Sierra Club v. Van Antwerp

• Court: District Court, District of Columbia
• Decided: June 30, 2010
• Docket: Civil Action No. 2007-1756
• Status: Published

Opinion

UNITED STATES DISTRICT COURT FOR THE DISTRICT OF COLUMBIA ____________________________________ ) SIERRA CLUB, et al., ) ) Plaintiffs, ) ) ) Civil Action No. 07-1756 (RCL) v. ) ) ROBERT L. VAN ANTWERP, ) et al., ) ) Defendants. ) ____________________________________)

MEMORANDUM OPINION

I. INTRODUCTION

This case concerns a 500-acre multi-use development located in a Tampa, Florida suburb

known as Cypress Creek Town Center (CCTC). Plans for the project include retail stores,

financial institutions, hotels, restaurants, theaters, offices, and multi-family housing. The project

site is located on wetlands, which will need to be “filled” in order for the project to be completed

as planned. Because the project site involves the filling of wetlands, the Clean Water Act

(CWA) required the project’s developers to obtain a special permit prior to construction. Further,

the project’s developers were required to comply with other federal, state, and local

environmental regulations.

The Army Corps of Engineers (Corps) issued a permit for the development in May 2007

and construction started shortly thereafter. Six months later, plaintiffs, three environmental

groups and individuals, filed suit alleging violations under the National Environmental Policy

Act (NEPA), the CWA, and the Endangered Species Act (ESA). Meanwhile, during the initial

stages of construction, turbid, silt-laden water was discharged from the development site in

1 violation of the Corps permit. After the discharges, the Corps received this Court’s approval to

remand the case in order to re-evaluate the permit. After review, the Corps reissued virtually the

same permit, concluding that the discharges resulted from human error, rather than a flaw with

the permit. Plaintiffs continued their legal challenge alleging: (1) that the Corps violated NEPA

by failing to prepare an Environmental Impact Statement and by failing to otherwise take a “hard

look” at the project’s adverse impacts and potential alternatives; (2) that the Corps violated the

CWA by failing to require practicable alternatives and by arbitrarily and capriciously concluding

there would be no significant degradation of Cypress Creek and its wetlands, and no violations of

state water quality standards; and (3) that the Corps and the Fish and Wildlife Service (FWS)

violated the ESA by failing to engage in formal consultation on the development’s impact on

protected species.

Currently before the court are plaintiffs’ motion for summary judgment, government

defendants’ motion for summary judgment, and intervening defendant’s cross-motion for

summary judgment. For the reasons set forth in this opinion, plaintiffs’ motion for summary

judgment will be granted in part and denied in part. Likewise, government defendants’ motion

for summary judgment and intervening defendants’ cross-motion for will be granted in part and

denied in part. Specifically, plaintiff’s motion for summary judgment on their NEPA and CWA

claims will be granted but their motion for summary judgment on the ESA claim will be denied.

Consequently, government defendants’ motion for summary judgment and intervening

defendants’ cross-motion for summary judgment regarding plaintiffs’ ESA claim will be granted.

II. BACKGROUND

The CCTC project site consists of 502.412 acres in Pasco County, Florida, approximately

nine miles outside of Tampa, Florida. The project site includes 155.46 acres of wetlands.

2 Wetland systems are comprised of cypress swamp, mixed wetland forests, freshwater marshes,

wet prairies and small ponds. Because the proposed project involves the filling of wetlands that

are “waters of the United States,” pursuant to the CWA, a Section 404 permit is required from

the Corps before the project can proceed. This is because wetlands provide storage areas for

storm and flood waters as well as water purification functions.

CCTC’s uplands include pastureland, wooded lands and scrubby areas, which provide a

buffer zone that protects Cypress Creek. The area also provides wildlife habitat for a number of

species. The CCTC project was initially approved by local governments having jurisdiction over

the project. In addition, the intervening defendants, the “applicants” in the instant case, were

required to obtain an Environmental Resource Permit from the Southwest Florida Water

Management District for the project. The Environmental Resource Permit also serves as the State

Water Quality Certification under the CWA.

A. Issuance of the 2007 CWA Permit

In September 2005, Sierra Properties submitted a permit application to the Corps for the

CCTC project. The Corps issued a Public Notice on October 31, 2005 and initiated consultation

with the FWS in December 2005 concerning the impact on certain protected animal species,

specifically the Wood Stork and the Eastern Indigo Snake. The Corps received public comments

from state and local agencies, elected officials, organizations, and individual citizens and

reviewed the comments. The CWA permit process culminated in a May, 2007 Environmental

Assessment (EA) and Statement of Findings. In the EA, the Corps outlined the process it had

implemented to assess the environmental review. Specifically, the Corps engaged in an “informal

consultation” with the FWS regarding the potential impact on threatened and endangered

species. The FWS concurred with the Corps’ determination that the project would likely not

3 adversely affect the Wood Stork and Indigo Snake. FWS also concurred with the Corps’

determination that the project would have no affect on the Scrub Jay. Concluding that the CCTC

project failed to impose any significant environmental impacts, the EA also constituted the

Corps’ Finding of No Significant Impact under NEPA. Based on these findings, the Corps

issued a permit on May 15, 2007.

The 2007 permit authorized the construction of a new town center, including a main

street regional mall and power center, which included retail businesses, financial institutions,

hotels, restaurants, theaters, gas stations, offices and residential housing. CCTC will also

provide parking for more than 14,000 cars. However, within two months of the issuance of the

2007 permit, the site began releasing turbid, silt-laden water into Cypress Creek. While the

Corps demanded that the discharges stop and the applicant assured the Corps that the issue was

under control, the discharges continued through 2008. On February 1, 2008, the Corps suspended

the 2007 CWA permit and concluded it would investigate the causes of the violations to

determine whether the violations undermined the Corps’ permit decision.

B. Issuance of the 2009 CWA Permit

After suspending the 2007 CWA permit, the Corps conducted a review of the causes of

the discharges coming from the CCTC site. The Corps issued a public notice advising of the

reevaluation and considered additional information. During remand, the plaintiffs submitted

additional information about CCTC’s potential environmental impacts. After completing

additional environmental reviews, the Corps issued a Supplemental Environmental Assessment

(SEA), which concluded the prohibited discharges from the site were caused by “human error”

rather than as a result of the 2007 permit. On September 3, 2009, the Corps issued a slightly

modified permit allowing the CCTC project to continue.

4 C. Procedural Posture

Plaintiffs, three environmental groups, asserted this challenge to the CCTC permit in

2007, claiming that the CCTC permit would degrade Cypress Creek and its wetlands. Plaintiffs

asserted that the wetland destruction was unnecessary and unlawful; that the Corps and FWS

were required to formally consult on impacts to federally listed species; and that an EIS should

have been prepared pursuant to NEPA. After the discharges from the site began and the Corps

suspended the 2007 permit, the Court granted the Corps’ request for a voluntary remand and stay

of all litigation, noting that the Corps “may conduct additional environmental review” pursuant

to the ESA, NEPA and the CWA. On September 3, 2009, the Corps notified the Court and the

parties that the Corps had issued another CWA permit. Plaintiff’s Revised Supplemental

Complaint challenges the 2009 CWA permit. Currently before the Court is Plaintiffs’ motion for

summary judgment [Dkt. 70], Defendants’ motion for summary judgment [Dkt. 73], and

Intervening Defendants’ cross motion for summary judgment [Dkt. 74]. Subsequent to the filings

of the motions for summary judgment, plaintiffs’ filed a motion for expedited argument due to

construction activity at the CCTC project site.

D. DISCUSSION

A. Legal Standard

Generally, summary judgment should be granted only if the moving party has shown that

there are no genuine issues of material fact and that the moving party is entitled to judgment as a

matter of law. Fed.R.Civ.P. 56; Celotex Corp. v. Catrett, 477 U.S. 317, 322 (1986); Waterhouse

v. District of Columbia, 298 F.3d 989, 991 (D.C. Cir. 2002). In determining whether a genuine

issue of material fact exists, the Court must view all facts in the light most favorable to the non-

5 moving party. See Matsushita Elec. Indus. Co. v. Zenith Radio Corp., 475 U.S. 574, 587 (1986).

The non-moving party’s opposition, however, must consist of more than mere unsupported

allegations or denials and must be supported by affidavits or other competent evidence setting

forth specific facts showing that there is a genuine issue for trial. Fed.R.Civ.P. 56(e); see Celotex

Corp., 477 U.S. at 324.

However, a federal agency’s compliance with its statutory and regulatory obligations is

subject to the Administrative Procedure Act (APA). The APA creates a cause of action for

challenges to final agency decisions, findings or conclusions alleged to be “arbitrary, capricious,

an abuse of discretion, or otherwise not in accordance with the law.” 5 U.S.C. § 706(2)(A).

While the court’s review must be “searching and careful, the ultimate standard of review is a

narrow one” and the court “is not empowered to substitute its judgment for that of the agency.”

Citizens to Preserve Overton Park v. Volpe, 401 U.S. 402, 416 (1971). The standard is

deferential in order to guard against “undue judicial interference” with the lawful exercise of

agency discretion and prevents “judicial entanglement in abstract policy disagreements which

courts lack both the expertise and information to resolve. Norton v. Southern Utah Wilderness

Alliance, 542 U.S. 55, 66 (2004). In applying this standard, action will be set aside if the agency

identified no “rational connection between the facts found and the choice made,” if the

“explanation for its decision [is] counter to the evidence before the agency, or is so implausible

that is could not be ascribed to a difference in view or the product of agency expertise.” Motor

Vehicle Mfrs. Ass’n v. State Farm Mut. Auto Ins. Co., 463 U.S. 29, 43 (1983). Under the APA’s

standard of review, there is a presumption of validity of agency action. Ethyl Corp. v. EPA, 541

F.2d 1, 34 (D.C. Cir. 1976) (en banc). Nevertheless, the “arbitrary and capricious” standard is not

meant to reduce judicial review to a “rubber-stamp” of agency action. Id.

6 B. NEPA

Congress passed the National Environmental Policy Act (NEPA) in 1969 in order to

insure that all agencies of the federal government consider the environmental effects of proposed

actions. Sierra Club v. Watkins, 808 F.Supp. 852, 858 (D.C.D. 1991). NEPA’s primary purpose

is to make certain “that the agency, in reaching its decision, will have available, and will

carefully consider, detailed information concerning significant environmental impacts.”

Roberston v. Methow Valley Citizens Council, 490 U.S. 332, 349 (1989). In addition to

providing information to the decisionmakers at the agency, NEPA also “guarantees that the

relevant information will be made available to the larger audience that may also play a role in

both the decisionmaking process and the implementation of that decision.” Id. This audience

includes the public because the documentation “gives the public the assurance that the agency

has indeed considered environmental concerns in its decisionmaking process, and, perhaps more

significantly, provides a springboard for public comment.” Sierra Club v. Watkins, 808 F.Supp.

at 858 (quoting Baltimore Gas & Electric Co. v. Natural Resources Defense Council, 462 U.S.

87, 97 (1983); Robertson, 490 U.S. at 349). Instead of “mandating particular environmental

results, NEPA imposes procedural requirements on federal agencies to analyze the

environmental impact of their proposals and actions.” O’Reilly v. United States Army Corp of

Engineers, 477 F.3d 225, 228 (5th Cir. 2007).

At the heart of NEPA is § 4332(a)(C), which requires that a government agency prepare

an environmental impact statement (EIS) whenever a proposed government action qualifies as a

“major Federal action significantly affecting the quality of the human environment.” 1 When it is

1 Intervening defendants’ Notice of Supplemental Authority [Dkt. 89] point the Court to a recent Supreme Court decision, Monsanto Co. et al. v. Geerston Seed Farms, 2010 WL 2471057 (U.S. S. Ct. June 21, 2010) for the principle that an agency need not prepare an EIS if it concludes, after the preparation of an EA, that the proposed action will not have a significant environmental impact. While this rule of law is correct, see 40 C.F.R. §§ 1508.9(a),

7 not readily discernible how significant the environmental effects of a proposed action will be,

federal agencies may prepare an Environmental Assessment (“EA”). 40 C.F.R. § 1501.4(b). In

other words, an environmental assessment (EA) is made in order to determine whether an EIS is

required. See 40 C.F.R. § 1508.9; Grand Canyon Trust v. Federal Aviation Administration, 290

F.3d 339, 340 (D.C. Cir. 2002). Specifically, an EA is a “concise public document . . . that serves

to . . . [b]riefly provide sufficient evidence and analysis for determining whether to prepare an

[EIS] or a finding of no significant impact.” 40 C.F.R. § 1508.9(a)(1); see also 33 C.F.R. §§

230.10-230.11 (explaining the Corps’ requirements for an EA).

However, “[i]f any ‘significant’ environmental impacts might result from the proposed

agency action then an EIS must be prepared before agency action is taken.” Grand Canyon

Trust, 290 F.3d at 339 (emphasis in original). Significance is determined by evaluating both the

context of the action and the intensity of the impact. 40 C.F.R. § 1508.27. Intensity refers to the

severity of the impact. The applicable regulation provides that the following factors should be

considered in evaluating intensity:

(1) Impacts that may be both beneficial and adverse. A significant effect may exist even if the Federal agency believes that on balance the effect will be beneficial.

(2) The degree to which the proposed action affects public health or safety.

(3) Unique characteristics of the geographic area such as proximity to historic or cultural resources, park lands, prime farmlands, wetlands, wild and scenic rivers, or ecologically critical areas.

(4) The degree to which the effects on the quality of the human environment are likely to be highly controversial.

(5) The degree to which the possible effects on the human environment are highly uncertain or involve unique or unknown risks.

1508.13, it is not the “holding” of Monsanto as counsel claims, and the Court reminds counsel of its obligation of candor to the Court. See also Black’s Law Dictionary (8th ed. 2004), which defines “holding” as “a court’s determination of a matter of law pivotal to its decision.”

8 (6) The degree to which the action may establish a precedent for future actions with significant effects or represents a decision in principle about a future consideration.

(7) Whether the action is related to other actions with individually insignificant but cumulatively significant impacts. Significance exists if it is reasonable to anticipate a cumulatively significant impact on the environment. Significance cannot be avoided by terming an action temporary or by breaking it down into small component parts.

(8) The degree to which the action may adversely affect districts, sites, highways, structures, or objects listed in or eligible for listing in the National Register of Historic Places or may cause loss or destruction of significant scientific, cultural, or historical resources.

(9) The degree to which the action may adversely affect an endangered or threatened species or its habitat that has been determined to be critical under the Endangered Species Act of 1973.

(10) Whether the action threatens a violation of Federal, State, or local law or requirements imposed for the protection of the environment.

40 C.F.R. § 1508.27.

Under the “long-established standard in this circuit,” the court reviews an agency’s

finding of no significant impact, or in other words, decision to not prepare an EIS, in order to

determine whether the agency has accurately identified the relevant environmental concerns and

has taken a “hard look” at the potential environmental consequences of their actions. Grand

Canyon Trust, 290 F.3d at 340. Specifically, the agency must (1) accurately identify the relevant

environmental concern; (2) take a “hard look” at the environmental consequences of the action;

(3) make a “convincing case” that the potential environmental impact is not significant enough to

require a EIS; and (4) show that “even if there is an impact of true significance, [an EIS] is

unnecessary because changes or safeguards in the project sufficiently reduce the impact to a

9 minimum.” 2 Mich. Gambling Opposition v. Kempthorne, 525 F.3d 23, 29 (D.C. Cir. 2008)

(citing TOMAC v. Norton, 433 F.3d 852, 861 (D.C. Cir. 2006)); see also Robertson, 490 U.S. at

350.

However, because NEPA is a procedural and not a results-driven statute, even agency

action with adverse environmental effects can be NEPA-compliant so long as the agency has

considered those effects and determined that competing policy values outweigh those costs. Ohio

Valley Envtl. Coal. v. Aracoma Coal Co., 556 F.3d 177, 191 (4th Cir. 2009) (citing Robertson,

490 U.S. at 350.) Even if the court finds the contrary views more persuasive, the court will not

second-guess the agency’s decision so long as the agency followed NEPA’s procedures. Marsh

v. Or. Natural Res. Council, 490 U.S. 360, 378 (1989).

In the instant case, it is clear from the record that the Corps failed to comply with

NEPA’s procedural requirements. While the Corps seems to argue that it was only required to

take a “hard look” at potential environmental concerns, the Corps is also required to make a

convincing case that there would not be significant environmental impacts. Even though the

Corps took the necessary hard look at some potential environmental impacts, its determination

that there would not be significant environmental impacts is so contrary to the record that the

Court can find it to be nothing short of arbitrary and capricious.

Under NEPA, if “any significant environmental impact might result” from an agency’s

actions, an EIS is required. Grand Canyon Trust, 290 F.3d at 339 (second emphasis added).

Significance is determined by evaluating both the context of the action and the intensity of the

2 The additional requirement to make a “convincing case” differs somewhat from the requirements of Overton Park. The Court of Appeals determined that this additional requirement is appropriate in the context of the NEPA: “This burden should rest on the Government, both because of the high value placed on the protection of the environment by the National Environmental Policy Act of 1969, and because of the risk of error which results from not writing an impact statement on a project requiring one.” Md.-Nat’l Capital Park & Planning Comm’n v. U.S. Postal Serv., 487 F.2d 1029, 1040 n.10 (D.C. Cir. 1973) (citing Int’l Harvester Co. v. Ruckelshaus, 478 F.2d 615 (D.C. Cir. 1973)).

10 impact and intensity refers to the severity of the impact. The criteria in NEPA’s regulations for

evaluating significance of environmental impacts highlight the need for an EIS because the

CCTC site satisfies at least several of the criteria. See Fund for Animals v. Norton, 281 F. Supp.

2d 209, 235 (D.D.C. 2003) (“[O]ne or more significance factors can justify setting aside a

[Finding of No Significant Impact].”).

Primarily, an EIS should have been prepared because the project site has “unique

characteristics . . . such as proximity to . . . wetlands . . . or ecologically critical areas.” 40 C.F.R.

§ 1508.27(b)(3). In fact, the project site is directly on top of these unique wetlands. The Corps

itself has found that such wetlands provide “valuable storage areas for storm and flood waters”

and “water purification” functions. A.R. 6670. Specifically, the Cypress Creek “buffer” would

be eliminated by the CCTC project in order to allow for the construction of storm ponds. This

construction will “reduce the existing buffer by 300-500 feet resulting in a buffer width of only

50 feet in most areas.” A.R. 3975, 4602. The Corps itself determined that the buffer provides a

protective function for the Creek through sediment removal, erosion control, and moderation of

storm water runoff. A.R. 3975. The results of the removal of these buffer areas will result in an

increase in surges of runoff with high levels of eroded sediment. In other words, the removal of

the buffer areas can result in the same kind of discharge of turbid water that occurred in 2008.

Further, the Cypress Creek project location is ecologically critical because of the “critical

wildlife linkage” that connects to other conservation lands in the area. See A.R. 6672; 40 C.F.R.

§ 1507.28(b)(3).

Additionally, an EIS should have been prepared because the CCTC project “is related to

other actions with individually insignificant but cumulatively significant impacts.” The

regulations instruct that “[s]ignificance exists if it is reasonable to anticipate a cumulatively

11 significant impact on the environment.” This Circuit has held that NEPA requires “agencies to

consider the cumulative impacts of proposed actions.” Natural Resources Defense Council v.

Hodel, 865 F.2d 288, 297 (D.C. Cir. 1988). A cumulative impact is defined as “the impact on

the environment which results from the incremental impact of the action when added to other

past, present, and reasonably foreseeable future actions regardless of what agency . . . undertakes

such other actions.” 40 C.F.R. § 1508.7. The Corps contends that no EIS was needed based on

potential cumulative impacts because “[n]o cumulative impacts analysis is required where the

agency action itself will not result in impacts and therefore not contribute to the accumulation of

the impact in question.” (Fed. Defs.’ Mem. in Opp’n to Summ J. (citing 40 C.F.R. § 1508.7)).

However, the agency action could, and in fact has, resulted in environmental impacts and for the

Corps to contend that it is unreasonable to assert that the CCTC project may have a cumulative

impact on the environment flies in the face of logic. It not only may have an impact, it already

has. The Corps did not fully consider cumulative impacts because it erroneously concluded that

the CCTC project site would have no environmental impact at all, which, as discussed above, is

contrary to the record.

Further, an EIS should have been prepared because the project site may adversely affect

an endangered or threatened species. 40 C.F.R. § 1508.27(b)(9). Destroying the habitats of the

Indigo Snake and the Wood Stork clearly may adversely affect these protected species. While

this fact is not fatal to the ultimate substantive determinations, under NEPA this fact requires an

EIS. The Corps correctly states that “agencies may take project-related mitigation into account

when determining whether an action will have significant impacts” and that “[a]n EIS is not

required if the project is modified to add mitigating measures that compensate for any adverse

environmental impacts.” (Cross motion for S.J 32.) This analysis is applicable to the Wood

12 Stork. However, the 24-page Cumulative Impacts Analysis does not address the Indigo Snake,

presumably because under its ESA analysis, the snake was not observed at site visits. However,

the fact that the Corps required protective measures for the Indigo Snake under the EPA in the

chance it is found during construction demonstrates that the project site has the potential of

adversely effecting the protected species. This potential is all that is necessary to require

preparation of an EIS under NEPA. See Grand Canyon Trust, 290 F.3d at 339. While these

measures speak to the direct “taking,” or killing, of the snake, they fail to mitigate against the

potential loss of habitat. Nevertheless, a cumulative analysis was not performed regarding the

Indigo Snake.

Finally, an EIS should have been prepared because the project site “threatens violation of

Federal, State, [and] local law[s], imposed for the protection of the environment.” 40 C.F.R. §

1508.27(b)(10). The Corps looked at the 2008 discharge and accepted the applicant’s assessment

that it was a result of “human error.” However, NEPA regulations make no exception for human

error. NEPA’s requirement that an EIS be prepared if an action may significantly affect the

environment is highlighted when, after the issuance of a permit, significant environmental

concerns actually occur. The potential for adverse environmental consequences from the CCTC

project site escalates after the site has already had adverse environmental consequences. The

2008 discharge did, in fact, violation Federal, State and local environmental law. While it is true

that NEPA is a procedural statute and even agency action with adverse environmental effects can

be NEPA-compliant, see Robertson, 490 U.S. at 350, the procedural requirements of the statute

still must be followed. See Rock Creek Pack Station v. Blackwell, 344 F.Supp.2d 192, 200

(D.D.C. 2004) (“[I]t is well settled that NEPA does not require a particular agency to reach a

particular result based on the information it collects and analyzes, but only prescribes the

13 necessary process.”). Given the 2008 discharge violated environmental law, in addition to the

other applicable § 1508.27(b) factors, the Corps acted arbitrarily when it refused to prepare the

standard EIS.

Plaintiffs assert that an EIS should have been prepared because the “degree to which the

effects on the quality of the human environment are likely to be highly controversial.” 40 C.F.R.

§ 1508(b)(4). “The term ‘controversial’ refers to cases where a substantial dispute exists as to

the size, nature, or effect of the major federal action rather than to the existence of opposition to a

use.” Town of Cave Creek v. Federal Aviation Administration, 325 F.3d 320, 331 (D.C. Cir.

2003). Here, the record fails to demonstrate that controversy surrounding the effect of the permit

exists. While declarations were submitted to the Corps from numerous experts who claimed that

CCTC will have significant adverse impacts on Cypress Creek and its wetlands, 3 these

declarations alone fail to rise to the level of “controversy” under NEPA.

While the Corps took a hard look at some of the environmental consequences of the

issuance of the permit, it failed to make a “convincing case” that the potential environmental

impact is not significant enough to require preparation of an EIS. It is important to note that the

preparation of an EIS does not foreclose the CCTC project; it simply mandates the Corps to

follow NEPA’s procedures. The Court of Appeals has made clear the importance of NEPA’s

procedural requirements. Specifically, “[t]he purpose is not merely to force the agency to

reconsider its proposed action, but, more broadly, to inform Congress, other agencies, and the

general public about the environmental consequences of a certain action in order to spur all

interested parties to rethink the wisdom of the action.” Natural Resources Defense Council v.

3 Specifically, Dr. Bradley Stith, a Florida Scrub Jay expert, opined CCTC will adversely affect the Jay and sever the critical wildlife linkage onsite. A.R. 10555-62. Dr. Mark Rains, a hydrological expert, opined that CCTC will have significant adverse impacts on the Cypress Creek and its wetlands. Dr. C. Kenneth Dodd, a biologist who authored the rule listing the Indigo Snake while working at FWS, opined that CCTC will adversely impact the Indigo Snake by destroying its habitat and severing wildlife linkage.

14 Hodel, 865 F.2d 288, 296 (D.C. Cir. 1988). Although the Court is not persuaded as to the

existence of the “controversy” factor, the Court does find that several factors exist, therefore

requiring preparation of an EIS. The Corps presents the Court with no “rational connection”

between the record and its decision to not prepare an EIS. See Motor Vehicles Mfrs Ass’n, 463

U.S. at 43. Therefore, Plaintiff’s motion for summary judgment regarding its NEPA claim is

granted.

C. CWA

The Clean Water Act was enacted “to restore and maintain chemical, physical, and

biological integrity of the nation’s waters.” 33 U.S.C. § 1251(a). Section 404 of the CWA, 33

U.S.C. § 1344, prohibits the filling or dredging of wetlands without first receiving a permit from

the Army Corps of Engineers. 33 U.S.C. § 1344. Section 404 authorizes the Corps to issue

individual or general permits for discharges of dredged and fill material into wetlands. 33 U.S.C.

§ 1344(a),(e). The Environmental Protection Agency, together with the Corps, developed

guidelines to implement the policies of the CWA and the Corps is required to follow these

guidelines in deciding whether to issue a Section 404 permit. See 33 U.S.C. § 1344(b); 40 C.F.R.

§ 230.2. These guidelines provide that a permit may not be issued if “(i) there is a practicable

alternative which would have less adverse impact and does not have other significant adverse

environmental consequences, (ii) the discharge will result in significant degradation, (iii) the

discharge does not include all appropriate and practicable measures to minimize potential harm,

or (iv) there does not exist sufficient information to make a reasonable judgment as to whether

the proposed discharge will comply with the [Corps’] Guidelines for permit issuance.” 40 C.F.R.

§ 230.12(a)(3)(i-iv); see also 33 C.F.R. § 320.4(a)(2)(ii) (public interest review to consider the

“practicability of using reasonable alternative locations and methods to accomplish the objective

15 of the proposed structure or work”). Because the applicant failed to show that practicable

alternatives did not exist, the Corps failed to act in accordance with the law when it approved the

CWA permit.

I. The Corps’ determination that practicable alternatives did not exist was arbitrary and capricious

Pursuant to the CWA, the Corps may permit discharges that impact wetlands only if the

applicant has shown that no practicable alternative exists that is less damaging to the aquatic

ecosystem. 40 C.F.R. § 230.10(a). A practicable alternative is one that is “available and capable

of being done after taking into consideration cost, existing technology, and logistics in light of

overall project purposes.” Id.

In applying this standard, the Corps is required to follow a two step procedure. First, an

accurate statement of the project’s “basic purpose” is necessary, which the Corps defines. See 40

C.F.R. § 230.10(a)(3). Second, the Corps must determine whether the basic purpose is “water

dependant.” Id. If the purpose is not water dependant, the availability of practicable alternatives

is presumed. 40 C.F.R. § 230.10(a)(3); Berson v. EPA, 850 F.2d 36, 39 (2nd Cir. 1988);

Resource Inv’s v. United States Army Corps of Eng’rs, 151 F.3d 1162, 1167 (9th Cir. 1998);

Utahns for Better Transp. v. U.S. Dept. of Transp., 305 F.3d 1152, 1163 (10th Cir. 2002). The

preamble to the 404 Guidelines state that in the case of such non-water dependant activities, “it is

reasonable to assume there will generally be a practicable site available upland or in a less

vulnerable part of the aquatic ecosystem.” 45 Fed. Reg. 85339. When this presumption applies,

the permit applicant must rebut the presumption by “clearly demonstrating that a practicable

alternative is not available.” Sierra Club v. Van Antwerp, 2010 WL 200838, *5 (11th Cir. Jan.

21, 2010) (quoting 40 C.F.R. § 230.10(a)(3). Unless the permit applicant clearly demonstrates

otherwise, the Corps must presume that all practicable alternatives that do not involve the

16 discharge of pollutants into a wetland have a less adverse environmental impact. Id. Where the

presumption applies, the permit applicant bears the burden by providing “detailed, clear and

convincing information proving that an alternative with less adverse impact is impracticable.” Id.

(emphasis in original) (quoting Greater Yellowstone Coalition v. Flowers, 359 F.3d 1257, 1269

(10th Cir. 2004). Moreover, the Corps may rely on information submitted by the applicant but

must independently verify such information. 40 C.F.R. § 1506.5(a) (“The agency shall

independently evaluate the information submitted and shall be responsible for its accuracy.”)

When considering alternatives, “practicable” is defined at 40 C.F.R. § 230.10(a)(2) as “available

and capable of being done after taking into consideration cost, existing technology, and logistics

in light of overall project purposes.”

Here, the CCTC is not water dependant. Therefore, the applicant had the duty to rebut the

presumption of practicable alternatives by clearly demonstrating that a practicable alternative

was unavailable. The Court finds that the Corps failed to require the applicant to provide

detailed, clear and convincing information proving that an alternative with a less adverse impact

was impracticable. Consequently, the Corps unlawfully granted the section 404 permit.

a. The applicant failed to show that a reduction in CCTC’s size was impracticable

The Corps accepted the applicant’s determination that reducing the size of the CCTC

project was infeasible because of cost. The Corps calculated the costs of the CCTC project by

data provided by the applicant that showed the total costs of CCTC as compared to the net rental

income of the operation and the resulting “return on costs” of CCTC. According to the applicant,

if the project achieved less than an 8.0% rate of return, it would no longer be attractive to

investors and would be financially unworkable. However, the applicant (1) never proved that an

17 8% rate of return was necessary and (2) never proved that even if an 8% rate of return was

necessary, that the costs provided by the applicant were accurate.

i. Applicant never proved an 8% rate of return was necessary

The applicant submitted to the Corps that an 8% rate of return was necessary in order to

obtain financing for the project. The rate of return is “a calculation of potential income from a

project” that “reflects required returns, or goals, of investors contemplating acquisitions.” (Fed.

Defs.’ Mem. in Opp’n to Summ J. at 17). The applicable test is “whether the alternative with

less wetlands impact is “impracticable,” and the burden is on the Applicant . . . with independent

verification by the [Corps], to provide detailed, clear and convincing information proving

impracticability.” Utahns for Better Transp., 305 F.3d at 1186 (emphasis in original).

During the original analysis done by the Corps, the agency found the information

submitted by the applicant to be “conflicting.” A.R. 4467-68. When the Corps pursued the issue,

the applicant confirmed that financing could be secured with a lower than 8% rate of return.

A.R. 5385; AR 4501. However, the Corps subsequently conducted further inquiry and concluded

that the 8% rate of return was a “reasonable minimum.” AR 12286. The Corps now submits that

plaintiff’s challenge to the 8% rate of return is moot because the Corps conducted the subsequent

inquiry and found the rate to be “reasonable.”

The Corps points the Court to four pieces of evidence that supports the assertion than an

8.0% minimum rate of return was required to maintain the project’s economic feasibility and

obtain financing: (1) the 2006 Real Estate Research Corporation Real Estate Report (RERC

report) (AR 5417-75); (2) the August 21, 2008 Ernst & Young Report (AR 11236-47); (3) the

Real Estate Capital Markets Scoreboard showing a Survey of Initial Capitalization Rates

adjusted for New Project Development (AR 4600); and (4) a table compiling rates of return for

18 Major New Retail Development Projects from SEC filings (AR 4619). Consequently, the Corps

asserts that its “economists further found that ‘the data and methods used to demonstrate the

reasonableness of an 8.0% minimum [rate of return] are acceptable, reasonable and consistent

with basic economic practice and theory.’ Thus, the Corps independently verified the permittee’s

claim that 8.0% was the minimum rate of return to assure financial feasibility of the project.”

(Fed. Defs.’ Mem. in Opp’n to Summ J. at 19 (citing AR 122856; 15347)).

In spite of the fact that the applicant proved that the 8% rate of return is “reasonable,” the

applicant never proved anything less than an 8% rate of return would be impracticable. Even

within one of the pieces of evidence the Corps relies on as supporting a mandatory minimum of

an 8.0% rate of return, a 7.7% and 7.6% rates of return were listed as “average” rates of return

for regional malls and power centers in the Tampa area. In another piece of evidence relied upon

by the Corps, it would require a 9.1% minimum rate of return. In other words, the 8.0% rate of

return is “impracticable” using the evidence the Corps directs the Court to deferentially rely on.

The intervening defendants illustrate this point: “The 8% rate of return figure is based on a

going-in capitalization rate for established regional malls of 7.6% plus an upward adjustment of

1.5% to 3.0% to account for risks associated with new projects like CCTC . . . The administrative

record . . . makes clear that 8% is a conservative figure to use as a minimum rate of return

because 1.5% to 3.0% adjustment would actually support a minimum rate of return of 9.10% to

10.6%.” (Interv. Defs.’ Reply Mem. at 13). Taking the Corps evidence at face value

demonstrates the 8.0% rate of return itself would be unworkable. The Corps’ own unacceptable

rate of return highlights the arbitrary and capricious nature of the 8.0% minimum.

The burden is on the applicant to prove impracticability with clear and convincing

information. It is the Corps duty to hold the applicant to this standard as required by the CWA.

19 Here, the applicant proved a preference for an 8.0% rate of return but never proved it was

impracticable to realize anything less than 8.0 percent. “[U]nder the CWA, there is a “very

strong” presumption that practicable alternatives exist when a proposed project is not water-

dependent, and that the agency carries the burden to rebut that presumption by showing the

alternatives to be impracticable.” Nw. Bypass Group v. U.S. Army Corps of Engineers, 490

F.Supp.2d 184 (D.N.H. 2007) (citing Buttrey v. United States, 690 F.2d 1170, 1180 (5th Cir.

1982); Nat’l Wildlife Fed’n v. Whistler, 27 F.3d 1341, 1344 (8th Cir. 1994)); see also 40 C.F.R. §

230.10(a)(3).

ii. Applicant never proved its cost calculations were accurate

Plaintiffs contend that even if an 8% rate of return was necessary for the financial

feasibility of the project, the applicant never proved it was impracticable to reduce the CCTC

project in size. According to the applicant’s calculations, after building costs, or “hard costs,” the

largest cost is the “net land cost,” which the applicant lists as $52,474,500. AR04345. However,

instead of listing the actual “cost” of the land in its calculations, the applicant lists the land’s

“value.” Id. Specifically, the applicant listed the “base value” of the land under the “TOTAL

COSTS” as costing $72,837,500. After accounting for office, hotel, and residential sales, the

cost of the “net land cost” amounted to $46,380,000. Id.

The Corps argues that after examining the appropriateness of the applicant’s use of 2006

market value rather than the actual purchase price, or “cost,” it determined that it correctly relied

on the financial feasibility studies that used the market value. In support of this proposition, the

Corps directs the Court to the fact that it may rely on information submitted by the applicant.

(Fed. Defs.’ Mem. in Opp’n to Summ J. at 14 (citing AR15348-9; Friends of the Earth v. Hinz,

800 F.2d 822, 834 (9th Cir. 1986)). The same case directs that the Corps’ regulations provide

20 that “when information for an EA is prepared by the applicant, ‘the district engineer is

responsible for independent verification and use of the data, evaluation of the environmental

issues, and for the scope and content of the EA.’” Friends of the Earth, 800 F.2d at 835 (citing

33 C.F.R. Part 230, App. B § 8(b); 40 C.F.R. § 1506.5(b)). Thus, “while the Corps could, and

did, base its permit decision exclusively on the information provided by [the applicant], the

Corps nonetheless has an obligation to independently verify the information supplied to it.” Id.

Here, the Corps’ independent verification consisted of inquiring into the appropriateness

of the data set by its Socioeconomic Branch, which concluded that “the developer is forgoing the

opportunity to sell the land and earn a profit. Therefore, the opportunity costs of developing the

land is equivalent to the price the development could sell the land for on the open market.”

AR12288. However, the “TOTAL COSTS” do not provide for hypothetical opportunity costs

within the rate of return analysis. By using “land value” instead of land “cost” in its cost

calculations, the applicant was able to foreclose the consideration of practicable alternatives,

which the regulations mandate. The Corps argues that the calculations are “within the agency’s

technical expertise” and that the “Corps’ conclusion is entitled to deference.” Fed. Defs.’ Mem.

in Opp’n to Summ J. at 15 (citing City of Waukesha v. EPA, 320 F.3d 228, 247 (D.C. Cir. 2003).

However, the Court of Appeals in City of Waukesha was discussing deference to the agency

“when it is evaluating scientific data within its technical expertise.” City of Waukesha, 320 F.3d

at 247 (quoting Huls Am. v. Browner, 83 F.3d 445, 452 (D.C. Cir. 1996)). Using the actual “cost”

in a column marked “cost” is far from technical and even further from reasonable. See Black’s

Law Dictionary (8th ed. 2004) (defining “cost” as the “amount paid or charged for something;

price or expenditure”).

21 Further, the preamble to the 404 Guidelines confirms the plain meaning of the term

“cost.” The notice explains that the word “cost” was used instead of the word “economic.” This

is because “[t]he term economic might be construed to include consideration of the applicant’s

financial standing, or investment, or market share, a cumbersome inquiry which is not

necessarily material to the objectives of the Guidelines.” 45 Fed. Reg. 85339. As such, the

applicant failed to show, and the Corps failed to verify, the use of accurate financial information.

As a consequence, the applicant was permitted to control the numbers in order to prevent

alternatives from being practicable. This slanting of financial information is not permitted under

the CWA.

The 404(b)(1) Guidelines define practicable alternatives as those that are available and

capable of being done taking into account “cost, existing technology, and logistics on light of

overall project purpose.” 40 C.F.R. §230.10(a)(2). The plain meaning of the regulations require

the Corps to examine whether the “overall project purposes,” of the CCTC project could be

pursued with less wetlands destruction and taking into account the cost of the smaller project.

See id.; § 230.3(q). While the overall project purpose would obviously include the rate of return

and potential income from a project, that rate of return calculation cannot be misrepresented to

increase itself. The cost of the land in the rate or return, or profit, calculation is independent from

the market value of the land. The plain language of the regulation directing the Corps to take cost

into consideration cannot be confused with potential, hypothetical future profit, as the Corps is

allowing the applicant to do so here. 4 The justification that the applicant could have potentially

sold the land in 2007 for $72 million is unrelated to whether CCTC can be reduced in size and

4 Plaintiffs also argue that even if the Corps accepted the applicant’s opportunity “cost” figures in the cost calculations, it should have required market values from 2009 instead of 2007, when the original permit was processed. Given that the Court has decided the Corps’ independent inquiry into the cost calculations was inadequate, there is no need to decide this issue.

22 still earn the 8.0% profit. Consequently, the Corps impermissibly allowed the applicant to

employ mathematical manipulation in order to show that practicable alternatives were

unavailable.

b. The applicant failed to show that a reduction in the number of parking spaces was impracticable

Plaintiffs contend that another practicable alternative would be to require the applicant to

reduce the number of parking spaces. According to the Corps, nearly half of the wetlands loss is

for parking. The Corps scrutinized the type and quantity of parking and required the applicant to

submit data verifying the applicant’s claims that a reduction of parking would be impracticable.

The applicant supplied information from industry sources showing that potential department

store tenants would require a minimum of 5 spaces/ 1000 square feet to up to 20 spaces/ 1000

square feet for retail centers with restaurants. See AR 5412, 5530, 5532, 5553. The applicant also

surveyed five other regional malls and the “results revealed that the project proposed more

parking than any existing mall in the evaluation.” AR 6647. The applicant contended that the

additional parking spaces are required because of the higher number of restaurants at CCTC as

compared to the other regional malls.

The Corps accepted the applicant’s contention and concluded that it “can reject an

alternative as impracticable if it would not fully meet the needs of the type of tenant sought by

the applicant.” Specifically, the Corps points to the fact that the 5 spaces / 1000 square feet

“merely reflects the low end of the range of parking ratios required by potential tenants.” (Fed.

Defs.’ Mem. in Opp’n to Summ J. 20). However, the Corps is required to presume that an

alternative is practicable unless the project applicant clearly demonstrates otherwise. See 40

U.S.C. § 230.10(a)(3). While a “low end” of parking may be less desirable for the applicant, this

does not make the alternative “impracticable,” as required by the CWA. The record

23 demonstrates that CCTC would have more parking than any existing comparable mall. The

applicant failed to demonstrate, and the Corps failed to verify, why parking ratios that appear on

the low end of a spectrum are impracticable.

II. The Corps lawfully concluded that the modified permit would not cause or contribute to significant degradation of Cypress Creek or it wetlands or violate water quality standards.

The § 404(b)(1) Guidelines also require the Corps to consider whether the issuance of a

permit “will cause or contribute to significant degradation of the waters of the United States.” 40

C.F.R. § 230.10(c). A discharge contributes to significant degradation if it has significantly

adverse effects on human health or welfare, on aquatic life and other wildlife dependent on

aquatic ecosystems, on aquatic ecosystem diversity, productivity, and stability, or on

recreational, aesthetic, and economic values. 40 C.F.R. § 230.10(c). In making this

determination, the Corps is required to examine individual, cumulative, and secondary impacts to

wildlife, fish, wetlands, nutrient and pollutant assimilation, drinking water supplies and

aesthetics. 40 C.F.R. § 230.11. Significant means anything “more than trivial.” 45 Fed. Reg. at

85,343.

The Corps’ initial permitting decision was based on assurances that adequate measures

were in place to insure compliance with CWA regulations and that the project would not

significantly degrade Cypress Creek and surrounding wetlands or violate water quality standards.

(Fed. Defs.’ Mem. in Opp’n to Summ J. at 22). The Corps also relied on the stormwater

treatment system and surface water quality monitoring plan incorporated into the permit. The

stormwater treatment system includes a series of ponds which function as water purifiers. During

the initial discharge of turbid waters, the Corps suspended the applicant’s 2007 permit and

determined that CCTC has imposed “significant, unacceptable impacts to wetlands and water

24 quality.” AR 10886-87. However, after the discharge the Corp examined the causes of the

violations and determined that the discharges where temporary in nature and did not alter the

Corps’ original conclusions that the permit would not cause or contribute to degradation of the

waters of Cypress Creek and surrounding wetlands. AR 15340-41; 15359-67. Further, through

coordination with state and local agencies, the Corps determined that the stormwater

management design remained sufficient. A.R. 15340. The record demonstrates that the Corps

thoroughly and reasonably considered the relevant factors. As such, the Corps lawfully

concluded that the modified permit would not cause or contribute to significant degradation of

Cypress Creek or its surrounding wetlands.

Additionally, the Guidelines require the Corps to consider whether issuance of a permit

will violate applicable state water quality standards. 40 C.F.R. § 230.10(b). CWA section 401

incorporates state water quality standards into section 404 permits and requires each applicant to

obtain a certification from the state that the proposed discharge will be consistent with state

water quality requirements. 33 U.S.C. § 1341(a)(1). Here, the Corps relied on the State’s

certification that the project complied with all applicable effluent limitations and water quality

standards, which is reflected in the state water quality permit. Under Corps regulations, the

State’s water quality certification is conclusive as to water quality considerations unless EPA

advises other water quality impacts be considered. 33 C.F.R. § 320.4(d). As such, The Corps

properly concluded that the modified permit would not violate water quality standards.

D. The Corps and FWA did not violate the ESA

The Endangered Species Act is designed to “ensure that endangered species are protected

from government action.” Center for Biological Diversity v. Dept. of Interior, 563 F.3d 466, 474

(D.C. Cir. 2009). Under the ESA, each federal agency is required to ensure that any action taken

25 by the agency is “not likely to jeopardize the continued existence of any endangered species or

threatened species or result in the destruction or adverse modification” of critical animal habitats.

16 U.S.C. § 1536(a)(2). Regulations promulgated by the Endangered Species Committee (which

is comprised of several federal agencies) define “action” to mean “all activities or programs of

any kind,” including “the granting of licenses.” American Bird Conservancy v. FCC, 516 F.3d

1027, 1034 (D.C. Cir. 2008); 50 C.F.R. § 402.02. The purpose of the ESA is to provide “a means

whereby the ecosystems upon which endangered species and threatened species depend may be

conserved, [and] a program for the conservation of such endangered species and threatened

species . . . .” 16 U.S.C. § 1531(b).

Specifically, the Corps must determine “at the earliest possible time” whether any action

it takes “may affect” endangered species, and, if so, it must consult with FWS. 50 C.F.R. §

402.14(a); see 16 U.S.C. § 1536(a)(2). If the Corps determines that an action may affect

endangered or threatened species or critical habitats, it must initiate formal consultation with the

[FWS], at least unless preparation of a biological assessment or participation in informal

consultation indicates that a proposed action is “not likely” to have an adverse affect. 50 C.F.R. §

402.14(a)-(b). Informal consultation includes “all discussions, correspondence, etc., between the

Service and the Federal agency or the designated non-Federal representative prior to formal

consultation, if required.” 50 C.F.R. § 402.02.

Once the consultation process is complete, the Secretary of FWS is required to give the

Corps a written biological opinion “setting forth the Secretary’s opinion, and a summary of the

information on which the opinion is based, detailing how the agency action affects the species or

its critical habitat.” 16 U.S.C. § 1536(b)(3)(A); see also 50 CFR § 402.14(h). If the FWS

concludes that the agency action would place the listed species in jeopardy or adversely modify

26 its critical habitat, the FWS is required to “suggest those reasonable and prudent alternatives

which he believes would not violate [§ 7(a)(2) ] and can be taken by the Federal agency . . . in

implementing the agency action.” 16 U.S.C. § 1536(b)(3)(A); see also 50 CFR § 402.14(h)(3). In

order to qualify as a “reasonable and prudent alternative,” an alternative course of action must be

able to be implemented in a way “consistent with the scope of the Federal agency’s legal

authority and jurisdiction.” § 402.02. Following the issuance of a “jeopardy” opinion, the agency

must either terminate the action, implement the proposed alternative, or seek an exemption from

the Cabinet-level Endangered Species Committee pursuant to 16 U.S.C. § 1536(e).

Here, the Corps contends that the requisite informal consultation was completed pursuant

to 50 C.F.R. § 402.13(a) prior to issuing the challenged permit. After the informal consultation

process, the Corps contends that it determined that the proposed action was not likely to

adversely affect any listed species and the FWS concurred, therefore ending the inquiry and

satisfying the ESA. Specifically, the Corps asserts that during “numerous wildlife surveys from

2002 to 2005,” no Indigo Snakes were observed on the CCTC site and that even if there are

Indigo Snakes on site, the permittee was recommended to “follow standardized Eastern Indigo

Snake Protection Measures in the unlikely event that a snake would appear during project

construction.” (Fed. Defs.’ Mem. in Opp’n to Summ J. at 37). Specifically, the protection

measures required the permittee to educate construction workers about the snake and instructed

them not to kill the snakes. However, plaintiffs contend that “despite the fact that habitat loss is

the greatest threat to the Indigo’s survival, neither the Corps nor FWS have ever considered the

effect of destroying the Indigo’s habitat on the CCTC site.” (Mot. for Summ. J. at 41 (emphasis

omitted) (citing A.R. 6682)). Considering the fact that there is nothing in the record to

support a conclusion that the Eastern Indigo Snake actually occupies the CCTC site, the Court

27 finds the Corps’ determinations were not arbitrary or capricious. Plaintiffs have failed to carry

their burden of showing that FWS’ “not likely to adversely effect” determination was arbitrary

and capricious.

Additionally, the Corps contends that although the record includes conflicting

information about whether Wood Storks have been observed on the project site, information

submitted by the applicant indicted that the storks were observed on the CCTC site. Further, the

FWS concluded that the project could serve as Wood Stork foraging habitat. However, FWS

agreed with the Corps that mitigation measures which are in place will result in a net gain of

approximately five acres of potential wood stork foraging habitat, which included “compensation

for the temporal lag necessary for the sites to achieve foraging value equal to that provided by

the existing wood stork habitat on site.” (Fed. Defs.’ Mem. in Opp’n to Summ J. at 40). While it

is true that controversy exists about the efficiency of wetland mitigation generally, the Court’s

role is “not to resolve scientific disputes.” Natural Res. Def. Council v. FAA, 564 F.3d 549, 561

(2nd Cir. 2009). Plaintiffs have not submitted any information to cause the Court to second-

guess the Corps’ determination that wetland mitigation is sufficient. Therefore, Plaintiffs have

failed to show that the Corps determinations were arbitrary and capricious.

Finally, the Corps contends that based on the fact that there was no suitable scrub jay

habitat in the project area, the Corps has no obligation to consult with the FWS regarding the

Scrub Jay. The FWS determined that there was no suitable scrub jay habitat in the project area,

FWS1126, and the Corps is under no obligation to consult with the FWS with respect to that

species. See 16 U.S.C. § 1536(a)(3).

28 E. RELIEF

The Supreme Court has instructed that where “the record before the agency does not

support the agency action, . . . the proper course, except in rare circumstances, is to remand to the

agency for additional investigation or explanation.” Florida Power & Light Co. v. Lorion, 470

U.S. 729, 744 (1985); see also County of Los Angeles v. Shalala, 192 F.3d 1005, 1023 (D.C. Cir.

1999). Similarly, the D.C. Circuit has stated the decision “whether to remand or vacate “depends

on [1] the seriousness of the order’s deficiencies (and thus the extent of doubt whether the

agency chose correctly) and [2] the disruptive consequences of an interim change that may itself

be changed.” Milk Train v. Veneman, 310 F.3d 747, 755-56 (D.C. Cir. 2002) (quoting Allied-

Signal v. U.S. Nuclear Regulatory Comm’n, 988 F.2d 146, 150-51 (D.C. Cir. 1993); see also

WorldCom, Inc. v. FCC, 288 F.3d 429, 434 (D.C. Cir. 2002) (remand without vacatur where

“non-trivial likelihood” that agency would be able to justify rule on remand). Here, the Court

finds it appropriate to remand this case at this time and have the parties file supplemental

submissions addressing the exact parameters of appropriate relief, including possible vacatur,

consistent with this opinion.

F. CONCLUSION

The Corps has failed to fulfill its statutory duties under NEPA and the CWA.

Unfortunately, this is a familiar course of action for the Corps when processing permit

applications. As another member of this Court has stated, the Corps “resorted to arbitrary and

capricious meaning – manipulating models and changing definitions where necessary – to make

this project seem compliant with [CWA] and [NEPA] when it is not.” Envtl Def. v. Army Corps

of Eng’s, 515 F.Supp. 2d. 69, 74 (D.D.C. 2007). The record here shows a similarly disturbing

pattern. The Corps failed to prepare a required EIS for the project site pursuant to NEPA and

29 failed to require the applicant to demonstrate that practicable alternatives were not available

pursuant to CWA.

For the reasons set forth in this opinion, plaintiff’s motion for summary judgment will be

granted in part and denied in part. Likewise, government defendants’ motion for summary

judgment will be granted in part and denied in part and intervening defendants’ cross-motion for

summary judgment will be granted in part and denied in part. Specifically, plaintiffs’ motion for

summary judgment on their NEPA and CWA claims will be granted but their motion for

summary judgment on the ESA claim will be denied. Consequently, government defendants’

motion for summary judgment and intervening defendants’ cross-motion for summary judgment

on plaintiff’s ESA claim will be granted.

A separate order shall issue this date.

June 30, 2010 _/s/ Royce C. Lamberth ____ Chief Judge United States District Court