at 1–7 to 1– 8, 4–1. For example, headwater streams

reduce the amount of sediment delivered to downstream waters by trapping sediment

from water and runoff. See, e.g., M. Dieterich and N.H. Anderson, ‘‘Dynamics of Abiotic Parameters, Solute Removal and Sediment Retention in Summer-Dry Headwater Stream of Western Oregon,’’ Hydrobiologia 379: 1–15 (1998). Headwater streams shape river channels by accumulating and gradually or episodically releasing sediment and large woody debris into river channels. They are also responsible for most nutrient cycling and removal, and thus transforming and changing the amount of nutrients delivered

to downstream waters. See, e.g., Report at 4– 18 (citing B.J. Peterson, et al., ‘‘Control of Nitrogen Export from Watersheds by Headwater Streams,’’ Science 292: 86–90 (2001)). A close connection exists between the water quality of these streams and the water quality of traditional navigable waters, interstate waters, and the territorial seas. See,

e.g., State of Ohio Environmental Protection Agency, Nonpoint Source Impacts on Primary Headwater Streams (Columbus, OH: Ohio Environmental Protection Agency, 2003). Activities such as discharging a pollutant into one part of the tributary system are well-documented to affect other parts of the system, even when the point of discharge is far upstream from the navigable water that experiences the effect of the discharge. See,

e.g., F.M. Dunnivant and E. Anders, A Basic

Introduction To Pollutant Fate and Transport: An Integrated Approach With Chemistry, Modeling, Risk Assessment, and Environmental Legislation (Hoboken, NJ: John Wiley & Sons, Inc., 2006).

Headwater streams provide unique habitat and protection for amphibians, fish, and other aquatic or semi-aquatic species living in and near the stream that may use the downstream waters for other portions of their life stages. See, e.g., Report at 1–8; J.L. Meyer, et al., ‘‘The Contribution of Headwater Streams to Biodiversity in River Networks,’’ Journal of the American Water Resources


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Association 43(1): 86–103 (2007). They also serve as migratory corridors for fish. Tributaries can improve or maintain biological integrity and can control water temperatures in the downstream waters. See,

e.g., Report at 4–14 (citing J.L. Ebersole, et. al., ‘‘Cold water patches in warm streams: Physicochemical characteristics and the influence of shading,’’ Journal of the

American Water Resources Association 39:355–368 (2003); B. Gardner, and P.J. Sullivan, ‘‘Spatial and temporal stream temperature prediction: Modeling nonstationary temporal covariance

structures,’’ Water Resources Research 40:1– 9 (2004); B.R. Johnson, et al., ‘‘Use of spatially explicit physicochemical data to measure downstream impacts of headwater stream disturbance,’’ Water Resources

Research 46:W09526 (2010)). Headwater streams also provide refuge habitat for riverine organisms seeking protection from temperature extremes, flow extremes, low dissolved oxygen, high sediment levels, or the presence of predators, parasites, and competitors. See, e.g., id. at 4–32 (citing J.C.

Scrivener, et al., ‘‘Juvenile Chinook salmon (Oncorhynchus tshawytscha) utilization of Hawks Creek, a small and nonnatal tributary of the Upper Fraser River,’’ Canadian Journal of Fisheries and Aquatic Sciences 51:1139– 1146 (1994); R.A. Curry, et al., ‘‘Use of small streams by young brook trout spawned in a lake,’’ Transactions of the American Fisheries Society 126:77–83 (1997); A.M.

Pires, et al., ‘‘Seasonal changes in fish community structure of intermittent streams in the middle reaches of the Guadiana basin, Portugal,’’Journal of Fish Biology 54:235–249 (1999); M.J Bradford, et al., ‘‘Ecology of juvenile Chinook salmon in a small nonnatal stream of the Yukon River drainage and the

role of ice conditions on their distribution and survival,’’ Canadian Journal of ZoologyRevue Canadienne De Zoologie 79:2043– 2054 (2001); M.A. Cairns, et al., ‘‘Influence of summer stream temperatures on black spot infestation of juvenile coho salmon in the Oregon Coast Range,’’ Transactions of the American Fisheries Society 134:1471–1479 (2005); Wigington, P. J., et al., ‘‘Coho salmon dependence on intermittent streams,’’ Frontiers in Ecology and the Environment 4:513–518 (2006)). Headwater streams serve as a source of food materials such as insects, larvae, and organic matter to nourish the fish, mammals, amphibians, and other organisms in downstream streams, rivers, and lakes. See, e.g., id. at 4–22, 4–24 (citing S.G., Fisher, and G.E. Likens, ‘‘Energy flow in Bear Brook, New Hampshire: An integrative approach to stream ecosystem metabolism,’’ Ecological Monographs 43:421–439 (1973); J.L. Meyer, ‘‘The microbial loop in flowing waters,’’ Microbial Ecology 28:195–199 (1994); J.B. Wallace, et al., ‘‘Multiple trophic levels of a

forest stream linked to terrestrial litter inputs,’’ Science 277:102–104 (1997); R.O. Hall, and J.L. Meyer, ‘‘The trophic significance of bacteria in a detritus-based stream food web,’’ Ecology 79:1995–2012 (1998); R.O. Hall, et al., ‘‘Organic matter flow

in stream food webs with reduced detrital resource base,’’ Ecology 81:3445–3463 (2000);

T. Gomi, et al., ‘‘Understanding processes and downstream linkages of headwater systems,’’ Bioscience 52:905–916 (2002); C. Augspurger, et al., ‘‘Tracking carbon flow in

a 2-week-old and 6-week-old stream biofilm food web,’’ Limnology and Oceanography 53:642–650 (2008)). Disruptions in these biological processes affect the ecological functions of the entire downstream system. See, e.g., L.A. Kaplan, et al., ‘‘Patterns of Dissolved Organic Carbon in Transport,’’ Limnology and Oceanography 25: 1034–1043 (1980); R.L. Vannote, et. al., ‘‘The River Continuum Concept,’’ Canadian Journal of Fisheries and Aquatic Sciences 37: 130–37 (1980). Headwater streams can help to maintain base flow in the larger rivers downstream, which is particularly important in times of drought. See, e.g., Report at 4–4, 4–66 (citing P.D. Brooks, and M.M. Lemon, ‘‘Spatial variability in dissolved organic matter and inorganic nitrogen concentrations in a semiarid stream, San Pedro River,
Arizona,’’Journal of Geophysical ResearchBiogeosciences 112:G03S05.D (2007); Tetzlaff, and C. Soulsby, ‘‘Sources of baseflow in larger catchments—using tracers to develop a holistic understanding of runoff generation,’’Journal of Hydrology 359:287– 302 (2008)). At the same time, the network of headwater streams can regulate the flow of water into downstream waters, mitigating low flow and high flow extremes, reducing local and downstream flooding, and preventing excess erosion caused by flooding. See, e.g., United States, U.S. EPA

and USDA/ARS Southwest Watershed Research Center, EPA/600/R–08/134, ARS/

2330462008: The Ecological and Hydrological Significance of Ephemeral and

Intermittent Streams in the Arid and Semiarid American Southwest (Washington, DC:

U.S. EPA and USDA/ARS Southwest Watershed Research Center, Levick et al., 2008) (Levick et al. 2008).

F. Ephemeral and Intermittent Tributaries Significantly Affect the Chemical, Physical, or Biological Integrity of (a)(1) Through (a)(3)

Waters

Tributaries do not need to flow perennially to have a significant nexus to downstream waters. Approximately 59% of streams across the United States (excluding Alaska) flow intermittently or ephemerally; ephemeral and intermittent streams are particularly prevalent in the arid and semi-arid Southwest, where they account for over 81%

of streams. Levick et al. 2008. Despite their intermittent or ephemeral flow, these streams nonetheless perform the same important ecological and hydrological functions

documented in the scientific literature as perennial streams, through their movement of water, nutrients, and sediment to

downstream waters. Id. The importance of intermittent and ephemeral streams is documented in a 2008 peer-reviewed report by EPA’s Office of Research and Development and the U.S. Department of Agriculture’s Agricultural Research Service, which addresses the hydrological and ecological significance of ephemeral and

intermittent streams in the arid and semi-arid

Southwestern United States and their connections to downstream waters; the report is a state-of-the-art synthesis of current knowledge of the ecology and hydrology in these systems. Id. Intermittent and ephemeral streams are chemically, physically, and biologically connected to downstream waters, and these

connections have effects downstream. See, e.g., id. In some areas, stormflows channeled into alluvial floodplain aquifers by intermittent and ephemeral streams are the major source of annual streamflow in rivers. Perennial flows are not necessary for

chemical connections. Periodic flows in ephemeral or intermittent tributaries can have a strong influence on biogeochemistry by connecting the channel and other landscape elements. See, e.g., Report at 4–16 (citing H.M. Valett, et. al., ‘‘Biogeochemical and Metabolic Responses to the Flood Pulse in a Semiarid Floodplain,’’ Ecology 86(1): 220–234 (2005)). This episodic connection can be very important for transmitting a

substantial amount of material into

downstream rivers. See, e.g., id. (citing Nadeau and Rains (2007)). Ephemeral desert streams have been shown to export particularly high sediment loadings. See, e.g.,

id. at 4–10 (citing M.A. Hassan, ‘‘Observations of Desert Food Bores,’’ Earth Surface Processes and Landforms 15:481–485 (1990)). Ephemeral streams can also temporarily and effectively store large

amounts of sediment that would otherwise wash downstream, contributing to the maintenance of downstream water quality and productive fish habitat. See, e.g., S.H.
Duncan, et al., ‘‘Transport of Road-Surface Sediment through Ephemeral Stream Channels,’’ Water Resources Bulletin 23(1): 113–119 (1987). This temporary storage of sediment thus helps maintain the chemical and biologic integrity of downstream waters.

The Report provides case studies of prairie

streams and Southwest intermittent and ephemeral streams, two stream types whose jurisdictional status has been called into question in the past. These case studies highlight the importance of these streams to downstream waters, despite their small size and ephemeral or intermittent flow regime. Prairie streams are frequently subjected to the extremes of drying and flooding, and intermittent or flashy hydrology is prevalent in river networks throughout most of the Great Plains. Report at 4–40 (citing W.J. Matthews, ‘‘North American Prairie Streams as Systems for Ecological Study,’’ Journal of the North American Benthological Society 7:387–409 (1988); A.V. Zale et al., ‘‘The Physicochemistry, Flora, and Fauna of

Intermittent Prairie Streams: A Review of the

Literature,’’ United States Fish and Wildlife Service Biological Report 89:1–44 (1989); N.L. Poff, ‘‘A Hydrogeography of Unregulated

Streams in the United States and an Examination of Scale Dependence in Some Hydrological Descriptors,’’ Freshwater Biology 36:71–91 (1996); W.K. Dodds, et al., ‘‘Life on the Edge: The Ecology of Great Plains Prairie Streams,’’ Bioscience 54:205– 216 (2004)). Prairie streams typically represent a collection of spring-fed, perennial pools and reaches, embedded within larger, intermittently flowing segments. Id. at 4–55 (citing T.R. Labbe, and K.D. Fausch, ‘‘Dynamics of Intermittent Stream Habitat Regulate Persistence of a Threatened Fish at Multiple Scales,’’ Ecological Applications 10:1774–1791 (2000)). These streams have


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significant chemical, physical, and biological connections to downstream waters, despite extensive alteration of historical prairie regions by agriculture, water impoundment, water withdrawals, and other human activities, and the challenges these alterations create for assessing connectivity.

Id. (citing W.J. Matthews, and H.W. Robinson, ‘‘Influence of Drainage Connectivity, Drainage Area and Regional Species Richness on Fishes of the Interior Highlands in Arkansas,’’ American Midland

Naturalist 139:1–19 (1998); W.K. Dodds, et al., ‘‘Life on the Edge: The Ecology of Great Plains Prairie Streams,’’ Bioscience 54:205– 216 (2004)). The most notable connections are via flood propagation, contaminated sediment transport, nutrient retention, and the extensive transport and movement of fish species (including eggs and larvae) throughout these networks. Id. at 4–55 (citing H.F. Matthai, Floods of June 1965 in South Platte River Basin, Colorado, Water Supply Paper 1850–B (Washington, DC: U.S. Geological Survey, 1969); A.J. Horowitz, et al., ‘‘The Effect of Mining on the Sedimenttrace Element Geochemistry of Cores from the Cheyenne River Arm of Lake Oahe, South Dakota, USA,’’ Chemical Geology 67:17–33 (1988); DC Marron, ‘‘The Transport of Mine Tailings as Suspended Sediment in the Belle Fourche River, West-central South Dakota,

USA,’’ International Association of Hydrologic Sciences 184:19–26 (1989); W.K. Dodds, et al., ‘‘Nitrogen Transport from Tallgrass Prairie Watersheds,’’ Journal of Environmental Quality 25:973–981 (1996); K.D. Fausch, and K.R. Bestgen, ‘‘Ecology of Fishes Indigenous to the Central and Southwestern Great Plains,’’ in F.L. Knopf and F.B. Samson, ed., Ecology and Conservation of Great Plains Vertebrates, (New York, NY: Springer-Verlag, 1997), pp. 131–166; S.P. Platania, and C.S. Altenbach, ‘‘Reproductive Strategies and Egg Types of Seven Rio Grande Basin Cyprinids,’’ Copeia 1998:559–569 (1998); K.M. Fritz, and W.K. Dodds, ‘‘Resistance and Resilience of Macroinvertebrate Assemblages to Drying and Flood in a Tallgrass Prairie Stream System,’’ Hydrobiologia 527:99–112 (2004); K.M. Fritz, and W.K. Dodds, ‘‘Harshness:

Characterization of Intermittent Stream Habitat over Space and Time,’’ Marine and

Freshwater Research 56:13–23 (2005); N.R.

Franssen, et al., ‘‘Effects of Floods on Fish Assemblages in an Intermittent Prairie

Stream,’’ Freshwater Biology 51:2072–2086 (2006); R.B. Alexander, et al., ‘‘Differences in Phosphorus and Nitrogen Delivery to the Gulf of Mexico from the Mississippi River

Basin,’’ Environmental Science & Technology 42:822–830 (2008); J.S. Perkins, and K.B. Gido, ‘‘Stream Fragmentation Thresholds for a Reproductive Guild of Great Plains Fishes,’’

Fisheries 36:371–383 (2011)).

Southwestern intermittent and ephemeral streams exert strong influences on the structure and function of downstream waters, and the case study (included in the Report) echoes many of the findings of the functions of intermittent and ephemeral tributaries generally, which are described above. The case study focuses on the heavily studied San Pedro River, located in southeast Arizona, in particular, as a representative example of the hydrological behavior and the connectivity of rivers in the Southwest, but also examines

evidence relevant to other Southwestern streams. The chemical, physical, and biological connections of Southwestern intermittent and ephemeral streams highlighted in the case study are summarized below. Flows from ephemeral streams are one of the major drivers of the dynamic hydrology of Southwest rivers (particularly of floods during monsoon seasons. Id. at 4–60, 4–67 (citing DC Goodrich, et al., ‘‘Linearity of Basin Response as a Function of Scale in a Semiarid Watershed,’’ Water Resources

Research 33:2951–2965 (1997); F. Yuan, and S. Miyamoto, ‘‘Characteristics of Oxygen-18 and Deuterium Composition in Waters from the Pecos River in American Southwest,’’ Chemical Geology 255:220–230 (2008)).

Downstream river fishes and invertebrates are adapted to the variable flow regimes that are influenced strongly by ephemeral tributary systems, which provide isolated pools as refuges for fish during dry periods.

Id. at 4–68 to 4–69 (citing K.R. John,

‘‘Survival of Fish in Intermittent Streams of the Chirichua Mountains, Arizona’’ Ecology 45:112–119 (1964); T.R. Labbe, and K.D. Fausch, ‘‘Dynamics of Intermittent Stream Habitat Regulate Persistence of a Threatened Fish at Multiple Scales,’’ Ecological Applications 10:1774–1791 (2000); J.N. Rinne, and D. Miller, ‘‘Hydrology, Geomorphology and Management: Implications for Sustainability of Native Southwestern Fishes,’’ Reviews in Fisheries

Science 14:91–110 (2006); D.A. Lytle, et al., ‘‘Evolution of Aquatic Insect Behaviors

across a Gradient of Disturbance Predictability,’’ Proceedings of the Royal Society—Series B 275:453–462 (2008)). Ephemeral tributaries in the Southwest also supply water to mainstem river alluvial aquifers, which aids in the sustaining river

baseflows downstream. Id. at 4–64 (citing DC Goodrich, et al., ‘‘Linearity of Basin Response

as a Function of Scale in a Semiarid Watershed,’’ Water Resources Research 33:2951–2965 (1997); J.B. Callegary, et al., ‘‘Rapid Estimation of Recharge Potential in Ephemeral-Stream Channels using Electromagnetic Methods, and Measurements of Channel and Vegetation Characteristics,’’ Journal of Hydrology 344:17–31 (2007)). Ephemeral tributaries export sediment downstream during major hydrologic events; the sediment, in turn, contributes to materials that comprise alluvial aquifers and shape the fluvial geomorphology (the science of how rivers and streams form given the landscape setting) of downstream waters. Id. at 4–65 (citing G.C. Nanson, and J.C. Croke, ‘‘A Genetic Classification of Floodplains,’’ Geomorphology4:459–486 (1992)). The nutrient and biogeochemical integrity of downstream Southwestern rivers, such as the San Pedro River, is heavily influenced by nutrient export from ephemeral tributaries

after storm flow events. Id. at 4–18, 4–66 (citing P.D. Brooks, and M.M. Lemon, ‘‘Spatial Variability in Dissolved Organic Matter and Inorganic Nitrogen Concentrations in a Semiarid Stream, San Pedro River, Arizona,’’Journal of Geophysical Research-Biogeosciences 112:G03S05 (2007)). Extensive downstream river riparian communities are supported by water, sediment and nutrients exported to the river from ephemeral tributaries; these riparian communities have a profound influence on the river attributes through shading, allochthonous (originating from outside of the channel) inputs of organic matter, detritus, wood, and invertebrates to

the river. Id. at 4–65 to 4–66 (citing S.V. Gregory, et al., ‘‘An Ecosystem Perspective of Riparian Zones: Focus on Links between Land and Water,’’ Bioscience 41:540–551 (1991); R.J. Naiman, et al., Riparia: Ecology, Conservation, and Management of

Streamside Communities (Burlington, MA: Elsevier, Inc., 2005); J.C. Stromberg, et al., ‘‘Effects of Stream Flow Intermittency on Riparian Vegetation of a Semiarid Region River (San Pedro River, Arizona),’’ River Research and Applications 21:925–938 (2005), M. Baillie, et al., ‘‘Quantifying Water Sources to a Semiarid Riparian Ecosystem, San Pedro River, Arizona,’’ Journal of Geophysical Research 112:G03S02 (2007); National Research Council, Riparian Areas: Functions and Strategies for Management (Washington, DC: National Academy Press, 2002)).

E. Tributary Lakes, Ponds, and Wetlands Significantly Affect the Chemical, Physical, or Biological Integrity of (a)(1) Through (a)(3)

Waters

As discussed elsewhere in this preamble, riparian and floodplain wetlands have a significant nexus to downstream waters, and

wetlands that are tributaries are a subset of

such wetlands. The fact that a wetland tributary is in-stream often enhances its ability to filter pollutants and contaminants that would otherwise make it downstream;

in-stream wetlands also attenuate floodwaters. Lakes and ponds serve many important functions that affect the chemical, physical, and biological conditions

downstream. Lake tributaries can act as sinks, storing floodwaters, sediment, and nutrients, as these materials have the opportunity to settle out, at least temporarily, as water moves through the lake to

downstream waters. See, e.g., R.W. Phillips, et al., ‘‘Connectivity and Runoff Dynamics in Heterogeneous Basins,’’ Hydrological

Processes 25(19): 3061–3075 (2011). The

attenuation of floodwaters can also maintain

stream flows downstream. Id. Lakes, as with other tributaries, can also act as sources, contributing flow, nutrient, sediment, and

other materials downstream. Total Maximum Daily Loads (TMDLs) for nutrients have been established for many in-stream lakes across the country in recognition of the ability of lakes to transport nutrients downstream, contributing to downstream impairments. See, e.g. Maine Department of Environmental
Protection, Phosphorus Control Action Plan and Total Maximum Daily (Annual Phosphorous) Load Report, Daigle Pond, New Canada, Aroostook County, Maine, Daigle Pond PCAP—TMDL Report, Maine DEPLW— 0789 (Maine DEP, 2006); U.S. Environmental Protection Agency, ‘‘Section 6 Echo Park Lake TMDLs,’’ Los Angeles Area Lakes TMDLs, January 2011 Revised Draft (2011). Lakes can also serve as habitat for species that then move downstream. For instance,

brook trout that are stocked in headwater


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lakes in Idaho and Montana are capable of invading most downstream habitat, including through very steep channel slopes and waterfalls. S.B. Adams, et al., ‘‘Geography of Invasion in Mountain Streams: Consequences of Headwater Lake Fish Introductions,’’ Ecosystems 4(4): 296–307. These non-native species can then affect the biological integrity of downstream waters by impacting populations of native fish species, such as cutthroat trout, downstream. See, e.g., J.B. Dunham, et al., ‘‘Alien Invasions in Aquatic Ecosystems: Toward an Understanding of Brook Trout Invasions and Potential Impacts

on Inland Cutthroat Trout in Western North
America,’’ Reviews in Fish Biology and

Fisheries 12(4): 373–391 (2002). For example,

non-native trout were introduced in headwater tributary lakes to the Little Kern

River in the southern Sierra Nevada anddispersed downstream, causing the nearextinction of the native Little Kern golden trout. R.A. Knapp, and K.R. Matthews,

‘‘Effects on Nonnative Fishes on Wilderness Lake Ecosystems in the Sierra Nevada and Recommendations for Reducing Impacts,’’ in D. N. Cole, et al., ed., Wilderness Science in a Time of Change Conference, Volume 5: Wilderness Ecosystems, Threats, and Management, Missoula, Montana, May 23–

27, 1999, Proceedings RMRS–P–15–VOL–5 (Ogden, UT: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, 2000), 312–317. These studies demonstrate the ability of organisms to travel from tributary lakes to downstream waters, which is not limited to just non-native species; many other species can also move downstream and back again.

One type of wetlands located in-stream are

unidirectional wetlands that are connected to the river network through a channel (e.g., wetlands that serve as stream origins; a

definition of ‘‘unidirectional wetlands’’ can be found in part I section 4.B above). These tributary wetlands are generally exemplary of tributary wetlands as a whole, and because the Report focuses in part on these wetlands, they are discussed here in further detail.

These are wetlands from which a stream channel originates. Report at 5–1 to 5–2. They are part of the stream network itself, and along with first- and second-order streams, form the headwaters of the river

network. Such wetlands have a direct hydrologic connection to the tributary

network via unidirectional flow from

wetland to the headwater stream. Channel origin wetlands generally have important chemical, physical, and biological effects on (a)(1) through (a)(3) waters, including hydrologic, water quality, and habitat functions, regardless if the outflow from the wetland to the stream is perennial, intermittent, or ephemeral. Id. Like other wetlands, wetlands that serve as stream origins can transport channel-forming sediment and woody debris, transport stored organic matter, remove and transform pollutants and excess nutrients such as nitrogen and phosphorus, attenuate and store floodwaters, contribute to stream baseflow through groundwater recharge, and provide habitat for breeding fish, amphibians,reptiles, birds, and other aquatic and semiaquatic species that move from the wetlands

to the river network. Id. at 5–41. Wetlands that serve as stream origins connect via perennial, intermittent, or ephemeral drainages to river networks. Id. at 5–22 to 5–23 (citing M.C. Rains, et al., ‘‘The Role of Perched Aquifers in Hydrological Connectivity and Biogeochemical Processes in Vernal Pool Landscapes, Central Valley, California,’’ Hydrological Processes 20:1157– 1175 (2006); M.C. Rains, et al., ‘‘Geological Control of Physical and Chemical Hydrology in California Vernal Pools,’’ Wetlands 28:347–362 (2008); T.R. Morley, et al., ‘‘The Role of Headwater Wetlands in Altering Streamflow and Chemistry in a Maine, USA Catchment,’’Journal of the American Water

Resources Association 47:337–349 (2011)). Regardless of the permanence of flow, such wetlands have an impact on downstream

water. Id. at 5–1 to 5–2. Wetland seeps, for example, can form where groundwater discharges from breaks in slope. Id. at 5–21 (citing B.R. Hall, et al., ‘‘Environmental Influences on Plant Species Composition in Ground-water Seeps in the Catskill Mountains of New York,’’ Wetlands 21:125– 134 (2001); M.A. O’Driscoll, and D.R. DeWalle, ‘‘Seeps Regulate Stream Nitrate Concentration in a Forested Appalachian Catchment,’’Journal of Environmental Quality 39:420–431 (2010)). They often have perennial connections to the stream, providing important sources of water downstream, particularly during summer

baseflow. Id. at 5–22 (citing T.R. Morley, et al., ‘‘The Role of Headwater Wetlands in Altering Streamflow and Chemistry in a Maine, USA Catchment,’’ Journal of the

American Water Resources Association 47:337–349 (2011)). In Maine, for example, seeps were found to provide 40 to 80% of stream water during baseflow periods. Id. In other cases, surface connections between channel origin wetlands and streams are intermittent or ephemeral. For example, California vernal pools spill water a great number of days during the years via channels, providing water downstream. Id. (citing M.C. Rains, et al., ‘‘The Role of Perched Aquifers in Hydrological Connectivity and Biogeochemical Processes in Vernal Pool Landscapes, Central Valley, California,’’ Hydrological Processes 20:1157– 1175 (2006); M.C. Rains, et al., ‘‘Geological Control of Physical and Chemical Hydrology in California Vernal Pools,’’ Wetlands 28:347–362 (2008)). In addition to surface water connections, groundwater flow can hydrologically connect wetlands that serve as stream origins with the stream network. Id.

at 5–23.

The hydrologic connection of the wetland to the stream can affect streamflow by altering baseflow or storm flow through several mechanisms, including surface storage and groundwater recharge. Id. at 5– 25. Studies at the larger scale have shown that wetlands, by storing water, reduce peak streamflows and, thus, downstream flooding.

Id. (citing J. Jacques, and D. L. Lorenz, Techniques for Estimating the Magnitude and Frequency of Floods of Ungauged

Streams in Minnesota, Report 87–4170 (Washington, DC: U.S. Geological Survey, 1988); Vining, K.C., Simulation of Streamflow and Wetland Storage, Starkweather Coulee Subbasin, North Dakota, Water Years 1981–98, WaterResources Investigations Report 02–4113 (Bismarck, ND: U.S. Geological Survey, 2002), 33 p.; P. McEachern, et al., ‘‘Landscape Control of Water Chemistry in Northern Boreal Streams of Alberta,’’ Journal of Hydrology 323:303–324 (2006); R.A. Gleason, et al. Estimating Water Storage Capacity of Existing and Potentially Restorable Wetland Depressions in a Subbasin of the Red River of the North, U.S. Geological Survey Open-File Report 2007– 1159 (Reston, VA: U.S. Geological Survey, 2007), 36 p.). In some cases, however, where wetlands that serve as stream origins are already saturated prior to rainfall, they can convey stormwater quickly downstream and thus actually increase flood peaks. Id. at 227 (citing Bay, R., ‘‘Runoff from Small Peatland Watersheds,’’Journal of Hydrology 9:90–102 (1969); A. Bullock, and M. Acreman, ‘‘The Role of Wetlands in the Hydrological Cycle,’’ Hydrology and Earth System Sciences 7:358– 389 (2003)). This is because the wetland soil, if completely saturated, cannot store any additional water, making the wetland enable

to store floodwater.

Wetlands that serve as stream origins have important chemical connections to downstream waters that affect the integrity of

those waters. These wetlands contain diverse microbial populations that perform various chemical transformations, acting as source of compounds and influencing the water quality

downstream. Id. at 5–28 (citing K.R. Reddy, and R.D. DeLaune, Biogeochemistry of Wetlands: Science and Applications, 774 p. (2008)). Sulfate-reducing bacteria found in some headwater wetlands produce methylated mercury, which is then transported downstream by surface flows. Id. (citing O.K. Linqvist, et al., ‘‘Mercury in the

Swedish Environment—Recent Research on Causes, Consequences, and Remedial

Measures,’’ Water Air and Soil Pollution 55:xi-xiii (1991); G. Mierle, and R. Ingram,

‘‘The Role of Humic Substances in the Mobilization of Mercury from Watersheds,’’

Water Air and Soil Pollution 56:349–357 (1991); C.T. Driscoll, et al., ‘‘The Role of Dissolved Organic Carbon in the Chemistry and Bioavailability of Mercury in Remote Adirondack Lakes,’’ Water Air and Soil

Pollution 80:499–508 (1995); B.A. Branfireun, et al., ‘‘In situ Sulphate Stimulation of Mercury Methylation in a Boreal Peatland:

Toward a Link Between Acid Rain and Methylmercury Contamination in Remote

Environments,’’ Global Biogeochemical Cycles 13:743–750 (1999)). Wetlands, including those that serve as stream origins, are the principle sources of dissolved organic carbon (DOC) in forests to downstream

waters. Id. (citing P.J. Mulholland, and E.J. Kuenzler, ‘‘Organic Carbon Export from Upland and Forested Wetland Watersheds,’’ Limnology and Oceanography 24:960–966 (1979); N.R. Urban, et al., ‘‘Export of Dissolved Organic Carbon and Acidity from Peatlands,’’ Water Resources Research 25:1619–1628 (1989); B.W. Eckhardt and T.R. Moore, ‘‘Controls on Dissolved Organic

Carbon Concentrations in Streams of Southern Quebec,’’ Canadian Journal of Fisheries and Aquatic Sciences 47:1537–1544 (1990); J.-F. Koprivnjak and T.R. Moore,


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‘‘Sources, Sinks, and Fluxes of Dissolved Organic Carbon in Subarctic Fen Catchments,’’ Arctic and Alpine Research 24:204–210 (1992); P. Kortelainen, ‘‘Content of Total Organic Carbon in Finnish Lakes and Its Relationship to Catchment Characteristics,’’ Canadian Journal of Fisheries and Aquatic Sciences 50:1477–1483 (1993); T.A. Clair, et al., ‘‘Exports of Carbon and Nitrogen from River Basins in Canada’s Atlantic Provinces,’’ Global Biogeochemical Cycles 8:441–450 (1994); D. Hope, et al., ‘‘A Review of the Export of Carbon in River Water: Fluxes and Processes,’’ Environmental

Pollution 84:301–324 (1994); P.J. Dillon and L.A. Molot, ‘‘Effects of Landscape Form on Export of Dissolved Organic Carbon, Iron, and Phosphorus from Forested Stream Catchments,’’ Water Resources Research 33:2591–2600 (1997); S.E. Gergel, et al., ‘‘Dissolved Organic Carbon as an Indicator of

the Scale of Watershed Influence on Lakes and Rivers,’’ Ecological Applications 9:1377– 1390 (1999)). Export of DOC to downstream waters supports primary productivity, effects pH and buffering capacity, and regulates exposure to UV–B radiation. Id. at 5–29 (citing K.N. Eshelman and H.F. Hemond, ‘‘The Role of Organic Acids in the Acid-base

Status of Surface Waters at Bickford Watershed, Massachusetts,’’ Water Resources

Research 21:1503–1510 (1985); L.O. Hedin, et al., ‘‘Patterns of Nutrient Loss from Unpolluted Old-growth Temperate Forests: Evaluation of Biogeochemical Theory,’’ Ecology 76:493–509 (1995); D.W. Schindler and P.J. Curtis, ‘‘The Role of DOC in Protecting Freshwaters Subjected to Climate Warming and Acidification from UV Exposure,’’ Biogeochemistry 36:1–8 (1997); J.C. Nuff and G.P. Asner, ‘‘Dissolved Organic Carbon in Terrestrial Ecosystems: Synthesis and a Model,’’ Ecosystems 4:29–48 (2001)).

Wetlands also act as sinks and transformers for pollutants, including excess nutrients, through such processes as denitrification, ammonia volatilization, microbial and plant biomass assimilation, sedimentation, sorption and precipitation, biological uptake, and long-term storage of plant detritus. Id. (citing K.C. Ewel and H.T. Odum, Cypress Swamps (Gainesville, FL: University Presses of Florida, 1984); S.J. Nixon and V.J. Lee, Wetlands and Water Quality: A Regional Review of Recent Research in the United States on the Role of Freshwater and Saltwater Wetlands as Sources, Sinks, and Transformers of Nitrogen, Phosphorus, and Various Heavy Metals, Technical Report Y– 86–2 (Vicksburg, MS: U.S. Army Corps of Engineers, Waterways Experiment Station, 1986); C. Johnston, ‘‘Sediment and Nutrient Retention by Freshwater Wetlands: Effects on Surface Water Quality,’’ Critical Reviews in

Environmental Control 21:491–565 (1991); K.R. Reddy, et al., ‘‘Phosphorus Retention in Streams and Wetlands: A Review,’’ Critical

Reviews in Environmental Science and Technology 29:83–146 (1999); W.J. Mitsch and J.G. Gosselink, Wetlands, 4th edition (Hoboken, NJ: John Wiley & Sons Inc., 2007); K.R. Reddy, and R.D. DeLaune, Biogeochemistry of Wetlands: Science and Applications (Boca Raton, FL: CRC Press, 2008); R.H. Kadlec and S.D. Wallace, Treatment Wetlands, 2nd edition (Boca Raton, FL: CRC Press, 2009)). Specifically, wetlands reduce phosphorus, nitrate, and ammonium by large percentages. Id. at 5–30 (citing F.E. Dierberg and P.L. Brezonik, ‘‘Nitrogen and Phosphorus Mass Balances in a Cypress Dome Receiving Wastewater,’’ in K.C. Ewel and H.T. Odum, ed., Cypress Swamps (Gainesville, FL: University Presses of Florida, 1984), pp. 112–118; E.J. Dunne, et al., ‘‘Phosphorus Release and Retention by Soils of Natural Isolated Wetlands,’’ International Journal of Environment and

Pollution 28:496–516 (2006); T.E. Jordan, et al., ‘‘Comparing Functional Assessments of

Wetlands to Measurements of Soil Characteristics and Nitrogen Processing,’’

Wetlands 27:479–497 (2007)). These processes are important for protecting downstream waters from pollutants from agricultural runoff. Wetland microbial processes reduce other pollutants, such as pesticides, hydrocarbons, heavy metals, and

chlorinated solvents. Id. (citing R.R. Brooks, et al., ‘‘Cobalt and Nickel Uptake by the Nyssaceae,’’ Taxon 26:197–201 (1977); C.M.

Kao, et al., ‘‘Non-point Source Pesticide Removal by a Mountainous Wetland,’’ Water Science and Technology46:199–206 (2002); P.I. Boon, ‘‘Biogeochemistry and Bacterial Ecology of Hydrologically Dynamic Wetlands,’’ in D. P. Batzer and R. R. Sharitz, ed., Ecology of Freshwater and Estuarine

Wetlands (Berkeley, CA: University of California Press, 2006), pp. 115–176).

Tributary wetlands have important biological connections downstream that impact the integrity of (a)(1) through (a)(3) waters. Emergent and aquatic vegetation found in wetlands disperse by water, wind, and hitchhiking on migratory animals from tributary wetlands downstream. Id. at 5–31 (citing M.B. Soons and G.W. Heil, ‘‘Reduced Colonization Capacity in Fragmented Populations of Wind-Dispersed Grassland Forbs,’’Journal of Ecology 90:1033–1043 (2002); M.B. Soons, ‘‘Wind Dispersal in Freshwater Wetlands: Knowledge for Conservation and Restoration,’’ Applied Vegetation Science 9:271–278 (2006); C. Nilsson, et al., ‘‘The Role of Hydrochory in Structuring Riparian and Wetland Vegetation,’’ Biological Reviews 85:837–858 (2010)). Similarly, fish move between the river network and wetlands during times of surface water connections, and tributary wetlands by definition are connected on the

surface to downstream waters. Id. at 5–32 (citing J.W. Snodgrass, et al., ‘‘Factors affecting the occurrence and structure of fish assemblages in isolated wetlands of the upper coastal plain, USA,’’ Canadian Journal of Fisheries and Aquatic Sciences 53:443– 454 (1996); K.D. Zimmer, et al., ‘‘Effects of

fathead minnow colonization and removal on a prairie wetland ecosystem,’’ Ecosystems 4:346–357 (2001); M.J. Baber, et al., ‘‘Controls

on fish distribution and abundance in temporary wetlands,’’ Canadian Journal of Fisheries and Aquatic Sciences 59:1441–1450 (2002); M.A. Hanson, et al., ‘‘Biotic interactions as determinants of ecosystem structure in prairie wetlands: An example using fish,’’ Wetlands 25:764–775 (2005); B.R. Herwig, et al., ‘‘Factors influencing fish distributions in shallow lakes in prairie and prairie-parkland regions of Minnesota, USA,’’ Wetlands 30:609–619 (2010)). Mammals that can disperse overland can also contribute to connectivity. Id. (citing C.E. Shanks, and G.C. Arthur, ‘‘Muskrat movements and population dynamics in Missouri farm ponds and

streams,’’Journal of Wildlife Management 16:138–148 (1952); W.R. Clark, ‘‘Ecology of muskrats in prairie wetlands,’’ in H.R. Murkin, et al., ed., Prairie Wetland Ecology: The Contribution of the Marsh Ecology Research Program, (Ames, IA: Iowa State University Press, 2000), pp. 287–313). Insects

also hitchhike on birds and mammals from tributary wetlands to the stream network,

which can then serve as a food source for

downstream waters. Id. (citing J. Figuerola, and A.J. Green, ‘‘Dispersal of Aquatic Organisms by Waterbirds: A Review of Past Research and Priorities for Future Studies,’’ Freshwater Biology47:483–494 (2002); J. Figuerola, et al., ‘‘Invertebrate Eggs Can Fly:

Evidence of Waterfowl-Mediated Gene Flow in Aquatic Invertebrates,’’ American

Naturalist 165:274–280 (2005)). Insects that are flight-capable also use both stream and tributary wetlands, moving from the stream

to the wetland to find suitable habitat for overwintering, refuge from adverse conditions, hunting, foraging, or breeding. Id. at 5–33 (citing D.D. Williams, ‘‘Environmental Constraints in Temporary Fresh Waters and Their Consequences for the

Insect Fauna,’’ Journal of the North American Benthological Society 15:634–650 (1996); A.J. Bohonak and D.G. Jenkins, ‘‘Ecological and Evolutionary Significance of Dispersal by Freshwater Invertebrates,’’ Ecology Letters 6:783–796 (2003)). Amphibians and reptiles, including frogs, toads, and newts, also move between streams or rivers and tributary wetlands to satisfy part of their life history requirements, feed on aquatic insects, and avoid predators. Id. (citing V.S. Lamoureux and D.M. Madison, ‘‘Overwintering Habitats of Radio-Implanted Green Frogs, Rana clamitans,’’ Journal of Herpetology 33:430– 435 (1999); K.J. Babbitt, et al., ‘‘Patterns of Larval Amphibian Distribution Along a Wetland Hydroperiod Gradient,’’ Canadian Journal of Zoology-Revue Canadienne De Zoologie 81:1539–1552 (2003); S.B. Adams, et al., ‘‘Instream Movements by Boreal Toads (Bufo boreas boreas),’’ Herpetological Review 36:27–33 (2005); D.M. Green, ‘‘Bufo

americanus, American Toad,’’ in M. Lannoo, ed., Amphibian Declines: The Conservation Status of United States Species (Berkeley, CA: University of California Press, 2005), pp. 692–704; T.W. Hunsinger and M.J. Lannoo, ‘‘Notophthalmus viridescens, Eastern Newt,’’ in M. Lannoo, ed., Amphibian Declines: The Conservation Status of United States Species (Berkeley, CA: University of California Press, 2005), pp. 912–914; J.W. Petranka, and C.T. Holbrook, ‘‘Wetland Restoration for Amphibians: Should Local Sites Be Designed to Support Metapopulations or Patchy Populations?,’’ Restoration Ecology 14:404– 411 (2006); A.L. Subalusky, et al., ‘‘Ontogenetic Niche Shifts in the American Alligator Establish Functional Connectivity between Aquatic Systems,’’ Biological

Conservation 142:1507–1514 (2009)).

Lake, pond, and wetland tributaries, including wetlands that serve as stream origins, have important chemical, physical,


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and biological connections downstream that affect (a)(1) through (a)(3) waters. Their direct hydrologic connection to the stream network facilitates the significant impact they have downstream. This impact on downstream waters occurs regardless of whether their flow is perennial, intermittent, or ephemeral. Thus, lake, pond, and wetland tributaries serve the same important functions as stream tributaries, which in turn greatly impact downstream (a)(1) through (a)(3) waters, particularly when their functional contributions to the chemical, physical, and biological conditions of downstream waters

are combined at a watershed scale.

F. Man-Made or Man-Altered Tributaries Significantly Affect the Physical, Chemical and Biological Integrity of (a)(1) Through (a)(3) Waters

The agencies’ proposed rule clarifies that

man-made and man-altered tributaries as defined in the proposed rule are ‘‘waters of the United States’’ because the significant nexus between a tributary and a traditional navigable water or interstate water is not broken where the tributary flows through a

culvert or other structure. Note that the proposal excludes certain ditches from CWA jurisdiction by rule in paragraphs (b)(3) and (b)(4). The scientific literature indicates that structures that convey water do not affect the connectivity between streams and downstream rivers. Indeed, because such

structures can reduce water losses from evapotranspiration and seepage, such structures likely enhance the extent of connectivity by more completely conveying

the water downstream.

Man-made and man-altered tributaries include impoundments, ditches, canals, channelized streams, piped, and the like. Ditches and canals are wide-spread across the United States. Ditches may have been streams that were channelized. They are purposely constructed to allow the hydrologic flow of the tributary to continue

downstream. Man-made and man-altered tributaries, despite human manipulation, usually continue to have chemical, physical, or biological connections downstream and to serve important functions downstream. Because these tributaries are hydrologically connected to downstream waters, the chemical and some biological connections to downstream waters that are supported by thishydrologic connection are still intact. Oftentimes man-made tributaries create connections where they did not previously exist, such as canals that connect two rivers

in different watersheds.

Tributary ditches and other man-made or

man-altered waters that meet the definition of ‘‘tributary’’ have a significant nexus to (a)(1) through (a)(3) waters due to their impact, either individually or with other tributaries, on the chemical, physical, or biological integrity of those downstream waters. Tributary ditches and the like, as with other tributaries, have chemical, physical, and biological connections with downstream waters that substantially impact those waters. Tributary ditches and canals can have perennial, intermittent, or ephemeral flow. As described above, tributaries of all flow regimes have a significant nexus to downstream (a)(1) through (a)(3) waters. Due to the often straightened and channelized nature of ditches, these tributaries quickly move water downstream to (a)(1) through (a)(3) waters. Ditches and canals, like other tributaries, export sediment, nutrients, and other

materials downstream. Due to their often channelized nature, ditches are very effective at transporting water and these materials, including nitrogen, downstream. See, e.g., J.P. Schmidt, et al., ‘‘Nitrogen Export from Coastal Plain Field Ditches,’’ Journal of Soil

and Water Conservation 62(4):235–243; J.S. Strock, et al., ‘‘Managing Natural Processes in Drainage Ditches for Nonpoint Source Nitrogen Control.’’ Journal of Soil and Water

Conservation 62(4): 188–196 (2007). Ditches provide habitat for fish and other aquatic organisms. See, e.g., P.C. Smiley, Jr., et al., ‘‘Contribution of Habitat and Water Quality to the Integrity of Fish Communities in Agricultural Drainage Ditches,’’ Journal of

Soil and Water Conservation 63(6):218A– 219A (2008). Fish and other aquatic organisms utilize canals and ditches to move to different habitats, sometimes over long distances. F.J. Rahel, ‘‘Biogeographic Barriers, Connectivity and Homogenization

of Freshwater Faunas: It’s a Small World after All,’’ Freshwater Biology 52(4): 696–710 (2007).

These significant connections and functions continue even where the tributary

has a natural or man-made break in its channel, bed and banks, or OHWM. The presence of a channel, bed and banks, and OHWM upstream or downstream of the break

is an indication that connections still exist. The significant nexus between a tributary

and a downstream water is not broken where the tributary flows underground for a portion of its length, such as in karst topography. The hydrologic connection still exists, meaning that the chemical and biological connections that are mediated by the hydrologic connection also still exist. Similarly, flow through boulder fields does not sever the hydrologic connection. When a tributary flows through a wetland enroute to another or the same tributary, the significant nexus still exists even though the bed and banks or ordinary high watermark is broken for the length of the wetland. As discussed in Part II, section 1.G. of this appendix, in-stream wetlands provide numerous benefits downstream, and the presence of the wetland in stream can provide additional water quality benefits to the receiving waters. Flow in flat areas with very low gradients may temporarily break the tributary’s bed and banks or OHWM, but these systems continue to have a significant nexus downstream. These are just illustrative examples of break in ordinary high watermark; there are several other types, all of which do not break the significant nexus between a tributary and the downstream (a)(1) through (a)(3) water.

There are more than 80,000 dams in the United States, with over 6,000 exceeding 15 meters in height. Report at 3–48 (citing U.S. Army Corps of Engineers, National Inventory of Dams (2009)). The purpose of a dam is to impound (store) water for any of several reasons (e.g. flood control, human water supply, irrigation, livestock water supply, energy generation, containment of mine tailings, recreation or pollution control). See http://www.damsafety.org/layout/ subsection.aspx?groupid=14&contentid=47. Many dams fulfill a combination of the above functions. Because the purpose of a dam is to retain water effectively and safely, the water retention ability of a dam is of prime importance. Water may pass from the reservoir to the downstream side of a dam by: passing through the main spillway or outlet works; passing over an auxiliary spillway; overtopping the dam; seepage through the abutments; and seepage under the dam. Id. All water retention structures are subject to seepage through their foundations and abutments. Department of the Army, U.S. Army Corps of Engineers, Engineering and Design—Design, Construction and Maintenance of Relief Wells, EM 1110–2– 1914 (Washington, DC: Department of the Army, 1992), p. 1–1. Thus waters behind a dam still maintain a hydrologic connection to

downstream waters.

Numerous studies have shown that dams impede biotic movements, reducing biological connectivity between upstream and downstream locations. Report at 3–48 (citing E.A. Greathouse, et al., ‘‘Indirect Upstream Effects Of Dams: Consequences Of Migratory Consumer Extirpation In Puerto
Rico,’’ Ecological Applications 16: 339–352 (2006); C.J. Hall, et al., ‘‘The Historic

Influence of Dams on Diadromous Fish Habitat with a Focus on River Herring and Hydrologic Longitudinal Connectivity,’’ Landscape Ecology 26: 95–107(2011)). Dams alter but typically do not sever the hydrologic connection between upstream and downstream waters. (See Part II, section 2.C. of this appendix). Upstream of large dams riparian areas are permanently inundated, increasing hydrological connectivity. Downstream, peak flows and the potential for overbank lateral flow are reduced; however, dams may also reduce flow variability downstream, resulting in higher minimum flows and reduced flow intermittency and thereby increasing hydrological (and potentially biological) connectivity. Id. (citing N.L. Poff, et al., ‘‘Homogenization of Regional River Dynamics by Dams and Global Biodiversity Implications,’’ Proceedings of the National Academy of Sciences of the United States of America 104: 5732–5737 (2007)). Where an impoundment does stop flow, it also has significant effects on downstream waters. For example, the downstream segments have a reduced quantity of waters, less sediment, and reduced species biological connectivity with upstream refugia.

Because dams reduce the amount of sediment delivered downstream, the reservoirs behind dams are actually very effective at retaining sediment, which can have significant effects in downstream waters. For instance, the Mississippi River’s natural sediment load has been reduced by an estimated 50% through dam construction in the Mississippi Basin. M.D. Blum, and H. H. Roberts, ‘‘Drowning of the Mississippi Delta Due to Insufficient Sediment Supply and Global Sea-Level Rise,’’ Nature

Geoscience 2(7): 488–491 (2009).

Man-made or man-altered tributaries continue to have chemical, physical, and


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biological connections that significantly affect the integrity of (a)(1) through (a)(3) waters. Though the man-made or man-altered nature of such tributaries can change the nature of the connections, it does noteliminate them. Thus, man-made and manaltered tributaries continue to serve the same important functions as ‘‘natural’’ tributaries, which in turn greatly impact downstream (a)(1) through (a)(3) waters, particularly when

their functional contributions to the chemical, physical, and biological conditions

of downstream waters are combined at a

watershed scale.

ii. Adjacent Waters

Adjacent waters, including adjacent wetlands, alone or in combination with other adjacent waters in the watershed, have a substantial impact on the chemical, physical, or biological integrity of traditional navigable waters, interstate waters, and the territorial seas. In addition, waters adjacent to tributaries serve many important functions that directly influence the integrity of downstream waters including traditional navigable waters, interstate waters, and the territorial seas. Adjacent waters store water, which can reduce flooding of downstream waters, and the loss of adjacent waters has been shown, in some circumstances, to increase downstream flooding. Adjacent waters maintain water quality and quantity, trap sediments, store and modify potential pollutants, and provide habitat for plants and animals, thereby sustaining the biological productivity of downstream rivers, lakes and estuaries, which may be traditional navigable waters, interstate waters, or the territorial seas. The scientific literature and Report supports these conclusions, as discussed in greater detail below.

1. Adjacent Waters Under This Proposed Rule Have a Significant Nexus to (a)(1) Through (a)(3) Waters

The discussion below summarizes the key points made in the Report and explains the technical basis for supporting a conclusion that adjacent waters, as defined in this proposed rule, have a significant nexus to waters identified in paragraphs (a)(1) through (a)(3) of the proposed rule. The geographic position of an ‘‘adjacent’’ water relative to the stream is indicative of the relationship they share, with many of its defining characteristics resulting from the movement of materials and energy between the two. A review and analysis of the scientific literature supports the conclusion that individually or in combination with similarly situated waters in a watershed, adjacent waters have a significant effect on the chemical, physical, and biological integrity of downstream traditionally navigable waters, interstate waters, and the territorial seas.

a. Riparian and Floodplain Waters Significantly Affect the Chemical, Physical, or Biological Integrity of (a)(1) Through (a)(3)

Waters

Waters, including wetlands, often lie within landscape settings that have bidirectional hydrological exchange with (a)(1) through (a)(5) waters (e.g., wetlands and open waters in riparian areas and flood plains). Such waters play an integral role in the chemical, physical, and biological integrity of the waters to which they are adjacent. Riparian areas and floodplains often describe the same geographic region. Report at 3–4. Therefore, the discussion of the functions of waters, including wetlands, in riparian areas will typically apply to floodplains unless otherwise noted. Where connections arise specifically from the act of inundation of adjacent land during times of higher-than-normal water, the term ‘‘floodplain’’ is solely used to describe the

area.

Riparian areas are transition zones between terrestrial and aquatic ecosystems that are distinguished by gradients in biophysical conditions, ecological processes, and biota. Id., Report at 31. Waters including wetlands in riparian areas significantly influence exchanges of energy and matter with aquatic ecosystems. See, e.g., id. (citing National Research Council, Riparian Areas: Functions and Strategies for Management (Washington, DC: The National Academies Press, 2002).

Floodplains are low gradient areas bordering stream or river channels, lakes, and impoundments that were formed by sediment deposition from those waters under present

climatic conditions. These natural geomorphic features are inundated during moderate to high water events. Id. (citing L.B. Leopold, A View of the River (Cambridge, MA: Harvard University Press, 1994); W.R. Osterkamp, Annotated Definitions of Selected Geomorphic Terms and Related Terms of Hydrology, Sedimentology, Soil Science and Ecology, USGS Open File Report 2008–1217 (Reston, VA: U.S. Department of the Interior, U.S. Geological Survey, 2008)). By ‘‘present climactic conditions,’’ the agencies mean that currently or recently active floodplains will be used to help

determine whether wetlands or waters are adjacent to ‘‘waters of the United States.’’ The proposed definition is limited to the present climactic conditions in order to best represent the floodplain that has an active and significant relationship with the stream or river channel. Historic floodplains that played a role in the river or lake dynamics in the past only will not be used to determine whether a water is adjacent. Floodplains

formed under different climactic conditions that no longer connect to the stream channel

that formed them are terraces. Id. It should be noted that ‘‘floodplain’’ as defined in today’s proposed rule does not necessarily equate to the 100-year floodplain as defined by the Federal Emergency Management Agency (FEMA). However, the FEMA defined floodplain may often coincide with the current definition proposed in this rule. Flood insurance rate maps are based on the probability of a flood event occurring (e.g., 100-year floods have a 1% probability of occurring in a given year or 500 year-floods have a 0.2% probability of occurring in a particular year). Flood insurance rate maps are not based on an ecological definition of the term ‘‘floodplain,’’ and therefore may not be appropriate for identifying adjacent wetlands and waters for the purposes of CWA jurisdiction. Flood insurance rate maps are developed by applying models and other information to identify areas that would be inundated by a flood event of a particular probability of recurring. Riparian waters take many different forms. Some may be wetlands, which are defined in paragraph (c)(6) of the proposed rule. Others may be ponds, oxbow lakes, or other types of open waters. Oxbow lakes, commonly found in floodplains, are formed when river

meanders are cutoff from the rest of the river.

Id. at 5–42.

b. Riparian and Floodplain Waters Significantly Affect the Physical Integrity of (a)(1) Through (a)(3) Waters

Scientific research shows waters and wetlands in riparian areas and floodplains to be important in protecting the physical integrity of aquatic resources. Because riparian and floodplain waters exhibit bidirectional exchange of water with the waters to which they are adjacent, they play an important role in determining the volume and duration of stream flow. Riparian and floodplain waters also have an essential role in regulating and stabilizing sediment transport to downstream waters. These

characteristics are fundamental to the physical integrity of streams as well as downstream traditional navigable waters, interstate waters, and the territorial seas.

Riparian and floodplain wetlands are important for the reduction or delay of

floods. Id.at 3–22 (citing A. Bullock and M. Acreman, ‘‘The Role of Wetlands in the Hydrological Cycle,’’ Hydrology and Earth System Sciences 7:358–389 (2003)). Waters in riparian areas control flooding during times of high precipitation or snowmelt by capturing water from overbank flow and storing excess stream water. Id. at 5–6. One study found that peak flows in the Cache River in Arkansas decreased by 10–20% mainly because of floodplain water storage.

Id. (citing R. Walton, et al., ‘‘Hydrology of the Black Swamp Wetlands on the Cache River, Arkansas,’’ Wetlands 16:279–287 (1996). Research has shown that floodplain wetlands
in Ohio store about 40% of the flow of small

streams. Id. at 5–6 to 5–7 (citing D.E. Gamble, et al., An Ecological and Functional Assessment of Urban Wetlands in Central Ohio. Columbus, Ohio, EPA Technical Report WET/2007–3B, (Columbus, OH: Ohio Environmental Protection Agency, Wetland Ecology Group, Division of Surface Water, 2007)). These and similar findings point to the close hydrological influence that waters in riparian and floodplain areas have on

streams.

Some adjacent waters are bordering or contiguous with (a)(1) through (a)(5) waters. Because of their close physical proximity to nearby water bodies, they readily exchange their waters through the saturated soils surrounding the stream or through surface exchange. This commingling of waters allows bordering or contiguous waters to both provide chemically transformed waters to

streams and to absorb excess stream flow.

Flow between neighboring waters and streams is more longitudinal (downslope) at

headwaters and more lateral further

downstream. Id. at 5–38, Table 5–3. These connections in part determine stream flow volume and duration. Waters, including wetlands, in riparian areas connect to neighboring water bodies through various surface and subsurface connections. See, e.g., id. at 3–4 (citing National Research Council,


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Riparian Areas: Functions and Strategies for Management (Washington, DC: National Academy Press, 2002)). Floodplains, similarly, are closely associated with the groundwater found beneath and beside river channels (which are considered shallow aquifers) and waters in floodplains readily exchange water with such aquifers. Id. at 3– 14 (citing J.A. Stanford and J. V. Ward, ‘‘An Ecosystem Perspective of Alluvial Rivers: Connectivity and the Hyporheic Corridor,’’ Journal of the North American Benthological Society 12:48–60 (1993); C. Amoros and G. Bornette, ‘‘Connectivity and Biocompexity in Waterbodies of Riverine Floodplains,’’ Freshwater Biology47:761–776 (2002); G.C. Poole, et al., ‘‘Multiscale Geomorphic Drivers

of Groundwater Flow Paths: Subsurface Hydrologic Dynamics and Hyporheic Diversity,’’Journal of the North American Benthological Society 25:288–303 (2006)). Riparian and floodplain wetlands are frequently contiguous with streams and other water bodies and significantly influence the hydrology of such water bodies. Id. at 5–6 (citing R.J. Naiman, et al., Riparia: Ecology, Conservation, and Management of

Streamside Communities (Burlington, MA: Elsevier Academic Press, 2005); P. Vidon, et al., ‘‘Hot Spots and Hot Moments in Riparian Zones: Potential for Improved Water Quality Management,’’Journal of the American

Water Resources Association 46:278–298 (2010)). Floodplain wetlands are important for the reduction or delay of floods. Id. (citing A. Bullock and M. Acreman, ‘‘The Role of Wetlands in the Hydrological Cycle,’’ Hydrology and Earth System Sciences 7:358– 389 (2003)). Oxbow lakes also retain flood

waters. Id. at 5–44. Adjacent ponds generally function similarly to oxbow lakes.

Waters in riparian areas filter sediment washed down from uplands and collect

sediment from overbank flow as the river or

stream floods. Id. at 5–7. For example, riparian areas were observed to collect 80–

90% of the sediment from farmlands in a study in North Carolina. Id. (citing A. Cooper, et al., ‘‘Riparian Areas as Filters for Agricultural Sediment,’’ Soil Science Society of America Proceedings 51:416–420 (1987); R.B. Daniels and J.G. Gilliam, ‘‘Sediment and Chemical Load Reduction by Grass and Riparian Filters,’’ Soil Science Society of America Journal 60:246–251 (1996); R.J. Naiman and H. Decamps, ‘‘The Ecology of Interfaces: Riparian Zones,’’ Annual Review of Ecology and Systematics 28:621–658 (1997)). Maintaining the equilibrium between sediment deposition and sediment transport is important to maintain the physical shape and structure of stream channels. Significant changes to upstream channels can affect the chemical, physical, and biological condition of downstream (a)(1) through (a)(3) waters.

The physical effects of excess sediment can impair chemical and ecological integrity in a variety of ways. Id. at 5–9 (citing P.J. Wood and P.D. Armitage, ‘‘Biological Effects of Fine Sediment in the Lotic Environment,’’ Environmental Management 21:203–217 (1997)). Excess sediment is linked to increasing contaminant and nutrient concentrations, all of which tributaries can transmit downstream, affecting water quality. Excess sediment may block and absorb sunlight transmission through the water column, inhibiting plant photosynthesis and warming the water in the stream. Sediment may fill the interstitial spaces between rocks in a streambed, which many fish and aquatic species use for mating, reproduction, and shelter from predators. This kind of physical degradation of tributary streambeds results in

less suitable habitat available for animals and fish that move between upstream and downstream waters. Riparian waters that retain sediments thus protect downstream

waters from the effects of excess sediment.

Oxbow lakes play similar roles in the floodplain as they are an integral part of alluvial floodplains of meandering rivers. Id. at 5–42 (citing K.O. Winemiller, et al., ‘‘Fish Assemblage Structure in Relation to Environmental Variation among Brazos River Oxbow Lakes,’’ Transactions of the American Fisheries Society 129:451–468 (2000), K. Glinska-Lewczuk, ‘‘Water Quality Dynamics of Oxbow Lakes in Young Glacial Landscape

of NE Poland in Relation to Their Hydrological Connectivity,’’ Ecological Engineering 35:25–37 (2009)). They connect to rivers by periodic overland flow, typically from the river during flooding events, and

bidirectional shallow subsurface flow through fine river soils (bidirectional means flow from river to lake and lake to river). Id. at 5–43 to 5–44. Oxbow lakes generally have an important influence on the condition and

function of rivers. Id. at 5–48 to 5–49. That influence can vary with the distance from the river and the age of the oxbow, reflecting the frequency and nature of the exchange of materials that takes place between the two

water bodies.

Because adjacent waters support riparian vegetation, they affect the capacity of riparian vegetation to influence stream flow, morphology, and habitat provided in the nearby water body. Vegetation in riparian

waters influences the amount of water in the stream by capturing and transpiring stream flow and intercepting groundwater and

overland flow. Id. at 3–22, 5–7 (citing P. Meyboom, ‘‘Three Observations on Streamflow Depletion by Phreatophytes,’’ Journal of Hydrology 2:248–261 (1964)). Riparian vegetation in adjacent waters also reduces stream bank erosion, serving to maintain the physical integrity of the channel. See, e.g., id. at 5–8 (citing C.E. Beeson and P. F. Doyle, ‘‘Comparison of Bank Erosion at Vegetated and Non-Vegetated Channel Bends,’’Journal of the American

Water Resources Association 31:983–990 (1995)). In addition, inputs of woody debris from aquatic vegetation into waters make important contributions to the channel’s geomorphology and the stream’s aquatic

habitat value. Id. (citing N.H. Anderson and J. R. Sedell, ‘‘Detritus Processing by Macroinvertebrates in Stream Ecosystems,’’ Annual Review of Entomology 24:351–377 (1979); M.E. Harmon, et al., ‘‘Ecology of Coarse Woody Debris in Temperature Ecosystems,’’ Advances in Ecological

Research 15:133–302 (1986); F. Nakamura and F. J. Swanson, ‘‘Effects of Coarse Woody Debris on Morphology and Sediment Storage of a Mountain Stream System in Western Oregon,’’ Earth Surface Processes and Landforms 18:43–61 (1993); T.E. Abbe and D. R. Montgomery, ‘‘Large Woody Debris Jams, Channel Hydraulics and Habitat Formation in Large Rivers,’’ Regulated Rivers: Research & Management 12:201–221 (1996); R.J. Naiman and H. Decamps, ‘‘The Ecology of Interfaces: Riparian Zones,’’ Annual Review of Ecology and Systematics 28:621–658 91997); A.M. Gurnell, et al., ‘‘Large Wood and Fluvial Processes,’’ Freshwater Biology 47:601–619 (2002)). Also, the riparian vegetation that overhangs streams provides shade, providing a critically important function of reducing fluctuations in water temperature helping to reduce excessive algal production and to maintain life-supporting oxygen levels in streams and other waters. Id. at 5–9 (citing S.V. Gregory, et al., ‘‘An Ecosystem Perspective of Riparian Zones: Focus on Links between Land and Water,’’

Bioscience 41:540–551 (1991); E.C. Volkmar and R.A. Dahlgren, ‘‘Biological Oxygen Demand Dynamics in the Lower San Joaquin River, California,’’ Environmental Science & Technology40:5653–5660 (2006)). Even small changes in water temperature can have significant impacts on the type and number of species present in waters, with higher temperatures generally associated with degraded habitat which supports only those species that can tolerate higher temperatures and reduced levels of dissolved oxygen. Higher water temperatures are associated

with streams and rivers with less valuable

recreational and commercial fisheries. As discussed below, these physical

characteristics of headwater streams influence what types of organisms live in the region.

Headwaters and nearby wetlands supply downstream waters with dissolved organic carbon as a result of decomposition processes from dead organic matter such as plants. The biological consequences of this dissolved organic carbon are discussed in more detail below. The presence of dissolved organic carbon can affect how light penetrates the water, an important factor in the growth of plants, algae, and other primary producers, and can protect aquatic organisms from the

harmful effects of UV–B radiation. Id. at 5– 28 to 5–29 (citing K.N. Eshelman and H.F. Hemond, ‘‘The role of organic acids in the

acid-base status of surface waters at Bickford Watershed, Massachusetts,’’ Water Resources

Research 21:1503–1510 (1985); J.E. Hobbie and R.G. Wetzel, ‘‘Microbial control of dissolved organic carbon in lakes: Research for the future,’’ Hydrobiologia 229:169–180 (1992); D.W. Schindler and P.J. Curtis, ‘‘The role of DOC in protecting freshwaters subjected to climate warming and acidification from UV exposure,’’ Biogeochemistry 36:1–8 (1997); K.R. Reddy and R.D. DeLaune, Biogeochemistry of Wetlands: Science and Applications, (Boca Raton, FL: CRC Press, 2008)).

c. Riparian and Floodplain Waters Significantly Affect the Chemical Integrity of (a)(1) Through (a)(3) Waters

As stated above in the section on tributaries, pollutants such as petroleum waste products and other harmful pollutants dumped into any part of the tributary system are likely to flow downstream, or to be washed downstream, and thereby pollute traditional navigable waters, interstate


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waters, and the territorial seas from which American citizens take their drinking water, shellfish, fin fish, water-based recreation, and many other uses. Some wetlands perform the valuable function of trapping or filtering out some pollutants (such as fertilizers, silt, and some pesticides), thereby reducing the likelihood that those pollutants will reach and pollute the tributaries of the downstream navigable or interstate waters (and eventually pollute those downstream waters themselves). However, many other pollutants (such as petroleum wastes and toxic chemical wastes), if dumped into wetlands or other waters that are adjacent to tributary streams, may reach those tributaries themselves, and thereafter flow downstream to pollute the nation’s drinking water supply, fisheries, and recreation areas.

Riparian and floodplain waters play a critical role in controlling the chemicals that

enter streams and other ‘‘waters of the United States’’ and as a result are vital in protecting the chemical, physical, and biological integrity of downstream (a)(1) through (a)(3) waters. Runoff (the water that has not evaporated or infiltrated into the groundwater) from uplands is a large source of pollution, but research has shown that wetlands and other riparian waters trap and chemically transform a substantial amount of the nutrients, pesticides, and other pollutants before they enter streams, river, lakes and

other waters.

Chemicals and other pollutants enter waters from point sources, non-point sources, atmospheric deposition, upstream reaches, and through the hyporheic zone, a region beneath and alongside a stream bed where surface water and shallow groundwater mix.

Id. at 5–10 (citing SW. Nixon and V.J. Lee, Wetlands and Water Quality: A Regional Review of Recent Research in the United States on the Role of Freshwater and Saltwater Wetlands as Sources, Sinks, and Transformers of Nitrogen, Phosphorus, and Various Heavy Metals, Technical Report Y– 86–2, (Vicksburg, MS: U.S. Army Corp of Engineers, Waterways Experiment Station, 1986); D.F. Whigham and T.E. Jordan, ‘‘Isolated Wetlands and Water Quality,’’

Wetlands 23:541–549 (2003); S.L.Whitmire and S.K. Hamilton, ‘‘Rates of Anaerobic

Microbial Metabolism in Wetlands of Divergent Hydrology on a Glacial Landscape,’’ Wetlands 28:703–714 (2008)). Throughout the stream network, but especially in headwater streams and their adjacent wetlands, chemicals are sequestered, assimilated, transformed, or lost to the atmosphere by microbes, fungi, algae, and macrophytes present in riparian waters

and soils. Id. (citing SW. Nixon and V.J. Lee, Wetlands and Water Quality: A Regional Review of Recent Research in the United States on the Role of Freshwater and Saltwater Wetlands as Sources, Sinks, and Transformers of Nitrogen, Phosphorus, and Various Heavy Metals, Technical Report Y– 86–2, (Vicksburg, MS: U.S. Army Corp of Engineers, Waterways Experiment Station, 1986); C. Johnston, ‘‘Sediment and Nutrient Retention by Freshwater Wetlands: Effects on Surface Water Quality,’’ Critical Reviews in

Environmental Control 21:491–565 (1991); P.I. Boon, ‘‘Biogeochemistry and Bacterial Ecology of Hydrologically Dynamic Wetlands,’’ in D.P. Batzer and R.R. Sharitz, ed., Ecology of Freshwater and Estuarine

Wetlands (Berkeley, CA: University of California Press, 2006), pp. 115–176; W.J. Mitsch and J.G. Gosselink, Wetlands, 4th edition, (Hoboken, NJ: John Wiley & Sons Inc., 2007); K.R., Reddy and R.D. DeLaune, Biogeochemistry of Wetlands: Science and Applications (Boca Raton, FL: CRC Press, 2008). These chemical processes reduce or eliminate pollution that would otherwise enter streams, rivers, lakes and other waters and subsequently downstream traditional navigable waters, interstate waters, or the

territorial seas. The removal of the nutrients nitrogen and phosphorus is a particularly important role for riparian waters. Nutrients are necessary to support aquatic life, but the presence of excess nutrients can lead to eutrophication and the depletion of oxygen nearby waters and in waters far downstream.

See, e.g., id. at 1–8. Eutrophication is a large problem in waters across the United States including such significant ecosystems as the Chesapeake Bay and Lake Spokane in Washington. W.M. Kemp, et al., ‘‘Eutrophication of Chesapeake Bay: Historical Trends and Ecological

Interactions,’’ Marine Ecology Progress Series 303(21):1–29 (2005); D.J. Moore and J. Ross, Spokane River and Lake Spokane Dissolved Oxygen Total Maximum Daily Load: Water Quality Improvement Report, Publication No. 07–10–073 (Spokane, WA: Washington State Department of Ecology, 2010); R.R. Murphy, et al., ‘‘Long-Term Trends in Chesapeake Bay Seasonal Hypoxia, Stratification, and Nutrient Loading,’’ Estuaries and Coasts 34(6):1293–1309 (2011). Eutrophication is the process by which plants and algae grow in

waters to such an extent that the abundance of vegetation monopolizes the available oxygen, detrimentally affecting other aquatic organisms. Id. Oxbow lakes also have high mineralization rates, suggesting that similar to adjacent wetlands they process and trap nutrients from runoff. Report at 5–45 to 5– 46 (citing K.O. Winemiller, et al., ‘‘Fish Assemblage Structure in Relation to Environmental Variation among Brazos River Oxbow Lakes,’’ Transactions of the American Fisheries Society 129:451–468 (2000)). Protection of these waters therefore helps maintain the chemical integrity of the

nation’s waters.

The removal of nitrogen is an important function of all waters, including wetlands, in the riparian areas. Riparian areas regularly remove more than half of dissolved nitrogen found in surface and subsurface water by plant uptake and microbial transformation.

Id. at 5–11 (citing P. Vidon, et al., ‘‘Hot Spots and Hot Moments in Riparian Zones: Potential for Improved Water Quality Management,’’Journal of the American

Water Resources Association 46:278–298 (2010)). Denitrification in surface and subsurface flows is highest where there is high organic matter and/or anoxic

conditions. Id. Denitrification occurs in wetland soils where there is high organic matter, low oxygen, denitrifying microbes, and saturated soil conditions, and rates increase with proximity to streams. Id. (citing S.V. Gregory, et al., ‘‘An Ecosystem Perspective of Riparian Zones: Focus on
Links between Land and Water,’’ Bioscience 41:540–551 (1991); P. Vidon, et al., ‘‘Hot Spots and Hot Moments in Riparian Zones: Potential for Improved Water Quality Management,’’Journal of the American

Water Resources Association 46:278–298 (2010)). Riparian waters are therefore important in maintaining the conditions important for denitrification, which in turn protects streams, rivers, lakes and other waters from nitrogen pollution.

Plant uptake of dissolved nitrogen in subsurface flows also accounts for large quantities of nitrogen removal. Riparian

forests have been found to remove 75% of dissolved nitrate transported from agricultural fields in Maryland. Id. (citing P.
Vidon, et al., ‘‘Hot Spots and Hot Moments in Riparian Zones: Potential for Improved Water Quality Management,’’ Journal of the

American Water Resources Association 46:278–298 (2010)). Likewise, riparian forests in Georgia remove 65% of nitrogen and 30% of phosphorus from agricultural sources. Id. at 5–11 to 5–12 (citing Vidon, et al. 2010). A Pennsylvania forest removed 26% of the

nitrate from the subsurface. Id. at 5–12 (citing J.D. Newbold, et al., ‘‘Water Quality Functions of a 15-Year-Old Riparian Forest Buffer System,’’Journal of the American

Water Resources Association 46:299–310 (2010)). The vegetation associated with riparian waters also removes nitrogen from
subsurface flows. Therefore, the conservation of riparian waters helps protect downstream waters from influxes of dissolved nitrogen.

Phosphorus is another potentially harmful nutrient that is captured and processed in riparian waters. Id. (citing T.A. Dillaha and
S.P. Inamdar, ‘‘Buffer Zones as Sediment Traps or Sources,’’ in N.E. Haycock, T.P. Burt, K.W.T. Goulding, and G. Pinay, ed., Buffer Zones: Their Processess and Potential

in Water Protection, Proceedings of the
International Conference on Buffer Zones, September 1996 (Hertfordshire, UK: Quest Environmental, 1997), pp. 33–42; A.N. Sharpley and S. Rekolainen, ‘‘Phosphorus in Agriculture and Its Environmental Implications,’’ in H. Tunney, et al., ed., Phosphorus Losses from Soil to Water (Cambridge, UK: CAB International, 1997), pp. 1–54; G.C. Carlyle and A.R. Hill, ‘‘Groundwater Phosphate Dynamics in a River Riparian Zone: Effects of Hydrologic Flowpaths, Lithology, and Redox Chemistry,’’Journal of Hydrology 247:151– 168 (2001)). Biogeochemical processes, sedimentation, and plant uptake account for high rates of removal of particulate phosphorus in riparian areas. Id. (citing C.C.
Hoffmann, et al., ‘‘Phosphorus Retention in Riparian Buffers: Review of Their Efficiency,’’Journal of Environmental Quality 38:1942–1955 (2009)). The amount of contact the water has with nearby soils determines the ability of the riparian area to remove phosphorus. Id. This function of upstream riparian waters is crucial for maintaining the chemical and biological integrity of the waters to which they are adjacent, and for preventing eutrophication in downstream traditional navigable waters, interstate waters, and the territorial seas.


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d. Riparian and Floodplain Waters Significantly Affect the Biological Integrity of (a)(1) Through (a)(3) Waters

Waters and wetlands located in both riparian areas and floodplains support the biological integrity of downstream (a)(1) through (a)(3) waters in a variety of ways.They provide habitat for aquatic and watertolerant plants, invertebrates, and vertebrates, and provide feeding, refuge, and breeding areas for invertebrates and fish. Seeds, plants,

and animals move between waters in the riparian zone and floodplains and the adjacent streams, and from there colonize or utilize downstream waters, including traditional navigable waters.

Organic matter from adjacent wetlands is critical to aquatic food webs, particularly in headwaters, where it is the primary source of energy flow due to low light conditions that inhibit photosynthesis. Id. at 5–13 (citing J.L. Tank, et al., ‘‘A Review of Allochthonous Organic Matter Dynamics and Metabolism in
Streams,’’Journal of the North American Benthological Society 29:118–146 (2010)).

Headwater streams tend to be located in heavily vegetated areas compared to larger waters, so they are more likely to contain leaf litter, dead and decaying plants, and other organic matter that forms the basis of headwater food webs. The organic matter is processed by microbes and insects that make the energy available to higher levels of stream life such as amphibians and fish. Studies have shown that macroinvertebrates rely on leaf inputs in headwater streams and that excluding organic litter from a stream resulted in significant changes to the food web at multiple levels. Id. (citing G.W. Minshall, ‘‘Role of Allochthonous Detritus in the Tropic Structure of a Woodland Springbrook Community,’’ Ecology48:139– 149 (1967); J.B. Wallace, et al., ‘‘Multiple Trophic Levels of a Forest Stream Linked to Terrestrial Litter Inputs,’’ Science 277:102– 104 (1997); J.L. Meyer, et al., ‘‘Leaf Litter as a Source of Dissolved Organic Carbon in
Streams,’’ Ecosystems 1:240–249 (1998)). Fish and amphibian species found in

headwaters travel downstream and in turn become part of the food web for larger aquatic organisms in rivers and other waters. Organic material provided by riparian waters to small, headwater streams is therefore important not only to the small streams that directly utilize this source of energy to support their biological populations but also to the overall biological integrity of

downstream waters that also benefit from the movement of fish and other species that contribute to the food web of larger streams

and rivers.

Floodplain water bodies, including oxbow lakes, accumulate organic carbon, an important function influenced by the size and frequency of floods from adjacent rivers. See, e.g., id. at 5–45 (citing A. Cabezas, et al., ‘‘Changing Patterns of Organic Carbon and Nitrogen Accretion on the Middle Ebro Floodplain (NE Spain),’’ Ecological Engineering 35:1547–1558 (2009)). These stored chemicals are available for exchange with river water when hydrological connections form. Organic materials are the

basis for the food web in stream reaches where photosynthetic production of energy is absent or limited, particularly in headwater systems where vegetative litter alone makes up the base of the aquatic food web. The maintenance of floodplain waters is therefore an important component of protecting the biological integrity of downstream waters

into which the headwaters flow.

The waters, including wetlands, in the riparian area play an important role in the removal of pesticides. Id. at 5–14 (citing P. Vidon, et al., ‘‘Hot Spots and Hot Moments in Riparian Zones: Potential for Improved Water Quality Management,’’ Journal of the

American Water Resources Association 46:278–298 (2010). Microbes near plant roots break down these pesticides. See, e.g., id. (citing G. Voos, and P.M. Groffman, ‘‘Relationships between microbial biomass and dissipation of 2,4–D and dicamba in soil,’’ Biology and Fertility of Soils 24:106– 110 (1996)). Uptake by aquatic plants has also been shown to be an important mechanism of removal of the pesticides

alachlor and atrazine. Id. (citing K.G. Paterson and J.L. Schnoor, ‘‘Fate of Alachlor and Atrazine in a Riparian Zone Field Site,’’

Water Environment Research 64:274–283 (1992)). Riparian waters also trap and hold pesticide contaminated runoff preventing it from harming neighboring waters.

Riparian areas are dynamic places that support a diversity of aquatic, amphibious, and terrestrial species adapted to the unique habitat created by periodic flooding events.

Id. at 5–15 (citing W.J. Junk, et al., ‘‘The flood pulse concept in river-floodplain systems,’’

in D.P. Dodge, ed., Proceedings of the International Large River Symposium Ottawa (Ottawa, Canada: Canadian Special Publication of Fisheries and Aquatic Sciences 106, 1989), pp. 110–127; K. Tockner, et al., ‘‘An Extension of the Flood Pulse Concept,’’ Hydrological Processes 14:2861–2883 (2000); C.T. Robinson, et al., ‘‘The Fauna of Dynamic Riverine Landscapes,’’ Freshwater Biology47:661–677 (2002)). Plants, invertebrates, and vertebrates use waters, including wetlands, in the riparian areas for habitat, nutrients, and breeding. As a result, the waters, including wetlands, in the riparian areas act as sources of organisms, particularly during inundation events, replenishing neighboring waters with organisms, seeds, and organic matter. Inundation and hydrological connectivity of riparian areas greatly increase the area of aquatic habitats and species diversity. Id. at 5–15 to 5–16 (citing W.J. Junk et al. 1989; R. Jansson, et al., ‘‘Hydrochory Increases Riparian Plant Species Richness: A Comparison between a Free-Flowing and a Regulated River,’’ Journal of Ecology 93:1094–1103 (2005)). Aquatic animals, including amphibians and fish, take advantage of the waters present in riparian areas, either inhabiting them or moving between the riparian water and neighboring

waters. Id. at 5–15, 5–17, 5–19 (citing G.H. Copp, ‘‘The habitat diversity and fish reproductive function of floodplain ecosystems,’’ Environmental Biology of

Fishes 26:1–27 (1989); L.A. Smock, et al., ‘‘Lotic macroinvertebrate production in three dimensions: Channel surface, hyporheic, and floodplain environments,’’ Ecology 73:876– 886 (1992); L.A. Smock, ‘‘Movements of invertebrates between stream channels and forested floodplains,’’Journal of the North American Benthological Society 13:524–531 (1994); C. T. Robinson, et al., ‘‘The fauna of dynamic riverine landscapes,’’ Freshwater Biology47:661–677 (2002); J.S. Richardson, et al., ‘‘Riparian communities associated with

Pacific Northwest headwater streams: Assemblages, processes, and uniqueness,’’ Journal of the American Water Resources

Association 41:935–947 (2005); C. Ilg, et al., ‘‘Long-term reactions of plants and

macroinvertebrates to extreme floods in floodplain grasslands,’’ Ecology 89:2392– 2398 (2008); D.E. Shoup, and D. H. Wahl, ‘‘Fish diversity and abundance in relation to interannual and lakespecific variation in abiotic characteristics of floodplain lakes of the lower Kaskaskia River, Illinois,’’ Transactions of the American Fisheries Society 138:1076–1092 (2009)). Likewise, seeds, plant fragments, and whole plants move between riparian and floodplain waters

and the river network. Id. at 5–15 (citing R.L. Schneider, and R.R. Sharitz, ‘‘Hydrochory and regeneration in a bald cypress water tupelo swamp forest,’’ Ecology 69:1055–1063 (1988); B. Middleton, ‘‘Hydrochory, seed banks, and regeneration dynamics along the landscape boundaries of a forested wetland,’’ Plant Ecology 146:169–184 (2000); C. Nilsson, et al., ‘‘The role of hydrochory in structuring riparian and wetland vegetation,’’ Biological Reviews 85:837–858 (2010)).

Hydrological connections are often drivers of biological connections, and flooding events enhance the existing connections between floodplain waters and the river network. As a result, waters within floodplains have important functions for aquatic health. Many species have cycles timed to flooding events, particularly in circumstances where flooding is associated with annual spring snowmelt or high precipitation. Id. at 5–15 to 5–17, 5–20 (citing J.R. Thomas, et al., ‘‘A landscape perspective

of the stream corridor invasion and habitat characteristics of an exotic (Dioscorea oppositifolia) in a pristine watershed in Illinois,’’ Biological Invasions 8:1103–1113 (2006); L.M. Tronstad, et al., ‘‘Aerial colonization and growth: Rapid invertebrate responses to temporary aquatic habitats in a river floodplain,’’ Journal of the North American Benthological Society 26:460–471 (2007); A. Gurnell, et al., ‘‘Propagule deposition along river margins: Linking hydrology and ecology,’’Journal of Ecology 96:553–565 (2008)). Waters within floodplains act as sinks of seeds, plant fragments, and invertebrate eggs, allowing for cross-breeding and resulting gene flow across

time. Id. at 5–19 to 5–21 (citing K.M. Jenkins, and A.J. Boulton, ‘‘Connectivity in a dryland river: Short-term aquatic microinvertebrate recruitment following floodplain inundation,’’ Ecology 84:2708–2723 (2003);D. Frisch, and S.T. Threlkeld, ‘‘Floodmediated dispersal versus hatching: Early recolonisation strategies of copepods in floodplain ponds,’’ Freshwater Biology 50:323–330 (2005); B. Vanschoenwinkel, et al., ‘‘Wind mediated dispersal of freshwater invertebrates in a rock pool metacommunity: Differences in dispersal capacities and modes,’’ Hydrobiologia 635:363–372 (2009)).


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Micro- and macroinvertebrates colonize nutrient rich waters within floodplains during periods of inundation, facilitating an increase in population and sustaining them though times of limited resources and population decline. Id. at 5–19 (citing W.J. Junk, et al., ‘‘The flood pulse concept in river-floodplain systems,’’ in D.P. Dodge, ed., Proceedings of the International Large River Symposium Ottawa (Ottawa, Canada: Canadian Special Publication of Fisheries and Aquatic Sciences 106, 1989), pp. 110– 127; B. Malmqvist, ‘‘Aquatic invertebrates in riverine landscapes,’’ Freshwater Biology 47:679–694 (2002); C. Ilg, et al., ‘‘Long-term reactions of plants and macroinvertebrates to extreme floods in floodplain grasslands,’’ Ecology 89:2392–2398 (2008)). Such animals are adapted to high floods, desiccation (drying out), or other stresses that come with these regular, systemic fluctuations. Id. at 5– 20 (citing Jenkins and Boulton 2003). Floodplain waters therefore maintain various biological populations, which periodically replenish adjacent jurisdictional waters, serving to maintain their biological integrity.

Plants and animals use waters, including wetlands, in the riparian areas and floodplains for habitat, food, and breeding. Oxbow lakes in the floodplain provide critical fish habitat needed for feeding and rearing, leading researchers to conclude that the entire floodplain should be considered a single functional unit, essential to the river’s biological integrity. Id. at 5–17 (citing D.E. Shoup and D.H. Wahl, ‘‘Fish Diversity and

Abundance in Relation to Interannual and Lake-Specific Variation in Abiotic Characteristics of Floodplain Lakes of the Lower Kaskaskia River, Illinois,’’ Transactions of the American Fisheries Society 138:1076–1092 (2009)). Since adjacent ponds are structurally and biologically similar to oxbow lakes they serve similar functions relative to the nearby river or stream. Waters, including wetlands, in the riparian areas also provide food sources for stream invertebrates, which colonize during

inundation events. Id. at 5–19 (citing W.J. Junk, et al., ‘‘The Flood Pulse Concept in River-Floodplain Systems,’’ in D.P. Dodge, ed., Proceedings of the International Large River Symposium Ottawa (Ottawa, Canada: Canadian Special Publication of Fisheries and Aquatic Sciences 106, 1989), pp. 110– 127; C. Ilg, et al., ‘‘Long-term Reactions of

Plants and Macroinvertebrates to Extreme Floods in Floodplain Grasslands,’’ Ecology 89:2392–2398 (2008)). Riparian waters also form an integral part of the food web, linking primary producers and plants to higher

animals. Id. (citing B. Malmqvist, ‘‘Aquatic Invertebrates in Riverine Landscapes,’’ Freshwater Biology47:679–694 (2002); G.U.Y. Woodward and A.G. Hildrew, ‘‘Food Web Structure in Riverine Landscapes,’’ Freshwater Biology47:777–798 (2002), T.K. Stead, et al., ‘‘Secondary Production of a Stream Metazoan Community: Does the Meiofauna Make a Difference?,’’ Limnology and Oceanography 50:398–403 (2005), D.J. Woodford and A.R. McIntosh, ‘‘Evidence of Source-Sink Metapopulations in a Vulnerable Native Galaxiid Fish Driven by Introduced

Trout,’’ Ecological Applications 20:967–977 (2010)). Likewise, floodplains are important foraging, hunting, and breeding sites for fish and amphibians. Id. at 5–15 (citing G.H. Copp, ‘‘The Habitat Diversity and Fish Reproductive Function of Floodplain Ecosystems,’’ Environmental Biology of

Fishes 26:1–27 (1989); J.S. Richardson, et al., ‘‘Riparian Communities Associated with

Pacific Northwest Headwater Streams: Assemblages, Processes, and Uniqueness,’’ Journal of the American Water Resources

Association 41:935–947 (2005)).

Plants and animals move back and forth between riparian or floodplain waters and

the river network. This movement is assisted in some cases when flooding events create hydrological connections. For instance, these floodplain and riparian wetlands provide refuge, feeding, and rearing habitat for many fish species. Id. at 5–17 (citing C.H. Wharton, et al., The Ecology of Bottomland Hardwood Swamps of the Southeast: A Community Profile, FWS/OBS–81/37 (Washington, DC: U.S. Department of the Interior, Fish and Wildlife Service, Biological Services Program, 1982); M.P. Matheney and C.F. Rabeni, ‘‘Patterns of Movement and Habitat Use by Northern Hogsuckers in an Ozark

Stream,’’ Transactions of the American Fisheries Society 124:886–897 (1995); A.A.

Pease, et al., ‘‘Habitat and Resource Use by Larval and Juvenile Fishes in an Arid-Land River (Rio Grande, New Mexico),’’ Freshwater Biology 51:475–486 (2006); J.A. Henning, et al., ‘‘Use of Seasonal Freshwater Wetlands by Fishes in a Temperate River Floodplain,’’Journal of Fish Biology 71:476– 492 (2007); C.A. Jeffres, et al., ‘‘Ephemeral Floodplain Habitats Provide Best Growth Conditions for Juvenile Chinook Salmon in a California River,’’ Environmental Biology of

Fishes 83:449–458 (2008)). Seeds ingested by animals such as carp are dispersed in stream channels and associated waters. See, e.g., id. at 5–16 (citing B.J.A. Pollux, et al., ‘‘Consequences of Intraspecific Seed-Size

Variation in Sparganium emersum for Dispersal by Fish,’’ Functional Ecology 21:1084–1091 (2007)). Also, phytoplankton move between floodplain wetlands and the

river network. Id. at 5–17 (citing D.G. Angeler, et al., ‘‘Phytoplankton community similarity in a semiarid floodplain under contrasting hydrological connectivity regimes,’’ Ecological Research 25:513–520 (2010)). In turn, the primary productivity conditions in the floodplain results in large populations of phytoplankton that enrich river networks when hydrological

connections form. Id. (citing P.W. Lehman, et al., ‘‘The Influence of Floodplain Habitat on the Quantity and Quality of Riverine Phytoplankton Carbon Produced During the Flood Season in San Francisco Estuary,’’ Aquatic Ecology42:363–378 (2008)). This influx of carbon into the river system nourishes the downstream waters, for example, supporting fisheries.

However, even when hydrological connections are absent, some organisms can move between riparian waters and their neighboring tributaries by overland movement in order to complete their life cycle. River-dwelling mammals, such as river otters, move from the river to riparian

wetlands. Id. at 5–18 (citing D.G. Newman and C.R. Griffin, ‘‘Wetland Use by River Otters in Massachusetts,’’ Journal of Wildlife Management 58:18–23 (1994)). Several species of amphibians and reptiles including frogs, snakes and turtles use both streams and neighboring waters. Id. at 1–10, 5–4 to 5–5 (Table 5–1), 5–15 (citing J.S. Richardson, et al., ‘‘Riparian Communities Associated with

Pacific Northwest Headwater Streams: Assemblages, Processes, and Uniqueness,’’ Journal of the American Water Resources

Association 41:935–947 (2005)). Movement

between wetlands and the river network also occurs by the dispersal of seed and plant fragments and the wind dispersal of

invertebrates. Id. at 5–15, 5–20 (citing R.L. Schneider and R.R. Sharitz, ‘‘Hydrochory and Regeneration in a Bald Cypress Water Tupelo Swamp Forest,’’ Ecology 69:1055–1063 (1988); B. Middleton, ‘‘Hydrochory, Seed Banks, and Regeneration Dynamics Along the Landscape Boundaries of a Forested Wetland,’’ Plant Ecology 146:169–184 (2000); A.M. Gurnell, ‘‘Analogies Between Mineral Sediment and Vegetative Particle Dynamics in Fluvial Systems,’’ Geomorphology 89:9–22 (2007); A. Gurnell, et al., ‘‘Propagule Deposition Along River Margins: Linking Hydrology and Ecology,’’ Journal of Ecology 96:553–565 (2008); C. Nilsson, et al., ‘‘The Role of Hydrochory in Structuring Riparian and Wetland Vegetation,’’ Biological Reviews 85:837–858 (2010); L.M. Tronstad, et al., ‘‘Aerial Colonization and Growth: Rapid Invertebrate Responses to Temporary Aquatic Habitats in a River Floodplain,’’Journal of the North American Benthological Society 26:460–471 (2007)). Animals, particularly migratory fish, may thus move between adjacent waters and (a)(1) through (a)(3) waters. And even when some species do not traverse the entire distance from adjacent waters to downstream waters, the

downstream waters still benefit from the ecological integrity that persists because of the close relationship that adjacent waters have with nearby waters. This is because the chemical and biological properties that arise from interactions between adjacent waters

and tributaries move downstream and support the integrity of (a)(1) through (a)(3)

waters.

Biological connections between adjacent waters and river systems do not always increase with hydrologic connections. In some cases, the lack of connection improves the biological contribution provided by riparian waters towards neighboring streams, rivers, and lakes. For instance, the periodic hydrologic disconnectedness of oxbow lakes is necessary for the accumulation of plankton, an important source of carbon more easily assimilated by the aquatic food

chain than terrestrial forms of carbon. Id. at 5–46 (citing C. Baranyi, et al., ‘‘Zooplankton Biomass and Community Structure in a Danube River Floodplain System: Effects of Hydrology,’’ Freshwater Biology47:473–482 (2002); S. Keckeis, et al., ‘‘The Significance of Zooplankton Grazing in a Floodplain System of the River Danube,’’ Journal of

Plankton Research 25:243–253 (2003)). Similarly, some degree of hydrological disconnectedness is important in increasing the number of mollusk species and macroinvertebrate diversity in oxbow lakes, which in turn support the diversity of


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mollusks throughout the aquatic system. Id. at 5–46 to 5–47 (citing W. Reckendorfer, et al., ‘‘Floodplain Restoration by Reinforcing Hydrological Connectivity: Expected Effects on Aquatic Mollusc Communities,’’Journal of Applied Ecology43:474–484 (2006); K. Obolewski, et al., ‘‘Effect of Hydrological Connectivity on the Molluscan Community Structure in Oxbow Lakes of the Lyna River,’’ Oceanological and Hydrobiological Studies 38:75–88 (2009).

2. Confined Surface and Shallow Subsurface Hydrologic Connections Significantly Affect the Chemical, Physical, or Biological Integrity of (a)(1) Through (a)(3) Waters

Wetlands and open waters, including those outside the riparian zone and floodplain, can be connected downstream through unidirectional flow from the wetland or open water to a nearby tributary. Such connections can occur through a confined surface or a shallow subsurface hydrologic connection. Report at 3–7, 5–23. Outside of the riparian zone and floodplain, surface hydrologic connections between adjacent waters and jurisdictional waters can occur via confined flows (e.g. a swale, gully, ditch, or other discrete feature). For purposes of this rule,

confined surface connections are defined as permanent, intermittent or ephemeral surface connections through directional flowpaths, such as (but not limited to) swales, gullies, rills, and ditches. In some cases, these connections will be a result of ‘‘fill and spill’’ hydrology. A directional flowpath is a path where water flows repeatedly from the wetland or open water to the nearby jurisdictional water that at times contains water originating in the wetland or open water as opposed to just directly from precipitation. For the purposes of this rule, ‘‘fill and spill’’ describes situations where wetlands or open waters fill to capacity during intense precipitation events or high cumulative precipitation over time and then spill to the downstream jurisdictional water.

Id. at 5–62 (citing T.C. Winter and D.O. Rosenberry, ‘‘Hydrology of Prairie Pothole Wetlands during Drought and Deluge: A 17- year Study of the Cottonwood Lake Wetland Complex in North Dakota in the Perspective of Longer Term Measured and Proxy Hydrological Records,’’ Climatic Change 40:189–209 (1998); S.G. Leibowitz, and K.C. Vining, ‘‘Temporal connectivity in a prairie pothole complex,’’ Wetlands 23:13–25 (2003)). Water connected through such flows originate from the adjacent wetland or open water, travel to the downstream jurisdictional water, and are connected to those downstream waters by swales or other directional flowpaths on the surface.

A confined surface hydrologic connection, which may be perennial, intermittent or ephemeral, supports periodic flows between the adjacent water and the jurisdictional water. For example, wetland seeps are likely to have perennial connections to streams that provide important sources of baseflow, particularly during summer. Id. at 5–22 (citing T.R. Morley, et al., ‘‘The Role of Headwater Wetlands in Altering Streamflow and Chemistry in a Maine, USA catchment,’’ Journal of the American Water Resources

Association 47:337–349 (2011)). Other

wetlands are connected to streams via intermittent or ephemeral conveyances and

can contribute flow to downstream waters via their surface hydrologic connection. Id. at 5– 22 (citing M.C. Rains, et al., ‘‘The Role of Perched Aquifers in Hydrological Connectivity and Biogeochemical Processes in Vernal Pool Landscapes, Central Valley, California,’’ Hydrological Processes 20:1157– 1175 (2006); M.C. Rains, et al., ‘‘Geological Control of Physical and Chemical Hydrology in California Vernal Pools,’’ Wetlands 28:347–362 (2008); B.P. Wilcox, et al., ‘‘Evidence of Surface Connectivity for Texas Gulf Coast Depressional Wetlands,’’

Wetlands 31:451–458 (2011)).The surface hydrologic connection of the neighboring water to the jurisdictional water and the close proximity of the waters enhance the neighboring waters substantial effects the waters have on downstream (a)(1) through (a)(3) waters. Wetlands and open waters that are connected to (a)(1) through (a)(5) waters through a confined surface hydrologic connection will have an impact on downstream (a)(1) through (a)(3) waters, regardless of whether the outflow is permanent, intermittent, or ephemeral. See, e.g., id. at 5–1 to 5–2.

Wetlands and open waters with confined surface connections can affect the physical integrity of waters to which they connect. Such waters can provide an important source of baseflow to the streams to which they are adjacent, helping to sustain the water levels in the nearby streams. Id. at 5–22 (citing T.R. Morley, et al., ‘‘The Role of Headwater Wetlands in Altering Streamflow and Chemistry in a Maine, USA catchment,’’ Journal of the American Water Resources

Association 47:337–349 (2011); M.C. Rains, et al., ‘‘The Role of Perched Aquifers in Hydrological Connectivity and Biogeochemical Processes in Vernal Pool Landscapes, Central Valley, California,’’ Hydrological Processes 20:1157–1175 (2006);

M.C. Rains, et al., ‘‘Geological Control of Physical and Chemical Hydrology in California Vernal Pools,’’ Wetlands 28:347– 362 (2008); B.P. Wilcox, et al., ‘‘Evidence of Surface Connectivity for Texas Gulf Coast Depressional Wetlands,’’ Wetlands 31:451– 458 (2011)) and T.M. Lee, et al., Effect of

Groundwater Levels and Headwater Wetlands on Streamflow in the Charlie Creek Basin, Peace River Watershed, West-Central Florida, U.S. Geological Survey Scientific Investigations Report 2010–5189 (Reston, Virginia: U.S. Department of the Interior, U.S. Geological Survey, 2010). Waters with a

confined surface connection to downstream jurisdictional waters can affect streamflow by altering baseflow or stormflow through several mechanisms, including surface storage and groundwater recharge. Report at 5–25. Wetlands effectively store water because the entire aboveground portion of

the wetland basin is available for water storage, in contrast to upland areas where soil particles or rock reduce water storage volume for a given volume of that soil or rock (i.e., the specific yield). Id. at 5–25 (citing A.I. Johnson, Specific Yield—Compilation of Specific Yields for Various Materials, USGS Water Supply Paper 1662–D (Washington, DC: U.S. Department of the Interior, U.S. Geological Survey, 1967)). By storing water, these waters can reduce peak streamflow, and thus, downstream flooding. Id. at 5–25 (citing A. Bullock, and M. Acreman, ‘‘The Role of Wetlands in the Hydrological Cycle,’’ Hydrology and Earth System Sciences 7:358– 389 (2003); P. McEachern, et al., ‘‘Landscape Control of Water Chemistry in Northern Boreal Streams of Alberta,’’ Journal of Hydrology 323:303–324 (2006)). Antecedent moisture conditions, available wetland storage, and evaporation rates could impact water storage, as some waters connected to jurisdictional waters via discrete features may actually reduce flows in the streams they neighbor during dry periods. Id. at 5– 26 (citing A. Bullock, and M. Acreman, ‘‘The Role of Wetlands in the Hydrological Cycle,’’ Hydrology and Earth System Sciences 7:358– 389 (2003)). Thus, wetlands and open waters with a confined hydrologic connection to jurisdictional waters may function as a sink in dry periods if storage capacity is not exceeded and evaporation rates surpass groundwater recharge. Id. at 5–26 to 5–27.

Wetlands and open waters with confined

surface connections can affect the chemical integrity of waters to which they connect. Such waters can affect water quality of jurisdictional waters through source and sink functions, often mediated by transformation

of chemical constituents. The surface hydrologic connections to nearby jurisdictional waters provide pathways for

materials transformed in the wetlands and open waters (such as methylmercury or degraded organic matter) to reach and affect the nearby waters and the downstream (a)(1) through (a)(3). Id. at 5–27. Functions that occur in the wetlands and open waters can affect downstream (a)(1) through (a)(3) waters when compounds that are transformed in

wetland environments move to downstream waters via the surface hydrologic connection.

Id. at 5–28 (citing T.C. Winter and J.W. LaBaugh, ‘‘Hydrologic Considerations in Defining Isolated Wetlands,’’ Wetlands 23:532–540 (2003)). For example, methylmercury (which can form in peatlands) can be transported through entrainment with organic matter exports, and can move through surface flows from peatlands with confined surface connections

to downstream waters. Id. at 5–28 (citing O. Linqvist, et al., ‘‘Mercury in the Swedish Environment—Recent Research on Causes, Consequences, and Remedial Measures,’’

Water Air and Soil Pollution 55:xi–xiii (1991); G. Mierle, and R. Ingram, ‘‘The Role

of Humic Substances in the Mobilization of Mercury from Watersheds,’’ Water Air and

Soil Pollution 56:349–357 (1991); V.L. St.

Louis, et al., ‘‘Importance of Wetlands as Sources of Methyl mercury to Boreal Forest Ecosystems,’’ Canadian Journal of Fisheries and Aquatic Sciences 51:1065–1076 (1994); C.T. Driscoll, et al., ‘‘The Role of Dissolved Organic Carbon in the Chemistry and Bioavailability of Mercury in Remote Adirondack Lakes,’’ Water Air and Soil

Pollution 80:499–508 (1995); P. Porvari, and M. Verta, ‘‘Total and Methyl mercury

Concentrations and Fluxes from Small Boreal Forest Catchments in Finland,’’

Environmental Pollution 123:181–191 (2003)). The mercury that is transported

downstream can enter the food chains of the


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(a)(1) through (a)(3) waters and negatively impact wildlife inhibiting those downstream

waters. Id. at 5–28. Export of dissolved organic matter from neighboring waters

connected via a confined surface connection can have potentially negative effects on downstream waters because contaminants, such as MeHg and other trace metals, can be adsorbed to the organic matter. Id. at 5–28 (citing E.M. Thurman, Organic Geochemistry of Natural Waters (Boston, MA: Martinus Nijhoff/Dr. W. Junk Publishers, 1985); C.T. Driscoll, et al., ‘‘The Role of Dissolved Organic Carbon in the Chemistry and Bioavailability of Mercury in Remote Adirondack Lakes,’’ Water Air and Soil

Pollution 80:499–508 (1995)). Dissolved organic matter, however, is also an important source of energy for downstream aquatic

communities. Id. at 5–28 (citing J.E. Hobbie and R.G. Wetzel, ‘‘Microbial control of dissolved organic carbon in lakes: Research for the future,’’ Hydrobiologia 229:169–180 (1992); K.R. Reddy and R.D. DeLaune, Biogeochemistry of Wetlands: Science and Applications, 774 p. (2008)). Wetlands with confined surface hydrologic connections to the stream are connected to jurisdictional tributary system and therefore can efficiently transport dissolved organic carbon and other dissolved organic matter to the nearby jurisdictional water and downstream (a)(1) through (a)(3) waters. See, e.g., I.F. Creed, et al., ‘‘Cryptic Wetlands: Integrating Hidden Wetlands in Regression Models of the Export of Dissolved Organic Carbon from Forested Landscapes,’’ Hydrological Processes 17:3629–3648 (2003). Adjacent waters with a surface hydrologic connection to jurisdictional waters can also improve water quality through assimilation, transformation, or sequestration of nutrients and other pollutants. Report at 5–29 (citing, e.g., K.R. Reddy, and R.D. DeLaune, Biogeochemistry of Wetlands: Science and Applications, 774 p. (2008)). These processes can occur during times of lower hydroperiods when water is not present in the surface hydrologic connection between the adjacent water and the jurisdictional water. Pollutants can be attenuated or retained in such adjacent waters through processes including denitrification, ammonia volatilization, microbial and plant biomass assimilation, sedimentation, sorption and precipitation reactions, biological uptake, and long-term storage in plant detritus. Id. at 5–29 (citing K.R. Reddy, et al., ‘‘Phosphorus Retention in Streams and Wetlands: A Review,’’ Critical

Reviews in Environmental Science and Technology 29:83–146 (1999); K.R. Reddy and R.D. DeLaune, Biogeochemistry of Wetlands: Science and Applications, 774 p. (2008)). Through retention and mitigation of pollutants and other chemical compounds, adjacent waters with a surface hydrologic connection to jurisdictional waters can substantially improve water quality

downstream.

Wetlands and open waters with confined surface connections can affect the biological integrity of waters to which they connect. Movement of organisms between these adjacent waters and the nearby jurisdictional water is governed by many of the same factors that affect movement of organisms between riparian/floodplain waters and the

river network. Id. at 5–31. Because such waters are at least periodically hydrologically connected to the nearby jurisdictional tributary network on the surface, dispersal of organisms can occur actively through the surface connection or via wind dispersal, hitchhiking, walking, crawling, or flying. See, e.g., id. at 5–31. For example, waterborne dispersal of aquatic and emergent plants can occur between the jurisdictional water and the neighboring water due to the periodic hydrologic connection to the tributary

system. Id. at 5–31 (citing C. Nilsson, et al., ‘‘The Role of Hydrochory in Structuring Riparian and Wetland Vegetation,’’ Biological

Reviews 85:837–858 (2010)). Fish can also move between the jurisdictional water and the neighboring water to which it is connected via a surface hydrologic connection during periodic surficial hydrologic connections. Id. at 5–32 (citing J.W. Snodgrass, et al., ‘‘Factors affecting the occurrence and structure of fish assemblages in isolated wetlands of the upper coastal plain, USA,’’ Canadian Journal of Fisheries and Aquatic Sciences 53:443–454 (1996);

K.D. Zimmer, et al., ‘‘Effects of fathead

minnow colonization and removal on a prairie wetland ecosystem,’’ Ecosystems 4:346–357 (2001); M.J. Baber, et al., ‘‘Controls

on fish distribution and abundance in temporary wetlands,’’ Canadian Journal of Fisheries and Aquatic Sciences 59:1441–1450 (2002); M.A. Hanson, et al., ‘‘Biotic interactions as determinants of ecosystem structure in prairie wetlands: An example using fish,’’ Wetlands 25:764–775 (2005);, B.R. Herwig, et al., ‘‘Factors influencing fish distributions in shallow lakes in prairie and prairie-parkland regions of Minnesota, USA,’’

Wetlands 30:609–619 (2010)). Mammals and aquatic and semi-aquatic amphibians and reptiles that can disperse overland can also contribute to connectivity, as can aquatic birds, particularly given the close proximity of the neighboring water to the jurisdictional

water. Mammals and birds can act as transport vectors for hitchhikers like algae or aquatic insects. Id. at 5–32 (citing J.P. Roscher, ‘‘Alga Dispersal by Muskrat Intestinal Contents,’’ Transactions of the American Microscopical Society 86:497–498 (1967)); J. Figuerola and A.J. Green, ‘‘Dispersal of Aquatic Organisms by

Waterbirds: a Review of Past Research and Priorities for Future Studies,’’ Freshwater Biology47:483–494 (2002); J. Figuerola, et al., ‘‘Invertebrate Eggs Can Fly: Evidence of Waterfowl-Mediated Gene Flow in Aquatic Invertebrates,’’ American Naturalist 165:274– 280 (2005)). Amphibians and reptiles move between streams and their adjacent waters to satisfy part of their life-history requirements.

Id.at 5–33, Table 5–2. The hydrologic connection between neighboring waters with a surface connection to the jurisdictional

water allows for that movement to occur either in the water or over land. Aquatic

insects that use both streams and their adjacent waters can move outside of the stream network to the nearby wetland or open water to seek suitable habitat for overwintering, refuge from adverse conditions, hunting, foraging or breeding,

and then return to the stream for other lifehistory requirements. Id. at 5–33 (citing D.D. Williams, ‘‘Environmental Constraints in Temporary Fresh Waters and Their Consequences for the Insect Fauna,’’Journal of the North American Benthological Society 15:634–650 (1996); A.J. Bohonak and D.G. Jenkins, ‘‘Ecological and Evolutionary Significance of Dispersal by Freshwater Invertebrates,’’ Ecology Letters 6:783–796 (2003)). Neighboring waters with a confined surface hydrologic connection to jurisdictional waters help to maintain various biological populations, which periodically replenish adjacent jurisdictional waters, serving to maintain the biological integrity of (a)(1) through (a)(3) waters.

A shallow subsurface hydrologic connection is lateral water flow through a shallow subsurface layer, such as can be found in steeply sloping areas with shallow

soils and soils with a restrictive horizon that prevents vertical water flow, or in karst systems. K.J. Devito, et al., ‘‘GroundwaterSurface Water Interactions in Headwater Forested Wetlands of the Canadian Shield,’’ Journal of Hydrology 181:127–47 (1996); M.A. O’Driscoll and R.R. Parizek, ‘‘The Hydrologic Catchment Area of a Chain of Karst Wetlands in Central Pennsylvania,

USA,’’ Wetlands 23:171–79 (2003); B.J. Cook and F.R. Hauer, ‘‘Effects of Hydrologic Connectivity on Water Chemistry, Soils, and Vegetation Structure and Function in an Intermontane Depressional Wetland Landscape,’’ Wetlands 27:719–38 (2007). Shallow subsurface connections may be found below the ordinary root zone (below 12 inches), where other wetland delineation factors may not be present. The presence of an aquiclude (impervious layer) near the

surface leads to shallow subsurface flows through the soil, which favors local groundwater flowpaths that connect to nearby wetlands or streams. Report at 3–38.

Wetlands with shallow subsurface connections can affect the physical integrity of waters to which they connect. In general, the volume and sustainability of streamflow within river networks depends on contributions from groundwater, especially in areas with shallow groundwater tables and pervious (meaning water can easily pass through) subsurfaces. Id. at 3–12 (citing J.J. de Vries, ‘‘Seasonal Expansion and

Contraction of Stream Networks in Shallow Groundwater Systems,’’ Journal of Hydrology 170:15–26 (1995); T.C. Winter, ‘‘The Role of Groundwater in Generating Streamflow in Headwater Areas and in Maintaining Base Flow,’’Journal of the American Water

Resources Association 43:15–25 (2007); G.R. Kish, et al., ‘‘A Geochemical Mass-Balance Method for Base-Flow Separation, Upper Hillsborough River Watershed, West-Central Florida, 2003–2005 and 2009,’’ USGS Scientific Investigations Report 2010–5092 (Washington, DC: U.S. Department of the Interior, U.S. Geological Survey, 2010).

Because wetlands with shallow subsurface connections to streams and rivers provide some of these groundwater contributions, they influence the flow regime. Wetlands

connected via shallow subsurface

connections also can act as water sinks when evapotranspiration is high, but as water sources when evapotranspiration is low. Id.


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at 3–25. As a result, these adjacent waters moderate peak flows, reduce downstream flooding, and provide runoff to help maintain baseflow for streams during times of low

flows.

Wetlands and other waters with shallow

subsurface connections affect the chemical and biological integrity of downstream waters in ways similar to wetlands with

surface connections. The distance between these wetlands and jurisdictional waters may influence the connectivity since wetlands

with shorter distances to the stream network will have higher hydrological and biological connectivity than wetlands located further

from the same network. Id. at 3–43. The distance between the wetland and water may

also influence whether waters are connected via surface or shallow subsurface hydrologic connections, as wetlands and open waters

that are closer to rivers and streams will have a higher probability of being connected than more distant waters, assuming that conditions governing type and quantity of flows (e.g. slope, soil and aquifer permeability) are similar. Id at 5–2. For wetlands connected to tributaries through groundwater flows, less distant wetlands/ waters are generally connected through shallower flowpaths, assuming similar soil and geologic properties. Id. at 3–11 (Figure 3–5), 3–42. These shallower subsurface flows have the greatest interchange with surface waters and travel between points in the

shortest amount of time. Id. at 3–42.

3. Adjacent Waters, Including Wetlands, Separated From Other ‘‘Waters of the United States’’ by Man-Made Dikes or Barriers, Natural River Berms, Beach Dunes and the Like Significantly Affect the Chemical, Physical, or Biological Integrity of (a)(1) Through (a)(3) Waters

The terms earthen dam, dike, berm, and

levee are used to describe similar structures whose primary purpose is to help control flood waters. Such structures vary in scale

and size. A levee is an embankment whose primary purpose is to furnish flood protection from seasonal high water and which is therefore subject to water loading for periods of only a few days or weeks a year. Earthen embankments that are subject to water loading for prolonged periods (longer than normal flood protection requirements) are called earth dams. There are a wide variety of types of structures and

an even wider set of construction methods. These range from a poorly constructed, low earthen berm pushed up by a backhoe to a well-constructed, impervious core, riprap lined levee that protects houses and cropland. Generally, levees are built to detach the floodplain from the channel, decreasing overbank flood events. S.B. Franklin, et al., ‘‘Complex Effects of

Channelization and Levee Construction on Western Tennessee Floodplain Forest
Function,’’ Wetlands 29(2): 451–464 (2009). The investigation methods to determine the presence or absence of the hydrologic connection depend on the type of structure, the underlying soils, the presence of groundwater, and the depth of the water table. Department of the Army, U.S. Army Corps of Engineers, Engineering and Design—Design and Construction of Levees, EM 1110–2–1913 (Washington, DC, Department of the Army, 2000), p. 1–1.

Man-made berms and the like are fairly common along streams and rivers across the United States and often accompany stream channelization. S.B. Franklin, et al., ‘‘Complex Effects of Channelization and

Levee Construction on Western Tennessee Floodplain Forest Function,’’ Wetlands 29(2): 451–464 (2009). One study conducted in Portland, Oregon found that 42% of surveyed wetlands had dams, dikes, or berms. M. Kentula, et al., ‘‘Tracking Changes in

Wetlands with Urbanization: Sixteen Years of Experience in Portland, Oregon, USA,’’

Wetlands 24(4):734–743 (2004). Likewise,
over 90% of the tidal freshwater wetlands of the Sacramento-San Joaquin Delta have been diked or leveed. C. Simenstad, et al.,‘‘Preliminary Results from the SacramentoSan Joaquin Delta Breached Levee Wetland Study,’’ Interagency Ecological Program for the Sacramento-San Joaquin Estuary

Newsletter 12(4):15–21 (1999). At least 40,000 kilometers of levees, floodwalls, embankments, and dikes are estimated across the United States, with approximately 17,000 kilometers of levees in the Upper Mississippi Valley alone. SE. Gergel, et al., ‘‘Consequences of Human-altered Floods: Levees, Floods, and Floodplain Forests along the Wisconsin River,’’ Ecological Applications 12(6): 1755–1770 (2002).

Adjacent waters separated from the tributary network by dikes, levees, berms and the like continue to have a hydrologic

connection to downstream waters. This is because berms and similar features typically do not block all water flow. Indeed, even dams, which are specifically designed and constructed to impound large amounts of water effectively and safely, do not prevent all water flow, but rather allow seepage under the foundation of the dam and through

the dam itself. See, e.g., International Atomic Energy Agency, Factsheet on Investigating Leaks through Dams and Reservoirs, http:// www.tc.iaea.org/tcweb/publications/ factsheets/sheet20dr.pdf ; U.S. Bureau of Reclamation, Provo Office, Safety of Dams, http://www.usbr.gov/uc/provo/progact/ damsafety.html; Federal Energy Regulatory Commission (FERC), ‘‘Chapter 14: Dam Safety Performance Monitoring Program,’’ Engineering Guidelines for the Evaluation of Hydropower Projects (FERC, 2005), pp. 14–

36 to 14–39.

Seepage is the flow of a fluid through the soil pores. Seepage through a dam, through the embankments, foundations or abutments, or through a berm is a normal condition. D.A.

Kovacic, et al., ‘‘Effectiveness of Constructed Wetlands in Reducing Nitrogen and Phosphorus Export from Agricultural Tile Drainage,’’Journal of Environmental Quality 29(4): 1262–1274 (2000); Federal Energy Regulatory Commission (FERC), ‘‘Chapter 14: Dam Safety Performance Monitoring Program,’’ Engineering Guidelines for the Evaluation of Hydropower Projects (FERC, 2005), pp. 14–36 to 14–39. This is because water seeks paths of least resistance through

the berm or dam and its foundation. Michigan Department of Environmental Quality, Seepage Through Earth Dams (2002), http://www.michigan.gov/deq/0,1607,7-135- 3313

_3684

_3723-9515-,00.html. All earth and rock-fill dams are subject to seepage through the embankment, foundation, and abutments. Department of the Army, U.S. Army Corps of Engineers, Seepage Analysis and Control for Dams, EM 1110–2–1901, (Washington, DC: Department of the Army, Original 1986— Revised 1993), Page 1–1; Department of the Army, U.S. Army Corps of Engineers, Engineering and Design: General Design and

Construction Considerations for Earth and Rock-filled Dams, EM 1110–2–2300 (Washington, DC: Department of the Army, 2004), pp. 6–1 to 6–7. Concrete gravity and arch dams similarly are subject to seepage through the foundation and abutments. Department of the Army, U.S. Army Corps of Engineers, Seepage Analysis and Control for Dams, EM 1110–2–1901 (Washington, DC: Department of the Army, Original 1986— Revised 1993), Page 1–1. Levees and the like are subject to breaches and breaks during times of floods. C. Nilsson, et al., ‘‘Fragmentation and Flow Regulation of the World’s Large River Systems,’’ Science 308(5720):405–408 (2005). Levees are similarly subject to failure in the case of extreme events, such as the extensive levee failures caused by Hurricanes Katrina and Rita. J.W. Day, et al., ‘‘Restoration of the Mississippi Delta: Lessons from Hurricanes Katrina and Rita,’’ Science 315(5819): 1679– 1684 (2007). In designing levees and similar structures, seepage control is necessary to prevent possible failure caused by excessive uplift pressures, instability of the downstream slope, piping through the embankment and/or foundation, and erosion of material by migration into open joints in

the foundation and abutments. Id.; D.A.
Kovacic, et al., ‘‘Effectiveness of Constructed Wetlands in Reducing Nitrogen and Phosphorus Export from Agricultural Tile Drainage,’’Journal of Environmental Quality 29(4): 1262–1274 (2000); U.S. Department of the Interior, Bureau of Reclamation, Upper Colorado Region, see http://www.usbr.gov/ uc/provo/progact/damsafety.html; International Atomic Energy Agency, Investigating Leaks through Dams and

Reservoirs, see http://www-tc.iaea.org/ tcweb/publications/factsheets/sheet20dr.pdf; California Division of Safety of Dams, Embankment Design, see http:// damsafety.water.ca.gov/guidelines/

embankment.htm.

The rate at which water moves through the embankment depends on the type of soil in the embankment, how well it is compacted, the foundation and abutment preparation,

and the number and size of cracks and voids

within the embankment. All but the smallest earthen dams are commonly built with internal subsurface drains to intercept water seeping from the reservoir (i.e., upstream side) to the downstream side. Department of the Army, U.S. Army Corps of Engineers,

Construction Control for Earth and Rockfilled Dams, EM 1110–2–1911, September 30, 1995, Washington, DC 20314–1000, Page 1– 1. Where it is not intercepted by a subsurface drain, the seepage will emerge downstream

from or at the toe of the embankment. Michigan Department of Environmental Quality, Seepage Through Earth Dams (2002), http://www.michigan.gov/deq/0,1607,7-135-


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_3723-9515-,00.html. Seepage may vary in appearance from a ‘‘soft,’’ wet area to a flowing ‘‘spring.’’ It may show up first as an area where the vegetation is lush and darker green. Cattails, reeds, mosses, and other marsh vegetation may grow in a seepage area. Michigan Department of Environmental Quality, Seepage Through Earth Dams (2002), http://www.michigan. gov/deq/0,1607,7-135-3313

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_3723-9515- ,00.html.

Engineered berms are typically designed to interfere with the seasonal pattern of water level (hydroperiod) of the area behind the berm, reducing the frequency and severity of inundation. Berms are not designed to eliminate all hydrologic connection between

the channel on one side and the area behind the berm on the other. It is almost always impracticable to build a berm that will not be overtopped by a flood of maximum severity, and most berms are not designed to

withstand severe floods. See, e.g., Department of the Army, U.S. Army Corps of Engineers, Seepage Analysis and Control for Dams, EM 1110–2–1901, (Washington, DC: Department of the Army, Original 1986— Revised 1993), Page 1–1. Levees are designed to allow seepage and are frequently situated on foundations having natural covers of relatively fine-grain impervious to semipervious soils overlying pervious sands and gravels. Department of the Army, U.S. Army Corps of Engineers, Engineering and Design: Design Guidance for Levee Underseepage, ELT 1110–2–569, Washington, DC: Department of the Army, 2005), pp. 1–9. These surface strata constitute impervious or semipervious blankets when considered in connection with seepage. Principal seepage control measures for foundation underseepage are (a) cutoff trenches, (b) riverside impervious blankets, (c) landslide berms, (d) pervious toe trenches, and (e) pressure relief wells. Department of the Army, U.S. Army Corps of Engineers, Engineering and Design—Design and Construction of Levees, EM 1110–2–1913 (Washington, DC, Department of the Army, 2000), p. 1–1. Overtopping of an embankment dam is very undesirable because the embankment materials may be eroded away. Additionally, only a small number of concrete dams have been designed to be overtopped. Water normally passes through the main spillway or outlet works; it should pass over an auxiliary spillway only during periods of high reservoir levels and high water inflow. All embankment and most concrete dams have some seepage. See, e.g., http://www.damsafety.org/layout/ subsection.aspx?groupid=14&contentid=47. However, it is important to control the seepage to prevent internal erosion and instability. Proper dam construction, and maintenance and monitoring of seepage provide control.

Berm-like landforms known as natural levees occur naturally and do not isolate adjacent wetlands from the streams that form

them. Natural levees and the wetlands and waters behind them are part of the floodplain, including along some small

streams and streams in the Arid West. C.A. Johnston, et al., ‘‘Nutrient Dynamics in Relation to Geomorphology of Riverine Wetlands,’’ Soil Science Society of America Journal 65(2):557–577 (2001). Every flowing watercourse transports not only water, but sediment—eroding and rebuilding its banks and floodplains continually. Federal Interagency Stream Restoration Working Group, Stream Corridor Restoration: Principles, Processes and Practices, USDA National Engineering Handbook Part 653 (1999). Different deposition patterns occur under varying levels of streamflow, with higher flows having the most influence on the resulting shape of streambanks and floodplains. Id. In relatively flat landscapes drained by low-gradient streams, this natural process deposits the most sediment on the bank immediately next to the stream channel while floodplains farther from the channel are usually lower-lying wetlands (‘‘backswamps’’ or ‘‘backwater wetlands’’)

that receive less sediment. See, e.g., C.A. Johnston, et al., ‘‘The Potential Role of Riverine Wetlands as Buffer Zones,’’ in N.E. Haycock, et al., ed., Buffer Zones Their

Processes and Potential in Water Protection (Quest International, 1997), pp. 155–170. The somewhat elevated land thus built up at streamside is called a natural levee, and this entirely natural landform is physically and hydrologically similar to narrow, man-made

berms. See, e.g., L.B. Leopold, et al., Fluvial Processes in Geomorphology (Toronto: General Publishing Co. Ltd., 1964). Natural levees are discontinuous, which allows for a hydrologic connection to the stream or river via openings in the levees and thus the periodic mixing of river water and backwater. C.A. Johnston, et al., ‘‘Nutrient Dynamics in Relation to Geomorphology of Riverine Wetlands,’’ Soil Science Society of America Journal 65(2): 557–577 (2001). In addition, streams with natural levees, in settings with no human interference whatsoever, retain hydrologic connection with their wetlands behind the levees by periodic flooding during high water and via seepage through and under the levee. Similarly, man-made berms are typically periodically overtopped with water from the near-by stream, and as previously mentioned, are connected via

seepage.

Waters, including wetlands, separated from a stream by a natural or man-made berm serve many of the same functions as those discussed above on other adjacent waters. Furthermore, even in cases where a hydrologic connection may not exist, there are other important considerations, such as chemical and biological factors, that result in a significant nexus between the adjacent wetlands or waters and the nearby ‘‘waters of the United States,’’ and (a)(1) through (a)(3)

waters.

The movement of surface and subsurface both over berms and through soils and berms adjacent to rivers and streams is a hydrologic connection between wetlands and flowing

watercourses. The intermittent connection of surface waters over top of, or around, natural and manmade berms further strengthens the evidence of hydrologic connection between wetlands and flowing watercourses. Both natural and man-made barriers can be topped by occasional floods or storm events. See,

e.g., R.E. Turner, et al., ‘‘Wetland

Sedimentation from Hurricanes Katrina and Rita,’’ Science 314(5798): 449–452 (2006); P.A. Keddy, et al., ‘‘The Wetlands of Lakes Pontchartrain and Maurepas: Past, Present and Future,’’ Environmental Reviews 15: 43– 77 (2007). When berms are periodically overtopped by water, wetlands and waters behind the barriers are directly connected to and interacting with the nearby stream and its downstream waters. In addition, surface waters move to and from adjacent soils (including adjacent wetland soils) continually. Along their entire length,streams alternate between effluent (watergaining) and influent (water-losing) zones as the direction of water exchange with the

streambed and banks varies. Federal Interagency Stream Restoration Working Group, Stream Corridor Restoration: Principles, Processes and Practices, USDA National Engineering Handbook Part 653 (1999). The adjacent areas involved in this surface water exchange with a stream or river are known as the hyporheic zone. Hyporheic zone waters are part of total surface waters temporarily moving through soil or sediment. Like within-channel waters, these waters are oxygenated and support living communities of organisms in the hyporheic zone.

Because a hydrologic connection between adjacent wetlands and waters and downstream waters still exists despite the presence of a berm or the like, the chemical and biological connections that rely on a hydrologic connection also exist. For instance, adjacent waters behind berms can still serve important water quality functions, serving to filter pollutants and sediment before they reach downstream waters.

Wetlands behind berms can function to filter pollutants before they enter the nearby tributary, with the water slowly released to the stream through seepage or other hydrological connections. See, e.g., L.L. Osborne and D.A. Kovacic, ‘‘Riparian Vegetated Buffer Strips in Water-Quality Restoration and Stream Management,’’ Freshwater Biology 29(2): 243–258 (1993);

D.A. Kovacic, et al., ‘‘Effectiveness of Constructed Wetlands in Reducing Nitrogen and Phosphorus Export from Agricultural Tile Drainage,’’Journal of Environmental Quality 29(4): 1262–1274 (2000). Their ability to retain sediment and floodwaters may be enhanced by the presence of the berm. For instance, some backwater wetlands in floodplain/riparian areas exhibit higher

sedimentation rates than streamside locations. E.J. Kuenzler, et al., ‘‘Distributions and Budgets of Carbon, Phosphorus, Iron and Manganese in a Floodplain Swamp Ecosystem,’’ Water Resources Research Institute Report 157 (Chapel Hill, NC: University of North Carolina, 1980); C.A. Johnston, et al., ‘‘Nutrient Dynamics in Relation to Geomorphology of Riverine Wetlands,’’ Soil Science Society of America Journal 65(2): 557–577 (2001). The presence of manmade levees can actually increase denitrification rates, meaning that the adjacent waters can more quickly transform nitrogen. SE. Gergel, et al., ‘‘Do Dams and Levees Impact Nitrogen Cycling? Simulating

the Effects of Flood Alterations on Floodplain Denitrification,’’ Global Change Biology 11(8): 1352–1367 (2005). However, the presence of manmade berms does limit


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the ability of the river to connect with its adjacent wetlands through overbank flooding and thus limits sediment, water and nutrients transported from the river to the adjacent

waters. Id.; J.L. Florsheim and J.F. Mount, ‘‘Changes in Lowland Floodplain

Sedimentation Processes: Pre-disturbance to Post-rehabilitation, Cosumnes River, CA,’’ Geomorphology 56(3–4):305–323 (2003). However, the presence of a berm does not completely eliminate the transport of

sediments and water from the river to the nearby adjacent wetland, as suspended

sediments and water can overflow both natural and man-made levees, though the transport is usually more pronounced in settings with natural levees. See, e.g., R.E.
Turner, et al., ‘‘Wetland Sedimentation from Hurricanes Katrina and Rita,’’ Science 314(5798):449–452 (2006); P.A. Keddy, et al.,

‘‘The Wetlands of Lakes Pontchartrain and Maurepas: Past, Present and Future,’’

Environmental Reviews 15:43–77 (2007). Sediment deposition over levees is particularly enhanced by extreme events like

hurricanes. Id.; D.J. Reed, et al., ‘‘Reducing the Effects of Dredged Material Levees on

Coastal Marsh Function: Sediment Deposition and Nekton Utilization,’’ Environmental Management 37(5):671–685 (2006). Wetlands behind berms, where the system is extensive, can help reduce the impacts of storm surges caused by hurricanes. J.W. Day, et al., ‘‘Restoration of the Mississippi Delta: Lessons from Hurricanes Katrina and Rita,’’ Science 315(5819):1679–1684 (2007).

Adjacent waters, including wetlands, separated from water bodies by berms and the like maintain ecological connection with those water bodies. Though a berm may reduce habitat functional value and may prevent some species from moving back and forth from the wetland to the river, many major species that prefer habitats at the interface of wetland and stream ecosystems remain able to utilize both habitats despite the presence of such a berm. Additional species that are physically isolated in either

stream or wetlands habitat still interact ecologically with species from the other component. Thus, adjacent wetlands with or

without small berms can retain numerous similarities in ecological function. For example: Wetland bird species such as wading birds are able to utilize both wetland and adjacent stream/ditch habitats; wetland amphibians would be able to bypass the berm in their adult stage; aquatic invertebrates and

fish would still interact with terrestrial/ wetland predators and prey in common food web relationships despite the presence of a

berm. See, e.g., G.S. Butcher, and B. Zimpel,

‘‘Habitat Value of Isolated Waters to Migratory Birds,’’ Prepared by Cornell Laboratory of Ornithology and The Cadmus Group, Inc. for U.S. Environmental Protection Agency Office of Wetlands Protection, (Washington, DC: Cornell and Cadmus, 1991); M.F. Willson and K.C. Halupka, ‘‘Anadromous Fish as Keystone Species in Vertebrate Communities,’’ Conservation Biology 9(3):489–497 (1995); C.J. Cederholm, et al., ‘‘Pacific Salmon

Carcasses: Essential Contributions of Nutrients and Energy for Aquatic and Terrestrial Ecosystems,’’ Fisheries 24(10):6– 15 (1999); S.S. Schwartz and D.G. Jenkins, ‘‘Temporary Aquatic Habitats: Constraints and Opportunities,’’ Aquatic Ecology 34:3–8 (2000); D.T. Bilton, et al., ‘‘Dispersal in Freshwater Invertebrates,’’ Annual Review of Ecology and Systematics 32:159–81 (2001).

One example of adjacent waters behind

berms and the like are interdunal wetlands located in coastal areas, including some areas of the Great Lakes and along barrier islands.

Interdunal wetlands form in swales or depressions within open dunes or between beach ridges along the coast and experience a fluctuating water table seasonally and yearly in synchrony with sea or lake level changes. W.E. Odum, ‘‘Non-Tidal Freshwater Wetlands in Virginia,’’ Virginia Journal of

Natural Resources Law 7: 421–434 (1988); D.A. Albert, Borne of the Wind: An Introduction to the Ecology of Michigan Sand

Dunes (Lansing, MI: Michigan Natural Features Inventory, 2000), 63 pp.; D.A. Albert, Between Land and Lake: Michigan’s Great Lakes Coastal Wetlands, Bulletin E– 2902 (East Lansing, MI: Michigan Natural Features Inventory, Michigan State University Extension, 2003), 96 pp; D.A. Albert, Natural Community Abstract for

Interdunal Wetland (Lansing, MI: Michigan Natural Features Inventory, 2007), 6 pp. For those along the ocean coast, they are typically formed as a result of oceanic processes where the wetlands establish behind relict dune ridges (dunes that were formed along a previously existing coast line). Wetlands in the interdunal system are in close proximity to each other and to the surrounding (a)(1) through (a)(3) waters. Their proximity to one another and to the (a)(1) through (a)(3) waters indicates a close physical relationship between interdunal wetland systems and the traditional navigable waters, interstate waters, or the territorial seas. Despite the presence of the beach dunes, interdunal wetlands have chemical, physical, or biological connections that greatly influence the integrity of the nearby (a)(1) through (a)(3) waters. The wetlands are hydrologically connected to these (a)(1) through (a)(3) waters through unconfined, directional flow and shallow subsurface flow during normal precipitation events and extreme events. As previously noted, they are linked to the rise and fall of the surrounding tides—the water-level fluctuations of the nearby (a)(1) through (a)(3) waters are important for the dynamics of the wetlands. D.A. Albert, Between Land and Lake: Michigan’s Great Lakes Coastal Wetlands, Bulletin E–2902 (East Lansing, MI: Michigan Natural Features Inventory, Michigan State University Extension, 2003), 96 pp. The wetlands provide floodwater storage and attenuation, retaining and slowly releasing floodwaters before they reach the nearby (a)(1) through (a)(3) waters. Like other adjacent wetlands, interdunal wetlands also have important chemical connections to the nearby (a)(1) through (a)(3) waters, as they serve important water quality benefits. The wetlands store sediment and pollutants that would otherwise reach the surrounding (a)(1) through (a)(3) waters. The wetlands are biologically connected to the surrounding (a)(1) through (a)(3) waters. For instance, they provide critical habitats for species that utilize both the wetlands and the nearby (a)(1) through (a)(3) waters, supporting high diversity and structure. Habitat uses include basic food, shelter, and reproductive requirements. Aquatic insects, amphibians, and resident and migratory birds all use interdunal wetlands as critical habitat, and the wetlands provide better shelter than the nearby exposed beach. D.A. Albert, Borne of the Wind: An Introduction to the Ecology of Michigan Sand Dunes (Lansing, MI: Michigan Natural Features Inventory, 2000), 63 pp.; S.M. Smith, et al., ‘‘Development of Vegetation in Dune Slack Wetlands of Cape Cod National Seashore (Massachusetts, USA),’’ Plant Ecology 194(2): 243–256 (2008). In marine coastal areas, the wetlands are often the only freshwater system in the immediate landscape, thus providing critical drinking water for the species that utilize both the wetlands and the nearby (a)(1) through (a)(3) waters, although some

interdunal wetlands are brackish in nature. See, e.g., C.M. Heckscher and C.R. Bartlett, ‘‘Rediscovery and Habitat Associations of

Photuris Bethaniensis McDermott (Coleoptera: Lampyridae),’’ The Coleopterists

Bulletin 58(3): 349–353 (2004).

Wetlands behind the extensive levee system in the Yazoo Basin are an example of adjacent waters behind man-made barriers. A regional hydrogeomorphic approach guidebook for the Yazoo Basin of the Lower Mississippi River Alluvial Valley assesses the

functions of these wetlands. R.D. Smith and C.V. Klimas, A Regional Guidebook for Applying the Hydrogeomorphic Approach to Assessing Wetland Functions of Selected Regional Wetland Subclasses, Yazoo Basin, Lower Mississippi River Alluvial Valle, Prepared for the U.S. Army Corps of Engineers, ERDC/EL TR–02–4 (2002). An extensive levee system was built along the river system to prevent flooding of the Mississippi River, resulting in drastic effects to the hydrology of the basin. Id. at 47. Despite the alteration of hydrology in the basin, extensive wetlands systems still exist

behind the man-made and natural levees and maintain a hydrologic connection to the river system. These wetlands detain floodwater, detain precipitation, cycle nutrients, export organic carbon, remove elements and compounds, maintain plant communities, and provide fish and wildlife habitat. Id. The functions in turn provide numerous and substantial benefits to the nearby river.

4. Conclusions Regarding Adjacent Waters

The scientific literature documents that waters which are adjacent to (a)(1) through (a)(5) waters, including wetlands, oxbow lakes and adjacent ponds, are integral parts of tributary networks to (a)(1) through (a)(3) waters because they are directly connected to streams via permanent surface features that concentrate, mix, transform, and transport water and other materials, including food resources, downstream to larger rivers. Adjacent wetlands and other adjacent waters filter pollutants before they enter the tributary system, they attenuate flow during flood events, they regulate flow rate and timing, they trap sediment, and they input organic material into rivers and streams, providing the basic building blocks for their


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healthy functioning. These waters also are biologically connected to downstream waters by providing habitat and refuge to many species, and storing and releasing food

sources. The scientific literature demonstrates that adjacent waters in a watershed together exert a strong influence on the character and functioning of rivers,

streams and lakes.

Adjacent waters, as defined, alone or in combination with other adjacent waters in a watershed, significantly affect the chemical, physical, or biological integrity of traditional navigable waters, interstate waters, and the

territorial seas. Based on studies of waters in riparian areas, flood plains, and their hydrologic connections through the tributary system there is sufficient scientific evidence regarding the important functions of these adjacent wetlands to demonstrate that, alone or in combination with similarly situated waters in the region, wetlands and open waters adjacent to any tributary have a significant effect on the chemical, physical, or biological integrity of traditional navigable waters, interstate waters, or the territorial

seas. The reviewed scientific literature supports the conclusion that adjacent waters generally play a larger role in the ecological condition of smaller tributary systems, which, in turn, determines the effects on the chemical, physical, and biological health of larger downstream waters.

iii. ‘‘Other Waters’’

The Report includes a focused evaluation

of the connections and effects to downstream waters for several regional types of streams and wetlands: Prairie streams, southwest intermittent and ephemeral streams, oxbow lakes, Carolina and Delmarva bays, prairie potholes, and vernal pools. These regional types were chosen for evaluation because they represent a broad geographic area as well as a diversity of water types based on their origin, landscape setting, hydrology, and other factors. Most prairie streams and southwest intermittent and ephemeral streams are likely to be considered tributaries to (a)(1) through (a)(3) waters (with the exception of streams, for example, located in closed basins, which lack an (a)(1) through (a)(3) water or a connection thereto); similarly, most oxbow lakes are likely to be considered adjacent to (a)(1) through (a)(5) waters. Carolina and Delmarva bays, prairie potholes, and vernal pools may or may not be considered adjacent to (a)(1) through (a)(5)

waters. Where waters are not considered tributaries (e.g. waters in a solely intrastate

closed basin that does not contain a traditional navigable water, interstate water, or a territorial sea, or a connection thereto) or where waters, including wetlands, do not meet the proposed regulatory definition of adjacent, they should be evaluated to determine whether they are (a)(7) waters. The agencies seek comment on establishing such categories, as well as on other options for addressing ‘‘other waters.’’

The term ‘‘other waters’’ refers to waters that cannot be considered ‘‘adjacent’’ to downstream jurisdictional waters and that

are not tributaries of such waters. ‘‘Other waters’’ are found outside the riparian zone and the floodplain, as waters within these areas are considered to be ‘‘adjacent.’’ As such, wetlands that are ‘‘other waters’’ typically will have unidirectional flow. As mentioned in Part II, section 2.B. above, many unidirectional wetlands are considered adjacent and interact with downstream jurisdictional waters through channels, shallow subsurface flow, or by providing additional functions such as storage and mitigating peak flows. Unidirectional

wetlands that lack a confined surface

connection or a shallow subsurface

connection to downstream waters and are surrounded by uplands will typically fall under the definition of ‘‘other waters,’’ and

are often referred to in scientific literature and policy as ‘‘geographically isolated waters.’’ The term ‘‘geographically isolated’’ should not be used to implicate the lack of connectivity to downstream waters, as these

wetlands are often connected to downstream waters through deeper groundwater connections, biological connections, or spillage. The degree of connectivity of such wetlands will vary depending on landscape

features such as distance from downstream waters and proximity to other wetlands of similar nature that as a group connect to jurisdictional downstream waters. Report at

3–43, 5–2.

For purposes of assessing whether a particular water is a ‘‘water of the United States’’ because it, alone or in combination with other similarly situated waters, has a significant nexus to an (a)(1) through (a)(3) water, the agencies are proposing to define each of the elements of Justice Kennedy’s significant nexus standard in the definition of ‘‘significant nexus.’’

A. In the Region

The agencies have determined that because

the movement of water from watershed drainage basins to river networks and lakes shapes the development and function of these systems in a way that is critical to their long term health, the watershed is a reasonable and technically appropriate interpretation of Justice Kennedy’s standard. See, e.g., D.R. Montgomery, ‘‘Process Domains and the River Continuum,’’ Journal of the American Water Resources Association 35:397–410 (1999).

Using a watershed as the framework for conducting significant nexus evaluations is scientifically supportable. Watersheds are generally regarded as the most appropriate spatial unit for water resource management. See, e.g., J.M. Omernik and R.G. Bailey, ‘‘Distinguishing Between Watersheds and Ecoregions,’’Journal of the American Water

Resources Association 33.5: 939–40 (1997); D.R. Montgomery, ‘‘Process Domains and the
River Continuum,’’ Journal of the American

Water Resources Association 35: 397–410 (1999); T.C. Winter ‘‘The Concept of Hydrologic Landscapes,’’ Journal of the

American Water Resources Association 37: 335–49 (2001); J.S. Baron, et al., ‘‘Meeting Ecological and Societal Needs for Freshwater,’’ Ecological Applications 12: 1247–60 (2002); J.D. Allan, ‘‘Landscapes and Riverscapes: The Influence of Land Use on Stream Ecosystems,’’ Annual Review of Ecology Evolution and Systematics 35: 257– 84 (2004); United States, EPA 841–B–08–002: U.S. Environmental Protection Agency, Handbook for Developing Watershed Plans to Restore and Protect Our Waters: Planning & Implementation Steps (Washington D.C.: U.S. EPA, March 2008); P.J. Wigington, et al., ‘‘Oregon Hydrologic Landscapes: A Classification Framework,’’ Journal of the

American Water Resources Association 49.1:163–82 (2013). Anthropogenic actions and natural events can have widespread effects within the watershed that collectively impact the quality of the relevant traditional navigable water, interstate water or territorial sea. United States, U.S. EPA and USDA/ARS Southwest Watershed Research Center, EPA/ 600/R–08/134, ARS/2330462008: The Ecological and Hydrological Significance of Ephemeral and Intermittent Streams in the

Arid and Semi-arid American Southwest (Washington, D.C.: U.S. EPA and USDA/ARS Southwest Watershed Research Center,

Levick et al., 2008) (Levick, et. al.). For these reasons, it is more appropriate to conduct a significant nexus determination at the watershed scale than to focus on a specific site, such as an individual stream segment. The watershed size reflects the specific water management objective, and is scaled up or down as is appropriate to meet that objective. If the objective is to manage the water quality in a particular receiving water body (the ‘‘target’’ water body), the watershed should include all those waters that are contributing to that target water since they will primarily determine the quality of the receiving water.

The watershed that drains to the single point of entry to a traditional navigable water, interstate water or territorial sea is a logical spatial framework for the evaluation of the nexus. This is because, from a water quality management perspective, the (a)(1), (a)(2) or (a)(3) water is the downstream affected water whose quality is dependent on the condition of the contributing upstream waters, including streams, lakes, and

wetlands. To restore or maintain the health of the downstream affected water, it is standard practice to evaluate the condition of the waters that are in the contributing watersheds and to develop a plan to address

the issues of concern. The functions of the contributing waters are inextricably linked and have a cumulative effect on the integrity of the downstream traditional navigable water, interstate water or territorial sea. The size of that watershed can be determined by identifying the geographic area that drains to the nearest traditional navigable water, interstate water or the territorial seas, and then using that point of entry watershed to conduct a significant nexus evaluation. P.E. Black, ‘‘Watershed Functions,’’Journal of the

American Water Resources Association 33.1:1–11 (1997).

The Corps is organized based on

watersheds and has used watershed framework approaches for water sources, navigation approaches for over 100 years, and in the regulatory program since its inception. Also, using a watershed

framework is consistent with over two decades of practice by EPA and many other governmental, academic, and other entities which recognize that a watershed approach

is the most effective framework to address water resource challenges. U.S. Environmental Protection Agency, The


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Watershed Protection Approach Framework (Oct. 1991). The agencies both recognize the importance of the watershed approach by investing in opportunities to advance watershed protection and in developing

useful watershed tools and services. For example, EPA is allowing states that are reorganizing programs to function on a watershed basis to have short-term backlogs

on CWA section 402 National Pollution Discharge Elimination System (NPDES) permit review—without penalty. This flexibility gives states time to synchronize the reissuance of major and minor permits within a watershed. By managing NPDES permits on a watershed basis, all the permits for discharges to the water body can be

coordinated and the most efficient and equitable allocation of pollution control responsibility can be made. U.S. Environmental Protection Agency, Why Watersheds?, EPA 800–F–96–001 (February 1996). Applying a watershed approach continues to be a priority of EPA, and is one of the three key strategies the agency is using to drive progress toward the Agency’s health and environmental goals over the next five years. U.S Environmental Protection Agency, FY 2011–2015 Strategic Plan: Achieving Our

Vision, 2010.

B. Similarly Situated

Scientists routinely aggregate the effects of groups of waters, multiplying the known effect of one water by the number of similar waters in a specific geographic area, or to a

certain scale. This kind of functional aggregation of non-adjacent (and other types of waters) is well-supported in the scientific

literature. See, e.g., R.J. Stevenson and F.R. Hauer, ‘‘Integrating Hydrogeomorphic and Index of Biotic Integrity Approaches for Environmental Assessment of Wetlands,’’ Journal of the North American Benthological Society 21(3): 502–513 (2002); S.G. Leibowitz, ‘‘Isolated Wetlands and Their Functions: An Ecological Perspective,’’

Wetlands 23:517–531 (2003); D. Gamble, et al., An Ecological and Functional Assessment of Urban Wetlands in Central Ohio, Ohio EPA Technical Report WET/ 2007–3B (Columbus, OH: Ohio Environmental Protection Agency, 2007); C.R. Lane and E. D’Amico, ‘‘Calculating the Ecosystem Service of Water Storage in Isolated Wetlands using LiDAR in North Central Florida, USA,’’ Wetlands 30:967–977 (2010); B.P. Wilcox, et al., ‘‘Evidence of Surface Connectivity for Texas Gulf Coast Depressional Wetlands,’’ Wetlands 31(3):451–8 (2011). Similarly, streams and rivers are routinely aggregated by scientists to

estimate their combined effect on

downstream waters in the same watershed. This is because chemical, physical, or biological integrity of downstream waters is directly related to the aggregate contribution of upstream waters that flow into them, including any tributaries and connected wetlands. As a result, the scientific literature and the Report consistently documents that the health of larger downstream waters is directly related to the aggregate health of waters located upstream, including waters such as wetlands that may not be hydrologically connected but function together to prevent floodwaters and contaminants from reaching downstream

waters.

In the aggregate, similarly situated wetlands may have significant effects on the quality of water many miles away, particularly in circumstances where numerous similarly situated waters are located in the region and are performing like

functions that combine to influence

downstream waters. See, e.g., A. Jansson et al., ‘‘Quantifying the Nitrogen RetentionCapacity of Natural Wetlands in the LargeScale Drainage Basin of the Baltic Sea,’’ Landscape Ecology 13:249–262 (1998); W.J.

Mitsch et al., ‘‘Reducing Nitrogen Loading to the Gulf of Mexico from the Mississippi River Basin: Strategies to Counter a Persistent Ecological Problem,’’ BioScience 51(5): 373– 388 (2001); M.G. Forbes, et al., ‘‘Nutrient Transformation and Retention by Coastal Prairie Wetlands, Upper Gulf Coast, Texas,’’

Wetlands 32(4):705–15 (2012). Cumulatively, many small wetlands can hold a large amount of snowmelt and precipitation, reducing the likelihood of flooding downstream. Report at 5–25 (citing D.E. Hubbard and R.L. Linder, ‘‘Spring Runoff Retention in Prairie Pothole Wetlands,’’ Journal of Soil and Water Conservation 41(2):122–125 (1986)).

Scientists can and do routinely classify similar waters and wetlands into groups for a number of different reasons; because of their inherent physical characteristics, because they provide similar functions, because they were formed by similar geomorphic processes, and by their level of biological diversity, for example. Classifying

wetlands based on their functions is also the basis for the U.S. Army Corps of Engineers hydrogeomorphic (HGM) classification of wetlands. M.M. Brinson, A Hydrogeomorphic Classification for Wetlands (Washington, D.C.: U.S. Army Corps of Engineers, 1993).

The HGM method is a wetlands assessment approach pioneered by the Corps in the 1990s, and extensively applied via regional handbooks since then. The Corps HGM method uses a conceptual framework for identifying broad wetland classes based on common structural and functional features, which includes a method for using local

attributes to further subdivide the broad classes into regional subclasses. Assessment methods like the HGM provide a basis for determining if waters provide similar

functions based on their structural attributes and indicator species. Scientists also directly measure attributes and processes taking place in particular types of waters during in-depth field studies that provide reference information that informs the understanding of the functions performed by many types of aquatic systems nationwide.

These waters, primarily depressional wetlands, small open waters and peatlands, are known to have important hydrologic, water quality, and habitat functions which vary as a result of the diverse settings in which they exist across the country. For example, a report that reviewed the results of multiple scientific studies concluded that depressional wetlands lacking a surface outlet functioned together to significantly reduce or attenuate flooding. Report at 5–26 (citing A. Bullock and M. Acreman, ‘‘The Role of Wetlands in the Hydrological Cycle,’’ Hydrology and Earth System Sciences 7:358– 389 (2003)). Some of the important factors which influence the variability of their functions and connectivity include the topography, geology, soil features, antecedent moisture conditions, and seasonal position of the water table relative to the wetland. Report

at 5–25.

When proposing that ‘‘other waters’’ are sufficiently close and should be considered similarly situated, it is recognized that they are more likely to have similar influence with regard to their effect on the chemical, physical, or biological integrity of a downstream water identified in paragraphs (a)(1) through (a)(3). If a water is a great distance from a group of similar ‘‘other waters,’’ it may be performing some of the same functions as those in the group, but

their distance from each other or from downstream (a)(1) through (a)(3) waters will decrease the probability that it has some kind of chemical, physical, or biological connectivity to the downstream water, assuming that conditions governing the type and quantity of flows (e.g. slope, soil, and aquifer permeability, etc.) are similar. Id. at

5–2, 5–41.

Consideration of the aggregate effects of wetlands and other waters often gives the most complete information about how such waters influence the chemical, physical, or biological integrity of downstream waters. In many watersheds, wetlands have a disproportionate effect on water quality

relative to their surface area because wetland plants slow down water flow, allowing suspended sediments, nutrients, and pollutants to settle out. They filter these materials out of the water received from large areas, absorbing or processing them, and then releasing higher quality water. National Research Council, Wetlands: Characteristics

and Boundaries (Washington, D.C.: National Academy Press, 1995), p. 38. For an individual wetland, this is most pronounced where it lies immediately upstream of a drinking water intake, for example. See, e.g., C.A. Johnston, et al., ‘‘The Cumulative Effect of Wetlands on Stream Water Quality and Quantity,’’ Biogeochemistry 10:105–141 (1990).

The structure and function of a river are highly dependent on the constituent materials that are stored in, or transported through the river. Most of the materials found in rivers originate outside of them. Thus, the fundamental way that ‘‘other waters’’ are able to affect river structure and function is by providing or altering the materials delivered to the river. Report at 1–13. Since the alteration of material fluxes depends on the functions within these waters and the degree of connectivity, it is appropriate to consider both these factors for purposes of significant nexus under this provision.

Numerous factors affect chemical, physical, and biological connectivity, operating at multiple spatial and temporal scales, and interacting with each other in complex ways, to determine where components of aquatic systems fall on the connectivity-isolation gradient at a given time. Some of these factors include climate, watershed characteristics, spatial distribution


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patterns, biota, and human activities and

alterations. Id. at 3–33. Recognizing the limits on the ability to observe or document all of these interacting factors, it is reasonable to look for visible patterns in the landscape

and waters that are often indicative of the connectivity factors, in determining what waters to aggregate. Due to relative similarity of soils, topography, or groundwater connections, for example, there may be a group of wetlands scattered throughout a watershed, at similar distances from the tributaries in the watershed and performing similar functions. It is appropriate to assess the significance of the nexus of those waters in the aggregate, consistent with Justice Kennedy’s standard.

C. Significant Nexus

The scientific literature regarding ‘‘other waters’’ documents their functions, including the chemical, physical, and biological impact they can have downstream. Available

literature indicates that ‘‘other waters’’ have important hydrologic, water quality, and habitat functions that have the ability to

affect downstream waters if and when a

connection exists between the ‘‘other water’’ and downstream waters. Report at 6–1. ‘‘Other waters’’ generally fit into the category

of unidirectional waters as described in the Report. However, there are some unidirectional waters that are in fact adjacent under (a)(6) to (a)(1) through (a)(5) waters (e.g., neighboring waters that are outside of the riparian area and/or floodplain but that

have a surface or shallow subsurface hydrologic connection to (a)(1) through (a)(5) waters). Connectivity of ‘‘other waters’’ to

downstream waters that do not meet the definition of adjacent will vary within a watershed and over time, which is why a case-specific significant nexus determination for ‘‘other waters’’ is necessary under (a)(7). See, e.g., id. at 6–2. The types of chemical, physical, and biological connections between

‘‘other waters’’ and downstream waters are described below for illustrative purposes. As described in the preamble above, when the agencies are conducting a case-specific determination for significant nexus under (a)(7), they examine the connections between the water (including any similarly situated waters in the region) and downstream waters

and determine if those connections significantly affect the chemical, physical, or biological integrity of the downstream water, using any available site-information and field observations where available, relevant scientific studies or data, or other relevant jurisdictional determinations that have been made on similar resources in the region.

The hydrologic connectivity of ‘‘other

waters’’ to downstream waters occurs on a gradient and can include waters that have groundwater or occasional surface water connections (through overland flow) to the tributary network and waters that have no hydrologic connection to the tributary

network. Id. at 5–1. The connectivity of

‘‘other waters’’ to downstream waters will vary within a watershed as a function of local factors (e.g. position, topography, and soil characteristics). Id. at 3–41 to 3–43. Connectivity also varies over time, as the tributary network and water table expand and contract in response to local climate. Id. at 3–31 to 3–33. Lack of connection does not necessarily translate to lack of impact; even when lacking connectivity, waters can still impact chemical, physical, and biological

conditions downstream. Id. at 3–29, 3–31.

The physical effect that ‘‘other waters’’

have downstream is less obvious than the physical connections of waters that are adjacent or waters that are tributary, due to the physical distance of ‘‘other waters’’ from the stream network. Despite this physical distance, they are frequently connected in some degree through either surface water or groundwater systems; over time, impacts in one part of the hydrologic system will be felt in other parts. T.C. Winter and J.W. LaBaugh, ‘‘Hydrologic Considerations in Defining Isolated Wetlands,’’ Wetlands 23:532–540 (2003) at 538. For example, ‘‘other waters’’ that overspill into downstream water bodies during times of abundant precipitation are connected over the long term. Id. at 539. Wetlands that lack surface connectivity in a particular season or year can, nonetheless, be highly connected in wetter seasons or years. Report at 5–22 to 5–25. Many ‘‘other waters’’ interact with groundwater, either by receiving groundwater discharge (flow of groundwater to the ‘‘other water’’), contributing to groundwater recharge (flow of

water from the ‘‘other water’’ to the groundwater), or both. Id. at 5–23 (citing R.F. Lide, et al., ‘‘Hydrology of a Carolina Bay Located on the Upper Coastal Plain of Western South Carolina,’’ Wetlands 15:47–57 (1995); K.J. Devito, et al., ‘‘Groundwater

Surface-Water Interactions in Headwater Forested Wetlands of the Canadian Shield,’’ Journal of Hydrology 181:127–47 (1996); R.K. Matheney and P.J. Gerla, ‘‘Environmental Isotopic Evidence for the Origins of Ground and Surface Water in a Prairie Discharge Wetland,’’ Wetlands 16:109–120 (1996); D.O. Rosenberry and T.C. Winter, ‘‘Dynamics of Water-Table Fluctuations in an Upland

between Two Prairie-Pothole Wetlands in North Dakota,’’ Journal of Hydrology 191:266–289 (1997); J.E. Pyzoha, et al., ‘‘A Conceptual Hydrologic Model for a Forested Carolina Bay Depressional Wetland on the Coastal Plain of South Carolina, USA,’’ Hydrological Processes 22:2689–2698 (2008)). Factors that determine whether a water recharges groundwater or is a site of groundwater discharge include topography, geology, soil features, and seasonal position

of the water table relative to the water. Id. at 5–24 (citing P.J. Phillips and R.J. Shedlock, ‘‘Hydrology and Chemistry of Groundwater

and Seasonal Ponds in the Atlantic CoastalPlain in Delaware, USA,’’ Journal of Hydrology 141:157–78 (1993); R.J. Shedlock, et al., ‘‘Interactions between Ground-Waterand Wetlands, Southern Shore of LakeMichigan, USA,’’ Journal of Hydrology 141:127–55 (1993); D.O. Rosenberry and T.C. Winter, ‘‘Dynamics of Water-Table Fluctuations in an Upland Between two Prairie-Pothole Wetlands in North Dakota,’’ Journal of Hydrology 191:266–89 (1997); J.E. Pyzoha, et al., ‘‘A Conceptual Hydrologic Model for a Forested Carolina Bay Depressional Wetland on the Coastal Plain of South Carolina, USA,’’ Hydrological

Processes 22: 2689–98 (2008)). Similarly, the magnitude and transit time of groundwater flow from an ‘‘other water’’ to downstream waters depend on several factors, including the intervening distance and the properties of

the rock or unconsolidated sediments between the water bodies (i.e., the hydraulic conductivity of the material). Id. at 5–24. Surface and groundwater hydrological connections are those generating the capacity

for ‘‘other waters’’ to affect downstream waters, as water from the ‘‘other water’’ may contribute to baseflow or stormflow through groundwater recharge. Id. at 5–25. Contributions to baseflow are important for maintaining conditions that support aquatic

life in downstream waters. As discussed further below, even in cases where waters lack a connection to downstream waters, they can influence downstream water through water storage and mitigation of peak flows.

Id. at 5–36.

The chemical effects that ‘‘other waters’’

have on downstream waters are linked to their hydrologic connection downstream, though a surface connection is not needed for a water to influence the chemical integrity of the downstream water. Because the majority of ‘‘other waters’’ are hydrologically

connected to downstream waters via surface or groundwater connections, most ‘‘other waters’’ can affect water quality downstream (although these connections do not meet the definition of adjacency). D.F. Whigham and T. E. Jordan, ‘‘Isolated Wetlands and Water Quality,’’ Wetlands 23:541–549 (2003) at 542.

‘‘Other waters’’ can act as sinks and transformers for nitrogen and phosphorus, metals, pesticides, and other contaminants that could otherwise negatively impact downstream waters. Report at 5–30 (citing R.R. Brooks, et al., ‘‘Cobalt and Nickel Uptake by the Nyssaceae,’’ Taxon 26:197–201 (1977); H.F. Hemond, ‘‘Biogeochemistry of Thoreau’s Bog, Concord, Massachusetts,’’ Ecological Monographs 50:507–526 (1980);

C.B. Davis, et al., ‘‘Prairie Pothole Marshes as Traps for Nitrogen and Phosphorus in Agricultural Runoff,’’ in B. Richardson, ed., Selected Proceedings of the Midwest Conference on Wetland Values and Management, June 17–19, 1981, St. Paul, MN, (St. Paul, MN: The Freshwater Society, 1981), pp. 153–163; H.F. Hemond, ‘‘The Nitrogen Budget of Thoreau’s Bog,’’ Ecology 64:99–109 (1983); K.C. Ewel and H.T. Odum, ed., Cypress Swamps, (Gainesville, Florida: University of Florida Press, 1984); J.T.Moraghan, ‘‘Loss and Assimilation of 15Nnitrate Added to a North Dakota Cattail Marsh,’’ Aquatic Botany46:225–234 (1993);

C.M. Kao, et al., ‘‘Non-point Source Pesticide Removal by a Mountainous Wetland,’’ Water Science and Technology46:199–206 (2002); P.I. Boon, ‘‘Biogeochemistry and Bacterial Ecology of Hydrologically Dynamic Wetlands,’’ in D.P. Batzer and R.R. Sharitz, ed., Ecology of Freshwater and Estuarine

Wetlands (Berkeley, CA: University of California Press, 2006), pp. 115–176; E.J.

Dunne, et al., ‘‘Phosphorus Release and Retention by Soils of Natural Isolated Wetlands,’’ International Journal of

Environment and Pollution 28:496–516 (2006); T.E. Jordan, et al., ‘‘Comparing

Functional Assessments of Wetlands to

Measurements of Soil Characteristics and Nitrogen Processing,’’ Wetlands 27:479–497


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(2007); S.L. Whitmire and S.K. Hamilton,

‘‘Rates of Anaerobic Microbial Metabolism in Wetlands of Divergent Hydrology on a Glacial Landscape,’’ Wetlands 28:703–714 (2008)). Also see, e.g., T.M. Isenhart, Transformation and Fate of Nitrate in Northern Prairie Wetlands, Ph.D. Dissertation (Ames, Iowa: Iowa State University, 1992). The body of published scientific literature and the Report indicate that sink removal of nutrients and other pollutants by ‘‘other waters’’ is significant and geographically widespread. Report at 5–30. Water quality characteristics of ‘‘other waters’’ are highly variable, depending primarily on the sources of water, characteristics of the substrate, and

land uses within the watershed. D.F. Whigham and T.E. Jordan, ‘‘Isolated Wetlands and Water Quality,’’ Wetlands 23:541–549 (2003) at 541. These variables

inform whether an ‘‘other water’’ has a significant nexus to an (a)(1) through (a)(3) water. For instance, some prairie potholes may improve water quality and may efficiently retain nutrients that might otherwise cause water quality problems downstream; in such systems it may be their lack of a direct hydrologic connection that enables the prairie potholes to more effectively retain nutrients. Id. at 543.

‘‘Other waters’’ can be biologically

connected to each other and to downstream waters through the movement of seeds, macroinvertebrates, amphibians, reptiles, birds, and mammals. Report at 5–31 to 5–33; S.G. Leibowitz, ‘‘Isolated Wetlands and Their Functions: An Ecological Perspective,’’

Wetlands 23:517–531 (2003) at 519. The movement of organisms between ‘‘other waters’’ and downstream waters is governed by many of the same factors that affect movement of organisms between adjacent wetlands and downstream waters (See Part II Section 2.A.d.). Report at 5–31. Generally, ‘‘other waters’’ are further away from stream channels than adjacent waters, making hydrologic connectivity less frequent, and increasing the number and variety of landscape barriers over which organisms must disperse. Id. Plants, though non-mobile, have evolved many adaptations to achieve dispersal over a variety of distances, including water-borne dispersal during periodic hydrologic connections, ‘‘hitchhiking’’ on or inside highly mobile animals, and more typically via wind dispersal of seeds and/or pollen. Id. at 5–31 (citing S.M. Galatowitsch and A.G. van der Valk, ‘‘The Vegetation of Restored and Natural Prairie Wetlands,’’Ecological Applications 6:102–112 (1996); H.R. Murkin and P.J. Caldwell, ‘‘Avian Use of Prairie Wetlands,’’ in H.R. Murkin, et al., ed., Prairie Wetland Ecology: The Contribution of the Marsh Ecology Research Program, (Ames, IA: Iowa State University Press, 2000), pp. 249– 286; J.M. Amezaga, et al., ‘‘Biotic Wetland Connectivity—Supporting a New Approach for Wetland Policy,’’ Acta OecologicaInternational Journal of Ecology 23:213–222 (2002); J. Figuerola and A.J. Green, ‘‘Dispersal of Aquatic Organisms by Waterbirds: a

Review of Past Research and Priorities for Future Studies,’’ Freshwater Biology47:483– 494 (2002); M.B. Soons and G.W. Heil, ‘‘Reduced Colonization Capacity in Fragmented Populations of Wind-Dispersed Grassland Forbs,’’ Journal of Ecology 90:1033–1043 (2002); M.B. Soons, ‘‘Wind Dispersal in Freshwater Wetlands: Knowledge for Conservation and
Restoration,’’ Applied Vegetation Science 9:271–278 (2006); C. Nilsson, et al., ‘‘The Role of Hydrochory in Structuring Riparian and Wetland Vegetation,’’ Biological Reviews 85:837–858 (2010)). Mammals that disperse overland can also contribute to connectivity and can act as transport vectors for hitchhikers such as algae. Id. at 5–32 (citing C.E. Shanks and G.C. Arthur, ‘‘Muskrat Movements and Population Dynamics in Missouri Farm Ponds and Streams,’’ Journal of Wildlife Management 16:138–148 (1952); J.P. Roscher, ‘‘Alga Dispersal by Muskrat Intestinal Contents,’’ Transactions of the American Microscopical Society 86:497–498 (1967); W.R. Clark, ‘‘Ecology of Muskrats in Prairie Wetlands,’’ in H. R. Murkin, et al., ed., 2000, pp. 287–313)). Invertebrates also utilize birds and mamals to hitchhike, and these hitchhikers can be an important factor structuring invertebrate metapopulations in ‘‘other waters’’ and in aquatic habitats separated by hundreds of kilometers. Id. (citing J. Figuerola and A.J. Green, ‘‘Dispersal of Aquatic Organisms by Waterbirds: A

Review of Past Research and Priorities for Future Studies,’’ Freshwater Biology47:483– 494 (2002); J. Figuerola, et al., ‘‘InvertebrateEggs Can Fly: Evidence of WaterfowlMediated Gene Flow in Aquatic Invertebrates,’’ American Naturalist 165:274– 280 (2005); M.R. Allen, ‘‘Measuring and Modeling Dispersal of Adult Zooplankton,’’ Oecologia 153:135–143 (2007); D. Frisch, et al., ‘‘High Dispersal Capacity of a Broad Spectrum of Aquatic Invertebrates Via Waterbirds,’’ Aquatic Sciences 69:568–574 (2007)). Numerous flight-capable insects use both ‘‘other waters’’ and downstream waters; these insects move outside the tributary

network to find suitable habitat for overwintering, refuge from adverse conditions, hunting, foraging, or breeding, and then can return back to the tributary network for other lifecycle needs. Id. at 5–33 (citing D.D. Williams, ‘‘Environmental Constraints in Temporary Fresh Waters and Their Consequences for the Insect Fauna,’’ Journal of the North American Benthological Society 15:634–650 (1996); A.J. Bohonak and D.G. Jenkins, ‘‘Ecological and Evolutionary Significance of Dispersal by Freshwater Invertebrates,’’ Ecology Letters 6:783–796 (2003)). Amphibians and reptiles also move

between ‘‘other waters’’ and downstream waters to satisfy part of their life history requirements. Id. at 5–33. Alligators in the Southeast, for instance, can move from tributaries to shallow, seasonal limesink wetlands for nesting, and also use thesewetlands as nurseries for juveniles; subadults then shift back to the tributary network through overland movements. Id. (citing A.L. Subalusky, et al., ‘‘Ontogenetic Niche Shifts in the American Alligator Establish Functional Connectivity between Aquatic Systems,’’ Biological Conservation 142:1507–1514 (2009); A.L. Subalusky, et al., ‘‘Detection of American Alligators in Isolated, Seasonal Wetlands,’’ Applied Herpetology 6:199–210 (2009)). Similarly, amphibians and small reptile species, such as frogs, toads, and newts, commonly use both tributaries and ‘‘other waters,’’ during one or more stages of their life cycle, and can at times disperse over long distances. Id. (citing V.S. Lamoureux and D.M. Madison, ‘‘Overwintering Habitats of Radio-Implanted Green Frogs, Rana clamitans,’’ Journal of Herpetology 33:430–435 (1999); K.J. Babbitt, et al., ‘‘Patterns of Larval Amphibian Distribution along a Wetland Hydroperiod Gradient,’’ Canadian Journal of ZoologyRevue Canadienne De Zoologie 81:1539– 1552 (2003); S.B. Adams, et al., ‘‘Instream Movements by Boreal Toads (Bufo boreas

boreas),’’ Herpetological Review 36:27–33 (2005); D.M. Green, ‘‘Bufo americanus, American Toad,’’ in M. Lannoo, ed., Amphibian Declines: The Conservation Status of the United States Species (Berkeley, CA: University of California Press, 2005), pp. 692–704; T.W. Hunsinger and M. J. Lannoo,

‘‘Notophthalmus viridescens, Eastern Newt,’’

in M. Lannoo, ed., 2005, pp. 912–914; J.W. Petranka and C.T. Holbrook, ‘‘Wetland Restoration for Amphibians: Should Local Sites Be Designed to Support Metapopulations or Patchy Populations?,’’ Restoration Ecology 14:404–411 (2006)).

Even when a surface or groundwater hydrologic connection between a water and a downstream water is visibly absent, many waters still have the ability to substantially influence the integrity of downstream waters. However, such circumstances would be

uncommon. Id. at 5–22 to 5–25. Aquatic systems that may seem disconnected hydrologically are often connected but at irregular timeframes or through subsurface flow, and perform important functions that can be vital to the chemical, physical, or biological integrity of downstream waters. Some wetlands that are not adjacent may be hydrologically disconnected most of the time but connected to the stream network during rare high-flow events. The lack of a hydrologic connection also allows for water storage in ‘‘other waters,’’ attenuating peak streamflows, and, thus, downstream flooding, and also reducing nutrient and soil pollution in downstream waters. Report at 5–25 to 5– 26, 5–36. Prairie potholes a great distance from any tributary, for example, are thought to store significant amounts of runoff. Id. at 5–36 (citing R.P. Novitzki, ‘‘Hydrologic

Characteristics of Wisconsin’s Wetlands and Their Influence on Floods,’’ in P. Greeson, et al., ed., Wetland Functions and Values: The Status of Our Understanding, Proceedings of the National Symposium on Wetlands (Minneapolis, MN: American Water Resources Association, 1979), pp. 377–388; D.E. Hubbard and R.L. Linder, ‘‘Spring

Runoff Retention in Prairie Pothole Wetlands,’’Journal of Soil and Water

Conservation 41:122–125 (1986); J. Jacques and D.L. Lorenz, ‘‘Techniques for Estimating the Magnitude and Frequency of Floods in

Minnesota,’’ Water Resources Investigations Report 87–4170, (St. Paul, MN: U.S. Geological Survey, 1988); K.C. Vining,

‘‘Simulation of Streamflow and Wetland Storage, Starkweather Coulee Subbasin, North Dakota, Water Years 1981–98,’’ WaterResources Investigations Report 02–4113 (Bismarck, North Dakota: U.S. Geological


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Survey, 2002); R.A. Gleason, et al., Estimating Water Storage Capacity of Existing and Potentially Restorable Wetland Depressions in a Subbasin of the Red River of the North, U.S. Geological Survey OpenFile Report 2007–1159 (Reston, VA: U.S. Geological Survey, 2007); D.L. Lorenz, et al., ‘‘Techniques for Estimating the Magnitude and Frequency of Peak Flows on Small Streams in Minnesota Based on Through

Water Year 2005,’’ USGS Scientific Investigations Report 2009–5250, (Reston, VA: U.S. Geological Survey, 2010)). Filling wetlands reduces water storage capacity in the landscape and causes runoff from rainstorms to overwhelm the remaining available water conveyance system. See, e.g., C.A. Johnston, et al., ‘‘The Cumulative Effect of Wetlands on Stream Water Quality and Quantity,’’ Biogeochemistry 10:105–141 (1990); A.L. Moscrip and D.R. Montgomery, ‘‘Urbanization, Flood Frequency, and Salmon Abundance in Puget Lowland Streams,’’ Journal of the American Water Resources

Association 33:1289–1297 (1997); N.E. Detenbeck, et al., ‘‘Evaluating Perturbations and Developing Restoration Strategies for Inland Wetlands in the Great Lakes Basin,’’

Wetlands 19(4): 789–820 (1999); N.E. Beck, et al., ‘‘Relationship of Stream Flow Regime in the Western Lake Superior Basin to Watershed Type Characteristics,’’ Journal of Hydrology 309(1–4): 258–276 (2005). Wetlands, even when lacking a hydrologic connection downstream, improve downstream water quality by accumulating nutrients, trapping sediments, and transforming a variety of substances. See,

e.g., National Research Council, Wetlands:

Characteristics and Boundaries (Washington, DC: National Academy Press, 1995), p. 38.

Under today’s proposal, on a case-specific basis, ‘‘other waters’’ that have a significant nexus to an (a)(1) through (a)(3) water are ‘‘waters of the United States’’ under (a)(7).

The scientific literature and data in the Report and elsewhere support that some ‘‘other waters’’ (including some of those in the case studies), along with other similarly situated waters in the region, do greatly affect the chemical, physical, or biological integrity of (a)(1) through (a)(3) waters, and thus would be jurisdictional under (a)(7).

Though much of the literature cited in the Report relates to ‘‘other waters’’ that arewetlands, the Report indicates that nonwetland waters that are not (a)(1) through (a)(6) waters also can have chemical, physical, or biological connections that significantly impact downstream waters. For instance, non-adjacent ponds or lakes that are not part of the tributary network can still be connected to downstream waters through chemical, physical, and biological connections. Lake storage has been found to attenuate peak streamflows in Minnesota. Id. at 5–25 (citing J. Jacques and D.L. Lorenz, Techniques for Estimating the Magnitude and Frequency of Floods of Ungauged

Streams in Minnesota, USGS WaterResources Investigations Report 84–4170 (Washington, DC: U.S. Geological Survey, 1988); D.L. Lorenz, et al., Techniques for Estimating the Magnitude and Frequency of

Peak Flows on Small Streams in Minnesota Based on Data through Water Year 2005, U.S. Geological Survey Scientific Investigations Report 2009–5250 (Reston, VA: U.S. Geological Survey, 2010)). Similar to wetlands, ponds are often used by invertebrate, reptile, and amphibian species

that also utilized downstream waters for various life history requirements, particularly because many ponds, particularly temporary ponds, are free of predators, such as fish, that prey on larvae. The American toad and Eastern newt are widespread habitat generalists that can move among streams, wetlands, and ponds to take advantage of each aquatic habitat, feeding on aquatic invertebrate prey, and avoiding predators.
See, e.g., Id. at 5–33 (citing K.J. Babbitt et al., ‘‘Patterns of Larval Amphibian Distribution along a Wetland Hydroperiod Gradient,’’ Canadian Journal of Zoology-Revue Canadienne De Zoologie 81:1539–1552 (2003); D.M. Green, ‘‘Bufo americanus, American Toad,’’ in M. Lannoo, ed., Amphibian Declines: The Conservation Status of United States Species, (Berkeley, CA: University of California Press, 2005), pp. 692–704; T.W. Hunsinger and M.J. Lannoo,

‘‘Notophthalmus viridescens, Eastern Newt,’’

in M. Lannoo, ed., Amphibian Declines: The Conservation Status of United States Species, (Berkeley, CA: University of California Press, 2005), pp. 912–914; J.W. Petranka and C.T. Holbrook, ‘‘Wetland Restoration for Amphibians: Should Local Sites Be Designed to Support Metapopulations or Patchy Populations?,’’ Restoration Ecology 14:404– 411 (2006)). Additionally, stream networks that are not part of the tributary system (e.g., streams in closed basins without an (a)(1) through (a)(3) water or losing streams and

other streams that cease to flow before reaching downstream (a)(1) through (a)(3) waters) may likewise have a significant impact on the chemical, physical, or biological integrity of downstream waters. Non-tributary streams may be connected via groundwater to downstream waters. Such streams may also provide habitat to insect, amphibian, and reptile species that also use the tributary network.

i. Additional Request for Public Comment on

‘‘Other Waters’’

The agencies are considering whether to determine by rule that prairie potholes, Carolina and Delmarva bays, pocosins, Texas coastal prairie wetlands, western vernal pools, and perhaps other categories of waters,

either alone or in combination with ‘‘other waters’’ of the same type in a single point of entry watershed have a significant nexus and are jurisdictional. R.W. Tiner, ‘‘Geographically Isolated Wetlands of the United States,’’ Wetlands 23(3):494–516 (2003); M.G. Forbes, et al., ‘‘Nutrient Transformation and Retention by Coastal Prairie Wetlands, Upper Gulf Coast, Texas,’’ Wetlands 32(4): 705–715 (2012). These waters would not require a case-by-case analysis. At the same time, the agencies could determine by rule that playa lakes, and perhaps other categories of waters, do not have a significant nexus and are not jurisdictional. These waters would not be subject to a case-by-case analysis of significant nexus. As the science develops, the agencies may determine that additional categories of ‘‘other waters’’ have a significant nexus and are thus categorically jurisdictional. The specific categories of ‘‘other waters’’ for which there is currently evidence of a significant nexus are discussed

below:

a. Prairie potholes are a complex of glacially formed wetlands, usually occurring in depressions that lack permanent natural outlets, that are found in the central United States and Canada. Report at 5–57. The vast area they occupy is variable in many aspects, including climatically, topographically, geologically, and in terms of land use and alteration, which imparts variation on the potholes themselves. Prairie potholes demonstrate a wide range of hydrologic permanence, from holding permanent standing water to wetting only in years with high precipitation, which in turn influences the diversity and structure of their biological communities. Owing in large part to their spatial and temporal variability, individual prairie potholes span the entire continuum of connectivity to and isolation from the river

network and other bodies of water. Potholes generally accumulate and retain water effectively due to the low permeability of their underlying soil, which can modulate flow characteristics of nearby streams and

rivers. Potholes also can accumulate chemicals in overland flow, thereby reducing chemical loading to other bodies of water. When potholes are artificially connected to streams and lakes through drainage, isolation is eliminated and they become sources of water and chemicals. Potholes also support a community of highly mobile organisms, from plants to invertebrates that move among potholes and that can biologically connect the entire complex to the river network. Based on these connections and the strength of their effects, individually or in combination with other prairie potholes in the watershed, on the chemical, physical, or biological integrity of an (a)(1) through (a)(3) water, the agencies could conclude by rule that prairie potholes have a significant nexus and are jurisdictional. The agencies’ determination will be informed by the final version of the Report and other available

scientific information.

b. Carolina and Delmarva bays are ponded depressional wetlands that occur along the Atlantic coastal plain from northern Florida to New Jersey. Id. at 5–49. Most bays receive water through precipitation, lose water through evapotranspiration, and lack naturalsurface outlets. Both mineral-based and peatbased bays have shown connections to shallow groundwater. Bays typically are in proximity to each other or to open waters, providing the potential for surface water connections in large rain events via overland flow. Fish are reported in bays that are known to dry out, indirectly demonstrating surficial connections. Amphibians and reptiles use bays extensively for breeding and for rearing young. These animals can disperse many meters on the landscape and can colonize, or serve as a food source to, downstream waters. Similarly, bays foster abundant insects that have the potential to become part of the downstream food chain.

Humans have ditched and channelized a high percentage of bays, creating new surface connections to ‘‘other waters’’ and allowing


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transfer of nutrients, sediment, and other pollutants such as methylmercury. Based on these connections and the strength of their effects, individually or in combination with other Carolina or Delmarva bays in the watershed, on the chemical, physical, or biological integrity of an (a)(1) through (a)(3) water, the agencies could conclude by rule that Carolina and Delmarva bays have a significant nexus and are jurisdictional. The agencies’ determination will be informed by the final version of the Report and other

available scientific information.

c. Vernal pools are shallow, seasonal wetlands that accumulate water during colder, wetter months and gradually dry up during warmer, drier months. Id. at 5–66. Western vernal pools are seasonal wetlands associated with topographic depressions, soils with poor drainage, mild, wet winters and hot, dry summers in western North America from southeastern Oregon to northern Baja California, Mexico (Id. at 5–67, citing E.T. Bauder and S. McMillan, ‘‘Current

Distribution and Historical Extent of Vernal

Pools in Southern California and Northern Baja California, Mexico,’’ pp. 56–70 in C.W. Witham, et al., editors, Ecology, Conservation, and Management, 1998). Because their hydrology and ecology are so tightly coupled with the local and regional geological processes that formed them, western vernal pools typically occur within ‘‘vernal pool landscapes,’’ or complexes of pools in which swales connect pools to each other and to seasonal streams (Id. at 5–67 to 5–68, citing W.A. Weitkamp, et al.,‘‘Pedogenesis of a Vernal Pool EntisolAlfisol-Vertisol Catena in Southern California,’’ Soil Science Society of America Journal 60:316323 (1996); D.W. Smith and W.L. Verrill, ‘‘Vernal Pool-Soil-Landform Relationships in the Central Valley, California,’’ pp. 15–23 in C.W. Witham, et al., editors, Ecology, Conservation, and Management of Vernal Pool Ecosystems— Proceedings from a 1996 Conference (California Native Plant Society, Sacramento, CA,1998); M.C. Rains, et al., ‘‘The Role of Perched Aquifers in Hydrological Connectivity and Biogeochemical Processes in Vernal Pool Landscapes, Central Valley, California,’’ Hydrological Processes 20:1157– 1175 (2008)). Despite differences in geology, climate, and biological communities, some common findings about the hydrologic connectivity of vernal pools in different regions, including Western vernal pools, include evidence for temporary or permanent outlets, frequent filling and spilling of higher pools into lower elevation swales and stream channels, and conditions supporting subsurface flows through pools withoutperched aquifers to nearby streams. Nonglaciated vernal pools in western states are reservoirs of biodiversity and can be connected genetically to other locations andaquatic habitats through wind- and animalmediated dispersal. Based on these connections and the strength of their effects, individually or in combination with other western vernal pools in the watershed, on the chemical, physical, or biological integrity of an (a)(1) through (a)(3) water, the agencies could conclude by rule that western vernal pools have a significant nexus and are jurisdictional. The agencies’ determination will be informed by the final version of the Report and other available scientific information. The jurisdictional status of vernal pools located in other areas will be determined on a case-by-case significant nexus analysis with any similar situated waters in the single point of entry watershed. For example, insects and amphibians that can live in streams or permanent pools opportunistically use glaciated vernal pools

in the Northeast and Midwest as alternative breeding habitat, refuge from predators or environmental stressors, hunting or foraging habitat, or stepping-stone corridors for dispersal and migration.

d. The word pocosin comes from the Algonquin Native American word for ‘‘swamp on a hill,’’ and these evergreen shrub and tree dominated landscapes are found from Virginia to northern Florida, but mainly in North Carolina. (C.J. Richardson, ‘‘Pocosins: Hydrologically Isolated or Integrated Wetlands on the Landscape?,’’

Wetlands 23(3):563–576 (2003)). Usually, there is no standing water present in these peat-accumulating wetlands, but a shallow

water table leaves the soil saturated for much of the year. They range in size from less than

an acre to several thousand acres. The slow movement of water through the dense organic matter in pocosins removes excess nutrients deposited by rainwater. The same organic matter also acidifies the water. This pure water is slowly released to downstream waters and estuaries, where it helps to maintain the proper salinity, nutrients, and acidity. (Id.) Because pocosins are the topographic high areas on the regional landscape, they serve as the source of water

for downstream areas. Pocosins often have seasonal connections to drainageways leading to estuaries or are contiguous with other wetlands draining into perennial streams or estuaries. (R.W. Tiner, ‘‘Geographically Isolated Wetlands of the United States,’’ Wetlands 23(3):494–516 (2003)). Other pocosins have been ditched and are directly connected to streams. (Id.) The draining of pocosins and decreased salinity in estuaries may be having a negative effect on brown shrimp in North Carolina. (Id.) Based on these connections and the strength of their effects, individually or in combination with other pocosins in the watershed, on the chemical, physical, or biological integrity of an (a)(1) through (a)(3) water, the agencies could conclude by rule pocosins have a significant nexus and are jurisdictional. The agencies’ determination will be informed by the final version of the Report and other available scientific

information.

e. Along the Gulf of Mexico from western Louisiana to south Texas, freshwater wetlands occur as a mosaic of depressions, ridges, intermound flats, and mima mounds. (M.G. Forbes, et al., ‘‘Nutrient Transformation and Retention by Coastal Prairie Wetlands, Upper Gulf Coast, Texas,’’

Wetlands 32(4): 705–715 (2012)). These coastal prairie wetlands were formed thousands of years ago by ancient rivers and bayous and once occupied almost a third of the landscape around Galveston Bay, Texas. Texas coastal prairie wetlands are locally abundant and in close proximity to other coastal prairie wetlands and function together cumulatively. (N. Enwright, et al., ‘‘Using Geographic Information Systems (GIS) to Inventory Coastal Prairie Wetlands Along the Upper Gulf Coast, Texas,’’

Wetlands 31:687–697 (2011)). Collectively as a complex, Texas coastal prairie wetlands may be geographically and hydrologically

connected to each other via swales and connected to downstream waters, contributing flow to those downstream waters. (B.P. Wilcox, et al., ‘‘Evidence of Surface Connectivity for Texas Gulf Coast Depressional Wetlands,’’ Wetlands 31(3):451–458 (2011)). Cumulatively, these

wetlands can control nutrient release levels and rates to downstream waters, as they capture, store, transform and pulse releases of nutrients to those waters. (M.G. Forbes, et al., ‘‘Nutrient Transformation and Retention by Coastal Prairie Wetlands, Upper Gulf

Coast, Texas,’’ Wetlands 32(4): 705–715 (2012)). Based on these connections and the strength of their effects, individually or in combination with other coastal prairie wetlands in the watershed, on the chemical, physical, or biological integrity of an (a)(1) through (a)(3) water, the agencies could conclude by rule Texas coastal prairie wetlands have a significant nexus and are jurisdictional. The agencies’ determination will be informed by the final version of the Report and other available scientific

information.

The agencies could also conclude that playa lakes in the Great Plains even in combination with other playa lakes in a single point of entry watershed always lack a significant nexus and therefore are not jurisdictional. Playa lakes are round, shallow wetlands found primarily in the High Plains, a subregion of the Great Plains in the western and Midwestern United States. (D.A. Haukos, and L.M. Smith, ‘‘Past and Future Impacts of Wetland Regulations on Playas,’’ Wetlands 23(3):577–589 (2003); R.W. Tiner, ‘‘Geographically Isolated Wetlands of the United States,’’ Wetlands 23(3):494–516 (2003)). Each playa typically occurs within a closed or terminal watershed, where all water in the watershed drains to the playa. (D.A. Haukos, and L.M. Smith, ‘‘Past and Future Impacts of Wetland Regulations on Playas,’’

Wetlands 23(3):577–589 (2003)). As such, playas typically do not drain to an (a)(1) through (a)(3) water. Most playas are fed by precipitation and associated runoff, though a few are fed by groundwater. (R.W. Tiner, ‘‘Geographically Isolated Wetlands of the United States,’’ Wetlands 23(3):494–516 (2003)). Most playas fill with water only after spring rainstorms when freshwater collects in the round depressions of the otherwise flat landscape of west Texas, Oklahoma, New Mexico, Colorado, and Kansas. Although playas play a role in groundwater recharge of the Ogallala Aquifer, in local floodwater storage, and in provision of wildlife habitat,

available scientific literature indicates that their chemical, physical, or biological connections to and effects on (a)(1) through (a)(3) waters are of a limited and tenuous

nature.

The agencies seek comment, data, and

information on whether there are


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9 The 1972 legislation extensively amended the Federal Water Pollution Control Act (FWPCA), which was originally enacted in 1948. Further

amendments to the FWPCA enacted in 1977 acknowledged the popular name of the statute as
the Clean Water Act. See Public Law 95–217, 91

Stat. 1566; 33 U.S.C. 1251 note. subcategories of ‘‘other waters’’ or specific

combinations of characteristics that are ‘‘likely, in the majority of cases, to perform important functions for an aquatic ecosystem incorporating navigable waters,’’ and, thus,

should be per se jurisdictional. For example, if there are additional studies addressing the connectivity of prairie potholes in the Red River Valley, including the factors influencing that connectivity and how it is important to particular downstream waters,

that would be relevant information.



### Appendix B

Legal Analysis

Background

Congress enacted the Federal Water Pollution Control Act Amendments of 1972, Public Law 92–500, 86 Stat. 816, as amended, (33 U.S.C. 1251 et seq.) (Clean Water Act or CWA) ‘‘to restore and maintain the chemical, physical, and biological integrity of the Nation’s waters.’’ 33 U.S.C. 1251(a).9 The U.S. Supreme Court first addressed the scope of ‘‘waters of the United States’’ protected by

the CWA in United States v. Riverside Bayview Homes, 474 U.S. 121 (1985), which involved wetlands adjacent to a traditional navigable water in Michigan. In a unanimous opinion, the Court deferred to the Corps’ ecological judgment that adjacent wetlands are ‘‘inseparably bound up’’ with the waters to which they are adjacent, and upheld the inclusion of adjacent wetlands in the regulatory definition of ‘‘waters of the United

States.’’ Id. at 134. The Court observed that the broad objective of the CWA to restore and maintain the integrity of the Nation’s waters ‘‘incorporated a broad, systemic view of the goal of maintaining and improving water quality. . . . Protection of aquatic ecosystems, Congress recognized, demanded broad federal authority to control pollution, for ‘[w]ater moves in hydrologic cycles and it is essential that discharge of pollutants be controlled at the source.’ In keeping with these views, Congress chose to define the waters covered by the Act broadly.’’ Id. at 132–33 (citing Senate Report 92–414).

The issue of CWA jurisdiction over ‘‘waters of the United States’’ was addressed again by the Supreme Court in Solid Waste Agency of Northern Cook Countyv. U.S. Army Corps of Engineers, 531 U.S. 159 (2001) (SWANCC ). In
SWANCC, the Court (in a 5–4 opinion) held that the use of ‘‘isolated’’ nonnavigable intrastate ponds by migratory birds was not by itself a sufficient basis for the exercise of Federal regulatory authority under the CWA.

The SWANCC Court noted that in Riverside it had ‘‘found that Congress’ concern for the protection of water quality and aquatic ecosystems indicated its intent to regulate wetlands ‘inseparably bound up’ with the

‘waters of the United States’ ’’ and that ‘‘it was the significant nexus between the wetlands and ‘navigable waters’ that informed our reading of the CWA’’ in that case. Id. at 167. SWANCC did not invalidate (a)(3) or other parts of the regulatory

definition of ‘‘waters of the United States.’’

Five years after SWANCC, the Court again

addressed the CWA term ‘‘waters of the

United States’’ in Rapanos v. United States, 547 U.S. 715 (2006). Rapanos involved two

consolidated cases in which the CWA had been applied to wetlands adjacent to nonnavigable tributaries of traditional navigable waters. All Members of the Court agreed that the term ‘‘waters of the United States’’ encompasses some waters that are notnavigable in the traditional sense. A fourJustice plurality in Rapanos interpreted the

term ‘‘waters of the United States’’ as covering ‘‘relatively permanent, standing or continuously flowing bodies of water . . . ,’’

id. at 739, that are connected to traditional navigable waters, id. at 742, as well as

wetlands with a ‘‘continuous surface connection . . .’’ to such water bodies, id. (Scalia, J., plurality opinion). The Rapanos plurality noted that its reference to ‘‘relatively permanent’’ waters did ‘‘not necessarily exclude streams, rivers, or lakes that might dry up in extraordinary circumstances, such as drought,’’ or

‘‘seasonal rivers, which contain continuous flow during some months of the year but no flow during dry months . . . .’’ Id. at 732 n.5 (emphasis in original). Justice Kennedy’s concurring opinion took a different approach. Justice Kennedy concluded that ‘‘to constitute ‘navigable waters’ under the Act, a water or wetland must possess a ‘significant nexus’ to waters that are or were navigable in fact or that could reasonably be so made.’’

Id. at 759 (citing SWANCC, 531 U.S. at 167, 172). He concluded that wetlands possess the requisite significant nexus if the wetlands

‘‘either alone or in combination with similarly situated [wet]lands in the region, significantly affect the chemical, physical, and biological integrity of other covered waters more readily understood as ‘navigable.’ ’’ 547 U.S. at 780. Justice Kennedy’s opinion notes that such a relationship with navigable waters must be more than ‘‘speculative or insubstantial.’’ Id.

at 780. In Rapanos, the four dissenting Justices, who would have affirmed the court of appeals’ application of the pertinent regulatory provisions, concluded that the

term ‘‘waters of the United States’’ encompasses, inter alia, all tributaries and wetlands that satisfy either the plurality’s standard or that of Justice Kennedy. Id. at 810 & n.14 (Stevens, J., dissenting). Neither the plurality nor the Kennedy opinions invalidated any of the regulatory provisions defining ‘‘waters of the United States.’’

The Circuit Courts of Appeals are not uniform as to the controlling standard for

‘‘waters of the United States’’ under Rapanos. The First, Third and Eighth Circuits have concluded that CWA jurisdiction exists if either Justice Kennedy’s standard or the plurality’s standard is met. United States v. Johnson, 467 F.3d 56, 66 (1st Cir. 2006), cert. denied, 552 U.S. 948 (2007); U.S. v. Donovan, 661 F.3d. 174, 176 (3rd Cir. 2011), cert. denied, 132 S.Ct. 2409 (2012); U.S. v. Bailey, 571 F.3d 791, 798–99 (8th Cir. 2009). The

Seventh and Ninth Circuits limited their holdings that the Kennedy standard applied to the facts of the cases before them, and did not foreclose the possibility that in some cases the plurality’s standard might apply. N.

Cal. River Watch v. City of Healdsburg, 496 F.3d 993, 999–1000 (9th Cir. 2007), cert. denied, 552 U.S. 1180 (2008); United States

v. Gerke Excavating, Inc., 464 F.3d 723, 725 (7th Cir. 2006), cert. denied, 552 U.S. 810 (2007). The Fifth and Sixth Circuits did not choose a controlling standard because the

waters at issue satisfied both standards.

United States v. Lucas, 516 F.3d 316, 326– 27 (5th Cir. 2008), cert. denied, 555 U.S. 822 (2008); United States v. Cundiff, 555 F.3d 200, 210–13 (6th Cir. 2009), cert. denied, 558 U.S. 818 (2009). The Eleventh Circuit has held that only the Kennedy standard determines jurisdiction. United States v. Robison, 505 F.3d 1208 (11th Cir. 2007), cert.
denied sub nom United States v. McWane

and McWane v. United States, 555 U.S. 1045 (2008). No Circuit Court has held that only the plurality standard applies.

Traditional Navigable Waters

EPA and the Corps are proposing no changes to the existing regulation related to traditional navigable waters and at paragraph (a)(1) will continue to assert jurisdiction over all waters which are currently used, or were used in the past, or may be susceptible to use in interstate or foreign commerce, including all waters which are subject to the ebb and

flow of the tide. See e.g., 33 CFR 328.3(a)(1); 40 CFR 230.3(s)(1); 40 CFR 122.2 (‘‘waters of the U.S.’’)). These ‘‘(a)(1) waters’’ are the ‘‘traditional navigable waters.’’ These (a)(1)

waters include all of the waters defined in 33 CFR part 329, which implements sections 9 and 10 of the Rivers and Harbors Act, and by numerous decisions of the Federal courts,plus all other waters that are navigable-infact (e.g., the Great Salt Lake, UT and Lake Minnetonka, MN).

To determine whether a water body constitutes an (a)(1) water under the regulations, relevant considerations include Corps regulations, prior determinations by the Corps and by the Federal courts, and case law. Corps districts and EPA regions would determine whether a particular water body is a traditional navigable water based on application of those considerations to the specific facts in each case.

As noted above, the (a)(1) waters include, but are not limited to, waters that meet any of the tests set forth in 33 CFR part 329 (e.g., the water body is (a) subject to the ebb and flow of the tide, and/or (b) the water body is presently used, or has been used in the past, or may be susceptible for use (with or without reasonable improvements) to transport interstate or foreign commerce). The Corps districts have made determinations in the past under these regulations for purposes of asserting jurisdiction under sections 9 and 10 of the Rivers and Harbors Act of 1899 (33 U.S.C. 401 and 403). Pursuant to 33 CFR 329.16, the Corps maintains lists of final determinations of navigability for purposes of Corps jurisdiction under the Rivers and Harbors Act

of 1899. While absence from the list should

not be taken as an indication that the water is not navigable (§ 329.16(b)), Corps districts and EPA Regions rely on any final Corps


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determination that a water body meets any of the tests set forth in part 329.

If the Federal courts have determined that a water body is navigable-in-fact under Federal law for any purpose, that water body qualifies as a ‘‘traditional navigable water’’ subject to CWA jurisdiction under 33 CFR 328.3(a)(1) and 40 CFR 230.3(s)(1). Corps districts and EPA regions are guided by the relevant opinions of the Federal courts in determining whether such water bodies are ‘‘currently used, or were used in the past, or may be susceptible to use in interstate or foreign commerce’’ (33 CFR 328.3(a)(1); 40 CFR 230.3(s)(1)) or ‘‘navigable-in-fact.’’

The definition of ‘‘navigable-in-fact’’ derives from a long line of cases originating

with The Daniel Ball, 77 U.S. 557 (1870). The Supreme Court stated:
Those rivers must be regarded as public navigable rivers in law which are navigable in fact. And they are navigable in fact when they are used, or are susceptible of being used, in their ordinary condition, as highways for commerce, over which trade and travel are or may be conducted in the customary modes of trade and travel on

water.

The Daniel Ball, 77 U.S. at 563.

In The Montello, the Supreme Court clarified that ‘‘customary modes of trade and travel on water’’ encompasses more than just navigation by larger vessels:

The capability of use by the public for purposes of transportation and commerce affords the true criterion of the navigability of a river, rather than the extent and manner of that use. If it be capable in its natural state of being used for purposes of commerce, no matter in what mode the commerce may be conducted, it is navigable in fact, and becomes in law a public river or highway.

The Montello, 87 U.S. 430, 441–42 (1874). In that case, the Court held that early fur trading using canoes sufficiently showed that the Fox River was a navigable water of the United

States. The Court was careful to note that the bare fact of a water’s capacity for navigation alone is not sufficient; that capacity must be indicative of the water’s being ‘‘generally and commonly useful to some purpose of trade or agriculture.’’ Id. at 442.

In Economy Light & Power, the Supreme Court held that a waterway need not be continuously navigable; it is navigable even

if it has ‘‘occasional natural obstructions or portages’’ and even if it is not navigable ‘‘at all seasons . . . or at all stages of the water.’’ Economy Light & Power Co. v. U.S., 256 U.S. 113, 122 (1921).

In United States v. Holt State Bank, 270 U.S. 49 (1926), the Supreme Court summarized the law on navigability as of

1926 as follows:

The rule long since approved by this court in applying the Constitution and laws of the

United States is that streams or lakes which are navigable in fact must be regarded as navigable in law; that they are navigable in fact when they are used, or are susceptible of being used, in their natural and ordinary condition, as highways for commerce, over which trade and travel are or may be conducted in the customary modes of trade and travel on water; and further that navigability does not depend on the particular mode in which such use is or may be had—whether by steamboats, sailing

vessels or flatboats—nor on an absence of occasional difficulties in navigation, but on the fact, if it be a fact, that the stream in its natural and ordinary condition affords a

channel for useful commerce.

Holt State Bank, 270 U.S. at 56.

In U.S. v. Utah, 283 U.S. 64 (1931) and

U.S. v. Appalachian Elec. Power Co, 311 U.S. 377 (1940), the Supreme Court held that so long as a water is susceptible to use as a highway of commerce, it is navigable-in-fact, even if the water has never been used for any commercial purpose. U.S. v. Utah, at 81–83 (‘‘The question of that susceptibility in the ordinary condition of the rivers, rather than of the mere manner or extent of actual use, is the crucial question.’’); U.S. v. Appalachian Elec. Power Co., 311 U.S. at 416 (‘‘Nor is lack of commercial traffic a bar to a conclusion of navigability where personal or private use by boats demonstrates the availability of the stream for the simpler types of commercial navigation.’’) Appalachian Power further held that a water is navigable-in-fact even if it is not navigable and never has been but may become so by reasonable improvements. 311 U.S. at 407–

08.

In 1971, in Utah v. United States, 403 U.S. 9 (1971), the Supreme Court held that the Great Salt Lake, an intrastate water body, was navigable under Federal law even though it ‘‘is not part of a navigable interstate or international commercial highway.’’ Id. at 10. In doing so, the Supreme Court stated that the fact that the Lake was used for hauling of animals by ranchers rather than for the transportation of ‘‘water-borne freight’’ was

an ‘‘irrelevant detail.’’ Id. at 11. ‘‘The lake was used as a highway and that is the gist

of the federal test.’’ Id.

Most recently, the Supreme Court explained:

The Daniel Ball formulation has been invoked in considering the navigability of waters for purposes of assessing federal regulatory authority under the Constitution, and the application of specific federal statutes, as to the waters and their beds. See, e.g., ibid.; The Montello, 20 Wall. 430, 439, 22 L.Ed. 391 (1874); United States v. Appalachian Elec. Power Co., 311 U.S. 377, 406, and n. 21, 61 S.Ct. 291, 85 L.Ed. 243 (1940) (Federal Power Act); Rapanos v. United States, 547 U.S. 715, 730–731, 126 S.Ct. 2208, 165 L.Ed.2d 159 (2006) (plurality opinion) (Clean Water Act); id., at 761, 126 S.Ct. 2208 (KENNEDY, J., concurring in judgment) (same). It has been used as well to determine questions of title to water beds under the equal-footing doctrine. See Utah,

supra, at 76, 51 S.Ct. 438; Oklahoma v. Texas, 258 U.S. 574, 586, 42 S.Ct. 406, 66 L.Ed. 771 (1922); Holt State Bank, supra, at 56, 46 S.Ct. 197. It should be noted, however, that the test for navigability is not applied in the same way in these distinct types of cases.
Among the differences in application are thefollowing. For state title under the equalfooting doctrine, navigability is determined at the time of statehood, see Utah, supra, at 75, 51 S.Ct. 438, and based on the ‘‘natural and ordinary condition’’ of the water, see Oklahoma, supra, at 591, 42 S.Ct. 406. In contrast, admiralty jurisdiction extends to water routes made navigable even if not formerly so, see, e.g., Ex parte Boyer, 109 U.S. 629, 631–632, 3 S.Ct. 434, 27 L.Ed. 1056 (1884) (artificial canal); and federal regulatory authority encompasses waters that only recently have become navigable, see, e.g., Philadelphia Co. v. Stimson, 223 U.S. 605, 634–635, 32 S.Ct. 340, 56 L.Ed. 570 (1912), were once navigable but are no longer, see Economy Light & Power Co. v. United States, 256 U.S. 113, 123–124, 41 S.Ct. 409, 65 L.Ed. 847 (1921), or are not navigable and never have been but may become so by reasonable improvements, see Appalachian Elec. Power Co., supra, at 407– 408, 61 S.Ct. 291. With respect to the federal commerce power, the inquiry regarding navigation historically focused on interstate

commerce. See The Daniel Ball, 1229*1229

supra, at 564. And, of course, the commerce power extends beyond navigation. See Kaiser

Aetna v. United States, 444 U.S. 164, 173– 174, 100 S.Ct. 383, 62 L.Ed.2d 332 (1979). In contrast, for title purposes, the inquiry depends only on navigation and not on

interstate travel. See Utah, supra, at 76, 51
S.Ct. 438. This list of differences is not exhaustive. Indeed, ‘‘[e]ach application of [the Daniel Ball] test . . . is apt to uncover variations and refinements which require

further elaboration.’’ Appalachian Elec. Power Co., supra, at 406, 61 S.Ct. 291.

PPL Montana v. Montana, 565 U.S.

___(2012).

Also of note are two decisions from the courts of appeals. In FPL Energy Marine Hydro, a case involving the Federal Power Act, the D.C. Circuit reiterated the fact that

‘‘actual use is not necessary for a navigability determination’’ and repeated earlier Supreme Court holdings that navigability and capacity of a water to carry commerce could be shown through ‘‘physical characteristics and experimentation.’’ FPL Energy Marine Hydro

LLCv. FERC, 287 F.3d 1151, 1157 (D.C. Cir. 2002). In that case, the D.C. Circuit upheld a FERC navigability determination that was based upon three experimental canoe trips taken specifically to demonstrate the river’s navigability. Id. at 1158–59.

The 9th Circuit has also implemented the Supreme Court’s holding that a water need only be susceptible to being used for waterborne commerce to be navigable-in-fact.

Alaska v. Ahtna, Inc., 891 F.2d 1404 (9th Cir. 1989). In Ahtna, the 9th Circuit held that

current use of an Alaskan river for commercial recreational boating was sufficient evidence of the water’s capacity to carry waterborne commerce at the time that

Alaska became a state. Id. at 1405. It was

found to be irrelevant whether or not the river was actually being navigated or being used for commerce at the time, because current navigation showed that the river always had the capacity to support such navigation. Id. at 1404.

In summary, when determining whether a water body qualifies as a ‘‘traditional navigable water’’ (i.e., an (a)(1) water),

relevant considerations include whether the water body meets any of the tests set forth in Part 329, or a Federal court has determined that the water body is


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10 For purposes of the CWA, EPA and the Corps have interpreted the term ‘‘traditional navigable waters’’ to include all of the ‘‘navigable waters of the United States,’’ defined in 33 CFR part 329 and by numerous decisions of the Federal courts, plus all other waters that are navigable-in-fact (e.g., the Great Salt Lake, UT and Lake Minnetonka, MN). This section explains why EPA and the Corps do not interpret the CWA or the Supreme Court’s

decisions in Solid Waste Agency of Northern Cook County (SWANCC) v. U.S. Army Corps of Engineers, 531 U.S. 159 (2001) and Rapanos v. United States, 547 U.S. 715 (2006), to restrict CWA jurisdiction over interstate waters to only those interstate waters that are traditional navigable waters or that connect to traditional navigable waters. 11 The Supreme Court has found that the term ‘‘waters of the United States’’ is ambiguous in some

respects. Rapanos, 547 U.S. at 752 (plurality opinion), 804 (dissent).

12 Section 303 of the Act requires the states to submit revised and new water quality standards to

the Administrator for review. CWA section 303(c)(2)(A). Such revised or new water quality standards ‘‘shall consist of the designated uses of the navigable waters involved and the water quality

criteria for such waters.’’ Id. If the Administrator

determines that a revised or new standard is not consistent with the Act’s requirements, or

determines that a revised or new standard is necessary to meet the Act’s requirements, and the state does not make required changes, ‘‘[t]he Administrator shall promptly prepare and publish proposed regulations setting forth a revised or new water quality standard for the navigable waters involved.’’ CWA section 303(c)(4). ‘‘navigable-in-fact’’ under Federal law for anypurpose, or the water body is ‘‘navigable-infact’’ under the standards that have been used by the Federal courts.

Interstate Waters

1. Interstate Waters

The agencies’ proposal today makes no change to the interstate waters section of the existing regulations and the agencies would continue to assert jurisdiction over interstate waters, including interstate wetlands. The language of the CWA is clear that Congress intended the term ‘‘navigable waters’’ to include interstate waters, and the agencies’ interpretation, promulgated contemporaneously with the passage of the
CWA, is consistent with the statute and legislative history. The Supreme Court’s

decisions in SWANCC and Rapanos did not address the interstate waters provision of the existing regulation.

A. The Language of the Clean Water Act, the Statute as a Whole, and the Statutory History Demonstrate Congress’ Clear Intent To Include Interstate Waters as ‘‘Navigable Waters’’ Subject to the Clean Water Act

While as a general matter, the scope of the terms ‘‘navigable waters’’ and ‘‘waters of the United States’’ is ambiguous, the language of the CWA, particularly when read as a whole, demonstrates that Congress clearly intended to continue to subject interstate waters to Federal regulation. The statutory history of Federal water pollution control places the terms of the CWA in context and provides further evidence of Congressional intent to include interstate waters within the scope of the ‘‘navigable waters’’ protected by the Act. Congress clearly intended to subject interstate waters to CWA jurisdiction without imposing a requirement that they be water that is navigable for purposes of Federal regulation under the Commerce Clause

themselves or be connected to water that is navigable for purposes of Federal regulation

under the Commerce Clause. 10 The CWA

itself is clear that interstate waters that were previously subject to Federal regulation remain subject to Federal regulation. The text of the CWA, specifically the CWA’s provision with respect to interstate waters and their water quality standards, in conjunction with the definition of navigable waters, provides clear indication of Congress’ intent. Thus, interstate waters are ‘‘navigable waters’’ protected by the CWA. (1) The Plain Language of the Clean Water Act and the Statute as a Whole Clearly Indicate Congress’ Intent to Include Interstate Waters Within the Scope of ‘‘Navigable Waters’’ for Purposes of the Clean Water Act

Under well settled principles, the phrase ‘‘navigable waters’’ should not be read in

isolation from the remainder of the statute. As the Supreme Court has explained:

The definition of words in isolation, however, is not necessarily controlling in statutory construction. A word in a statute may or may not extend to the outer limits of its definitional possibilities. Interpretation of a word or phrase depends upon reading the whole statutory text, considering the purpose and context of the statute, and consulting any precedents or authorities that inform the analysis.

Dolan v. U.S. Postal Service, 546 U.S. 481, 486 (2006); see also United States Nat’l. Bank of Oregon v. Indep. Ins. Agents of Am., Inc., 508 U.S. 439, 455 (1993).

While the term ‘‘navigable waters’’ is, in general, ambiguous, interstate waters are waters that are clearly covered by the plain language of the definition of ‘‘navigable

waters.’’ 11 Congress defined ‘‘navigable

waters’’ to mean ‘‘the waters of the United States, including the territorial seas.’’

Interstate waters are waters of the several States and, thus, the United States. While the 1972 Act was clearly not limited to interstate waters, it was clearly intended to include

interstate waters.

Furthermore, the CWA does not simply define ‘‘navigable waters.’’ Other provisions of the statute provide additional textual evidence of the scope of this term of the Act. Most importantly, there is a specific provision in the 1972 CWA establishing requirements for those interstate waters which were subject to the prior Water

Pollution Control Acts.

The CWA requires states to establish water quality standards for navigable waters and

submit them to the Administrator for

review. 12 Under section 303(a) of the Act, in order to carry out the purpose of this Act, any water quality standard applicable to

interstate waters which was adopted by any State and submitted to, and approved by, or is awaiting approval by, the Administrator pursuant to this Act as in effect immediately prior to the date of enactment of the Federal

Water Pollution Control Act Amendments of 1972, shall remain in effect unless the

Administrator determined that such standard is not consistent with the applicable requirements of the Act as in effect immediately prior to the date of enactment of

the Federal Water Pollution Control Act

Amendments of 1972. If the Administrator makes such a determination he shall, within

three months after the date of enactment of

the Federal Water Pollution Control Act Amendments of 1972, notify the State and specify the changes needed to meet such requirements. If such changes are not adopted by the State within ninety days after the date of such notification, the Administrator shall promulgate such changes in accordance with subsection (b). CWA section 303(a)(1) (emphasis added).

Under the 1965 Act, as discussed in more detail below, states were directed to develop water quality standards establishing water quality goals for interstate waters. By the early 1970s, all the states had adopted such water quality standards. Advanced Notice of Proposed Rulemaking, Water Quality Standards Regulation, 63 FR 36742, 36745, July 7, 1998. In section 303(a), Congress clearly intended for existing Federal regulation of interstate waters to continue under the amended CWA. Water quality

standards for interstate waters were not merely to remain in effect, but EPA was required to actively assess those water quality standards and even promulgate

revised standards for interstate waters if states did not make necessary changes. By the plain language of the statute, these water quality standards for interstate waters were to remain in effect ‘‘in order to carry out the purpose of this Act.’’ The objective of the Act is ‘‘to restore and maintain the chemical, physical, and biological integrity of the Nation’s waters.’’ CWA section 101(a). It would contravene Congress’ clearly stated intent for a court to impose an additional jurisdictional requirement on all rivers, lakes, and other waters that flow across, or form a part of, state boundaries (‘‘interstate waters’’ as defined by the 1948 Act, § 10, 62 Stat. 1161), such that interstate waters that were previously protected were no longer protected because they lacked a connection to a water that is navigable for purposes of Federal regulation under the Commerce Clause. Nor would all the existing water quality standards be ‘‘carry[ing] out the purpose of this Act,’’ if the only water quality standards that could be implemented through the Act (through, for example, National Pollutant Discharge Elimination System permits under section 402) were those water quality standards established for interstate waters that are also waters that are navigable for purposes of Federal regulation under the

Commerce Clause or that connect to waters that are navigable for purposes of Federal regulation under the Commerce Clause. Nowhere in section 303(a) does Congress

make such a distinction.

(2) The Federal Water Pollution Control

Statute That Became the Clean Water Act

Covered Interstate Waters

In 1972, when Congress rewrote the law governing water pollution, two Federal statutes addressed discharges of pollutants

into interstate waters and water that is


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13 Congress did not define the term ‘‘navigable waters’’ in the 1961 Amendments, or in subsequent
FWPCA Amendments, until 1972.

14 In 1967, the state of Arizona created the Water Quality Control Council (Council) to implement the requirements of the 1965 FWPCA. The Council adopted water quality standards for those waters that were considered ‘‘interstate waters’’ pursuant to the existing Federal law. The Council identified

the Santa Cruz River as an interstate water and promulgated water quality standards for the river in

accordance with Federal law.

15 The 1966 Amendments authorized civil fines for failing to provide information about an alleged discharge causing or contributing to water pollution. Public Law 89–753, 80 Stat. 1250 (1966);

see also S. Rep. No. 414, 92d Congress, 1st Sess. 10 (1972) (describing the history of the FWPCA). 16 In December 1970, administration of the

Federal Water Pollution Control Administration was transferred from the Secretary of the Interior to EPA. S. Rep. No. 414, 92d Congress, 1st Sess. (1972). navigable for purposes of Federal regulation under the Commerce Clause, and tributaries

of each: The Water Pollution Control Act of 1948, as amended, and section 13 of the Rivers and Harbors Act of 1899 (known as the ‘‘Refuse Act’’). Of the two, the Water

Pollution Control Act extended Federal authority over interstate waters and their tributaries. In contrast, the Refuse Act extended Federal jurisdiction over the ‘‘navigable waters of the United States’’ and their tributaries. These two separate statutes demonstrate that Congress recognized that interstate waters and ‘‘navigable waters of the United States’’ were independent lawful bases of Federal jurisdiction.

a. The Federal Water Pollution Control Act

Prior to 1972

From the outset, and through all the amendments pre-dating the 1972 Amendments, the Federal authority to abate water pollution under the Water Pollution Control Act, and the Federal Water Pollution Control Act (FWPCA) as it was renamed in 1956, extended to interstate waters. In addition, since first enacted in 1948, and throughout all the amendments, the goals of the Act have been, inter alia, to protect public water supplies, propagation of fish and aquatic life, recreation, agricultural, industrial, and other legitimate uses. See 62 Stat. 1155 and 33 U.S.C. 466 (1952), 33 U.S.C. 466 (1958), 33 U.S.C. 466 (1964), 33 U.S.C. 1151 (1970).

In 1948, Congress enacted the Water

Pollution Control Act in connection with the exercise of jurisdiction over the waterways of the Nation and in the consequence of the benefits to public health and welfare by the abatement of stream pollution. See Pub. L. No. 80–845, 62 Stat. 1155 (June 30, 1948).

The Act authorized technical assistance and financial aid to states for stream pollution abatement programs, and made discharges of pollutants into interstate waters and their tributaries a nuisance, subject to abatement and prosecution by the United States. See section 2(d)(1),(4), 62 Stat. at 1156–1157 (section 2(d)(1) of the Water Pollution Control Act of 1948, 62 Stat. at 1156, stated that the ‘‘pollution of interstate waters’’ in or adjacent to any State or States (whether the matter causing or contributing to such pollution is discharged directly into such waters or reaches such waters after discharge into a tributary of such waters), which endangers the health or welfare of persons in a State other than that in which the discharge originates, is declared to be a public nuisance and subject to abatement as provided by the Act. (emphasis added)); § 2(a), 62 Stat. 1155 (requiring comprehensive programs for ‘‘interstate waters and tributaries thereof’’); § 5, 62 Stat. 1158 (authorizing loans for sewage treatment to abate discharges into ‘‘interstate waters or into a tributary of such waters’’). Under the statute, ‘‘interstate waters’’ were defined as all rivers, lakes, and other waters that flow across, or form a part of, state boundaries. Section 10, 62 Stat.

1161.

In 1956, Congress strengthened measures for controlling pollution of interstate waters and their tributaries. Public Law 84–660, 70 Stat. 498 (1956) (directing further cooperation between the Federal and State Governments in development of comprehensive programs for eliminating or reducing ‘‘the pollution of interstate waters and tributaries’’ and improving the sanitary condition of surface and underground waters, and authorizing the Surgeon General to make joint investigations with States into the conditions of and discharges into ‘‘any waters of any State or States.’’).

In 1961, Congress amended the FWPCA to substitute the term ‘‘interstate or navigable

waters’’ for ‘‘interstate waters.’’ See Public Law 87–88, 75 Stat. 208 (1961). Accordingly, beginning in 1961, the provisions of the FWPCA applied to all interstate waters and navigable waters and the tributaries of each,

see 33 U.S.C. 466a, 466g(a) (1964). 13

In 1965, Congress approved a second set of major legislative changes, requiring each state to develop water quality standards for interstate waters within its boundaries by 1967. Public Law 89–234, 79 Stat. 908 (1965). 14 Failing establishment of adequate standards by the state, the Act authorized establishment of water quality standards by Federal regulation. Id. at 908. The 1965 Amendments provided that the discharge of

matter ‘‘into such interstate waters or portions thereof,’’ which reduces the quality of such waters below the water quality

standards established under this subsection (whether the matter causing or contributing to such reduction is discharged directly into

such waters or reaches such waters after discharge into tributaries of such waters), is subject to abatement through procedures specified in the Act, including (after conferences and negotiations and consideration by a Hearing Board) legal

action in the courts. Id. at 909. 15

b. The Refuse Act

Since its original enactment in 1899, the Refuse Act has prohibited the discharge of refuse matter ‘‘into any navigable water of the United States, or into any tributary of any navigable water.’’ Ch. 425, 30 Stat. 1152 (1899). It also has prohibited the discharge of such material on the bank of any tributary

where it is liable to be washed into a navigable water. Id. Violators are subject to fines and imprisonment. Id. at 1153 (codified at 33 U.S.C. 412). In 1966, the Supreme Court upheld the Corps’ interpretation of the Refuse Act as prohibiting discharges that pollute the navigable waters, and not just those discharges that obstruct navigation.

United States v. Standard Oil Co., 384 U.S. 224, 230 (1966). In 1970, President Nixon signed an Executive Order directing the Corps (in consultation with the Federal

Water Pollution Control Administration 16) to implement a permit program under section 13 of the RHA ‘‘to regulate the discharge of pollutants and other refuse matter into the navigable waters of the United States or their tributaries and the placing of such matter upon their banks.’’ E.O. 11574, 35 FR 19627, Dec. 25, 1970. In 1971, the Corps promulgated regulations establishing the Refuse Act Permit Program. 36 FR 6564, 6565, April 7, 1971. The regulations made it unlawful to discharge any pollutant (except those flowing from streets and sewers in a liquid state) into a navigable waterway or tributary, except pursuant to a permit. Under the permit program, EPA advised the Corps regarding the consistency of a proposed discharge with water quality standards and considerations, and the Corps evaluated a permit application for impacts on anchorage, navigation, and fish and wildlife resources.

Id. at 6566.

c. The Federal Water Pollution Control Act

Amendments of 1972

When Congress passed the Federal Water

Pollution Control Act Amendments of 1972 (referred to hereinafter as the CWA or CWA), it was not acting on a blank slate. It was amending existing law that provided for a Federal/State program to address water pollution. The Supreme Court has recognized that Congress, in enacting the CWA in 1972, ‘‘intended to repudiate limits that had been placed on federal regulation by earlier water pollution control statutes and to exercise its powers under the Commerce Clause to regulate at least some waters that would not be deemed ‘navigable’ under the classical understanding of that term.’’ Riverside Bayview Homes, 474 U.S. at 133; see also International Paper Co. v. Ouellette, 479 U.S. 481, 486, n.6 (1987).

The amendments of 1972 defined the term ‘‘navigable waters’’ to mean ‘‘the waters of the United States, including the territorial seas.’’ 33 U.S.C. 1362(7). While earlier versions of the 1972 legislation defined the term to mean ‘‘the navigable waters of the United States,’’ the Conference Committee deleted the word ‘‘navigable’’ and expressed the intent to reject prior geographic limits on the scope of Federal water-protection measures. Compare S. Conf. Rep. No. 1236, 92d Cong., 2d Sess. 144 (1972), with H.R. Rep. No. 911, 92 Cong., 2d Sess. 356 (1972) (bill reported by the House Committee provided that ‘‘[t]he term ‘navigable waters’ means the navigable waters of the United States, including the territorial seas’’); see also S. Rep. No. 414, 92d Cong., 1st Sess. 77 (‘‘Through a narrow interpretation of the

definition of interstate waters the implementation of the 1965 Act was severely limited. . . . Therefore, reference to the control requirements must be made to the navigable waters, portions thereof, and their tributaries.’’). Thus, Congress intended the scope of the 1972 Act to include, at a


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minimum, the waters already subject to Federal water pollution control law—both

interstate waters and waters that are navigable for purposes of Federal regulation

under the Commerce Clause. Those statutes covered interstate waters, defined interstate waters without requiring that they be a traditional navigable water or be connected to water that is a traditional navigable water, and demonstrated that Congress knew that

there are interstate waters that are not navigable for purposes of Federal regulation

under the Commerce Clause.

In fact, Congress amended the Federal

Water Pollution Control Act in 1961 to substitute the term ‘‘interstate or navigable waters’’ for ‘‘interstate waters,’’ demonstrating that Congress wanted to be very clear that it was asserting jurisdiction over both types of waters: interstate waters even if they were not navigable for purposes of Federal regulation under the Commerce Clause, and traditional navigable waters even if they were not interstate waters. At no point were the interstate waters already subject to Federal water pollution control authority required to be navigable or to connect to a traditional navigable water. Further, as discussed above, the legislative history clearly demonstrates that Congress was expanding jurisdiction—not narrowing it— with the 1972 amendments. Thus, it is reasonable to conclude that by defining ‘‘navigable waters’’ as ‘‘the waters of the United States’’ in the 1972 amendments, Congress included not just traditionally navigable waters, but all waters previously regulated under the Federal Water Pollution Control Act, including non-navigable

interstate waters.

Based on the statutory definition of navigable waters, the requirement of section 303(a) for water quality standards for interstate waters to remain in effect, the purposes of the Act, and the more than three decades of Federal water pollution control regulation that provides a context for reading those provisions of the statute, the intent of Congress is clear that the term ‘‘navigable

waters’’ includes ‘‘interstate waters’’ as an independent basis for CWA jurisdiction, whether or not they themselves are traditional navigable waters or are connected to a traditional navigable water.

B. Supreme Court Precedent Supports CWA Jurisdiction Over Interstate Waters Without Respect to Navigability

In two seminal decisions, the Supreme Court established that resolving interstate water pollution issues was a matter of

Federal law and that the CWA was the comprehensive regulatory scheme for addressing interstate water pollution. Illinois

v. Milwaukee, 406 U.S. 91 (1972); City of

Milwaukee v. Illinois, 451 U.S. 304 (1981). In both of these decisions, the Court held that Federal law applied to interstate waters. Moreover, these cases analyzed the applicable Federal statutory schemes and determined that the provisions of the Federal

Water Pollution Control Act and the CWA regulating water pollution applied generally to interstate waters. The holdings of these cases recognized the Federal interest in interstate water quality pollution; and City of Milwaukee recognized that CWA jurisdiction extends to interstate waters without regard to navigability.

In Illinois v. Milwaukee, the Court considered a public nuisance claim brought by the State of Illinois against the city of

Milwaukee to address the adverse effects of Milwaukee’s discharges of poorly treated sewage into Lake Michigan, ‘‘a body of

interstate water.’’ 406 U.S. at 93. In relevant part, the Court held that the Federal common law of nuisance was an appropriate mechanism to resolve disputes involving interstate water pollution. 406 U.S. at 107 (‘‘federal courts will be empowered to appraise the equities of suits alleging creation of a public nuisance by water pollution’’).

The Court further noted that in such actions

the Court could consider a state’s interest in protecting its high water quality standards from ‘‘the more degrading standards of a neighbor.’’ Id.

In reaching this conclusion, the Court examined in detail the scope of the Federal regulatory scheme as it existed prior to the October, 1972 FWPCA amendments. In its April, 1972 decision, the Court concluded

that the Federal Water Pollution Control Act ‘‘makes clear that it is federal, not state, law that in the end controls the pollution of interstate or navigable waters.’’ 406 U.S. at 102 (emphasis added). The Court, in this case, concluded that the regulatory provisions of the Federal Water Pollution Control Act did not address the right of a state to file suit to protect water quality. However, this was not because this statute

did not reach interstate waters. The Court specifically noted that section 10(a) of the

Federal Water Pollution Control Act ‘‘makes pollution of interstate or navigable waters subject ‘to abatement’ ’’ 406 U.S. at 102 (emphasis added). Rather, the Court noted that the plaintiff in this action was seeking relief outside the scope of the Federal Water

Pollution Control Act and that statute explicitly provided that independent ‘‘state and interstate action to abate pollution of interstate or navigable waters shall be encouraged and shall not . . . be displaced by Federal enforcement action.’’ 406 U.S. at 104 (citing section 10(b) of the Federal Water Pollution Control Act).

In addition, in Illinois v. Milwaukee, the Court acknowledged that it was essential for

Federal law to resolve interstate water pollution disputes, citing with approval the following discussion from Texas v. Pankey:
Federal common law and not the varying common law of the individual states is, we think, entitled and necessary to be recognized as a basis for dealing in uniform standard with the environmental rights of a State against improper impairment by

sources outside its domain

. . . . Until the field has been made the subject of comprehensive legislation or authorized administrative standards, only a federal common law basis can provide an adequate means for dealing with such claims as alleged federal rights.

406 U.S. at 107 n. 9, citing Texas v. Pankey, 441 F.2d 236, 241–242.

In City of Milwaukee, the Court revisited this dispute and addressed the expanded statutory provisions of the CWA regulating water pollution. The scope of the CWA

amendments led the Court to reverse its

decision in Illinois v. Milwaukee. In reaching this result, the Court concluded that Congress had elected to exercise its authority under Federal law to occupy the field of water pollution regulation. As a result, the Court

concluded that there was no basis for maintaining a Federal common law of

nuisance.
Congress has not left the formulation of appropriate federal standards to the courts through application of often vague and indeterminate nuisance concepts and maxims of equity jurisprudence, but rather has occupied the field through the establishment of a comprehensive regulatory program supervised by an expert administrative agency. The 1972

Amendments to the Federal Water Pollution Control Act were not merely another law ‘‘touching interstate waters’’. . . Rather, the Amendments were viewed by Congress as a ‘‘total restructuring’’ and ‘‘complete rewriting’’ of the existing water pollution legislation considered in that case.

451 U.S. at 317.

The Court’s analysis in Illinois v. Milwaukee made clear that Federal common law was necessary to protect ‘‘the environmental rights of States against improper impairment by sources outside its domain.’’ 406 U.S. at 107, n. 9. In the context of interstate water pollution, nothing in the Court’s language or logic limits the reach of this conclusion to only navigable interstate

waters. In City of Milwaukee, the Court found that the CWA was the ‘‘comprehensive regulatory program’’ that ‘‘occupied the field’’ (451 U.S. 317) with regard to interstate water pollution, eliminating the basis for an independent common law of nuisance to address interstate water pollution. Since the Federal common law of nuisance (as well as the statutory provisions regulating water pollution in the Federal Water Pollution Control Act) applied to interstate waters whether navigable or not, the CWA could only occupy the field of interstate water pollution if it too extended to non-navigable as well as navigable interstate waters.

With regard to the specifics of interstate water pollution, the City of Milwaukee Court noted that, in Illinois v. Milwaukee, it had

been concerned that Illinois did not have a forum in which it could protect its interests in abating water pollution from out of state, absent the recognition of Federal common

law remedies. 451 U.S. at 325. The Court then went on to analyze in detail the specific procedures created by the CWA ‘‘for a State affected by decisions of a neighboring State’s permit-granting agency to seek redress.’’ 451 U.S. at 326. The Court noted that ‘‘any State whose waters may be affected by the issuance of a permit’’ is to receive notice and the opportunity to comment on the permit. Id. (citing to CWA section 402(b)(3)(5). In addition the Court noted provisions giving EPA the authority to veto and issue its own permits ‘‘if a stalemate between an issuing and objecting state develops.’’ Id. (citing to CWA sections 402(d)(2)(A),(4)). In light of these protections for states affected by interstate water pollution, the court

concluded that


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17Nothing in subsequent Supreme Court case law regarding interstate waters in any way conflicts with the agencies’ interpretation. See International Paper v. Ouellette, 479 U.S. 481 (1987); Arkansas

v. Oklahoma, 503 U.S. 91 (1992). In both of these
cases, the Court detailed how the CWA had supplanted the Federal common law of nuisance to establish the controlling statutory scheme for addressing interstate water pollution disputes. Nothing in either decision limits the applicability of the CWA to interstate water pollution disputes involving navigable interstate waters or interstate waters connected to navigable waters. 18 It is worth noting the Justice Rehnquist was

also the author of City of Milwaukee. [t]he statutory scheme established by Congress provides a forum for the pursuit of such claims before expert agencies by means of the permit-granting process. It would be quite inconsistent with this scheme if federal

courts were in effect to ‘‘write their own ticket’’ under the guise of federal common law after permits have already been issued and permittees have been planning and operating in reliance on them.

451 U.S. at 326.

Nothing in the language or the reasoning of this discussion limits the applicability of these protections of interstate waters to navigable interstate waters or interstate waters connected to navigable waters. If these protections only applied to navigable interstate waters, a downstream state would be unable to protect many of its waters from out of state water pollution. This would hardly constitute a comprehensive regulatory scheme that occupied the field of interstate water pollution.

For these reasons, the holdings and the reasoning of these decisions establish that the regulatory reach of the CWA extends to all interstate waters without regard to navigability. 17

C. The Supreme Court’s Decisions in SWANCC and Rapanos Do Not Limit or Constrain Clean Water Act Jurisdiction Over Non-Navigable Interstate Waters

As noted above, the Supreme Court recognized that Congress, in enacting the CWA, ‘‘intended to repudiate limits that had been placed on federal regulation by earlier water pollution control statutes and to exercise its powers under the Commerce Clause to regulate at least some waters that would not be deemed ‘navigable’ under the classical understanding of that term.’’ Riverside Bayview, 474 U.S. at 133; see also International Paper Co. v. Ouellette, 479 U.S. 481, 486 n.6, (1987). In Riverside Bayview, and subsequently in SWANCC and Rapanos,

the Court addressed the construction of the CWA terms ‘‘navigable waters’’ and ‘‘the

waters of the United States.’’ In none of these cases did the Supreme Court address interstate waters, nor did it overrule prior Supreme Court precedent which addressed

the interaction between the CWA and Federal common law to address pollution of interstate waters. Therefore, the statute, even in light of SWANCC and Rapanos, does not impose an additional requirement that

interstate waters must be water that is navigable for purposes of Federal regulation

under the Commerce Clause or connected to water that is navigable for purposes of Federal regulation under the Commerce Clause to be jurisdictional waters for purposes of the CWA. At the outset, it is worth noting that neither

SWANCC nor Rapanos dealt with the jurisdictional status of interstate waters. Repeatedly in the SWANCC decision the Court emphasized that the question presented concerned the jurisdiction status of nonnavigable intrastate waters located in two

Illinois counties. SWANCC 531 U.S. at 165– 166, 171 (‘‘we thus decline to . . . hold that isolated ponds, some only seasonal, wholly

located within two Illinois counties fall under § 404(a) definition of navigable waters . . .’’) (emphasis added). Nowhere in Justice Rehnquist’s majority opinion in SWANCC

does the Court discuss the Court’s interstate

water case law. 18 The Court does not even discuss the fact that CWA jurisdictional regulations identify interstate waters as regulated ‘‘waters of the United States.’’ In fact, the repeated emphasis on the intrastate

nature of the waters at issue can be read as an attempt to distinguish SWANCC from the Court’s interstate water jurisprudence.

In Rapanos, the properties at issue were located entirely within the State of Michigan. 547 U.S. 715, 762–764. Thus, the Court had

no occasion to address the text of the CWA with respect to interstate waters or the agencies’ regulatory provisions concerning interstate waters. In addition, neither Justice Kennedy nor the plurality discusses the impact of their opinions on the Court’s interstate waters jurisprudence. The plurality decision acknowledges that CWA jurisdictional regulations include interstate waters. 547 U.S. 715, 724. However, the plurality did not discuss in any detail its views as to the continued vitality of regulations concerning such waters.

Moreover, one of the analytical underpinnings of the SWANCC and Rapanos decisions is irrelevant to analysis of regulations asserting jurisdiction over

interstate waters. In SWANCC, the Court declined to defer to agency regulations asserting jurisdiction over isolated waters

because
[w]here an administrative interpretation of a statute invokes the outer limits of Congress’ power, we expect a clear indication that Congress intended that result. . . .This requirement stems from our prudential desire not to needlessly reach constitutional issues and our assumption that Congress does not casually authorize administrative agencies to interpret a statute to push the limit of Congressional authority. . . . This concern is heightened where the administrative interpretation alerts the federal-state framework by permitting federal encroachment upon a traditional state power.

531 U.S. at 172–173 (citations omitted).

However, the Court’s analysis in Illinois v. Milwaukee and City of Milwaukee makes clear that Congress has broad authority to

create Federal law to resolve interstate water pollution disputes. As discussed above, the

Court in Illinois v. Milwaukee, invited further Federal legislation to address interstate water pollution, and in so doing concluded that State law was not an appropriate basis for addressing interstate water pollution issues. 406 U.S. at 107 n. 9 (citing Texas v. Pankey, 441 F.2d 236, 241–242). In City of Milwaukee, the Court indicated that central to its holding in Illinois v. Milwaukee was its concern ‘‘that Illinois did not have any forum to protect its interests [in the matters involving interstate water pollution].’’ 451 U.S. 325. As discussed above, the Court cited with approval the statutory provisions of the CWA regulating water pollution as an appropriate means to address that concern.

The City of Milwaukee and Illinois v. Milwaukee decisions make clear that assertion of Federal authority to resolve disputes involving interstate waters does not alter ‘‘the Federal-State framework by permitting Federal encroachment on a traditional State power.’’ 531 U.S. at 173. ‘‘Our decisions concerning interstate waters contain the same theme. Rights in interstate streams, like questions of boundaries, have been recognized as presenting Federal questions.’’ Illinois v. Milwaukee, 406 U.S. at 105 (internal quotations and citations omitted).

The Supreme Court’s analysis in SWANCC

and Rapanos materially altered the criteria for analyzing CWA jurisdictional issues for wholly intrastate waters. However, these decisions by their terms did not affect the body of case law developed to address interstate waters. The holdings in the Supreme Court’s interstate waters jurisprudence, in particular City of Milwaukee, apply CWA jurisdiction to interstate waters without regard to, or discussion of, navigability. In City of Milwaukee, the Court held that the CWA provided a comprehensive statutory scheme for addressing the consequences of interstate water pollution. Based on this analysis, the

Court expressly overruled its holding in

Illinois v. Milwaukee that the Federal common law of nuisance would apply to resolving interstate water pollution disputes. Instead, the Court held that such disputes would now be resolved through application of the statutory provisions of the CWA regulating water pollution.

It would be unreasonable to interpret

SWANCC or Rapanos as overruling City of

Milwaukee with respect to CWA jurisdiction over non-navigable interstate waters. Such an interpretation would result in no law to apply to water pollution disputes with regard to such waters, unless one were to assume that the Court intended (without discussion or analysis) to restore the Federal common law of nuisance as the law to apply in such

matters. Moreover, SWANCC and Rapanos acknowledge that CWA regulatoryjurisdiction extends to at least some nonnavigable waters. See, e.g., 547 U.S. at 779 (Kennedy, J.). Neither the SWANCC Court nor the plurality or Kennedy opinions in Rapanos purports to set out the complete boundaries of CWA jurisdiction. See, e.g., 547 U.S. at 731 (‘‘[w]e need not decide the precise extent to which the qualifiers ‘navigable’ and ‘of the United States’ restrict the coverage of the Act.’’) (plurality opinion).

In addition, as the Supreme Court has repeatedly admonished, if a Supreme Court precedent has direct application in a case yet appears to rest on a rationale rejected in some other line of decisions, lower courts should follow the case which directly controls,


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19 See id. at 9 (‘‘The scope of the 1899 Refuse Act is broadened; the administrative capability is strengthened.’’); id. at 43 (‘‘Much of the

Committee’s time devoted to this Act centered on an effort to resolve the existing water quality program and the separate pollution program developing under the 1899 Refuse Act.’’). Congress made an effort ‘‘to weave’’ the Refuse Act permit program into the 1972 Amendments, id. at 71, as the statutory text shows. See 33 U.S.C. 1342(a) (providing that each application for a permit under 33 U.S.C. 407, pending on October 18, 1972, shall be deemed an application for a permit under 33 U.S.C. 1342(a)).

20 City of Milwaukee v. Illinois, 451 U.S. at 317;

see also id. at 318 (holding that the CWA precluded Federal common-law claims because ‘‘Congress’ intent in enacting the [CWA] was clearly to establish an all-encompassing program of water pollution regulation’’); Middlesex County Sewerage

Auth. v. National Sea Clammers Ass’n, 453 U.S. 1, 22 (1981) (existing statutory scheme ‘‘was completely revised’’ by enactment of the CWA). 21 40 FR 31320, 31324 (July 25, 1975).

22 Section 404 of the Federal Water Pollution Control Act Amendments of 1972: Hearings Before
the Senate Comm. on Public Works, 94th Cong., 2d Sess. (1976); Development of New Regulations by the Corps of Engineers, Implementing Section 404 of the Federal Water Pollution Control Act Concerning Permits for Disposal of Dredge or Fill Material: Hearings Before the Subcomm. on Water Resources of the House Comm. on Public Works and Transportation, 94th Cong., 1st Sess. (1975). leaving to the Supreme Court the prerogative of overruling its precedents. Agostino v. Felton, 521 U.S. 203, 237 (1997); United

States v. Hatter, 532 U.S. 557, 566–567 (1981). Moreover, when the Supreme Court overturns established precedent, it is explicit.
See, Lawrence v. Texas, 539 U.S. 558, 578 (‘‘Bowers was not correct when it was decided, and it is not correct today. It ought not to remain binding precedent. Bowers v. Hardwick should be and now is overruled.’’).

D. The Agencies’ Longstanding Interpretation of the Term ‘‘Navigable Waters’’ To Include

‘‘Interstate Waters’’

EPA, the agency charged with implementing the CWA, has always interpreted the 1972 Act to cover interstate waters. Final Rules, 38 FR 13528, May 22, 1973 (the term ‘‘waters of the United States’’

includes ‘‘interstate waters and their tributaries, including adjacent wetlands’’). While the Corps of Engineers initially limited the scope of coverage for purposes of section

404 of the CWA to those waters that were subject to the Rivers and Harbors Act of 1899, after a lawsuit, the Corps amended its regulations to provide for the same definition

of ‘‘waters of the United States’’ that EPA’s regulations had always established. In 1975, the Corps’ revised regulations defined ‘‘navigable waters’’ to include ‘‘[i]nterstate waters landward to their ordinary high water mark and up to their headwaters.’’ In their final rules promulgated in 1977, the Corps adopted EPA’s definition and included

within the definition of ‘‘waters of the United

States’’ ‘‘interstate waters and their tributaries, including adjacent wetlands.’’ The preamble provided an explanation for

the inclusion of interstate waters:
The affects [sic] of water pollution in one state can adversely affect the quality of the waters in another, particularly if the waters

involved are interstate. Prior to the FWPCA amendments of 1972, most federal statutes pertaining to water quality were limited to interstate waters. We have, therefore, included this third category consistent with the Federal government’s traditional role to protect these waters from the standpoint of water quality and the obvious effects on interstate commerce that will occur through pollution of interstate waters and their

tributaries.
Final Rules, 42 FR 37122, July 19, 1977.

The legislative history similarly provides support for the agencies’ interpretation. Congress in 1972 concluded that the mechanism for controlling discharges and, thereby abating pollution, under the FWPCA and Refuse Act ‘‘has been inadequate in every vital aspect.’’ S. Rep. No. 414, 92d Cong., 1st Sess. 7 (1972). The Senate Committee on Public Works reported that development of water quality standards, assigned to the states under the 1965 FWPCA Amendments, ‘‘is lagging’’ and the ‘‘1948 abatement procedures, and the almost total lack of enforcement,’’ prompted the search for ‘‘more direct avenues of action against water polluters and water pollution.’’ Id. at
5. The Committee further concluded that although the Refuse Act permit program

created in 1970 ‘‘seeks to establish this direct approach,’’ it was too weak because it applied only to industrial polluters and too unwieldy because the authority over each permit application was divided between two Federal agencies. See id. at 5; see also id. at 70–72 (discussing inadequacies of Refuse Act program).

In light of the poor success of those programs, the Committee recommended a more direct and comprehensive approach which, after amendment in conference, was adopted in the 1972 Act. The text, legislative history and purpose of the 1972 Amendments all show an intent—through the revisions—to broaden, improve and strengthen, not to curtail, the Federal water pollution control program that had existed

under the Refuse Act and FWPCA. 19 The 1972 FWPCA Amendments were ‘‘not merely another law ‘touching interstate waters’ ’’ but were ‘‘viewed by Congress as a ‘total restructuring’ and ‘complete rewriting’ of the existing water pollution legislation.’’ 20

As the legislative history of the 1972 Act confirms, Congress’ use of the term ‘‘waters

of the United States’’ was intended to repudiate earlier limits on the reach of Federal water pollution efforts: ‘‘The conferees fully intend that the term ‘navigable waters’ be given the broadest possible constitutional interpretation unencumbered by agency determinations which have been made or may be made for administrative purposes.’’ See S. Conf. Rep. No. 1236, 92d Cong., 2d Sess. 144 (1972). The House and Senate Committee Reports further

elucidate the Conference Committee’s rationale for removing the word ‘‘navigable’’ from the definition of ‘‘navigable waters,’’ in 33 U.S.C. 1362(7). The Senate report stated:

The control strategy of the Act extends to navigable waters. The definition of this term means the navigable waters of the United States, portions thereof, tributaries thereof,

and includes the territorial seas and the Great Lakes. Through a narrow interpretation of the

definition of interstate waters the implementation of the 1965 Act was severely limited. Water moves in hydrologic cycles and it is essential that discharge of pollutants be controlled at the source. Therefore, reference to the control requirements must be made the navigable waters, portions thereof,

and their tributaries.

See S. Rep. 414, 92d Cong., 1st Sess. 77 (1971); see also H.R. Rep. No. 911, 92d Cong., 2d Sess. 131 (1972) (‘‘The Committee fully intends that the term ‘‘navigable waters’’ be given the broadest possible constitutional interpretation unencumbered by agency

determinations which have been made or may be made for administrative purposes.’’). These passages strongly suggest that Congress intended to expand Federal protection of waters. There is no evidence that Congress

intended to exclude interstate waters which were protected under Federal law if they were not water that is navigable for purposes of Federal regulation under the Commerce

Clause or connected to water that is navigable for purposes of Federal regulation

under the Commerce Clause. Such an exclusion would be contrary to all the stated goals of Congress in enacting the sweeping

amendments which became the CWA.

The CWA was enacted in 1972. EPA’s contemporaneous regulatory definition of ‘‘waters of the United States,’’ promulgated in 1973, included interstate waters. The definition has been EPA’s interpretation of the geographic jurisdictional scope of the CWA for approximately 40 years. Congress has also been aware of and has supported the Agency’s longstanding interpretation of the CWA. ‘‘Where ‘an agency’s statutory construction has been fully brought to the attention of the public and the Congress, and the latter has not sought to alter that interpretation although it has amended the statute in other respects, then presumably the legislative intent has been correctly

discerned.’ ’’ North Haven Board of

Education v. Bell, 102 456 U.S. 512, 535 (1982) (quoting United States v. Rutherford, 442 U.S. 544 n. 10 (1979) (internal quotes omitted)).

The 1977 amendments to the CWA were the result of Congress’ thorough analysis of the scope of CWA jurisdiction in light of EPA and Corps regulations. The 1975 interim final regulations promulgated by the Corps in

response to NRDCv. Callaway,21 aroused considerable congressional interest. Hearings on the subject of section 404 jurisdiction

were held in both the House and the

Senate.22 An amendment to limit the geographic reach of section 404 to waters that are navigable for purposes of Federal regulation under the Commerce Clauses and their adjacent wetlands was passed by the House, 123 Cong. Rec. 10434 (1977), defeated on the floor of the Senate, 123 Cong. Rec. 26728 (1977), and eliminated by the Conference Committee, H.R. Conf. Rep. 95– 830, 95th Cong., 1st Sess. 97–105 (1977). Congress rejected the proposal to limit the geographic reach of section 404 because it wanted a permit system with ‘‘no gaps’’ in its protective sweep. 123 Cong. Rec. 26707 (1977) (remarks of Sen. Randolph). Rather

than alter the geographic reach of section


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23 In Illinois v. Milwaukee, the Supreme Court noted that ‘‘Congress has enacted numerous laws touching interstate waters.’’ 406 U.S. at 101. 404, Congress amended the statute by exempting certain activities—most notably certain agricultural and silvicultural activities—from the permit requirements of

section 404. See 33 U.S.C. 1344(f).

Other evidence abounds to support the conclusion that when Congress rejected the attempt to limit the geographic reach of section 404, it was well aware of the jurisdictional scope of EPA and the Corps’

definition of ‘‘waters of the United States.’’ For example, Senator Baker stated (123 Cong. Rec. 26718 (1977)):
Interim final regulations were promulgated by the [C]orps [on] July 25, 1975.* * * Together the regulations and [EPA] guidelines established a management program that focused the decisionmaking process on significant threats to aquatic areas while avoiding unnecessary regulation of minor activities. On July 19, 1977, the [C]orps revised its regulations to further streamline the program and correct several misunderstandings. * * * Continuation of the comprehensive coverage of this program is essential for the protection of the aquatic environment. The once seemingly separable types of aquatic systems are, we now know, interrelated and interdependent. We cannot expect to preserve the remaining qualities of our water resources without providing appropriate protection for the entire resource. Earlier jurisdictional approaches under the [Rivers and Harbors Act] established artificial and often arbitrary boundaries. . . .

This legislative history leaves no room for doubt that Congress was aware of the agencies’ definition of navigable waters. While there was controversy over the assertion of jurisdiction over all adjacent wetlands and some non-adjacent wetlands, the agencies’ assertion of CWA jurisdiction

over interstate waters was uncontroversial.

Finally, the constitutional concerns which led the Supreme Court to decline to defer to agency regulations in SWANCC and Rapanos are not present here where the agency is asserting jurisdiction over interstate waters.

In SWANCC, the Court declined to defer to agency regulations asserting jurisdiction over non-adjacent, non-navigable, intrastate

waters because the Court felt such an interpretation of the statute invoked the outer limits of Congress’ power. The Court’s concern ‘‘is heightened where the administrative interpretation alters the federal-state framework by permitting federal encroachment upon a traditional state power.’’ 531 U.S. at 172–173 (citations omitted). Authority over interstate waters is squarely within the bounds of Congress’ Commerce Clause powers.23 Further, the Federal Government is in the best position to address issues which may arise when waters cross state boundaries, so this interpretation does not disrupt the Federal-State framework in the manner the Supreme Court feared thatthe assertion of jurisdiction over a nonadjacent, non-navigable, intrastate body of water based on the presence of migratory birds did. The Supreme Court’s analysis in Illinois v. Milwaukee and City of Milwaukee makes clear that Congress has broad authority to create Federal law to resolve interstate water pollution disputes. Therefore, as discussed in Section II.B above, it is appropriate for the agencies to adopt an interpretation of the extent of CWA jurisdiction over interstate waters that gives

full effect to City of Milwaukee unless and until the Supreme Court elects to revisit its holding in that case.

Thus, based on the language of the statute, the statutory history, the legislative history, and the caselaw, the agencies’ continue their longstanding interpretation of ‘‘navigable

waters’’ to include interstate waters.

Tributaries

In Rapanos, Justice Kennedy reasoned that Riverside Bayview and SWANCC ‘‘establish the framework for’’ determining whether an assertion of regulatory jurisdiction constitutes a reasonable interpretation of ‘‘navigable waters’’—‘‘the connection between a non-navigable water or wetland and a navigable water may be so close, or potentially so close, that the Corps may deem the water or wetland a ‘navigable water’ under the Act;’’ and ‘‘[a]bsent a significant nexus, jurisdiction under the Act is lacking.’’ 547 U.S. at 767. ‘‘The required nexus must be assessed in terms of the statute’s goals and purposes. Congress enacted the law to ‘restore and maintain the chemical, physical, and biological integrity of the Nation’s waters,’ 33 U.S.C. 1251(a), and it pursued that objective by restricting dumping and filling in ‘navigable waters,’ sections 1311(a), 1362(12).’’ Id. at 779. ‘‘Justice Kennedy

concluded that the term ‘‘waters of the United States’’ encompasses wetlands and other waters that ‘‘possess a ‘significant nexus’ to waters that are or were navigable in fact or that could reasonably be so made.’’

Id. at 759. He further concluded that wetlands possess the requisite significant nexus: ‘‘if the wetlands, either alone or in combination with similarly situated [wetlands] in the region, significantly affect the chemical, physical, and biological integrity of other covered waters more readily understood as ‘navigable.’ ’’ Id. at 780.

While Justice Kennedy’s opinion focused on adjacent wetlands in light of the facts of the cases before him, the agencies

determined it was reasonable and appropriate to undertake a detailed

examination of the scientific literature to determine whether tributaries, as a category and as the agencies propose to define them, significantly affect the chemical, physical, or biological integrity of downstream navigable waters, interstate waters, or territorial seas into which they flow. Based on this extensive analysis, the agencies concluded that tributaries with bed and banks, and ordinary high water marks, alone or in combination with other tributaries, as defined by the proposed regulation, in the watershed perform these functions and should be considered, as a category, to be ‘‘waters of the

United States.’’

The assertion of jurisdiction over this category of waters is fully consistent with Justice Kennedy’s opinion in Rapanos. ‘‘Justice Kennedy concluded that the term ‘‘waters of the United States’’ encompasses wetlands and other waters that ‘‘possess a ‘significant nexus’ to waters that are or were navigable in fact or that could reasonably be

so made.’’ Id. at 759. With respect to tributaries, Justice Kennedy rejected the plurality’s approach that only ‘‘relatively permanent’’ tributaries are within the scope of CWA jurisdiction. He stated that the plurality’s requirement of ‘‘permanent standing water or continuous flow, at least for a period of ‘some months’ . . . makes little practical sense in a statute concerned with downstream water quality.’’ Id. at 769. Instead, Justice Kennedy concluded that ‘‘Congress could draw a line to exclude irregular waterways, but nothing in the statute suggests it has done so;’’ in fact, he stated that Congress has done ‘‘[q]uite the opposite . . ..’’ Id. at 769. Further, Justice Kennedy concluded, based on ‘‘a full reading of the dictionary definition’’ of ‘‘waters,’’ that

‘‘the Corps can reasonably interpret the Act to cover the paths of such impermanent

streams.’’ Id. at 770 (emphasis added).

Moreover, Justice Kennedy’s opinion did not reject the agencies’ existing regulations governing tributaries. The consolidated cases

in Rapanos involved discharges into

wetlands adjacent to nonnavigable tributaries and, therefore, Justice Kennedy’s analysis focused on the requisite showing for

wetlands. Justice Kennedy described the Corps’ standard for asserting jurisdiction over tributaries: ‘‘the Corps deems a water a tributary if it feeds into a traditional navigable water (or a tributary thereof) and possesses an ordinary high water mark . . ..’’

Id. at 781, see also id at 761. He acknowledged that this requirement of a perceptible ordinary high water mark for ephemeral streams, 65 FR 12828, March 9, 2000, ‘‘[a]ssuming it is subject to reasonably consistent application, . . . may well provide a reasonable measure of whether specific

minor tributaries bear a sufficient nexus with other regulated waters to constitute navigable waters under the Act.’’ 547 U.S. at 781, see also id. at 761. With respect to wetlands, Justice Kennedy concluded that the breadth of this standard for tributaries precluded use of adjacency to such tributaries as the

determinative measure of whether wetlands adjacent to such tributaries ‘‘are likely to play an important role in the integrity of an aquatic system comprising navigable waters as traditionally understood.’’ Id. at 781. He did not, however, reject the Corps’ use of ‘‘ordinary high water mark’’ to assert regulatory jurisdiction over tributaries

themselves. Id.

In the foregoing passage regarding the existing regulatory standard for ephemeral streams, Justice Kennedy also provided a

‘‘but see’’ citation to a 2004 U.S. General Accounting Office (now the U.S. Government Accountability Office) (GAO) report ‘‘noting variation in results among Corps district

offices.’’ Id. In 2005, the Corps issued a regulatory guidance letter (RGL 05–05) to Corps districts on OHWM identification that was designed to ensure more consistent practice. The Corps has also issued documents to provide additional technical assistance for problematic OHWM

delineations. See, e.g., R.W. Lichvar and S.M.


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McColley, U.S. Army Corps of Engineers, A Field Guide to the Identification of the Ordinary High Water Mark (OHWM) in the Arid West Region of the Western United States: A Delineation Manual, ERDC/CRREL TR–08–12 (2008). Moreover, the agencies propose today for the first time a regulatory definition of ‘‘tributary.’’ The definition expressly addresses some of the issues with respect to identification of an OHWM that caused many of the inconsistencies reported by the GAO. For example, this proposed regulation clearly provides that a water that otherwise meets the proposed definition of tributary remains a jurisdictional tributary

even if there are natural or man-made breaks in the OHWM. The proposed definition also provides a non-exclusive list of examples of breaks in the OHWM to assist in clearly and consistently determining what meets the definition of tributary.

Most fundamentally, the agencies believe

that the scientific literature demonstrates that tributaries, as a category and as the agencies propose to define them, play a critical role in the integrity of aquatic systems comprising traditional navigable waters and interstate waters, and therefore are ‘‘waters of the United States’’ within the meaning of the

Clean Water Act.

Adjacent Waters

The CWA explicitly establishes authority over adjacent wetlands. Under section 404(g), states are authorized to assume responsibility

for administration of the section 404 permitting program with respect to ‘‘navigable waters (other than those waters which are presently used, or are susceptible to use in their natural condition or by reasonable improvement as a means to transport interstate or foreign commerce shoreward to their ordinary high water mark, including all waters which are subject to the

ebb and flow of the tide shoreward to their mean high water mark, or mean higher high water mark on the west coast, including wetlands adjacent thereto).’’ 33 U.S.C. 1344(g)(1) (emphasis added). While this provision mainly serves as a limitation on the scope of waters for which states may be authorized to issue permits, it also shows that Congress was concerned with the protection of adjacent wetlands and recognized their important role in protecting downstream traditional navigable waters. Indeed, the existing definition of adjacency was developed in recognition of the integral role wetlands play in broader aquatic

ecosystems: The regulation of activities that cause water pollution cannot rely on . . . artificial lines

. . . but must focus on all waters that together form the entire aquatic system. Water moves in hydrologic cycles, and the pollution of this part of the aquatic system, regardless of whether it is above or below an ordinary high water mark, or mean high tide line, will affect the water quality of the other waters within that aquatic system. For this reason, the landward limit of Federal jurisdiction under Section 404 must include any adjacent wetlands that form the border of or are in reasonable proximity to other waters of the United States, as these wetlands are part of this aquatic system. 42 FR 37128, July 19, 1977. As the Supreme Court found in United

States v. Riverside Bayview Homes, Inc., ‘‘the evident breadth of congressional concern for protection of water quality and aquatic ecosystems suggests that it is reasonable for the Corps to interpret the term ‘waters’ to encompass wetlands adjacent to waters as more conventionally defined.’’ 474 U.S. at

133.

In upholding the Corps’ judgment about the relationship between waters and their adjacent wetlands, the Supreme Court in Riverside Bayview acknowledged that the agencies’ regulations take into account functions provided by wetlands in support of this relationship. ‘‘[A]djacent wetlands may ‘serve significant natural biological functions, including food chain production, general habitat, and nesting, spawning, rearing and resting sites for aquatic . . . species.’ ’’ Id. at 133 (citing § 320.4(b)(2)(i)). The Court further stated that the Corps had reasonably concluded that ‘‘wetlands adjacent to lakes,
rivers, streams, and other bodies of water may function as integral parts of the aquatic

environment even when the moisture creating the wetlands does not find its source in the adjacent bodies of water.’’ 474 U.S. at

135.

Two decades later, a majority of justices in Rapanos concluded that the agencies’ regulatory definition of adjacent wetlands reasonable. Justice Kennedy stated:

As the Court noted in Riverside Bayview, ‘the Corps has concluded that wetlands may serve to filter and purify water draining into adjacent bodies of water, 33 CFR 320.4(b)(2)(vii)(1985), and to slow the flow of
surface runoff into lakes, rivers, and streams and thus prevent flooding and erosion, see § 320.4(b)(2)(iv) and (v).’ Where wetlands perform these filtering and runoff-control functions, filling them may increase downstream pollution, much as a discharge of toxic pollutants would.. . . In many cases, moreover, filling in wetlands separated from another water by a berm can mean that flood water, impurities, or runoff that would have

been stored or contained in the wetlands will instead flow out to major waterways. With these concerns in mind, the Corps’ definition of adjacency is a reasonable one, for it may be the absence of an interchange of waters prior to the dredge and fill activity that makes protection of the wetlands critical to the statutory scheme.

547 U.S. at 775 (citations omitted). The four dissenting justices similarly

concluded:

The Army Corps has determined that wetlands adjacent to tributaries of traditionally navigable waters preserve the quality of our Nation’s waters by, among other things, providing habitat for aquatic animals, keeping excessive sediment and toxic pollutants out of adjacent waters, and reducing downstream flooding by absorbing water at times of high flow. The Corps’ resulting decision to treat these wetlands as encompassed within the term ‘waters of the United States’ is a quintessential example of the Executive’s reasonable interpretation of a statutory provision. Id. at 778 (citing Chevron U.S.A. Inc. v. Natural Resources Defense Council, Inc., 467 U.S. 837, 842–845 (1984)).

For those wetlands adjacent to traditional navigable waters, Justice Kennedy concluded

in Rapanos that the agencies’ existing regulation ‘‘rests upon a reasonable inference of ecologic interconnection, and the assertion of jurisdiction for those wetlands is sustainable under the Act by showing adjacency alone.’’ 547 U.S. at 780. For other adjacent waters, including adjacent wetlands, Justice Kennedy’s significant nexus standard provides a framework for establishing categories of waters which are per se ‘‘waters of the United States.’’ First, he provided that wetlands are jurisdictional if they ‘‘either alone or in combination with similarly situated lands in the region, significantly affect the chemical, physical, and biological integrity of other covered waters more readily understood as ‘navigable.’ ’’ Id. at 780. Next, Justice Kennedy stated that ‘‘[t]hrough regulation or adjudication, the Corps may choose to identify categories of tributaries that, due to their volume of flow (either annually or on average), their proximity to navigable waters, or other relevant considerations, are significant enough that wetlands adjacent to them are likely, in the majority of cases, to perform important functions for an aquatic system incorporating navigable waters.’’ Id. at 780–81.

While the issue was not before the Supreme Court, it is reasonable to also assess

whether non-wetland waters have a significant nexus, as Justice Kennedy’s opinion makes clear that a significant nexus is a touchstone for CWA jurisdiction. The agencies have determined that adjacent waters as defined in today’s proposed rule, alone or in combination with other adjacent waters in the region that drains to a traditional navigable water, interstate water or the territorial seas, significantly affect the chemical, physical, and biological integrity of those waters. As explained in more detail in Section H, below, the proposed rule interprets the phrase ‘‘in the region’’ to mean

the watershed that drains to the nearest traditional navigable water or interstate water through a single point of entry. The agencies

have determined that because the movement of water from watershed drainage basins to river networks and lakes shapes the development and function of these systems in a way that is critical to their long term health, the watershed is a reasonable and technically appropriate reflection of Congressional intent.

The agencies have concluded that all waters that meet the proposed definition of ‘‘adjacent’’ are similarly situated for purposes of analyzing whether they, in the majority of cases, have a significant nexus to an (a)(1) through (a)(3) water. Based on the agencies’ review of the scientific literature, we have concluded that these waters, when bordering, contiguous or located in the floodplain or riparian area, or when otherwise meeting the definition of ‘‘adjacent,’’ provide many similar functions that significantly affect the chemical, physical, or biological integrity of traditional navigable waters, interstate waters, or the territorial seas. Further, because the proposed definition generally


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focuses on the location of the waters (i.e., those that are located near (a)(1) through (a)(5) waters), interpreting the term ‘‘similarly situated’’ to include all adjacent waters, as defined in the proposed rule, is

reasonable and consistent with the science. The geographic position of an ‘‘adjacent’’ water relative to the tributary is indicative of the relationship to it, with many of its defining characteristics resulting from the movement of materials and energy between the categories of waters. The scientific

literature documents that waters that are adjacent to (a)(1) through (a)(5) waters, including wetlands, oxbow lakes and adjacent ponds, are integral parts of stream networks because of their ecological functions and how they interact with each other, and with downstream traditional navigable waters, interstate waters, or the territorial seas. In other words, tributaries and their adjacent waters, and the downstream traditional navigable waters, interstate waters, and territorial seas into which those waters flow, are an integrated ecological system, and discharges of pollutants, including discharges of dredged or fill material, into any component of that ecological system, must be regulated under

the CWA to restore and maintain the chemical, physical, or biological integrity of

these waters.

Based on the science, as summarized below, the agencies have concluded that wetlands and waters adjacent to all tributaries that meet the proposed definition of ‘‘tributary’’ provide vital functions for downstream traditional navigable waters, interstate waters, or the territorial seas. In particular, the scientific literature supports the conclusion that waters adjacent to all tributaries as defined in section (a)(5) have a significant nexus to waters described in paragraphs (a)(1) through (a)(3). Because smaller streams, whether perennial, intermittent, or ephemeral, are much more common than larger streams, the volume of

a stream’s flow is not the best measure of its contribution to the chemical, physical, or biological integrity of downstream waters. Report at 4–2, 4–3. As discussed in more detail in Appendix A, small streams cumulatively exert a strong influence on downstream waters, partly by collectively providing a substantial amount of the river’s

water, id. at 4–3, 4–4 to 4–5, but also by playing unique roles that large streams typically do not, including providing habitat for aquatic macroinvertebrates which help

maintain the health of the downstream water. Waters adjacent to those small tributary streams, therefore, also significantly affect (a)(1) through (a)(3) waters through the movement of energy and materials between adjacent waters and those tributaries, resulting ultimately in significant downstream effects on the chemical, physical, and biological integrity of the (a)(1) through (a)(3) waters.

‘‘Other Waters’’

In Rapanos, Justice Kennedy provides an approach for determining what constitutes a ‘‘significant nexus’’ that can serve as a basis for defining ‘‘waters of the United States’’ through regulation. Justice Kennedy concluded that ‘‘to constitute ‘navigable waters’ under the Act, a water or wetland must possess a ‘significant nexus’ to waters that are or were navigable in fact or that could reasonably be so made.’’ Id. at 759 (citing SWANCC, 531 U.S. at 167, 172). Again, the four justices who signed on to Justice Stevens’ opinion would have upheld jurisdiction under the agencies’ existing regulations and stated that they would uphold jurisdiction under either the plurality or Justice Kennedy’s opinion. Justice Kennedy stated that wetlands should be considered to possess the requisite nexus in the context of assessing whether wetlands are jurisdictional: ‘‘if the wetlands, either alone or in combination with similarly situated [wetlands] in the region, significantly affect the chemical, physical, and biological integrity of other covered waters more readily understood as ‘navigable.’ ’’ Id. at 780. In light ofRapanos and SWANCC, the ‘‘significant nexus’’ standard for CWA jurisdiction that Justice Kennedy’s opinion applied to adjacent wetlands also can reasonably be applied to other waters such as ponds, lakes, and non-adjacent wetlands that may have a significant nexus to a traditional navigable water, an interstate water, or the

territorial seas.

The proposed rule includes a definition of significant nexus that is consistent with Justice Kennedy’s significant nexus standard. In characterizing the significant nexus standard, Justice Kennedy stated: ‘‘The required nexus must be assessed in terms of the statute’s goals and purposes. Congress
enacted the [CWA] to ‘restore and maintain the chemical, physical, and biological integrity of the Nation’s waters’ . . ..’’ 547 U.S. at 779. It clear that Congress intended

the CWA to ‘‘restore and maintain’’ all three forms of ‘‘integrity,’’ 33 U.S.C. 1251(a), so if any one form is compromised then that is contrary to the statute’s stated objective. It would subvert the intent if the CWA only protected waters upon a showing that they had effects on every attribute of a traditional navigable water, interstate water, or territorial sea. Therefore, a showing of a significant chemical, physical, or biological affect should satisfy the significant nexus

standard.

Justice Kennedy’s opinion provides guidance pointing to many functions of waters that might demonstrate a significant nexus, such as sediment trapping, nutrient recycling, pollutant trapping and filtering, retention or attenuation of flood waters, and runoff storage. See 547 U.S. at 775, 779–80. Furthermore, Justice Kennedy recognized that a hydrologic connection is not necessary to establish a significant nexus, because in some cases the absence of a hydrologic connection would show the significance of a water to the aquatic system, such as retention of flood waters or pollutants that would

otherwise flow downstream to the traditional navigable water or interstate water. Id. at 775. Finally, Justice Kennedy was clear that the requisite nexus must be more than ‘‘speculative or insubstantial’’ in order to be significant. Id. at 780. Justice Kennedy’s

standard is consistent with basic scientific principles about how to restore and maintain the integrity of aquatic ecosystems. Similarly Situated

For purposes of analyzing the significant nexus of tributaries and adjacent waters, tributaries that meet the proposed definition of ‘‘tributary’’ in a watershed draining to an (a)(1) through (a)(3) water are similarly situated, and adjacent waters that meet the proposed definition of ‘‘adjacent’’ in a watershed draining to an (a)(1) through (a)(3) water are similarly situated. That is reasonable because the agencies are identifying characteristics of these waters through the regulation and documenting the

science that demonstrates that these defined tributaries and defined adjacent waters provide similar functions in the watershed. As stated above, the functions of the tributaries are inextricably linked and have a cumulative effect on the integrity of the downstream traditional navigable water or

interstate water. There is also an obvious locational relationship between the (a)(1), (a)(2) or (a)(3) water and the streams, lakes,

and wetlands that meet the definition of tributaries and the definition of adjacent waters; these waters have a clear linear relationship resulting from the simple

existence of the channel itself and the

direction of flow. See Appendix A, Scientific

Evidence.

‘‘Other waters,’’ on the other hand, constitute a broad range of different types of waters performing different functions. In light of the range and degree of functions performed by waters that are neither tributaries nor adjacent waters under today’s proposed rule, the agencies propose a definition of similarly situated which takes into account similarity of functions provided and situation in the landscape. Since the focus of the significant nexus standard is on protecting the chemical, physical, and biological integrity of the nation’s waters, the agencies propose to interpret the phrase ‘‘similarly situated’’ in terms of whether the functions provided by the particular ‘‘other waters’’ are similar and, therefore, whether such ‘‘other waters’’ are collectively influencing the chemical, physical, or biological integrity of downstream waters. There are many functions of waters that might demonstrate a significant nexus, such as sediment trapping, nutrient recycling, pollutant trapping and filtering, retention or attenuation of flood waters, runoff storage, and provision of habitat. See 547 U.S. at 775, 779–80. This approach is consistent not only with the significant nexus standard, but with the science of aquatic systems.

The absence of a hydrologic connection

between ‘‘other waters’’ and traditional navigable waters, interstate waters, or the territorial seas may demonstrate the presence of a significant nexus between such waters, as Justice Kennedy recognized in his opinion. ‘‘Other waters’’ frequently function alone or cumulatively with similarly situated ‘‘other waters’’ in the region to capture runoff, rain water, or snowmelt and thereby protect the integrity of downstream waters by reducing potential flooding or trapping pollutants that

would otherwise reach a traditional navigable water or interstate water. See id. at
775. Such waters can be crucial in controlling flooding as well as in maintaining water quality by trapping or transforming


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pollutants such as excess nutrients or sediment, for example, or retaining precipitation or snow melt, thereby reducing contamination or flooding of traditional navigable waters, interstate waters, or the

territorial seas.

Significant Nexus

The agencies propose to define the term ‘‘significant nexus’’ consistent with language

in SWANCC and Rapanos. The proposed definition of ‘‘significant nexus’’ at (c)(7) relies most significantly on Justice Kennedy’s Rapanos opinion which recognizes that not all waters have this requisite connection to waters covered by paragraphs (a)(1) through (a)(3) of the proposed regulations. Justice Kennedy was clear that the requisite nexus must be more than ‘‘speculative or insubstantial. . ., ’’ Rapanos, 547 U.S. at 780, in order to be significant and the proposed rule defines significant nexus in precisely those terms. In Rapanos, Justice Kennedy stated that in both the consolidated

cases before the Court the record contained evidence suggesting the possible existence of a significant nexus according to the principles he identified. See id. at 783. Justice Kennedy concluded that ‘‘the end result in these cases and many others to be considered by the Corps may be the same as that suggested by the dissent, namely, that the Corps’ assertion of jurisdiction is valid.’’

Id. Justice Kennedy remanded the cases because neither the agency nor the reviewing courts properly applied the controlling legal

standard—whether the wetlands at issue had a significant nexus. See id. Justice Kennedy was clear however, that ‘‘[m]uch the same evidence should permit the establishment of a significant nexus with navigable-in-fact waters, particularly if supplemented by further evidence about the significance of the

tributaries to which the wetlands are

connected.’’ Id. at 784.

With respect to one of the wetlands at issue

in the consolidated Rapanos cases, Justice Kennedy stated:

In Carabell, No. 04–1384, the record also contains evidence bearing on the jurisdictional inquiry. The Corps noted in deciding the administrative appeal that
‘‘[b]esides the effects on wildlife habitat and water quality, the [district office] also notedthat the project would have a major, longterm detrimental effect on wetlands, flood retention, recreation and conservation and overall ecology

. . . . The Corps’ evaluation further noted that by ‘eliminat[ing] the potential ability of the wetland to act as a sediment catch basin,’’ the proposed project

‘‘would contribute to increased runoff and . . . accretion along the drain and further

downstream in Auvase Creek.’ . . . And it

observed that increased runoff from the site would likely cause downstream areas to ‘‘see an increase in possible flooding magnitude and frequency.’’

Id. at 785–86. Justice Kennedy also expressed concern that ‘‘[t]he conditional language in these assessments—‘potential ability,’ ‘possible flooding’—could suggest an undue degree of speculation.’’ Id.at 786.

Justice Kennedy’s observations regarding the above case provide guidance as to what it means for a nexus to be more than merely speculative or insubstantial and inform the proposed definition of ‘‘significant nexus.’’ It is important to note, however, that where Justice Kennedy viewed the language ‘‘more than speculative or insubstantial’’ to suggest an undue degree of speculation, scientists do not equate certain conditional language (such as ‘‘may’’ or ‘‘could’’) with speculation, but rather with the rigorous and precise language of science necessary when applying specific findings in another individual situation or more broadly across a variety of situations.

Certain terms used in a scientific context do not have the same implications that they have in a legal or policy context. Scientists use cautionary language, such as ‘‘may’’ or ‘‘could,’’ when applying specific findings on a broader scale to avoid the appearance of overstating their research results and to avoid inserting bias into their findings (such that the reader may think the results of one study are applicable in all related studies). Words like ‘‘potential’’ are commonly used in the biological sciences, but when viewed under a legal and policy veil, may seem to mean the same as ‘‘speculative’’ or ‘‘insubstantial.’’ Instead, potential in scientific terms means ability or capability. For example, when the term ‘‘potential’’ is used to describe how a wetland has the potential to act as a sink for floodwater and pollutants, scientists mean that wetlands in general do indeed perform those functions, but whether a particular wetland performs that function is dependent upon the circumstances that would create conditions for floodwater or pollutants in the watershed to reach that particular wetland to retain and transform. That does not mean, however, that this nexus to downstream waters is ‘‘speculative;’’ indeed the wetland would be expected to provide these functions under the proper circumstances.



### Definition of ‘‘Waters of the United

States’’ Under the Clean Water Act.

List of Subjects

33 CFR Part 328

Environmental protection, Administrative practice and procedure, Intergovernmental relations, Navigation, Water pollution control, Waterways.

40 CFR Part 110

Environmental protection, Water pollution control.

40 CFR Part 112

Environmental protection, Water pollution control.

40 CFR Part 116

Environmental protection, Water pollution control.

40 CFR Part 117

Environmental protection, Water pollution control.

40 CFR Part 122

Environmental protection, Water pollution control. 40 CFR Part 230

Environmental protection, Water pollution control.

40 CFR Part 232

Environmental protection, Water pollution control.

40 CFR Part 300

Environmental protection, Water pollution control.

40 CFR Part 302

Environmental protection, Water pollution control.

40 CFR Part 401

Environmental protection, Water pollution control.

Dated: March 25, 2014.

Gina McCarthy,

Administrator, Environmental Protection Agency.

Dated: March 24, 2014.

Jo Ellen Darcy,
Assistant Secretary of the Army (Civil Works), Department of the Army.



### Title 33—Navigation and Navigable

Waters

For the reasons set out in the preamble, title 33, chapter I of the Code of Federal Regulations is proposed to be

amended as follows:

**PART 328—DEFINITION OF WATERS**

**OF THE UNITED STATES**

■ 

### 1. The authority citation for part 328

continues to read as follows:

Authority: The Clean Water Act, 33 U.S.C.

1251 et seq.

■ 

### 2. Section 328.3 is amended by removing the introductory text and revising paragraphs (a), (b), and (c) to

read as follows:

**§ 328.3 Definitions.**



### (a) For purposes of all sections of the Clean Water Act, 33 U.S.C. 1251 et. seq. and its implementing regulations, subject to the exclusions in paragraph (b) of this section, the term ‘‘waters of

the United States’’ means:

(1) All waters which are currently used, were used in the past, or may be susceptible to use in interstate or foreign commerce, including all waters which are subject to the ebb and flow of the tide;

(2) All interstate waters, including interstate wetlands;

(3) The territorial seas; (4) All impoundments of waters identified in paragraphs (a)(1) through (3) and (5) of this section;

(5) All tributaries of waters identified in paragraphs (a)(1) through (4) of this
section;


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(6) All waters, including wetlands, adjacent to a water identified in paragraphs (a)(1) through (5) of this section; and

(7) On a case-specific basis, other waters, including wetlands, provided that those waters alone, or in combination with other similarly situated waters, including wetlands, located in the same region, have a significant nexus to a water identified in paragraphs (a)(1) through (3) of this

section.

(b) The following are not ‘‘waters of the United States’’ notwithstanding whether they meet the terms of paragraphs (a)(1) through (7) of this

section—

(1) Waste treatment systems, including treatment ponds or lagoons, designed to meet the requirements of

the Clean Water Act.

(2) Prior converted cropland. Notwithstanding the determination of an area’s status as prior converted cropland by any other Federal agency, for the purposes of the Clean Water Act the final authority regarding Clean Water Act jurisdiction remains with

EPA.

(3) Ditches that are excavated wholly in uplands, drain only uplands, and have less than perennial flow.

(4) Ditches that do not contribute flow, either directly or through another water, to a water identified in paragraphs (a)(1) through (4) of this

section.

(5) The following features: (i) Artificially irrigated areas that would revert to upland should application of irrigation water to that

area cease;

(ii) Artificial lakes or ponds created by excavating and/or diking dry land and used exclusively for such purposes as stock watering, irrigation, settling basins, or rice growing;

(iii) Artificial reflecting pools or swimming pools created by excavating and/or diking dry land;

(iv) Small ornamental waters created by excavating and/or diking dry land for primarily aesthetic reasons;

(v) Water-filled depressions created incidental to construction activity;

(vi) Groundwater, including groundwater drained through subsurface drainage systems; and

(vii) Gullies and rills and non-wetland

swales.

(c) Definitions— (1) Adjacent. The term adjacent means bordering, contiguous or neighboring. Waters, including wetlands, separated from other waters of the United States by man-made dikes or barriers, natural river berms, beach dunes and the like are ‘‘adjacent

waters.’’ (2) Neighboring. The term neighboring, for purposes of the term ‘‘adjacent’’ in this section, includes waters located within the riparian area or floodplain of a water identified in paragraphs (a)(1) through (5) of this section, or waters with a shallow subsurface hydrologic connection or confined surface hydrologic connection to such a jurisdictional water.

(3) Riparian area. The term riparian

area means an area bordering a water where surface or subsurface hydrology directly influence the ecological processes and plant and animal community structure in that area. Riparian areas are transitional areas between aquatic and terrestrial ecosystems that influence the exchange of energy and materials between those
ecosystems.

(4) Floodplain. The termfloodplain means an area bordering inland or coastal waters that was formed by sediment deposition from such water under present climatic conditions and is inundated during periods of moderate to high water flows.

(5) Tributary. The term tributary means a water physically characterized by the presence of a bed and banks and ordinary high water mark, as defined at 33 CFR 328.3(e), which contributes flow, either directly or through another water, to a water identified in paragraphs (a)(1) through (4) of this section. In addition, wetlands, lakes, and ponds are tributaries (even if they lack a bed and banks or ordinary high water mark) if they contribute flow, either directly or through another water to a water identified in paragraphs (a)(1) through (3) of this section. A water that otherwise qualifies as a tributary under

this definition does not lose its status as a tributary if, for any length, there are one or more man-made breaks (such as bridges, culverts, pipes, or dams), or one or more natural breaks (such as wetlands at the head of or along the run of a stream, debris piles, boulder fields, or a stream that flows underground) so long as a bed and banks and an ordinary high water mark can be identified upstream of the break. A tributary, including wetlands, can be a natural, man-altered, or man-made water and includes waters such as rivers, streams, lakes, ponds, impoundments, canals, and ditches not excluded in paragraph (b)(3) or (4) of this section.

(6) Wetlands. The term wetlands

means those areas that are inundated or saturated by surface or groundwater at a frequency and duration sufficient to support, and that under normal circumstances do support, a prevalence of vegetation typically adapted for life

in saturated soil conditions. Wetlands generally include swamps, marshes, bogs and similar areas.

(7) Significant nexus. The term significant nexus means that a water, including wetlands, either alone or in combination with other similarly situated waters in the region (i.e., the

watershed that drains to the nearest water identified in paragraphs (a)(1) through (3) of this section), significantly affects the chemical, physical, or biological integrity of a water identified in paragraphs (a)(1) through (3) of this section. For an effect to be significant, it must be more than speculative or insubstantial. Other waters, including wetlands, are similarly situated when they perform similar functions and are located sufficiently close together or sufficiently close to a ‘‘water of the United States’’ so that they can be evaluated as a single landscape unit with regard to their effect on the chemical, physical, or biological integrity of a water identified in paragraphs (a)(1) through (3) of this

section.

* * * * *

Title 40—Protection of Environment

For the reasons set out in the preamble, title 40, chapter I of the Code of Federal Regulations is proposed to be

amended as follows:

**PART 110—DISCHARGE OF OIL**

■ 

### 3. The authority citation for part 110

continues to read as follows:

Authority: The Clean Water Act, 33 U.S.C.

1321 et seq.

■ 

### 4. Section 110.1 is amended by revising the definition of ‘‘navigable

waters’’ to read as follows:

**§ 110.1 Definitions.**



### * * * * *

Navigable waters means the waters of the United States, including the

territorial seas.

(1) For purposes of all sections of the Clean Water Act, 33 U.S.C. 1251 et. seq. and its implementing regulations, subject to the exclusions in paragraph (2) of this definition, the term ‘‘waters

of the United States’’ means:

(i) All waters which are currently used, were used in the past, or may be susceptible to use in interstate or foreign commerce, including all waters which are subject to the ebb and flow of the tide;

(ii) All interstate waters, including interstate wetlands;

(iii) The territorial seas; (iv) All impoundments of waters identified in paragraphs (1)(i) through (iii) and (v) of this definition;


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(v) All tributaries of waters identified in paragraphs (1)(i) through (iv) of this definition;

(vi) All waters, including wetlands, adjacent to a water identified in paragraphs (1)(i) through (v) of this definition; and

(vii) On a case-specific basis, other waters, including wetlands, provided that those waters alone, or in combination with other similarly situated waters, including wetlands, located in the same region, have a significant nexus to a water identified in paragraphs (1)(i) through (iii) of this

definition.

(2) The following are not ‘‘waters of the United States’’ notwithstanding whether they meet the terms of paragraphs (1)(i) through (vii) of this

definition—

(i) Waste treatment systems, including treatment ponds or lagoons, designed to meet the requirements of the Clean

Water Act.

(ii) Prior converted cropland. Notwithstanding the determination of an area’s status as prior converted cropland by any other Federal agency, for the purposes of the Clean Water Act the final authority regarding Clean Water Act jurisdiction remains with

EPA.

(iii) Ditches that are excavated wholly in uplands, drain only uplands, and have less than perennial flow.

(iv) Ditches that do not contribute flow, either directly or through another water, to a water identified in paragraphs (1)(i) through (iv) of this

definition.

(v) The following features: (A) Artificially irrigated areas that would revert to upland should application of irrigation water to that

area cease;

(B) Artificial lakes or ponds created by excavating and/or diking dry land and used exclusively for such purposes as stock watering, irrigation, settling basins, or rice growing;

(C) Artificial reflecting pools or swimming pools created by excavating and/or diking dry land;

(D) Small ornamental waters created by excavating and/or diking dry land for primarily aesthetic reasons;

(E) Water-filled depressions created incidental to construction activity;

(F) Groundwater, including groundwater drained through subsurface drainage systems; and

(G) Gullies and rills and non-wetland

swales.

(3) Definitions— (i) Adjacent. The term adjacent means bordering, contiguous or neighboring. Waters, including wetlands, separated

from other waters of the United States by man-made dikes or barriers, natural river berms, beach dunes and the like are ‘‘adjacent waters.’’

(ii) Neighboring. The term neighboring, for purposes of the term ‘‘adjacent’’ in this section, includes waters located within the riparian area or floodplain of a water identified in paragraphs (1)(i) through (v) of this definition, or waters with a shallow subsurface hydrologic connection or confined surface hydrologic connection to such a jurisdictional water.

(iii) Riparian area. The term riparian

area means an area bordering a water where surface or subsurface hydrology directly influence the ecological processes and plant and animal community structure in that area. Riparian areas are transitional areas between aquatic and terrestrial ecosystems that influence the exchange of energy and materials between those
ecosystems.

(iv) Floodplain. The termfloodplain means an area bordering inland or coastal waters that was formed by sediment deposition from such water under present climatic conditions and is inundated during periods of moderate to high water flows.

(v) Tributary. The term tributary means a water physically characterized by the presence of a bed and banks and ordinary high water mark, as defined at 33 CFR 328.3(e), which contributes flow, either directly or through another water, to a water identified in paragraphs (1)(i) through (iv) of this definition. In addition, wetlands, lakes, and ponds are tributaries (even if they lack a bed and banks or ordinary high water mark) if they contribute flow, either directly or through another water to a water identified in paragraphs (1)(i) through (iii) of this definition. A water that otherwise qualifies as a tributary

under this definition does not lose its status as a tributary if, for any length,

there are one or more man-made breaks (such as bridges, culverts, pipes, or dams), or one or more natural breaks (such as wetlands at the head of or along the run of a stream, debris piles, boulder fields, or a stream that flows underground) so long as a bed and banks and an ordinary high water mark can be identified upstream of the break. A tributary, including wetlands, can be a natural, man-altered, or man-made

water and includes waters such as rivers, streams, lakes, ponds, impoundments, canals, and ditches not excluded in paragraph (2)(iii) or (iv) of

this definition.

(vi) Wetlands. The term wetlands

means those areas that are inundated or saturated by surface or groundwater at a frequency and duration sufficient to support, and that under normal circumstances do support, a prevalence of vegetation typically adapted for life

in saturated soil conditions. Wetlands generally include swamps, marshes, bogs and similar areas.

(vii) Significant nexus. The term significant nexus means that a water, including wetlands, either alone or in combination with other similarly situated waters in the region (i.e., the

watershed that drains to the nearest water identified in paragraphs (1)(i) through (iii) of this definition), significantly affects the chemical, physical, or biological integrity of a water identified in paragraphs (1)(i) through (iii) of this definition. For an effect to be significant, it must be more than speculative or insubstantial. Other waters, including wetlands, are similarly situated when they perform

similar functions and are located sufficiently close together or sufficiently

close to a ‘‘water of the United States’’ so that they can be evaluated as a single landscape unit with regard to their effect on the chemical, physical, or biological integrity of a water identified in paragraphs (1)(i) through (iii) of this

definition.

* * * * *

**PART 112—OIL POLLUTION**

**PREVENTION**

■ 

### 5. The authority citation for part 112

continues to read as follows:

Authority: The Clean Water Act, 33 U.S.C.

1321 et seq.

■ 

### 6. Section 112.2 is amended by revising the definition of ‘‘navigable

waters’’ to read as follows:

**§ 112.2 Definitions.**



### * * * * *

Navigable waters means the waters of the United States, including the

territorial seas.

(1) For purposes of all sections of the Clean Water Act, 33 U.S.C. 1251 et. seq. and its implementing regulations, subject to the exclusions in paragraph (b) of this section, the term ‘‘waters of

the United States’’ means:

(i) All waters which are currently used, were used in the past, or may be susceptible to use in interstate or foreign commerce, including all waters which are subject to the ebb and flow of the tide;

(ii) All interstate waters, including interstate wetlands;

(iii) The territorial seas; (iv) All impoundments of waters identified in paragraphs (1)(i) through (iii) and (v) of this definition;


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(v) All tributaries of waters identified in paragraphs (1)(i) through (iv) of this definition;

(vi) All waters, including wetlands, adjacent to a water identified in paragraphs (1)(i) through (v) of this definition; and

(vii) On a case-specific basis, other waters, including wetlands, provided that those waters alone, or in combination with other similarly situated waters, including wetlands, located in the same region, have a significant nexus to a water identified in paragraphs (1)(i) through (iii) of this

definition.

(2) The following are not ‘‘waters of the United States’’ notwithstanding whether they meet the terms of paragraphs (1)(i) through (vii) of this

definition ——

(i) Waste treatment systems, including treatment ponds or lagoons, designed to meet the requirements of the Clean

Water Act.

(ii) Prior converted cropland. Notwithstanding the determination of an area’s status as prior converted cropland by any other Federal agency, for the purposes of the Clean Water Act the final authority regarding Clean Water Act jurisdiction remains with

EPA.

(iii) Ditches that are excavated wholly in uplands, drain only uplands, and have less than perennial flow.

(iv) Ditches that do not contribute flow, either directly or through another water, to a water identified in paragraphs (1)(i) through (iv) of this

definition.

(v) The following features: (A) Artificially irrigated areas that would revert to upland should application of irrigation water to that

area cease;

(B) Artificial lakes or ponds created by excavating and/or diking dry land and used exclusively for such purposes as stock watering, irrigation, settling basins, or rice growing;

(C) Artificial reflecting pools or swimming pools created by excavating and/or diking dry land;

(D) Small ornamental waters created by excavating and/or diking dry land for primarily aesthetic reasons;

(E) Water-filled depressions created incidental to construction activity;

(F) Groundwater, including groundwater drained through subsurface drainage systems; and

(G) Gullies and rills and non-wetland

swales.

(3) Definitions— (i) Adjacent. The term adjacent means bordering, contiguous or neighboring. Waters, including wetlands, separated

from other waters of the United States by man-made dikes or barriers, natural river berms, beach dunes and the like are ‘‘adjacent waters.’’

(ii) Neighboring. The term neighboring, for purposes of the term ‘‘adjacent’’ in this section, includes waters located within the riparian area or floodplain of a water identified in paragraphs (1)(i) through (v) of this definition, or waters with a shallow subsurface hydrologic connection or confined surface hydrologic connection to such a jurisdictional water.

(iii) Riparian area. The term riparian

area means an area bordering a water where surface or subsurface hydrology directly influence the ecological processes and plant and animal community structure in that area. Riparian areas are transitional areas between aquatic and terrestrial ecosystems that influence the exchange of energy and materials between those
ecosystems.

(iv) Floodplain. The termfloodplain means an area bordering inland or coastal waters that was formed by sediment deposition from such water under present climatic conditions and is inundated during periods of moderate to high water flows.

(v) Tributary. The term tributary means a water physically characterized by the presence of a bed and banks and ordinary high water mark, as defined at 33 CFR 328.3(e), which contributes flow, either directly or through another water, to a water identified in paragraphs (1)(i) through (iv) of this definition. In addition, wetlands, lakes, and ponds are tributaries (even if they lack a bed and banks or ordinary high water mark) if they contribute flow, either directly or through another water to a water identified in paragraphs (1)(i) through (iii) of this definition. A water that otherwise qualifies as a tributary

under this definition does not lose its status as a tributary if, for any length,

there are one or more man-made breaks (such as bridges, culverts, pipes, or dams), or one or more natural breaks (such as wetlands at the head of or along the run of a stream, debris piles, boulder fields, or a stream that flows underground) so long as a bed and banks and an ordinary high water mark can be identified upstream of the break. A tributary, including wetlands, can be a natural, man-altered, or man-made

water and includes waters such as rivers, streams, lakes, ponds, impoundments, canals, and ditches not excluded in paragraph (2)(iii) or (iv) of

this definition.

(6) Wetlands. The term wetlands

means those areas that are inundated or saturated by surface or groundwater at a frequency and duration sufficient to support, and that under normal circumstances do support, a prevalence of vegetation typically adapted for life

in saturated soil conditions. Wetlands generally include swamps, marshes, bogs and similar areas.

(7) Significant nexus. The term significant nexus means that a water, including wetlands, either alone or in combination with other similarly situated waters in the region (i.e., the

watershed that drains to the nearest water identified in paragraphs (1)(i) through (iii) of this definition), significantly affects the chemical, physical, or biological integrity of a water identified in paragraphs (1)(i) through (iii) of this definition. For an effect to be significant, it must be more than speculative or insubstantial. Other waters, including wetlands, are similarly situated when they perform

similar functions and are located sufficiently close together or sufficiently

close to a ‘‘water of the United States’’ so that they can be evaluated as a single landscape unit with regard to their effect on the chemical, physical, or biological integrity of a water identified in paragraphs (1)(i) through (iii) of this

definition.

* * * * *

**PART 116—DESIGNATION OF**

**HAZARDOUS SUBSTANCE**

■ 

### 7. The authority citation for part 116

continues to read as follows:

Authority: The Clean Water Act, 33 U.S.C.

1251 et seq.

■ 

### 8. Section 116.3 is amended by revising the definition of ‘‘navigable

waters’’ to read as follows:

**§ 116.3 Definitions.**



### * * * * *

Navigable waters is defined in section 502(7) of the Act to mean ‘‘waters of the United States, including the territorial

seas.’’

(1) For purposes of all sections of the Clean Water Act, 33 U.S.C. 1251 et seq. and its implementing regulations, subject to the exclusions in paragraph (2) of this definition, the term ‘‘waters

of the United States’’ means:

(i) All waters which are currently used, were used in the past, or may be susceptible to use in interstate or foreign commerce, including all waters which are subject to the ebb and flow of the tide;

(ii) All interstate waters, including interstate wetlands;

(iii) The territorial seas; (iv) All impoundments of waters identified in paragraphs (1)(i) through (iii) and (v) of this definition;.


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(v) All tributaries of waters identified in paragraphs (1)(i) through (iv) of this definition;

(vi) All waters, including wetlands, adjacent to a water identified in paragraphs (1)(i) through (v) of this definition; and

(vii) On a case-specific basis, other waters, including wetlands, provided that those waters alone, or in combination with other similarly situated waters, including wetlands, located in the same region, have a significant nexus to a water identified in paragraphs (1)(i) through (iii) of this

definition.

(2) The following are not ‘‘waters of the United States’’ notwithstanding whether they meet the terms of paragraphs (1)(i) through (viii) of this

definition—

(i) Waste treatment systems, including treatment ponds or lagoons, designed to meet the requirements of the Clean

Water Act.

(ii) Prior converted cropland. Notwithstanding the determination of an area’s status as prior converted cropland by any other Federal agency, for the purposes of the Clean Water Act the final authority regarding Clean Water Act jurisdiction remains with

EPA.

(iii) Ditches that are excavated wholly in uplands, drain only uplands, and have less than perennial flow.

(iv) Ditches that do not contribute flow, either directly or through another water, to a water identified in paragraphs (1)(i) through (iv) of this

section.

(v) The following features: (A) Artificially irrigated areas that would revert to upland should application of irrigation water to that

area cease;

(B) Artificial lakes or ponds created by excavating and/or diking dry land and used exclusively for such purposes as stock watering, irrigation, settling basins, or rice growing;

(C) Artificial reflecting pools or swimming pools created by excavating and/or diking dry land;

(D) Small ornamental waters created by excavating and/or diking dry land for primarily aesthetic reasons;

(E) Water-filled depressions created incidental to construction activity;

(F) Groundwater, including groundwater drained through subsurface drainage systems; and

(G) Gullies and rills and non-wetland

swales.

(3) Definitions— (i) Adjacent. The term adjacent means bordering, contiguous or neighboring. Waters, including wetlands, separated

from other waters of the United States by man-made dikes or barriers, natural river berms, beach dunes and the like are ‘‘adjacent waters.’’

(ii) Neighboring. The term neighboring, for purposes of the term ‘‘adjacent’’ in this section, includes waters located within the riparian area or floodplain of a water identified in paragraphs (1)(i) through (v) of this definition, or waters with a shallow subsurface hydrologic connection or confined surface hydrologic connection to such a jurisdictional water.

(iii) Riparian area. The term riparian

area means an area bordering a water where surface or subsurface hydrology directly influence the ecological processes and plant and animal community structure in that area. Riparian areas are transitional areas between aquatic and terrestrial ecosystems that influence the exchange of energy and materials between those
ecosystems.

(4) Floodplain. The termfloodplain means an area bordering inland or coastal waters that was formed by sediment deposition from such water under present climatic conditions and is inundated during periods of moderate to high water flows.

(5) Tributary. The term tributary means a water physically characterized by the presence of a bed and banks and ordinary high water mark, as defined at 33 CFR 328.3(e), which contributes flow, either directly or through another water, to a water identified in paragraphs (1)(i) through (iv) of this definition. In addition, wetlands, lakes, and ponds are tributaries (even if they lack a bed and banks or ordinary high water mark) if they contribute flow, either directly or through another water to a water identified in paragraphs (1)(i) through (iii) of this definition. A water that otherwise qualifies as a tributary

under this definition does not lose its status as a tributary if, for any length,

there are one or more man-made breaks (such as bridges, culverts, pipes, or dams), or one or more natural breaks (such as wetlands at the head of or along the run of a stream, debris piles, boulder fields, or a stream that flows underground) so long as a bed and banks and an ordinary high water mark can be identified upstream of the break. A tributary, including wetlands, can be a natural, man-altered, or man-made

water and includes waters such as rivers, streams, lakes, ponds, impoundments, canals, and ditches not excluded in paragraph (2)(iii) or (iv) of

this definition.

(vi) Wetlands. The term wetlands

means those areas that are inundated or saturated by surface or groundwater at a frequency and duration sufficient to support, and that under normal circumstances do support, a prevalence of vegetation typically adapted for life

in saturated soil conditions. Wetlands generally include swamps, marshes, bogs and similar areas.

(vii) Significant nexus. The term significant nexus means that a water, including wetlands, either alone or in combination with other similarly situated waters in the region (i.e., the

watershed that drains to the nearest water identified in paragraphs (1)(i) through (iii) of this definition), significantly affects the chemical, physical, or biological integrity of a water identified in paragraphs (1)(i) through (iii) of this definition. For an effect to be significant, it must be more than speculative or insubstantial. Other waters, including wetlands, are similarly situated when they perform

similar functions and are located sufficiently close together or sufficiently

close to a ‘‘water of the United States’’ so that they can be evaluated as a single landscape unit with regard to their effect on the chemical, physical, or biological integrity of a water identified in paragraphs (1)(i) through (iii) of this

definition.

* * * * *

**PART 117—DETERMINATION OF**

**REPORTABLE QUANTITIES FOR**

**HAZARDOUS SUBSTANCES**

■ 

### 9. The authority citation for part 117

continues to read as follows:

Authority: The Clean Water Act, 33 U.S.C.

1251 et seq.

■ 

### 10. Section 117.1 is amended by revising the definition of ‘‘navigable

waters’’ to read as follows:

**§ 117.1 Definitions.**



### * * * * *

(i) Navigable waters means ‘‘waters of the United States, including the

territorial seas.’’

(1) For purposes of all sections of the Clean Water Act, 33 U.S.C. 1251 et. seq. and its implementing regulations, subject to the exclusions in paragraph (i)(2) of this section, the term ‘‘waters of

the United States’’ means:

(i) All waters which are currently used, were used in the past, or may be susceptible to use in interstate or foreign commerce, including all waters which are subject to the ebb and flow of the tide;

(ii) All interstate waters, including interstate wetlands;

(iii) The territorial seas; (iv) All impoundments of waters identified in paragraphs (i)(1)(i) through (iii) and (v) of this section;


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(v) All tributaries of waters identified in paragraphs (i)(1)(i) through (iv) of this
section;

(vi) All waters, including wetlands, adjacent to a water identified in paragraphs (i)(1)(i) through (v) of this section; and

(vii) On a case-specific basis, other waters, including wetlands, provided that those waters alone, or in combination with other similarly situated waters, including wetlands, located in the same region, have a significant nexus to a water identified in paragraphs (i)(1)(i) through (iii) of this

section.

(2) The following are not ‘‘waters of the United States’’ notwithstanding whether they meet the terms of paragraphs (i)(1)(i) through (vii) of this

section—

(i) Waste treatment systems, including treatment ponds or lagoons, designed to meet the requirements of the Clean

Water Act.

(ii) Prior converted cropland. Notwithstanding the determination of an area’s status as prior converted cropland by any other Federal agency, for the purposes of the Clean Water Act the final authority regarding Clean Water Act jurisdiction remains with

EPA.

(iii) Ditches that are excavated wholly in uplands, drain only uplands, and have less than perennial flow.

(iv) Ditches that do not contribute flow, either directly or through another water, to a water identified in paragraphs (i)(1)(i) through (iv) of this

section.

(v) The following features: (A) Artificially irrigated areas that would revert to upland should application of irrigation water to that

area cease;

(B) Artificial lakes or ponds created by excavating and/or diking dry land and used exclusively for such purposes as stock watering, irrigation, settling basins, or rice growing;

(C) Artificial reflecting pools or swimming pools created by excavating and/or diking dry land;

(D) Small ornamental waters created by excavating and/or diking dry land for primarily aesthetic reasons;

(E) Water-filled depressions created incidental to construction activity;

(F) Groundwater, including groundwater drained through subsurface drainage systems; and

(G) Gullies and rills and non-wetland

swales.

(3) Definitions— (i) Adjacent. The term adjacent means bordering, contiguous or neighboring. Waters, including wetlands, separated

from other waters of the United States by man-made dikes or barriers, natural river berms, beach dunes and the like are ‘‘adjacent waters.’’

(ii) Neighboring. The term neighboring, for purposes of the term ‘‘adjacent’’ in this section, includes waters located within the riparian area or floodplain of a water identified in paragraphs (i)(1)(i) through (v) of this section, or waters with a shallow subsurface hydrologic connection or confined surface hydrologic connection to such a jurisdictional water.

(iii) Riparian area. The term riparian

area means an area bordering a water where surface or subsurface hydrology directly influence the ecological processes and plant and animal community structure in that area. Riparian areas are transitional areas between aquatic and terrestrial ecosystems that influence the exchange of energy and materials between those
ecosystems.

(iv) Floodplain. The termfloodplain means an area bordering inland or coastal waters that was formed by sediment deposition from such water under present climatic conditions and is inundated during periods of moderate to high water flows.

(v) Tributary. The term tributary means a water physically characterized by the presence of a bed and banks and ordinary high water mark, as defined at 33 CFR 328.3(e), which contributes flow, either directly or through another water, to a water identified in paragraphs (i)(1)(i) through (iv) of this section. In addition, wetlands, lakes, and ponds are tributaries (even if they lack a bed and banks or ordinary high water mark) if they contribute flow, either directly or through another water to a water identified in paragraphs (i)(1)(i) through (iii) of this section. A water that otherwise qualifies as a tributary under this definition does not lose its status as a tributary if, for any length, there are one or more man-made breaks (such as bridges, culverts, pipes, or dams), or one or more natural breaks (such as wetlands at the head of or along the run of a stream, debris piles, boulder fields, or a stream that flows underground) so long as a bed and banks and an ordinary high water mark can be identified upstream of the break. A tributary, including wetlands, can be a natural, man-altered, or man-made

water and includes waters such as rivers, streams, lakes, ponds, impoundments, canals, and ditches not excluded in paragraph (i)(2)(iii) or (iv)

of this section.

(vi) Wetlands. The term wetlands

means those areas that are inundated or saturated by surface or groundwater at a frequency and duration sufficient to support, and that under normal circumstances do support, a prevalence of vegetation typically adapted for life

in saturated soil conditions. Wetlands generally include swamps, marshes, bogs and similar areas.

(vii) Significant nexus. The term significant nexus means that a water, including wetlands, either alone or in combination with other similarly situated waters in the region (i.e., the

watershed that drains to the nearest water identified in paragraphs (i)(1)(i) through (iii) of this section), significantly affects the chemical, physical, or biological integrity of a water identified in paragraphs (i)(1)(i) through (iii) of this section. For an effect to be significant, it must be more than speculative or insubstantial. Other waters, including wetlands, are similarly situated when they perform

similar functions and are located sufficiently close together or sufficiently

close to a ‘‘water of the United States’’ so that they can be evaluated as a single landscape unit with regard to their effect on the chemical, physical, or biological integrity of a water identified in paragraphs (i)(1)(i) through (iii) of

this section.

* * * * *

**PART 122—EPA ADMINISTERED**

**PERMIT PROGRAMS: THE NATIONAL**

**POLLUTANT DISCHARGE**

**ELIMINATION SYSTEM**

■ 

### 11. The authority citation for part 122

continues to read as follows:

Authority: The Clean Water Act, 33 U.S.C.

1251 et seq.

■ 

### 12. Section 122.2 is amended by revising the definition of ‘‘Waters of the United States’’ and removing the note

and editorial note at the end of the

section.

The revision reads as follows:

**§ 122.2 Definitions.**



### * * * * *

Waters of the United States or waters of the U.S. means:

(a) For purposes of all sections of the Clean Water Act, 33 U.S.C. 1251 et seq. and its implementing regulations, subject to the exclusions in paragraph (b) of this definition, the term ‘‘waters

of the United States’’ means:

(1) All waters which are currently used, were used in the past, or may be susceptible to use in interstate or foreign commerce, including all waters which are subject to the ebb and flow of the tide;

(2) All interstate waters, including interstate wetlands;

(3) The territorial seas;


## 22268 Federal Register/ Vol. 79, No. 76 / Monday, April 21, 2014 / Proposed Rules

(4) All impoundments of waters identified in paragraphs (a)(1) through (3) and (5) of this definition;

(5) All tributaries of waters identified in paragraphs (a)(1) through (4) of this definition;

(6) All waters, including wetlands, adjacent to a water identified in paragraphs (a)(1) through (5) of this definition; and

(7) On a case-specific basis, other waters, including wetlands, provided that those waters alone, or in combination with other similarly situated waters, including wetlands, located in the same region, have a significant nexus to a water identified in paragraphs (a)(1) through (3) of this

definition.

(b) The following are not ‘‘waters of the United States’’ notwithstanding whether they meet the terms of paragraphs (a)(1) through (7) of this

definition—

(1) Waste treatment systems, including treatment ponds or lagoons, designed to meet the requirements of

the Clean Water Act. This exclusion applies only to manmade bodies of water which neither were originally

created in waters of the United States (such as disposal area in wetlands) nor resulted from the impoundment of

waters of the United States. 1



### (2) Prior converted cropland. Notwithstanding the determination of an area’s status as prior converted cropland by any other Federal agency, for the purposes of the Clean Water Act the final authority regarding Clean Water Act jurisdiction remains with

EPA.

(3) Ditches that are excavated wholly in uplands, drain only uplands, and have less than perennial flow.

(4) Ditches that do not contribute flow, either directly or through another water, to a water identified in paragraphs (a)(1) through (4) of this

definition.

(5) The following features: (i) Artificially irrigated areas that would revert to upland should application of irrigation water to that

area cease;

(ii) Artificial lakes or ponds created by excavating and/or diking dry land and used exclusively for such purposes as stock watering, irrigation, settling basins, or rice growing;

(iii) Artificial reflecting pools or swimming pools created by excavating and/or diking dry land;

(iv) Small ornamental waters created by excavating and/or diking dry land for primarily aesthetic reasons;

(v) Water-filled depressions created incidental to construction activity; (vi) Groundwater, including groundwater drained through subsurface drainage systems; and

(vii) Gullies and rills and non-wetland

swales.

(c) Definitions— (1) Adjacent. The term adjacent means bordering, contiguous or neighboring. Waters, including wetlands, separated from other waters of the United States by man-made dikes or barriers, natural river berms, beach dunes and the like are ‘‘adjacent

waters.’’

(2) Neighboring. The term neighboring, for purposes of the term ‘‘adjacent’’ in this section, includes waters located within the riparian area or floodplain of a water identified in paragraphs (a)(1) through (5) of this section, or waters with a shallow subsurface hydrologic connection or confined surface hydrologic connection to such a jurisdictional water.

(3) Riparian area. The term riparian

area means an area bordering a water where surface or subsurface hydrology directly influence the ecological processes and plant and animal community structure in that area. Riparian areas are transitional areas between aquatic and terrestrial ecosystems that influence the exchange of energy and materials between those

ecosystems.

(4) Floodplain. The termfloodplain means an area bordering inland or coastal waters that was formed by sediment deposition from such water under present climatic conditions and is inundated during periods of moderate to high water flows.

(5) Tributary. The term tributary means a water physically characterized by the presence of a bed and banks and ordinary high water mark, as defined at 33 CFR 328.3(e), which contributes flow, either directly or through another water, to a water identified in paragraphs (a)(1) through (4) of this definition. In addition, wetlands, lakes, and ponds are tributaries (even if they lack a bed and banks or ordinary high water mark) if they contribute flow, either directly or through another water to a water identified in paragraphs (a)(1) through (3) of this definition. A water that otherwise qualifies as a tributary

under this definition does not lose its status as a tributary if, for any length,

there are one or more man-made breaks (such as bridges, culverts, pipes, or dams), or one or more natural breaks (such as wetlands at the head of or along the run of a stream, debris piles, boulder fields, or a stream that flows underground) so long as a bed and banks and an ordinary high water mark can be identified upstream of the break. A tributary, including wetlands, can be a natural, man-altered, or man-made

water and includes waters such as rivers, streams, lakes, ponds, impoundments, canals, and ditches not excluded in paragraphs (b)(3) or (4) of

this definition.

(6) Wetlands. The term wetlands

means those areas that are inundated or saturated by surface or groundwater at a frequency and duration sufficient to support, and that under normal circumstances do support, a prevalence of vegetation typically adapted for life

in saturated soil conditions. Wetlands generally include swamps, marshes, bogs and similar areas.

(7) Significant nexus. The term significant nexus means that a water, including wetlands, either alone or in combination with other similarly situated waters in the region (i.e., the

watershed that drains to the nearest water identified in paragraphs (a)(1) through (3) of this definition), significantly affects the chemical, physical, or biological integrity of a water identified in paragraphs (a)(1) through (3) of this definition. For an effect to be significant, it must be more than speculative or insubstantial. Other waters, including wetlands, are similarly situated when they perform

similar functions and are located sufficiently close together or sufficiently

close to a ‘‘water of the United States’’ so that they can be evaluated as a single landscape unit with regard to their effect on the chemical, physical, or biological integrity of a water identified in paragraphs (a)(1) through (3) of this

definition.

* * * * *

1

### At 45 FR 48620, July 21, 1980, the Environmental Protection Agency suspended until further notice in § 122.2, the last sentence, beginning ‘‘This exclusion applies . . .’’ in the

definition of ‘‘Waters of the United States.’’ This revision (48 FR 14153, Apr. 1, 1983) continues that suspension.

**PART 230—SECTION 404(b)(1)**

**GUIDELINES FOR SPECIFICATION OF**

**DISPOSAL SITES FOR DREDGED OR**

**FILL MATERIAL**

■ 

### 13. The authority citation for part 230

continues to read as follows:

Authority: The Clean Water Act, 33 U.S.C.

1251 et seq.

■ 

### 14. Section 230.3 is amended by revising paragraphs (s) and (t) and adding paragraph (u) to read as follows:

**§ 230.3 Definitions.**



### * * * * *

(s) For purposes of all sections of the Clean Water Act, 33 U.S.C. 1251 et seq.


## 22269 Federal Register/ Vol. 79, No. 76 / Monday, April 21, 2014 / Proposed Rules

and its implementing regulations, subject to the exclusions in paragraph (t) of this section, the term ‘‘waters of the

United States’’ means:

(1) All waters which are currently used, were used in the past, or may be susceptible to use in interstate or foreign commerce, including all waters which are subject to the ebb and flow of the tide;

(2) All interstate waters, including interstate wetlands;

(3) The territorial seas; (4) All impoundments of waters identified in paragraphs (s)(1) through (3) and (5) of this section;

(5) All tributaries of waters identified in paragraphs (s)(1) through (4) of this
section;

(6) All waters, including wetlands, adjacent to a water identified in paragraphs (s)(1) through (5) of this section; and

(7) On a case-specific basis, other waters, including wetlands, provided that those waters alone, or in combination with other similarly situated waters, including wetlands, located in the same region, have a significant nexus to a water identified in paragraphs (s)(1) through (3) of this

section.

(t) The following are not ‘‘waters of the United States’’ notwithstanding whether they meet the terms of paragraphs (s)(1) through (7) of this

section—

(1) Waste treatment systems, including treatment ponds or lagoons, designed to meet the requirements of

the Clean Water Act.

(2) Prior converted cropland. Notwithstanding the determination of an area’s status as prior converted cropland by any other Federal agency, for the purposes of the Clean Water Act the final authority regarding Clean Water Act jurisdiction remains with

EPA.

(3) Ditches that are excavated wholly in uplands, drain only uplands, and have less than perennial flow.

(4) Ditches that do not contribute flow, either directly or through another water, to a water identified in paragraphs (s)(1) through (4) of this

section.

(5) The following features: (i) Artificially irrigated areas that would revert to upland should application of irrigation water to that

area cease;

(ii) Artificial lakes or ponds created by excavating and/or diking dry land and used exclusively for such purposes as stock watering, irrigation, settling basins, or rice growing;

(iii) Artificial reflecting pools or swimming pools created by excavating and/or diking dry land; (iv) Small ornamental waters created by excavating and/or diking dry land for primarily aesthetic reasons;

(v) Water-filled depressions created incidental to construction activity;

(vi) Groundwater, including groundwater drained through subsurface drainage systems; and

(vii) Gullies and rills and non-wetland

swales.

(u) Definitions— (1) Adjacent. The term adjacent means bordering, contiguous or neighboring. Waters, including wetlands, separated from other waters of the United States by man-made dikes or barriers, natural river berms, beach dunes and the like are ‘‘adjacent

waters.’’

(2) Neighboring. The term neighboring, for purposes of the term ‘‘adjacent’’ in this section, includes waters located within the riparian area or floodplain of a water identified in paragraphs (s)(1) through (5) of this section, or waters with a shallow subsurface hydrologic connection or confined surface hydrologic connection to such a jurisdictional water.

(3) Riparian area. The term riparian

area means an area bordering a water where surface or subsurface hydrology directly influence the ecological processes and plant and animal community structure in that area. Riparian areas are transitional areas between aquatic and terrestrial ecosystems that influence the exchange of energy and materials between those

ecosystems.

(4) Floodplain. The termfloodplain means an area bordering inland or coastal waters that was formed by sediment deposition from such water under present climatic conditions and is inundated during periods of moderate to high water flows.

(5) Tributary. The term tributary means a water physically characterized by the presence of a bed and banks and ordinary high water mark, as defined at 33 CFR 328.3(e), which contributes flow, either directly or through another water, to a water identified in paragraphs (s)(1) through (4) of this section. In addition, wetlands, lakes, and ponds are tributaries (even if they lack a bed and banks or ordinary high water mark) if they contribute flow, either directly or through another water to a water identified in paragraphs (s)(1) through (3) of this section. A water that otherwise qualifies as a tributary under

this definition does not lose its status as a tributary if, for any length, there are one or more man-made breaks (such as bridges, culverts, pipes, or dams), or one or more natural breaks (such as wetlands at the head of or along the run of a stream, debris piles, boulder fields, or a stream that flows underground) so long as a bed and banks and an ordinary high water mark can be identified upstream of the break. A tributary, including wetlands, can be a natural, man-altered, or man-made water and includes waters such as rivers, streams, lakes, ponds, impoundments, canals, and ditches not excluded in paragraph (t)(3) or (4) of this section.

(6) Wetlands. The term wetlands

means those areas that are inundated or saturated by surface or groundwater at a frequency and duration sufficient to support, and that under normal circumstances do support, a prevalence of vegetation typically adapted for life

in saturated soil conditions. Wetlands generally include swamps, marshes, bogs and similar areas.

(7) Significant nexus. The term significant nexus means that a water, including wetlands, either alone or in combination with other similarly situated waters in the region (i.e., the

watershed that drains to the nearest water identified in paragraphs (s)(1) through (3) of this section), significantly affects the chemical, physical, or biological integrity of a water identified in paragraphs (s)(1) through (3) of this section. For an effect to be significant, it must be more than speculative or insubstantial. Other waters, including wetlands, are similarly situated when they perform similar functions and are located sufficiently close together or sufficiently close to a ‘‘water of the United States’’ so that they can be evaluated as a single landscape unit with regard to their effect on the chemical, physical, or biological integrity of a water identified in paragraphs (s)(1) through (3) of this

section.

**PART 232—404 PROGRAMS DEFINITIONS; EXEMPT ACTIVITIES** 

**NOT REQUIRING 404 PERMITS**

■ 

### 15. The authority citation for part 232

continues to read as follows:

Authority: The Clean Water Act, 33 U.S.C.

1251 et seq.

■ 

### 16. Section 232.2 is amended by revising the definition of ‘‘Waters of the

United States’’ to read as follows:

**§ 232.2 Definitions,**



### * * * * *

Waters of the United States or waters

means:

(1) For purposes of all sections of the Clean Water Act, 33 U.S.C. 1251 et. seq. and its implementing regulations, subject to the exclusions in paragraph (2) of this definition, the term ‘‘waters

of the United States’’ means:


## 22270 Federal Register/ Vol. 79, No. 76 / Monday, April 21, 2014 / Proposed Rules

(i) All waters which are currently used, were used in the past, or may be susceptible to use in interstate or foreign commerce, including all waters which are subject to the ebb and flow of the tide;

(ii) All interstate waters, including interstate wetlands;

(iii) The territorial seas; (iv) All impoundments of waters identified in paragraphs (1)(i) through (iii) and (v) of this definition;

(v) All tributaries of waters identified in paragraphs (1)(i) through (iv) of this
section;

(vi) All waters, including wetlands, adjacent to a water identified in paragraphs (1)(i) through (v) of this definition; and

(vii) On a case-specific basis, other waters, including wetlands, provided that those waters alone, or in combination with other similarly situated waters, including wetlands, located in the same region, have a significant nexus to a water identified in paragraphs (1)(i) through (iii) of this

definition.

(2) The following are not ‘‘waters of the United States’’ notwithstanding whether they meet the terms of paragraphs (1)(i) through (vii) of this

definition—

(i) Waste treatment systems, including treatment ponds or lagoons, designed to meet the requirements of the Clean

Water Act.

(ii) Prior converted cropland. Notwithstanding the determination of an area’s status as prior converted cropland by any other Federal agency, for the purposes of the Clean Water Act the final authority regarding Clean Water Act jurisdiction remains with

EPA.

(iii) Ditches that are excavated wholly in uplands, drain only uplands, and have less than perennial flow.

(iv) Ditches that do not contribute flow, either directly or through another water, to a water identified in paragraphs (1)(i) through (iv) of this

section.

(v) The following features: (A) Artificially irrigated areas that would revert to upland should application of irrigation water to that

area cease;

(B) Artificial lakes or ponds created by excavating and/or diking dry land and used exclusively for such purposes as stock watering, irrigation, settling basins, or rice growing;

(C) Artificial reflecting pools or swimming pools created by excavating and/or diking dry land;

(D) Small ornamental waters created by excavating and/or diking dry land for primarily aesthetic reasons; (E) Water-filled depressions created incidental to construction activity;

(F) Groundwater, including groundwater drained through subsurface drainage systems; and

(G) Gullies and rills and non-wetland

swales.

(3) Definitions— (i) Adjacent. The term adjacent means bordering, contiguous or neighboring. Waters, including wetlands, separated

from other waters of the United States by man-made dikes or barriers, natural river berms, beach dunes and the like are ‘‘adjacent waters.’’

(ii) Neighboring. The term neighboring, for purposes of the term ‘‘adjacent’’ in this section, includes waters located within the riparian area or floodplain of a water identified in paragraphs (1)(i) through (v) of this definition, or waters with a shallow subsurface hydrologic connection or confined surface hydrologic connection to such a jurisdictional water.

(iii) Riparian area. The term riparian

area means an area bordering a water where surface or subsurface hydrology directly influence the ecological processes and plant and animal community structure in that area. Riparian areas are transitional areas between aquatic and terrestrial ecosystems that influence the exchange of energy and materials between those

ecosystems.

(iv) Floodplain. The termfloodplain means an area bordering inland or coastal waters that was formed by sediment deposition from such water under present climatic conditions and is inundated during periods of moderate to high water flows.

(v) Tributary. The term tributary means a water physically characterized by the presence of a bed and banks and ordinary high water mark, as defined at 33 CFR 328.3(e), which contributes flow, either directly or through another water, to a water identified in paragraphs (1)(i) through (iv) of this definition. In addition, wetlands, lakes, and ponds are tributaries (even if they lack a bed and banks or ordinary high water mark) if they contribute flow, either directly or through another water to a water identified in paragraphs (1)(i) through (iii) of this definition. A water that otherwise qualifies as a tributary

under this definition does not lose its status as a tributary if, for any length,

there are one or more man-made breaks (such as bridges, culverts, pipes, or dams), or one or more natural breaks (such as wetlands at the head of or along the run of a stream, debris piles, boulder fields, or a stream that flows underground) so long as a bed and banks and an ordinary high water mark can be identified upstream of the break. A tributary, including wetlands, can be a natural, man-altered, or man-made

water and includes waters such as rivers, streams, lakes, ponds, impoundments, canals, and ditches not excluded in paragraph (2)(iii) or (iv) of

this definition.

(vi) Wetlands. The term wetlands

means those areas that are inundated or saturated by surface or groundwater at a frequency and duration sufficient to support, and that under normal circumstances do support, a prevalence of vegetation typically adapted for life

in saturated soil conditions. Wetlands generally include swamps, marshes, bogs and similar areas.

(vii) Significant nexus. The term significant nexus means that a water, including wetlands, either alone or in combination with other similarly situated waters in the region (i.e., the

watershed that drains to the nearest water identified in paragraphs (1)(i) through (iii) of this definition), significantly affects the chemical, physical, or biological integrity of a water identified in paragraphs (1)(i) through (iii) of this definition. For an effect to be significant, it must be more than speculative or insubstantial. Other waters, including wetlands, are similarly situated when they perform

similar functions and are located sufficiently close together or sufficiently

close to a ‘‘water of the United States’’ so that they can be evaluated as a single landscape unit with regard to their effect on the chemical, physical, or biological integrity of a water identified in paragraphs (1)(i) through (iii) of this

definition.

**PART 300—NATIONAL OIL AND**

**HAZARDOUS SUBSTANCES**

**POLLUTION CONTINGENCY PLAN**

■ 

### 17. The authority citation for part 300

continues to read as follows:

Authority: The Clean Water Act, 33 U.S.C.

1251 et seq.

■ 

### 18. Section 300.5 is amended by revising the definition of ‘‘navigable

waters’’ to read as follows:

**§ 300.5 Definitions.**



### * * * * *

Navigable waters as defined by 40 CFR 110.1, means the waters of the United States, including the territorial

seas.

(1) For purposes of all sections of the Clean Water Act, 33 U.S.C. 1251 et seq. and its implementing regulations, subject to the exclusions in paragraph (2) of this definition, the term ‘‘waters

of the United States’’ means:


## 22271 Federal Register/ Vol. 79, No. 76 / Monday, April 21, 2014 / Proposed Rules

(i) All waters which are currently used, were used in the past, or may be susceptible to use in interstate or foreign commerce, including all waters which are subject to the ebb and flow of the tide;

(ii) All interstate waters, including interstate wetlands;

(iii) The territorial seas; (iv) All impoundments of waters identified in paragraphs (1)(i) through (iii) and (v) of this definition;

(v) All tributaries of waters identified in paragraphs (1)(i) through (iv) of this definition;

(vi) All waters, including wetlands, adjacent to a water identified in paragraphs (1)(i) through (v) of this definition; and

(vii) On a case-specific basis, other waters, including wetlands, provided that those waters alone, or in combination with other similarly situated waters, including wetlands, located in the same region, have a significant nexus to a water identified in paragraphs (1)(i) through (iii) of this

definition.

(2) The following are not ‘‘waters of the United States’’ notwithstanding whether they meet the terms of paragraphs (1)(i) through (vii) of this

definition—

(i) Waste treatment systems, including treatment ponds or lagoons, designed to meet the requirements of the Clean

Water Act.

(ii) Prior converted cropland. Notwithstanding the determination of an area’s status as prior converted cropland by any other Federal agency, for the purposes of the Clean Water Act the final authority regarding Clean Water Act jurisdiction remains with

EPA.

(iii) Ditches that are excavated wholly in uplands, drain only uplands, and have less than perennial flow.

(iv) Ditches that do not contribute flow, either directly or through another water, to a water identified in paragraphs (1)(i) through (iv) of this

definition.

(v) The following features: (A) Artificially irrigated areas that would revert to upland should application of irrigation water to that

area cease;

(B) Artificial lakes or ponds created by excavating and/or diking dry land and used exclusively for such purposes as stock watering, irrigation, settling basins, or rice growing;

(C) Artificial reflecting pools or swimming pools created by excavating and/or diking dry land;

(D) Small ornamental waters created by excavating and/or diking dry land for primarily aesthetic reasons; (E) Water-filled depressions created incidental to construction activity;

(F) Groundwater, including groundwater drained through subsurface drainage systems; and

(G) Gullies and rills and non-wetland

swales.

(3) Definitions— (i) Adjacent. The term adjacent means bordering, contiguous or neighboring. Waters, including wetlands, separated

from other waters of the United States by man-made dikes or barriers, natural river berms, beach dunes and the like are ‘‘adjacent waters.’’

(ii) Neighboring. The term neighboring, for purposes of the term ‘‘adjacent’’ in this section, includes waters located within the riparian area or floodplain of a water identified in paragraphs (1)(i) through (v) of this definition, or waters with a shallow subsurface hydrologic connection or confined surface hydrologic connection to such a jurisdictional water.

(iii) Riparian area. The term riparian

area means an area bordering a water where surface or subsurface hydrology directly influence the ecological processes and plant and animal community structure in that area. Riparian areas are transitional areas between aquatic and terrestrial ecosystems that influence the exchange of energy and materials between those

ecosystems.

(iv) Floodplain. The termfloodplain means an area bordering inland or coastal waters that was formed by sediment deposition from such water under present climatic conditions and is inundated during periods of moderate to high water flows.

(v) Tributary. The term tributary means a water physically characterized by the presence of a bed and banks and ordinary high water mark, as defined at 33 CFR 328.3(e), which contributes flow, either directly or through another water, to a water identified in paragraphs (1)(i) through (iv) of this definition. In addition, wetlands, lakes, and ponds are tributaries (even if they lack a bed and banks or ordinary high water mark) if they contribute flow, either directly or through another water to a water identified in paragraphs (1)(i) through (iii) of this definition. A water that otherwise qualifies as a tributary

under this definition does not lose its status as a tributary if, for any length,

there are one or more man-made breaks (such as bridges, culverts, pipes, or dams), or one or more natural breaks (such as wetlands at the head of or along the run of a stream, debris piles, boulder fields, or a stream that flows underground) so long as a bed and banks and an ordinary high water mark can be identified upstream of the break. A tributary, including wetlands, can be a natural, man-altered, or man-made

water and includes waters such as rivers, streams, lakes, ponds, impoundments, canals, and ditches not excluded in paragraph (2)(iii) or (iv) of

this definition.

(vi) Wetlands. The term wetlands

means those areas that are inundated or saturated by surface or groundwater at a frequency and duration sufficient to support, and that under normal circumstances do support, a prevalence of vegetation typically adapted for life

in saturated soil conditions. Wetlands generally include swamps, marshes, bogs and similar areas.

(vii) Significant nexus. The term significant nexus means that a water, including wetlands, either alone or in combination with other similarly situated waters in the region (i.e., the

watershed that drains to the nearest water identified in paragraphs (1)(i) through (iii) of this definition), significantly affects the chemical, physical, or biological integrity of a water identified in paragraphs (1)(i) through (iii) of this definition. For an effect to be significant, it must be more than speculative or insubstantial. Other waters, including wetlands, are similarly situated when they perform

similar functions and are located sufficiently close together or sufficiently

close to a ‘‘water of the United States’’ so that they can be evaluated as a single landscape unit with regard to their effect on the chemical, physical, or biological integrity of a water identified in paragraphs (1)(i) through (iii) of this

definition.

* * * * *

■ 

### 19. In appendix E to part 300, section 1.5 Definitions is amended by revising the definition of ‘‘navigable waters’’ to

read as follows:

Appendix E to Part 300—Oil Spill Response.

1.5 Definitions. * * * Navigable waters as defined by 40 CFR 110.1, means the waters of the United States, including the territorial seas.

(1) For purposes of all sections of the Clean

Water Act, 33 U.S.C. 1251 et seq. and its implementing regulations, subject to the exclusions in paragraph (2) of this definition,

the term ‘‘waters of the United States’’

means:

(i) All waters which are currently used, were used in the past, or may be susceptible to use in interstate or foreign commerce, including all waters which are subject to the ebb and flow of the tide;

(ii) All interstate waters, including interstate wetlands;

(iii) The territorial seas;


## 22272 Federal Register/ Vol. 79, No. 76 / Monday, April 21, 2014 / Proposed Rules

(iv) All impoundments of waters identified in paragraphs (1)(i) through (iii) and (v) of this definition;

(v) All tributaries of waters identified in paragraphs (1)(i) through (iv) of this definition;

(vi) All waters, including wetlands, adjacent to a water identified in paragraphs (1)(i) through (v) of this definition; and

(vii) On a case-specific basis, other waters, including wetlands, provided that those waters alone, or in combination with other similarly situated waters, including wetlands, located in the same region, have a significant nexus to a water identified in paragraphs (1)(i) through (iii) of this

definition.

(2) The following are not ‘‘waters of the United States’’ notwithstanding whether they meet the terms of paragraphs (1)(i) through (vii) of this definition—

(i) Waste treatment systems, including treatment ponds or lagoons, designed to meet the requirements of the Clean Water Act.

(ii) Prior converted cropland. Notwithstanding the determination of an area’s status as prior converted cropland by any other Federal agency, for the purposes of the Clean Water Act the final authority regarding Clean Water Act jurisdiction

remains with EPA.

(iii) Ditches that are excavated wholly in uplands, drain only uplands, and have less than perennial flow.

(iv) Ditches that do not contribute flow, either directly or through another water, to a water identified in paragraphs (1)(i) through (iv) of this definition.

(v) The following features: (A) Artificially irrigated areas that would revert to upland should application of irrigation water to that area cease;

(B) Artificial lakes or ponds created by excavating and/or diking dry land and used exclusively for such purposes as stock watering, irrigation, settling basins, or rice growing;

(C) Artificial reflecting pools or swimming pools created by excavating and/or diking dry land;

(D) Small ornamental waters created by excavating and/or diking dry land for primarily aesthetic reasons;

(E) Water-filled depressions created incidental to construction activity;

(F) Groundwater, including groundwater drained through subsurface drainage systems;

and

(G) Gullies and rills and non-wetland

swales.

(3) Definitions— (i) Adjacent. The term adjacent means bordering, contiguous or neighboring. Waters, including wetlands, separated fromother waters of the United States by manmade dikes or barriers, natural river berms, beach dunes and the like are ‘‘adjacent

waters.’’

(ii) Neighboring. The term neighboring, for purposes of the term ‘‘adjacent’’ in this section, includes waters located within the riparian area or floodplain of a water identified in paragraphs (1)(i) through (v) of this definition, or waters with a shallow subsurface hydrologic connection or confined surface hydrologic connection to such a jurisdictional water. (iii) Riparian area. The term riparian area means an area bordering a water where surface or subsurface hydrology directly influence the ecological processes and plant and animal community structure in that area. Riparian areas are transitional areas between aquatic and terrestrial ecosystems that influence the exchange of energy and materials between those ecosystems.

(iv) Floodplain. The termfloodplain means an area bordering inland or coastal waters that was formed by sediment deposition from such water under present climatic conditions and is inundated during periods of moderate to high water flows.

(v) Tributary. The term tributarymeans a water physically characterized by the presence of a bed and banks and ordinary high water mark, as defined at 33 CFR 328.3(e), which contributes flow, either directly or through another water, to a water identified in paragraphs (1)(i) through (iv) of this definition. In addition, wetlands, lakes, and ponds are tributaries (even if they lack a bed and banks or ordinary high water mark) if they contribute flow, either directly or through another water to a water identified in paragraphs (1)(i) through (iii) of this definition. A water that otherwise qualifies as a tributary under this definition does not lose its status as a tributary if, for any length, there are one or more man-made breaks (such as bridges, culverts, pipes, or dams), or one or more natural breaks (such as wetlands at the head of or along the run of a stream, debris piles, boulder fields, or a stream that flows underground) so long as a bed and banks and an ordinary high water mark can be identified upstream of the break. A tributary, including wetlands, can be a natural, man-altered, or man-made water and includes waters such as rivers, streams, lakes, ponds, impoundments, canals, and ditches not excluded in paragraph (2)(iii) or (iv) of

this definition.

(vi) Wetlands. The term wetlands means those areas that are inundated or saturated by surface or groundwater at a frequency and duration sufficient to support, and that under normal circumstances do support, a prevalence of vegetation typically adapted for

life in saturated soil conditions. Wetlands generally include swamps, marshes, bogs and

similar areas.

(vii) Significant nexus. The term significant

nexus means that a water, including wetlands, either alone or in combination with other similarly situated waters in the region (i.e., the watershed that drains to the nearest water identified in paragraphs (1)(i) through (iii) of this definition), significantly affects the chemical, physical, or biological integrity of a water identified in paragraphs (1)(i) through (iii) of this definition. For an effect to be significant, it must be more than speculative or insubstantial. Other waters, including wetlands, are similarly situated when they perform similar functions and are located sufficiently close together or sufficiently close to a ‘‘water of the United States’’ so that they can be evaluated as a single landscape unit with regard to their effect on the chemical, physical, or biological integrity of a water identified in paragraphs (1)(i) through (iii) of this definition.



### * * * * * **PART 302—DESIGNATION, REPORTABLE QUANTITIES, AND** 

**NOTIFICATION**

■ 

### 20. The authority citation for part 302

continues to read as follows:

Authority: The Clean Water Act, 33 U.S.C.

1251 et seq.

■ 

### 21. Section 302.3 is amended by revising the definition of ‘‘navigable

waters’’ to read as follows:

**§ 302.3 Definitions.**



### * * * * *

Navigable waters means the waters of the United States, including the

territorial seas.

(1) For purposes of all sections of the Clean Water Act, 33 U.S.C. 1251 et. seq. and its implementing regulations, subject to the exclusions in paragraph (2) of this definition, the term ‘‘waters

of the United States’’ means:

(i) All waters which are currently used, were used in the past, or may be susceptible to use in interstate or foreign commerce, including all waters which are subject to the ebb and flow of the tide;

(ii) All interstate waters, including interstate wetlands;

(iii) The territorial seas; (iv) All impoundments of waters identified in paragraphs (1)(i) through (iii) and (v) of this definition;

(v) All tributaries of waters identified in paragraphs (1)(i) through (iv) of this definition;

(vi) All waters, including wetlands, adjacent to a water identified in paragraphs (1)(i) through (v) of this definition; and

(vii) On a case-specific basis, other waters, including wetlands, provided that those waters alone, or in combination with other similarly situated waters, including wetlands, located in the same region, have a significant nexus to a water identified in paragraphs (1)(i) through (iii) of this

definition.

(2) The following are not ‘‘waters of the United States’’ notwithstanding whether they meet the terms of paragraphs (1)(i) through (vii) of this

definition—

(i) Waste treatment systems, including treatment ponds or lagoons, designed to meet the requirements of the Clean

Water Act.

(ii) Prior converted cropland. Notwithstanding the determination of an area’s status as prior converted cropland by any other Federal agency, for the purposes of the Clean Water Act the final authority regarding Clean Water Act jurisdiction remains with

EPA.


## 22273 Federal Register/ Vol. 79, No. 76 / Monday, April 21, 2014 / Proposed Rules

(iii) Ditches that are excavated wholly in uplands, drain only uplands, and have less than perennial flow.

(iv) Ditches that do not contribute flow, either directly or through another water, to a water identified in paragraphs (1)(i) through (iv) of this

definition.

(v) The following features: (A) Artificially irrigated areas that would revert to upland should application of irrigation water to that

area cease;

(B) Artificial lakes or ponds created by excavating and/or diking dry land and used exclusively for such purposes as stock watering, irrigation, settling basins, or rice growing;

(C) Artificial reflecting pools or swimming pools created by excavating and/or diking dry land;

(D) Small ornamental waters created by excavating and/or diking dry land for primarily aesthetic reasons;

(E) Water-filled depressions created incidental to construction activity;

(F) Groundwater, including groundwater drained through subsurface drainage systems; and

(G) Gullies and rills and non-wetland

swales.

(3) Definitions— (i) Adjacent. The term adjacent means bordering, contiguous or neighboring. Waters, including wetlands, separated

from other waters of the United States by man-made dikes or barriers, natural river berms, beach dunes and the like are ‘‘adjacent waters.’’

(ii) Neighboring. The term neighboring, for purposes of the term ‘‘adjacent’’ in this section, includes waters located within the riparian area or floodplain of a water identified in paragraphs (1)(i) through (v) of this definition, or waters with a shallow subsurface hydrologic connection or confined surface hydrologic connection to such a jurisdictional water.

(iii) Riparian area. The term riparian

area means an area bordering a water where surface or subsurface hydrology directly influence the ecological processes and plant and animal community structure in that area. Riparian areas are transitional areas between aquatic and terrestrial ecosystems that influence the exchange of energy and materials between those

ecosystems.

(iv) Floodplain. The termfloodplain means an area bordering inland or coastal waters that was formed by sediment deposition from such water under present climatic conditions and is inundated during periods of moderate to high water flows.

(v) Tributary. The term tributary means a water physically characterized by the presence of a bed and banks and ordinary high water mark, as defined at 33 CFR 328.3(e), which contributes flow, either directly or through another water, to a water identified in paragraphs (1)(i) through (iv) of this definition. In addition, wetlands, lakes, and ponds are tributaries (even if they lack a bed and banks or ordinary high water mark) if they contribute flow, either directly or through another water to a water identified in paragraphs (1)(i) through (iii) of this definition. A water that otherwise qualifies as a tributary

under this definition does not lose its status as a tributary if, for any length,

there are one or more man-made breaks (such as bridges, culverts, pipes, or dams), or one or more natural breaks (such as wetlands at the head of or along the run of a stream, debris piles, boulder fields, or a stream that flows underground) so long as a bed and banks and an ordinary high water mark can be identified upstream of the break. A tributary, including wetlands, can be a natural, man-altered, or man-made

water and includes waters such as rivers, streams, lakes, ponds, impoundments, canals, and ditches not excluded in paragraph (2)(iii) or (iv) of

this definition.

(vi) Wetlands. The term wetlands

means those areas that are inundated or saturated by surface or groundwater at a frequency and duration sufficient to support, and that under normal circumstances do support, a prevalence of vegetation typically adapted for life

in saturated soil conditions. Wetlands generally include swamps, marshes, bogs and similar areas.

(vii) Significant nexus. The term significant nexus means that a water, including wetlands, either alone or in combination with other similarly situated waters in the region (i.e., the

watershed that drains to the nearest water identified in paragraphs (1)(i) through (iii) of this definition), significantly affects the chemical, physical, or biological integrity of a water identified in paragraphs (1)(i) through (iii) of this definition. For an effect to be significant, it must be more than speculative or insubstantial. Other waters, including wetlands, are similarly situated when they perform

similar functions and are located sufficiently close together or sufficiently

close to a ‘‘water of the United States’’ so that they can be evaluated as a single landscape unit with regard to their effect on the chemical, physical, or biological integrity of a water identified in paragraphs (1)(i) through (iii) of this

definition.

* * * * * **PART 401—GENERAL PROVISIONS**

■ 

### 22. The authority citation for part 401

continues to read as follows:

Authority: The Clean Water Act, 33 U.S.C.

1251 et seq.

■ 

### 23. Section 401.11 is amended by revising paragraph (l) to read as follows:

**§ 401.11 General definitions.**



### * * * * *

(l) The term navigable waters means the waters of the United States, including the territorial seas.

(1) For purposes of all sections of the Clean Water Act, 33 U.S.C. 1251 et. seq. and its implementing regulations, subject to the exclusions in paragraph (l)(2) of this section, the term ‘‘waters of

the United States’’ means:

(i) All waters which are currently used, were used in the past, or may be susceptible to use in interstate or foreign commerce, including all waters which are subject to the ebb and flow of the tide;

(ii) All interstate waters, including interstate wetlands;

(iii) The territorial seas; (iv) All impoundments of waters identified in paragraphs (l)(1)(i) through (iii) and (v) of this section;

(v) All tributaries of waters identified in paragraphs (l)(1)(i) through (iv) of this
section;

(vi) All waters, including wetlands, adjacent to a water identified in paragraphs (l)(1)(i) through (v) of this section; and

(vii) On a case-specific basis, other waters, including wetlands, provided that those waters alone, or in combination with other similarly situated waters, including wetlands, located in the same region, have a significant nexus to a water identified in paragraphs (l)(1)(i) through (iii) of this

section.

(2) The following are not ‘‘waters of the United States’’ notwithstanding whether they meet the terms of paragraphs (l)(1)(i) through (vii) of this

section—

(i) Waste treatment systems, including treatment ponds or lagoons, designed to meet the requirements of the Clean

Water Act.

(ii) Prior converted cropland. Notwithstanding the determination of an area’s status as prior converted cropland by any other Federal agency, for the purposes of the Clean Water Act the final authority regarding Clean Water Act jurisdiction remains with

EPA.

(iii) Ditches that are excavated wholly in uplands, drain only uplands, and have less than perennial flow.

(iv) Ditches that do not contribute flow, either directly or through another


## 22274 Federal Register/ Vol. 79, No. 76 / Monday, April 21, 2014 / Proposed Rules

water, to a water identified in paragraphs (l)(1)(i) through (iv) of this

section.

(v) The following features: (A) Artificially irrigated areas that would revert to upland should application of irrigation water to that

area cease;

(B) Artificial lakes or ponds created by excavating and/or diking dry land and used exclusively for such purposes as stock watering, irrigation, settling basins, or rice growing;

(C) Artificial reflecting pools or swimming pools created by excavating and/or diking dry land;

(D) Small ornamental waters created by excavating and/or diking dry land for primarily aesthetic reasons;

(E) Water-filled depressions created incidental to construction activity;

(F) Groundwater, including groundwater drained through subsurface drainage systems; and

(G) Gullies and rills and non-wetland

swales.

(3) Definitions— (i) Adjacent. The term adjacent means bordering, contiguous or neighboring. Waters, including wetlands, separated

from other waters of the United States by man-made dikes or barriers, natural river berms, beach dunes and the like are ‘‘adjacent waters.’’

(ii) Neighboring. The term neighboring, for purposes of the term ‘‘adjacent’’ in this section, includes waters located within the riparian area or floodplain of a water identified in paragraphs (l)(1)(i) through (v) of this section, or waters with a shallow subsurface hydrologic connection or confined surface hydrologic connection to such a jurisdictional water.

(iii) Riparian area. The term riparian

area means an area bordering a water where surface or subsurface hydrology directly influence the ecological processes and plant and animal community structure in that area. Riparian areas are transitional areas between aquatic and terrestrial ecosystems that influence the exchange of energy and materials between those
ecosystems.

(iv) Floodplain. The termfloodplain means an area bordering inland or coastal waters that was formed by sediment deposition from such water under present climatic conditions and is inundated during periods of moderate to high water flows.

(v) Tributary. The term tributary means a water physically characterized by the presence of a bed and banks and ordinary high water mark, as defined at 33 CFR 328.3(e), which contributes flow, either directly or through another water, to a water identified in paragraphs (l)(1)(i) through (iv) of this section. In addition, wetlands, lakes, and ponds are tributaries (even if they lack a bed and banks or ordinary high water mark) if they contribute flow, either directly or through another water to a water identified in paragraphs (l)(1)(i) through (iii) of this section. A water that otherwise qualifies as a tributary under this definition does not lose its status as a tributary if, for any length, there are one or more man-made breaks (such as bridges, culverts, pipes, or dams), or one or more natural breaks (such as wetlands at the head of or along the run of a stream, debris piles, boulder fields, or a stream that flows underground) so long as a bed and banks and an ordinary high water mark can be identified upstream of the break. A tributary, including wetlands, can be a natural, man-altered, or man-made water and includes waters such as rivers, streams, lakes, ponds, impoundments, canals, and ditches not excluded in paragraph (l)(2)(iii) or (iv)

of this section.

(vi) Wetlands. The term wetlands

means those areas that are inundated or saturated by surface or groundwater at a frequency and duration sufficient to support, and that under normal circumstances do support, a prevalence of vegetation typically adapted for life

in saturated soil conditions. Wetlands generally include swamps, marshes, bogs and similar areas.

(vii) Significant nexus. The term significant nexus means that a water, including wetlands, either alone or in combination with other similarly situated waters in the region (i.e., the

watershed that drains to the nearest water identified in paragraphs (l)(1)(i) through (iii) of this section), significantly affects the chemical, physical, or biological integrity of a water identified in paragraphs (l)(1)(i) through (iii) of this section. For an effect to be significant, it must be more than speculative or insubstantial. Other waters, including wetlands, are similarly situated when they perform

similar functions and are located sufficiently close together or sufficiently

close to a ‘‘water of the United States’’ so that they can be evaluated as a single landscape unit with regard to their effect on the chemical, physical, or biological integrity of a water identified in paragraphs (l)(1)(i) through (iii) of

this section.

* * * * *

[FR Doc. 2014–07142 Filed 4–18–14; 8:45 am]

**BILLING CODE 6560–50–P**