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Baykeeper v. U.S. Army Corps of Engineers

United States District Court, E.D. California
Sep 20, 2006
No. Civ. S-06-1908 FCD/GGH (E.D. Cal. Sep. 20, 2006)

Opinion

No. Civ. S-06-1908 FCD/GGH.

September 20, 2006


MEMORANDUM AND ORDER


This matter is before the court on plaintiffs Baykeeper and its Deltakeeper Chapter and National Resources Defense Council's ("plaintiffs") motion for a preliminary injunction to enjoin dredging adjacent to the Port of Stockton's West Complex Docks 14 and 15 (the "Dredging Activities") by defendants Port of Stockton and Stockton Port District (collectively, the "Port"), and to stay the effectiveness of Permit No. 200300038 (the "Permit") issued by defendants U.S. Army Corps of Engineers and its officials (collectively, the "Corps"), authorizing said dredging.

By this action, plaintiffs challenge the decision of the Corps to issue the dredge and fill Permit under Section 404 of the Clean Water Act ("CWA") and Section 10 of the Rivers and Harbors Act without first considering the harmful environmental impacts of the action in an Environmental Impact Statement ("EIS") pursuant to the National Environmental Policy Act of 1969 ("NEPA"), 42 U.S.C. § 4321 et seq. Specifically, plaintiffs contend the following: (1) that the subject Dredging Activities are an essential component of, and prerequisite for, the Port's West Complex Development Plan Project (the "Project"); (2) that assuming, arguendo, that the Dredging Activities could be separated from the larger Project under NEPA, the Port's EIR demonstrates that the cumulative impacts of the Dredging Activities and the Project cause significant environmental effects; and (3) that an EIS is independently compelled by the National Marine Fisheries Service's ("NMFS") determination that the Project will have a "substantial adverse effect" on federal endangered Chinook salmon and by the ongoing uncertainty regarding the Port's mitigation for dissolved oxygen impacts.

The court heard oral argument on plaintiffs' motion on September 15, 2006. Previously, on August 25, 2006, due to the undersigned's unavailability, United States District Court Judge Morrison England heard plaintiffs' underlying motion for a temporary restraining order ("TRO") seeking the same relief. Finding plaintiffs' showing of irreparable harm insufficient, Judge England denied plaintiffs' motion for a TRO but set the matter on an expedited briefing and hearing schedule before the undersigned on plaintiffs' motion for a preliminary injunction. At the conclusion of the September 15, 2006 hearing, the court announced its intention to issue a stand-still order pending the court's written decision on the motion to be filed on Tuesday, September 19, 2006. The court asked defendants whether they would have any objection to postponement of the Dredging Activities until that time; defendants stated that they had no objection but asked whether the court would like to visit the site prior to entry of its stand-still order. The court agreed to visit the site, and indicated that a stand-still order would be in effect upon the conclusion of that visitation, which occurred on September 18, 2006. The court stated that it would provide a written order on the motion no later than Wednesday, September 20, 2006.

Defendant did note for the record that a two-day postponement of the dredging would cost the Port $18,000.00.

During the site inspection, the Port represented that the dredging of Dock 15 was nearly complete and would be completed by the end of the day. As such, the court modified its order to permit the continued dredging of Dock 15 on September 18. (Minute Order, filed Sept. 18, 2006.) The court's stand-still order was to go in to effect upon the earlier of the completion of the Dock 15 dredging or Tuesday, September 19, 2006.

By the instant order, the court now renders its decision on plaintiffs' motion. Finding plaintiffs have demonstrated a strong likelihood of success on the merits of their NEPA claim and the possibility of irreparable harm, the court GRANTS plaintiffs a preliminary injunction enjoining the Dredging Activities pending final resolution of the case on the merits.

BACKGROUND

I. Project Setting

The Project is located on the 1,459-acre Rough and Ready Island ("Island"), which abuts the San Joaquin River's Deep Water Ship Channel ("DWSC") on the western edge of Stockton, California. (Ex. 1 to Perlmutter TRO Decl., filed Aug. 24, 2006; Ex. 4 at 1.) The Island is located upstream on the DWSC from the Port's "East Complex," which has housed the Port's operations for the last 70 years. (See id.) Shipping access to both the Island and the East Complex is wholly dependent on the Corps' ongoing dredging to maintain the DWSC at the 35-foot depth necessary for most modern commercial ships. (Ex. 17 at 3.)

Unless otherwise stated all further references to an "Exhibit" are to the Perlmutter TRO Declaration.

In July 2000, the U.S. Navy began transferring the Island to the Port. (Ex. 24 at 1.) Prior to 2001, no large-scale shipping had occurred on the Island since at least 1965, when the Navy discontinued its use as a military supply depot. (Ex. 32.) During the Navy's ownership, the river bottom adjacent to the Island's seven docks (Docks 14-20) accumulated extensive, and heavily contaminated, debris and sediment. (Ex. 11 at 3.) This sediment makes it impossible to use the Island for large-scale shipping without extensive additional dredging.

Currently, the shallow draft of approximately 20 feet at Docks 14 through 18 and approximately 30 feet at Docks 19 and 20 is not adequate to meet the needs of most modern ships. The Port must establish a draft of 35 feet, to remain viable and competitive in the marketplace. . . .

(Exs. 17-20 at 1.)

While the Port thus has a clear economic incentive to complete the Dredging Activities, counter-balancing that interest is the fact that the Project lies within the San Francisco Bay-Delta Watershed which provides critical habitat for five federally listed endangered or threatened species, including the Sacramento River winter-run Chinook salmon, the delta smelt, the green sturgeon, the Central Valley steelhead trout, and the Central Valley spring-run Chinook salmon. (Ex. 7 at 10.)

II. Application for a Section 404 Permit for the Project

In August 2003, the Port submitted an application to the Corps for a CWA, Section 404 permit for the larger Project — to dredge all Docks 14 to 20. Thereafter on September 26, 2003, the Corps issued its Public Notice ("PN") seeking public comment on the Port's proposed dredging activities, explaining that the "applicant's stated purpose is to provide economic development at Port of Stockton's West Complex by dredging the area for commercial shipping use." (Ex. 5 at 1.) The referenced "economic development" is the Project, approved by the Port in June 2004, after preparation of a lengthy Environmental Impact Report ("EIR") pursuant to state law. The Project would construct and operate extensive marine terminal, commercial, and industrial park facilities throughout the Island, effectively tripling the Port's current size and doubling the current level of ship traffic in the DWSC. (Ex. 7 at 5-7.) Its main components include a 531-acre marine terminal with seven redeveloped wharves; a 436-acre commercial and industrial park; an additional 409 acres of diversified maritime, commercial, and industrial land use; and an intermodal railyard. (Ex. 26 at 2-4, 12.) The Port estimates that the Project will create 150 annual vessel calls to the Port; increase traffic by 51,319 vehicles each day; and substantially increase train trips and the use of polluting yard equipment and diesel tugboats. (Id. at 6-9.)

For nearly three years after the Corps issued its PN in September 2003, the Corps and other federal and state agencies, including the Port, consistently treated the dredging of Docks 14-20 as an essential component of, and prerequisite for, the Project. Indeed, even before issuing the PN, the Corps had requested that NMFS initiate consultation under section 7 of the Endangered Species Act ("ESA"), because the Corps "ha[d] determined that the [dredging activities] may adversely affect" several federally listed threatened and endangered species. (Exs. 13-14.) Under the ESA, such consultation must be completed before the Corps can issue a Section 404 Permit. (See id.) On October 10, 2003, NMFS responded that it could not commence the consultation process until the Corps provided "a thorough analysis of the interrelated and interdependent actions that would occur as a result of the dredging activities, particularly the redevelopment of the former Rough and Ready Island naval base (West Complex) and the anticipated increase in Port activities." (Ex. 7 at 1.) The Corps and the Port agreed "to provide the requested information," and "[o]n November 6, 2003, staff from NMFS, the Corps and Jones and Stokes [consultants to the Port] met [and] agreed to consider the multiple West Complex activities as one project." (Id.) (Emphasis added.) Throughout the lengthy ESA consultation process, which culminated in NMFS' July 7, 2006 issuance of the required Biological Opinion ("BO"), the Corps, NMFS, and the Port continued to treat the dredging of Docks 14-20 as an integral, if not critical aspect, of the Project. (Id. at 2 [explaining the substantial delay in consultation while NFMS waited for the Port to provide the requested information about the larger Project]; id. at 2, 5-7 [BO's description of these "Interrelated and Interdependent Activities"]; see also Ex. 15 at 2-3 ¶¶ 5-6, 8, 10-11 [requesting more information about interdependent shipping activities, dock construction, and stormwater run-off from upland Island activities].) Significantly, the NMFS' cover letter to the BO expressly states that its conclusions apply to the "Port's West Complex Dredging project and associated and interrelated impacts of the West Complex Redevelopment project." (Ex. 6 at 2) (Emphasis added.)

Likewise, in its comment on the PN, the United States Environmental Protection Agency ("EPA") explained that "all aspects of the overall [DWSC] deepening/port development proposal should be evaluated together comprehensively as one project, and not broken up into separate permit actions." (Ex. 31 at 2) (Emphasis added.) The EPA also noted that the failure of the Corps' PN to fully disclose the U.S. Navy's leasing and transfer of the Island to the Port made it difficult, if not impossible, to discern how the proposed dredging "will enable other secondary (cumulative or growth-inducing) impacts in and around the area to be redeveloped." (Id.)

Finally, even the Port itself, during this three year period when the Corps was evaluating the permit application, implied that the dredging activities were essential to the viability of the Project. In permit applications to the California Regional Water Quality Control Board ("RWQCB") in December 2005 and January, March and May 2006, the Port repeatedly stated that "the shallow draft of approximately 20 feet at Docks 14 through 18 and approximately 30 feet at Docks 19 and 20 is not adequate to meet the needs of most modern ships. The Port must establish a draft of 35 feet, to remain viable and competitive in the marketplace. . . ." (Exs. 17-20 at 1.)

III. The Revised Application for a Section 404 Permit for the Dredging Activities at only Docks 14 and 15

Despite this longstanding treatment of the dredging activities at all docks as an integral part of the Project, on July 27, 2006, just three weeks after the NMFS' issuance of the BO on the Project, the Port submitted a revised Section 404 permit application for dredging only of Docks 14 and 15 (the aforementioned, "Dredging Activities"), asserting, for the first time, that the dredging of those docks was completely independent of the Project (the "Revised Application"). (Ex. 10.) With its application, the Port submitted a draft "Decision Document," prepared by its consultants, which provided a basis for the Corps' Environmental Assessment ("EA") and Finding of No Significant Impact ("FONSI") for the Dredging Activities. (Ex. 9.)

The Corps did not provide any public notice of, or opportunity for public comment on, the Revised Application. Indeed, prior to the Corps' issuance of the Permit three weeks later, these documents apparently were not made available for review by NMFS, the EPA, or even the Corps' own attorney. As the Corps' Assistant District Counsel, Lisa Clay (who had previously been involved in the review process), explained in an email sent to plaintiffs' counsel at 4:31 pm on August 16, 2006, "I expect that the EA/FONSI/Decision Document and permit document would be provided to me for review prior to final signature. As of this writing, I have not been provided any of those documents for review." (Ex. 21.) In fact, both the Permit and the EA/FONSI had been issued, and the Port had already commenced dredging pursuant to the Permit, apparently without Ms. Clay's knowledge. (Ex. 4; Perlmutter Decl., filed Aug. 24, 2006, ¶ 8.)

IV. The Dredging Activities Authorized by the Permit

The Corps issued an EA and FONSI and Section 404 Permit for the Dredging Activities on August 16, 2006, finding that the Dredging Activities are an environmentally benign "demonstration project" that is wholly independent of the Project, and thus not subject to NEPA's requirement of a detailed EIS. (Ex. 4 at 2.) The EA found:

The EA stated: "The proposed project is a minimization of the project noticed by the [Corps] on September 26, 2003. . . . The location and extent of the project have been minimized to encompass a smaller dredging area and to conduct a water quality demonstration project at the West Complex Docks 14 and 15." (Ex. 4 at 1.)

The project, as currently proposed, neither requires nor relies on any work at Docks 16-20. Accordingly, the Corps has determined that the proposed project has separate and independent utility from the proposal described in the original permit application [for Docks 14-20] and the 2004 EIR. Dredging Docks 14 and 15 will allow an adequate number of vessel calls to occur in a manner that is economically viable and will enhance terminal efficiency, regardless of whether Docks 16-20 are ever dredged. Moreover, unlike the original proposal, the proposed project serves as a demonstration project, which will include monitoring sediment and water quality following dredging operations. Should a permit be issued for the proposed project, the Corps is not in any way committed to approve work at Docks 16-20. The Port will need to submit a separate permit application to the Corps and other agencies specifically for Docks 16-20.

(Ex. 4 at 2.) These findings were primarily predicated on the Corps' determination that the 150 vessels ultimately projected to visit the Island at full Project build-out "could be accommodated at Docks 19 and 20 if no additional dredging were performed at the West Complex." (Ex. 4 at 4.)

The Permit authorized the Port to dredge approximately 130,000 cubic yards ("cy") of contaminated sediment, deepening to 35 feet the river bottom between the edge of Docks 14 and 15 and the southern margin of the DWSC. (Ex. 4 at 1.) This authorized amount is over one-third of the 326,000 cy proposed for dredging in the Port's original Permit for the entire Project. (See Ex. 5.) The dredging commenced on August 16, 2006, the same day as the issuance of the Permit.

At the time of the hearing, the dredging was approximately 50% complete. During the court's site inspection on September 18, 2006, the Port represented that the dredging of Dock 15 would be completed that day. A Port representative pointed out that modifications had been made to the marine terminal adjacent to Dock 15, and that no such modifications had been made to the terminal at Dock 14, which had not been dredged.

Plaintiffs received the EA and FONSI from the Corps on August 18, 2006 and moved for a TRO in this court on August 24, 2006, after defendants refused to agree to an expedited schedule for hearing of a preliminary injunction motion.

STANDARD

The court may grant a preliminary injunction if plaintiffs "demonstrat[e] either a combination of probable success on the merits and the possibility of irreparable harm or that serious questions are raised and the balance of hardships tips sharply in [their] favor." Earth Island Institute v. United States Forest Service, 442 F.3d 1147, 1158 (9th Cir. 2006) (emphasis in original) (internal quotations omitted). "These two formulations represent two points on a sliding scale in which the required degree of irreparable harm increases as the probability of success decreases." Save Our Sonoran, Inc. v. Flowers, 408 F.3d 1113, 1120 (9th Cir. 2005) (internal quotations omitted).

In Earth Island, the Ninth Circuit emphasized that with respect to the requisite showing of irreparable harm, where probable success on the merits has been demonstrated, a plaintiff need not show "actual harm," the "concrete probability of irreparable harm," or the "significant threat of irreparable injury," as such requirements impose too high a burden on the plaintiff. 442 F.3d at 1158-59. Rather, a plaintiff must demonstrate only the " mere possibility of irreparable injury" in cases where probable likelihood of success on the merits exists. Id. at 1159 (emphasis added).

ANALYSIS

I. Likelihood of Success on the Merits

____ A. Scope of Review

____ An agency's decision not to prepare an EIS under NEPA is reviewed under the "arbitrary and capricious" standard of the Administrative Procedures Act ("APA"), 5 U.S.C. § 706(2)(A), which requires the court to determine "whether the agency has taken a hard look at the consequences of its actions, based [its decision] on a consideration of the relevant factors, and provided a convincing statement of reasons to explain why a project's impacts are insignificant." Nat'l Parks and Conservation Ass'n v. Babbitt, 241 F.3d 722, 730 (9th Cir. 2001) (internal quotations and citation omitted).

NEPA, specifically, establishes important "action-forcing" procedures to ensure that the "broad national commitment to protecting and promoting environmental quality" is "infused into" the actions of the federal government. Robertson v. Methow Valley Citizens Council, 490 U.S. 332, 348 (1989). Perhaps most importantly, by focusing an agency's attention on the environmental consequences of a proposed project, the "action-forcing" nature of NEPA ensures that important effects will not be "overlooked or underestimated only to be discovered after resources have been committed or the die otherwise cast."Id. at 349. For this important reason, adequate environmental evaluation must occur sufficiently early in the planning process to be meaningful. 40 C.F.R. § 1501.2. NEPA does not, however, mandate particular results but "simply prescribes the necessary procedures;" ultimately, the statute prohibits uninformed, rather than unwise, agency action. Robertson, 490 U.S. at 350-51 (emphasis added).

B. Deference Owed to the Corps

The unusual facts in this case warrant a few preliminary observations regarding the Corps' conduct. While under NEPA the court owes deference to agency determinations, it certainly does not owe deference to a permit applicant. Here, it appears the Corps gave unquestioning deference to the permit applicant and now asks this court to do the same. Indeed, despite its centrality in this action, the Corps' briefing on the motion was, frankly, perfunctory, offering no analysis supported by its own expertise. At the hearing, the Corps stated it "read and assessed" the Port's application, although it became apparent that the Corps did not conduct an independent and searching analysis of the application prior to issuing the EA. There were numerous examples of this. The Corps conceded it primarily relied on the representations of the applicant because the applicant was "honorable" (presumably because the applicant was a public agency), as opposed to a "private landowner." ([Non-docketed] R.T. on PI, September 15, 2006, at 18, 19-20.) The Corps also admitted it failed to consult experts in the relevant fields of inquiry. (R.T. on PI at 18, 25-28.) Throughout the hearing the Corps readily deferred to the Port's counsel for any detailed explanation of the EA. (Id. at 11-12, 15-16.) Indeed, the Corps provided the court little evidentiary basis whatsoever for the findings in the EA. (Id. at 6, 16-18, 26.)

Clearly, NEPA requires more. It requires "independent evaluation by the agency based on record evidence." Florida Wildlife Federation v. U.S. Army Corps of Engineers, 401 F. Supp. 2d 1298, 1323 (S.D. Fla. 2005) (finding EA's conclusion of "independent utility" arbitrary and capricious where it was based on "[r]epresentations by the applicant alone, who clearly has an interest in obtaining the permit").

Ultimately, a judicial review of the Corps' EA/FONSI and Section 404 Permit must begin and end with the Corps. Thus, any fault found by the court in this NEPA action lies not with the Port's efforts to pursue dredging its West Complex docks, but rather with the Corps' failure to perform its review mandated by Congress. Understandably the Port seeks to pursue the development and protection of its interests and therefore has a vital stake in the outcome of this matter. However, the Corps, not the Port, must be the principal focus of this NEPA litigation, which is intended to scrutinize the Corps' decision not to perform an EIS. When placed under such scrutiny, the court finds, for the reasons set forth below, serious shortcomings in the Corps' discharge of its responsibilities.

C. NEPA Requires an EIS Whenever a Project "May" have a Significant Effect on the Environment

Here, there is no dispute that the Corps' issuance of a Section 404 permit is a "major Federal action" to which NEPA applies. 42 U.S.C. § 4332(2)© (NEPA requires federal agencies to prepare an EIS for all "major Federal actions significantly affecting the quality of the human environment"). Accordingly, the Corps acknowledges that it was required, as an initial step, to prepare an EA to determine whether the Dredging Activities may have any significant environmental effects. 40 C.F.R. § 1501.3, 1501.4(b), 1508.9, 1508.27. The purpose of an EA is to "briefly provide sufficient evidence and analysis" to determine whether the proposed action will have a significant impact. Id. at § 1508.27. An agency must consider the direct, indirect, and cumulative impacts on the environment. Id. at § 1508.8, 1508.27(b). If an agency finds no significant impact, then no further evaluation of the environmental effects is required.Id. at § 1508.9, 1508.13. The FONSI must be accompanied by a "convincing statement of reasons" explaining why the project's impacts are insignificant. Blue Mountain Biodiversity Project v. Blackwood, 161 F.3d 1208, 1212 (9th Cir. 1998). "The statement of reasons is crucial to determining whether the agency took a `hard lock' at the potential environmental impact of a project."Id.

If, on the other hand, "substantial questions" are raised as to whether the project " may have a significant effect upon the human environment" then the agency must prepare an EIS to detail the environmental consequences of the proposed action. Found. for N. Am. Wild Sheep v. USDA, 681 F.2d 1172, 1178 (9th Cir. 1982). Thus, to prevail on its claim that an agency should have prepared an EIS, a "plaintiff need not show that significant effects will in fact occur." Blue Mountain, 161 F.3d at 1212.

Here, plaintiffs argue the Corps should have considered the entire West Complex Project as part of its EA and should have prepared an EIS because the Port's own EIR concluded that the Project will have numerous significant environmental impacts. Defendants respond that the EA properly found that the Dredging Activities are wholly independent of the Project, and that standing alone the Dredging Activities do not have any significant environmental effects.

The court must therefore begin its analysis with the procedural issues ordained by the Corps' regulations and NEPA.

1. The Corps' regulations

Agencies may not improperly "segment" projects in order to avoid preparing an EIS; instead, they must consider related actions in a single EIS. Thomas v. Peterson, 753 F.2d 754, 758 (9th Cir. 1985). "Not to require this would permit dividing a project into multiple `actions,' each of which individually has an insignificant environmental impact, but which collectively have a substantial impact." Id. Moreover, the NEPA process must be integrated with agency planning "at the earliest possible time." 40 C.F.R. § 1501.2. Thus, the Corps cannot satisfy its obligation under NEPA by preparing an EIS for later phases of the Project after issuance of this 404 Permit. Thomas, 753 F.2d at 760.

Specifically, the Corps' regulations require it to consider the impacts of an entire project. When an applicant seeks a permit for an activity which is a component of a larger project, the Corps' regulations require it to assess "the impacts of the specific activity requiring a [Corps'] permit and those portions of the entire project over which the district engineer has sufficient control and responsibility to warrant Federal review." 33 C.F.R. § 325 (App. B, § 7(b)(1)); Sylvester v. Army Corps of Engineers, 884 F.2d 394, 398 (9th Cir. 1989). Thus, "while it is the development's impact on jurisdictional waters that determines the scope of the Corps' permitting authority, it is the impact of the permit on the environment at large that determines the Corps' NEPA responsibility." Sonoran, 408 F.3d at 1122. The Corps has control of and responsibility for portions of a project beyond Corps jurisdiction "where the Federal involvement is sufficient to turn an essentially private action into a Federal action. These are cases where the environmental consequences of the larger project are essentially products of the Corps' permit action." 33 C.F.R. § 325 (App. B, § 7(b)(2)).

Significantly, the Corps' regulations identify dredging permits for "shipping terminals" as an activity for which the Corps should expand the scope of its NEPA review to include the impacts of a larger upland project:

[A] shipping terminal normally requires dredging, wharves, bulkheads, berthing areas and disposal of dredged material in order to function. Permits for such activities are normally considered sufficient Federal control and responsibility to warrant extending the scope of analysis to include the upland portions of the facility.

33 C.F.R. § 325 (App. B, § 7(b)(3)). Courts have construed this example as requiring the Corps to consider the impacts of development on an island in granting a permit for modifications to a bridge that made access to the island possible. Arkansas Nature Alliance v. Army Corps, 266 F. Supp. 2d 876, 891-92 (E.D. Ark. 2003); see also Friends of the Earth v. Army Corps of Engineers, 109 F. Supp. 2d 30, 40-41 (D.D.C. 2000) (applying shipping terminal example to require Corps to expand scope of review for "floating casinos" to include upland impacts from hotels, parking garages and other related development).

The shipping terminal example appears to directly apply here. Preliminarily, the court notes that concurrently with the Dredging Activities at Dock 15, the Port has made modifications to that Dock's marine terminal. Such development is consistent with, as detailed above, the Corps' and Port's three-year treatment of the dredging activities of all docks, 14-20, as an integral and critical component of the Project. Indeed, the NMFS and EPA insisted that the Corps consider the entire Project in one integrated analysis. (Ex. 7 at 1; Ex. 31 at 2.) In Sonoran, the Ninth Circuit emphasized the significance of such comments from federal agencies — "not the usual suspects in opposing the action of [another] federal agency" — in determining that the Corps improperly narrowed its NEPA analysis to avoid preparing an EIS. 408 F.2d at 1122. Under the facts of this case, the Corps' regulation clearly applied to the Project, which included, among other things, dredging, development of marine terminals with redeveloped wharves, and an upland commercial and industrial park. Inexplicably, neither the Corps nor the Port directly addressed, in their briefs, the regulation's application to the facts here. At oral argument, the Corps conceded the regulation covered the Project (R.T. on PI at 11) but failed to explain why the Corps did not apply it in the EA.

At oral argument, the Port summarily dismissed the regulation as irrelevant, arguing that it was inapplicable as the marine terminal areas had already been developed. Not only is the Port's argument factually incorrect, any completion of portions of the development of the West Complex simply does not render the regulation inapplicable.

Accordingly, for these reasons, the court finds that plaintiffs have demonstrated a probable likelihood of success in demonstrating that the Corps acted arbitrarily in failing to follow its own regulations. Sierra Club v. Martin, 168 F.3d at 1, 4 (11th Cir. 1999) (the court "must overturn agency actions which do not scrupulously follow the regulations and procedures promulgated by the agency itself").

2. NEPA regulations

Similar to the Corps' regulations, NEPA regulations require agencies to consider "connected," "cumulative," and "similar" actions within a single EA or EIS. 40 C.F.R. § 1508.25. Plaintiffs argue that the Dredging Activities here meet the requirements of each of these types of action. For example, the regulations provide that actions are "connected" if they (1) "[a]utomatically trigger" other actions which may require an EIS; (2) "[c]annot or will not proceed unless other actions are taken previously or simultaneously"; or (3) are "interdependent parts of a larger action and depend on the larger action for their justification." 40 C.F.R. § 1508.25(a)(1). Where it would be "irrational, or at least unwise" to undertake one action without subsequent actions, the actions are connected. Save the Yaak Comm. v. Block, 840 F.2d 714, 720 (9th Cir. 1988) (road construction and timber sales had "clear nexus" and were thus "connected actions" requiring expanded scope of review);Thomas, 753 F.2d at 759 (road and timber sales were "inextricably intertwined"). "Connected actions" need not be federal actions. See Morgan v. Wolter, 728 F. Supp. 1483, 1493 (D. Id. 1989) (Corps required to consider impacts of private fish propagation facility prior to issuing 404 permit for water diversion project because the projects were "links in the same bit of chain").

To the contrary, when courts have found the "independent utility" of the specific permitted activity, they have held that the Corps did not need to include the larger project in its scope of review. The crux of the "independent utility test" is whether "each of two projects would have taken place with or without the other. . . . When one of the projects might reasonably have been completed without the existence of the other, the two projects have independent utility and are not connected for NEPA purposes." Great Basin Mine Watch v. Hankins, 456 F.3d 955, 969 (9th Cir. 2006).

In the instant case, the EA finds independent utility on the grounds that the "[d]redging of Docks 14 and 15 will allow an adequate number of vessel calls to occur in a manner that is economically viable and will enhance terminal efficiency regardless of whether Docks 16-20 are ever dredged" and that without any additional dredging at all, the entire Project could proceed apace because the Port "could accommodate most deeper draft vessel traffic at Docks 19 and 20." (Ex. 4 at 2, 4.) While these "grounds" may establish limited beneficial consequences of the Dredging Activities, they do not provide a rational basis for the finding of independent utility. That finding is belied by a confusing and self-contradictory record.

While the EA asserts the Dredging Activities' independence from the Project, it also asserts that the primary purpose of the Dredging Activities is to enable the subsequent dredging of the Project's other docks. Clearly and repeatedly, the EA proclaims the stated purpose of the Dredging Activities is a "demonstration project" — a "minimization of the [P]roject" originally noticed by the Corps in 2003 — which is intended "to substantiate the analysis and characterization of water quality and sediment prior to conducting dredging of more contaminated materials." (Ex. 4 at 2, 5) (Emphasis added.) The EA provides further that: "The demonstration project [would] . . . provide information to better respond to public comments . . . received by the Corps and the Central Valley Water Board on the full project." (Id.) (emphasis added); (see also Ex. 4 at 5 ["the limited pilot project . . . (would) gather . . . monitoring data prior to approval of the full project"] (emphasis added).) In sum, the EA found:

The Port's counsel admitted at hearing that the Port was responsible for the use of the term "demonstration project." The Port's counsel stated that it was her "fault" if the term, "demonstration project," caused any confusion for the court; she argued that the principal focus of the Dredging Activities was the efficiency and economic viability of Docks 14 and 15 after the dredging. As set forth below, her position is wholly unsupported by the record and indeed, the EA itself.

This information will facilitate dredging contaminated sediment from other docks. . . . [T]he information collected in the demonstration project will be used to develop control strategies and monitoring methodologies to safely remove contaminated material in future dredging operation at other West Complex docks.

(Ex. 4 at 12.) Thus, by the EA's express findings the Dredging Activities do not have independent utility from the Project as a whole.

The EA offers an alternative ground to find independent utility based upon a " water quality" demonstration component to the Dredging Activities. (Ex. 4 at 1 ["The smaller project . . . entails monitoring to generate additional data characterizing the chemistry and fate of the dredged sediment and associated water."]) While the collection and disposal of sediment offers opportunities to review the chemistry and fate of such materials, this characterization, under any reasonable interpretation, cannot transform the dredging of the DWSC into a "water quality" project. Clearly, the focus of the permitted activity was dredging to facilitate further dredging; any water quality assessment as a result of the dredging was ancillary.

The Corps offers yet a third and novel justification for the independent utility of the Dredging Activities — that the dredging will provide scientific support regarding dissolved oxygen ("DO") levels to permit further dredging. (Ex. 4 at 1, 2, 5, 12.) NEPA simply prohibits this justification for segmentation. Thomas, 753 F.2d at 758. Stated another way, NEPA requires the Corps to discern answers to the environmental questions before it decides to issue a Section 404 Permit; NEPA does not allow the Corps to issue a Section 404 Permit in order to gather data in anticipation of unanswered environmental questions.Robertson, 490 U.S. at 351.

Plaintiffs also point to additional evidence in the record to demonstrate that the Corps' conclusion of independent utility was arbitrary and capricious, including: (1) The Port's repeated insistence that "the shallow draft of approximately . . . 30 feet at Docks 19 and 20 is not adequate to meet the needs of most modern ships. The Port must establish a draft of 35 feet to remain viable and competitive in the marketplace. . . ." (Exs. 17-20 at 1); (2) The Corps' own conclusion in the EA that the Port "must expand its operations through deepening Docks 14 and 15 in order to remain competitive enough to stay in business." (Ex. 4 at 24); (3) The determinations by NMFS and EPA that the Dredging Activities and the Project are interdependent and related activities (Ex. 7 at 1-3, 5-7; Ex. 31); (4) For more than three years the Corps and Port treated the Dredging Activities as part of the entire West Complex Project; and (5) The Port itself concluded in the EIR that this Project would have significant adverse impacts on the environment. This evidence further supports the court's finding that plaintiffs have demonstrated a probable likelihood of success on the merits of this claim.

Finally, the court is troubled by the obvious haste with which the Corps permitted the Dredging Activities. Without explanation, the Port, after a lengthy but successful state permitting process advancing the Project through various controversies and legal challenges, abruptly changed course and applied for a Section 404 Permit for the dredging of only Docks and 14 and 15 as a "water quality demonstration project." This sudden turn of events should have served as a red-flag to the Corps or any federal agency. Instead, the Corps, according to its counsel "jumped on the application," (R.T. on PI at 8:21), apparently adopting the draft "Decision Document," prepared by the Port's consultants, as the basis for its analysis. Subsequently, without comment or review from the other previously involved federal agencies, the Corps issued the EA/FONSI and Permit within three weeks of the application.

In light of the Corps' virtually "automatic" response to the unusual application in this case, the court finds the Florida Wildlife Federation v. U.S. Army Corps of Engineers case instructive. 401 F. Supp. 2d 1298 (S.D. Fla. 2005). There, the court held that:

Not unlike the impropriety of segmentation to avoid significance, manipulation of a project design to conform to a concept of independent utility, particularly with the intention that a permit be expedited, undermines the underlying purposes of NEPA.
Id. at 1323. In Florida Wildlife, Palm Beach County, Florida entered into plans with the Scripps Research Institute to build a large Biotechnology Research Park on an 1,919-acre undeveloped parcel. The project plans called for a Scripps research facility as the core tenant, with additional facilities to be offered to other biotech-related businesses. The subject property contained wetlands and thus fill permits were required from the Corps. While the project plans went out for the entire project, the County applied for a Section 404 permit for the Scripps facility portion of the project only. Ultimately, the Corps issued an EA/FONSI and Section 404 permit for the Scripps facility. Id. at 1303-07.

Environmental groups sued the Corps for failure to comply with NEPA, arguing that the Corps failed to consider the project as a whole and improperly segmented the Scripps facility project for consideration on its own. Id. at 1311. The Florida district court agreed with the plaintiffs. That court found persuasive to its analysis that the Scripps facility had always been conceptualized as part of the integrated entire project. Id. at 1317. "The inescapable conclusion from the record is that the . . . [the Scripps facility project] was never intended to stand alone — not, that is, until time came to apply [to the Corps for a permit]." Id. at 1318 (emphasis added). As such, the court concluded that the "inescapable conclusion from the record is that the `independent utility' concept [was] developed post-hoc as an avenue to limit and expedite permit review." Id. at 1321. Similarly here, the court is persuaded that a very similar confluence of facts and circumstances in this case undermine any notion of "independent utility."

Therefore, for all of the above reasons, the court finds plaintiffs have demonstrated a strong likelihood of success in demonstrating that the EA's conclusion of independent utility for the Dredging Activities was arbitrary and capricious.

Because the court makes this finding it does not consider plaintiffs' alternative arguments that the Corps violated NEPA because the Dredging Activities are "cumulative" or "similar" action to the full Project.

D. The Corps is Required to Consider the Cumulative Impacts of the Dredging Activities and the Project

An agency's NEPA analysis must consider cumulative impacts even if two projects are not considered cumulative actions. Native Ecosystems Council v. Dombeck, 304 F.3d 886, 895-96 n. 2 (9th Cir. 2002) (agency violated NEPA by failing to analyze cumulative impacts of reasonably foreseeable future actions although those actions were not "cumulative actions"); accord Great Basin, 456 F.3d at 969, 971-73. 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 (Federal or non-Federal) or person undertakes such other actions. Cumulative impacts can result from individually minor but collectively significant actions taking place over a period of time.
40 C.F.R. § 1508.7. "[P]roper consideration of the cumulative impacts of a project requires some quantified or detailed information; . . . [g]eneral statements about possible effects and some risk do not constitute a hard look absent a justification regarding why more definitive information could not be provided." Klamath-Siskiyou Wildlands Ctr. v. BLM, 387 F.3d 989, 993 (9th Cir. 2004) (internal quotations and citations omitted). Thus, the Ninth Circuit has held that a reviewing agency cannot simply offer conclusions. Rather, it must identify and discuss the impacts that will be caused by each successive project, including how the combination of those various impacts is expected to affect the environment, so as to provide a reasonably thorough assessment of the projects' cumulative impacts. Id. "The analysis must be more than perfunctory,"id. at 994, and "must give a sufficiently detailed catalogue of past, present, and future projects, and provide adequate analysis about how these projects, and differences between the projects, are thought to have impacted the environment." Lands Council v. Powell, 395 F.3d 1019, 1028 (9th Cir. 2005).

Here, the EA contains a conclusory one-paragraph description of secondary and cumulative effects from the combined impacts of the Dredging Activities and other activities associated with the West Complex Project. (Ex. 4 at 18-19.) Specifically, the EA found:

The project would have secondary and cumulative effects primarily on traffic, noise, and air quality. These secondary effects would largely result from ship and vehicle traffic associated with operations at the West Complex. As described in the resource discussions above, the proposed action would not be expected to increase effects on these resources when compared to the no action alternative. In the case of traffic, noise, and air quality the proposed action would have beneficial effects on traffic, air quality, and noise by providing more efficient loading and operations and eliminating short haul trips associated with loading vessels exclusively at Docks 19 and 20 on the West Complex.

(Id.) These bare findings are wholly insufficient under the standards set forth by Congress and federal case law. They are vague and generalized; contain no quantified or detailed information; and lack any "detailed catalogue of past, present, or future projects." Lands Council, 395 F.3d at 1028. The Ninth Circuit has routinely invalidated such conclusory, incomplete cumulative impacts analyses. See e.g. Klamath-Siskiyou, 387 F.3d at 994 (rejected 12-page cumulative impacts sections in a series of EAs as inadequate because the EAs lacked a "quantified assessment" of the combined environmental impacts of the various projects, or any data to support its conclusions); Great Basin, 456 F.3d at 973-74 (finding cumulative impacts analyses in two EISs insufficient because they were conclusory and failed to provide specific, quantified information).

Nor can defendants persuasively claim that the West Complex Project was not "reasonably foreseeable" for the purposes of 40 C.F.R. § 1508.7. The Port had already approved this entire Project and purported to review these very impacts, which it found were "significant," as part of the Port's comprehensive redevelopment plan for the West Complex. Moreover, the Corps' suggestion that it did not need to examine the Project's cumulative impacts is of particular concern in light of the Corps' August 17, 2005 correspondence to the Port in which it wrote that "we have determined our scope of analysis for this project is all of the development, . . ., including development of Rough and Ready Island." (Supp. Perlmutter Decl., filed Sept. 7, 2006, at Ex. 2.) "In addition," the Corps explained, "we have identified the following potentially significant effects, including cumulative and secondary impacts." Id. (listing cumulative impacts "from ships, trucks, and associated port facilities"). Instead of actually undertaking the required cumulative impacts analysis, however, the Corps simply asserted that "[t]he project would have secondary and cumulative effects primarily on traffic, noise and air quality," and then summarily concluded that these impacts are not problematic.

This conclusion, however, relies on a flawed environmental baseline analysis. (Ex. 4 at 18-19.) In determining whether an action will significantly affect the environment, federal agencies are required to review the proposed action in light of at least two relevant factors: (1) the extent to which the action will cause adverse environmental effects in excess of those created by existing uses in the area affected by it; and (2) the absolute quantitative adverse environmental effects of the action itself, including the cumulative harm that results from its contribution to existing adverse conditions or uses in the affected area. Hanly v. Kleindienst, 471 F.2d 823, 830-31 (2d Cir. 1972). Thus, the EA was required to compare the effects of the ultimate 150 additional vessels and associated vehicular and rail traffic that the Dredging Activities and related Project would generate, to the existing baseline without those impacts. The Corps did not undertake this analysis in the EA.

For all of these reasons, the court finds that plaintiffs have alternatively demonstrated a probability of success on the merits in showing that, even if the Dredging Activities were properly segmented from the Project itself, the EA violated NEPA in failing to adequately consider the cumulative impacts of the two actions.

E. NMFS' Significance Determination and the Level of Uncertainty about the Effectiveness of the Port's Mitigation Efforts Warrants Preparation of an EIS

Plaintiffs argue alternatively that an EIS is independently compelled by NMFS' determination that the Project will have a "substantial adverse effect" on federal endangered Chinook Salmon and by the high level of uncertainty regarding the effectiveness of the Port's mitigation for DO impacts. First, regarding the NMFS' significance determination, as this court explained inKlamath-Siskiyou Wildlands Ctr. v. U.S. Forest Service, 373 F. Supp. 2d 1069, 1080-81 (E.D. Cal. 2004):

[F]or purposes of NEPA, a project need not jeopardize the continued existence of a threatened or endangered species to have a "significant" effect on the environment. Viability is a standard under the ESA, not under NEPA. Instead, NEPA's "significant effect" analysis is guided by regulations which outline relevant factors for determining whether an action will be significant . . . One such factor is "the degree to which the action may adversely affect an endangered or threatened species". . . 40 C.F.R. § 1508.27(a).

In this case, the BO not only found that the Project "may" affect federally listed species, but that the increased shipping enabled by the dredging would cause "a substantial adverse effect" on the endangered Chinook salmon. (Ex. 7 at 69 ["The projected entrainment values for Chinook salmon on the San Joaquin River due to the increased shipping activity represent a substantial adverse effect on this population of fish." (emphasis added)]; see id. at 45 ["The proposed action is likely to adversely affect [the five] listed species and habitat . . ."] (emphasis added); id. at 47 [Port's Project "is expected to adversely affect listed salmonids during both the construction and port operation phases"] (emphasis added).) As inKlamath-Siskiyou, "[s]tanding alone, this suggests the need for an EIS." 373 F. Supp. 2d at 1080-81 (finding EA's conclusion that the project "`will affect, is likely to adversely affect' the Northern Spotted Owl" alone an "important factor" supporting the need for an EIS).

Defendants respond, arguing that the EA found that the Dredging Activities will not increase shipping to the West Complex. Their argument, however, is based on a false premise. As set forth above, the Dredging Activities are not properly segmented from the Project, as the dredging of Docks 14 and 15 facilitate and enable the further dredging of the other Project docks, and thereby the Project, itself. In other words, the instant Dredging Activities are a mere step in furtherance of many other steps in the overall development of the massive West Complex Project. Accordingly, defendants cannot ignore the BO's significance findings, as the Project, as a whole, is the proper reference point under NEPA.

Moreover, given the level of uncertainty concerning the Port's mitigation measures, the Corps was obligated to consider the degree to which the Dredging Activities' effects were "highly controversial" or "highly uncertain." 40 C.F.R. § 1508.27(b)(4)-(5). While the Port asserted that it would adequately mitigate the existing critical DO deficit in the San Joaquin River and DWSC by using jet aeration devices to pump additional oxygen into the water, the NFMS noted in the BO that there was substantial uncertainty regarding the effectiveness of these mitigation measures. (Ex. 7 at 56.) Likewise, the RWQCB expressed concerns about the mitigation, noting that if aeration proved inadequate and species are harmed, then further study after the fact will be of no avail. (Supp. Perlmutter Decl., filed Sept. 7, 2006, Ex. 10 at 16, 18-20, 40-41, 130-31, 158, 161, 167-68.) Even the Port's own consultants had acknowledged that despite years of effort, they had not been able to demonstrate the effectiveness of the aeration devices or identify reliable means of improving them. (Exs. 11 and 12.)

Despite these concerns, the EA, does not mention any level of uncertainty. Rather it simply asserts that the Port's aeration would be effective and that "similar devices have proven to adequately disperse oxygenated water nearly completely both horizontally and vertically across the DWSC within 24 hours." (Ex. 4 at 9-10.) In Klamath-Siskiyou, this court found in very similar circumstances that an EIS was mandated; the court found that the EA's listing of mitigation measures without analytical data to support the conclusion violated NEPA and required an EIS. 373 F. Supp. 2d at 1085-86. Here, there is not only no data to support the EA's conclusion, there is not even a hint of the considerable uncertainty and controversy surrounding the issue, itself. (Exs. 3, 10, 11.)

Based on such evidence and supporting case law, plaintiffs have clearly demonstrated a likelihood of success in proving these arguments on the merits.

II. Irreparable Harm

Plaintiffs have shown a strong likelihood of success on the merits. Therefore, the required showing of irreparable harm is considerably diminished. Colorado River Indian Tribes v. Marsh, 605 F. Supp. 1425, 1429 (C.D. Cal. 1985) ("the more possibility of success on the merits that a plaintiff establishes, the less he or she must show in the way of irreparable harm"). As set forth below, plaintiffs have demonstrated the requisite possibility of irreparable harm to species and the environment.

Initially, defendants challenge plaintiffs' showing of irreparable harm, arguing that plaintiffs seek imposition of a presumption of irreparable harm based on the claimed environmental injury. Contrary to defendants' protestations, plaintiffs do not argue that they are entitled to such a presumption; indeed plaintiffs concede that no such presumption exists. (TRO PA, filed Aug. 24, 2006, at 21.) Rather, plaintiffs argue based on several Ninth Circuit cases that the procedural injury caused by the Corps' unlawful failure to prepare an EIS constitutes irreparable harm. (Id. at 21-22.) For example, inNat'l Parks, the Ninth Circuit held that "because NEPA can do no more than require the agency to produce and consider a proper EIS, the harm that NEPA intends to prevent is imposed when a decision . . . is made without the informed environmental consideration that NEPA requires." 241 F.3d at 738 n. 18; accord, Sonoran, 408 F.3d at 1124 (upholding the district court's grant of a preliminary injunction and rejecting the defendant's argument that plaintiff was relying on a presumption of irreparable harm).

Similar to Sonoran, here, plaintiffs proffer evidence of environmental harm in the form of depleted DO levels from the dredging affecting the endangered and threatened fish species as well as significant adverse affects on those species from increased ship traffic and channel volume due to the development of the West Complex Project. Here, it is undisputed both that the Project would exacerbate the existing critical DO deficit in the San Joaquin River and DWSC, and that adequate DO is essential to the survival of the five federal listed species in the area. (Schussman Decl., filed Sept. 1, 2006, Ex. A at [Port's EIR disclosing that proposed dredging activities contribute to the cumulative deficit of the DWSC and that the resultant cumulative impacts to DO in the DWSC are potentially significant]; Supp. Perlmutter Decl. at Ex. 1 [Port acknowledging that DO impacts are of "particular concern"]; Ex. 7 at 34, 48-49, 55-56, 61, 83 [BO discussing impacts of low DO].)

Specifically, as set forth above, the NMFS determined in the BO, not only that the Project "may" affect federally listed species, but that the development of the West Complex enabled by the dredging would cause "a substantial adverse effect" on the endangered Chinook salmon. (Ex. 7 at 45, 47, 69.) "Standing alone, this suggests the need for an EIS," and certainly supports a finding of a possibility of irreparable harm.Klamath-Siskiyou, 373 F. Supp. 2d at 1080-81. Defendants' argument, to the contrary, emphasizing the BO's ultimate "no jeopardy" finding under the ESA is unavailing. "[F]or purposes of NEPA, a project need not jeopardize the continued existence of a threatened or endangered species to have a "significant" effect on the environment." Id. In this case, plaintiffs properly rely on the BO's findings to substantiate their case for irreparable harm to species and the environment.

While defendants submit evidence (see Grimes, May and Steed Decls., filed Sept. 11, 2006), from the mandated RWQCB-monitoring program of DO levels, showing that the DO levels in the vicinity of the dredgers have met or exceeded the required standards, plaintiffs submit contrary evidence through their expert. Dr. Diran Tashjian disputes defendants' results based in part on his own testing performed on September 1, 2006, which found the DO levels at two locations near the dredging below the requisite 5.2 mg/L and also below the instantaneous acute lower limit of 4.0 mg/L set by the EPA to prevent mortality to salmonids (see Tashjian Decls., filed Sept. 7 and 11, 2006). Plaintiffs' expert concluded that these reduced DO levels are directly and adversely affecting any green sturgeon or endangered salmon in the vicinity. (Tashjian Decl., filed Sept. 7, 2006, ¶ 8.) At this juncture in the case and on the limited record before it, the court cannot resolve the parties' dispute on this issue; however, considering that plaintiffs' expert's testimony is consistent with the BO's findings, it is, at a minimum, some further evidence of a possibility of irreparable harm. (Ex. 7 at 34, 55-56, 90.)

In sum, in light of the strong showing on the merits of their NEPA claim, the court finds plaintiffs' evidence sufficient to demonstrate the possibility of irreparable harm.

Plaintiffs offered a myriad of other bases for the claimed irreparable injury here; however, because the court finds plaintiffs' showing sufficient with regard to the DO level issue, it does not consider their other claims of injury.

III. Balance of Hardships

Where, as here, plaintiffs have shown sufficiently strong likelihood of success and the possibility of irreparable harm, preliminary injunctive relief is appropriate regardless of the balance of hardships. Earth Island, 442 F.3d at 1158 (describing elements of the "alternative" test for granting a preliminary injunction). Nevertheless, the court notes that in this case, the balance of interests do not tip in defendants' favor. Weighing against the possibility of significant environmental injury here is the Port's claimed economic losses should a preliminary injunction issue. Those losses include an anticipated $423,000.00 in mobilization and demobilization fees paid to the dredging contractors. (Kasper Decl., filed Sept. 1, 2006.) Such financial hardship cannot outweigh potential irreversible harm to the environment. See, e.g., Earth Island, 442 F.3d at 1177 (economic losses suffered as a result of enjoined timber sales does not outweigh potential irreparable environmental harm and the public's interest in preserving the environment); Idaho Sporting Congress Inc. v. Alexander, 222 F.3d 562, 569 (9th Cir. 2000) (injunction proper where environmental harm was sufficiently likely, despite fact that it "could present financial hardship" to government agency); Nat'l Parks, 241 F.3d at 738 ("loss of anticipated revenue . . . does not outweigh the potential irreparable harm to the environment");Western Radio Servs. Co. v. Espy, 79 F.3d 896, 902-03 (9th Cir. 1996) (finding that "NEPA's purpose is to protect the environment, not the economic interests of those adversely affected by agency decisions") (internal quotations omitted).

In Earth Island, the court appears to have applied the "traditional" test for entry of a preliminary injunction. Id. at 1158, 1177-78.

Moreover, the court must consider that the Port voluntarily undertook the risk that the dredging would not be commenced or completed this Fall. Defendants admit the Port "let the dredging contract and . . . publicly set its electric dredge in the water before obtaining its final permit from the Corps." (Opp'n, filed Sept. 1, 2006, 42:1-3.) Indeed, at the time the Port entered into the dredging contracts, it had not submitted to the Corps the Revised Application for permission to dredge at Docks 14 15. (Exs. 9-10 [application submitted on July 27, 2006].) The Port did not secure approval from the Corps to dredge Docks 14 and 15 until August 16, 2006 — nearly one month after the Port entered into the dredging contracts. In short, the Port knowingly accepted the risk that dredging may not even commence in 2006. Nevertheless, the financial loss that will be incurred as a result of this order is not insubstantial. However, in all such cases when the court finds the nation's environmental laws have been violated, economic loss (here, in the amount of several hundred thousand dollars) must yield to NEPA.

CONCLUSION

Therefore, for the foregoing reasons, the court GRANTS plaintiffs' motion for a preliminary injunction:

IT IS HEREBY ORDERED that the Port, and its respective agents, partners, employees, contractors, assignees, successors, representatives, and all persons acting under authority from, in concert with, or for it in any capacity, are enjoined from further dredging adjacent to Docks 14 and 15 of the West Complex and the Corps' Permit, authorizing said dredging, is stayed, pending final resolution of the case on the merits.

In the court's discretion and in light of the nature of the case, the court relieves plaintiffs of the obligation to file a bond. Fed.R.Civ.P. 65(c); See People ex rel. Van de Kamp v. Tahoe Regional Plan, 766 F.2d 1319 (9th Cir. 1985) (bond not required because of the "chilling effect" on public interest litigants seeking to protect the environment).

IT IS SO ORDERED.


Summaries of

Baykeeper v. U.S. Army Corps of Engineers

United States District Court, E.D. California
Sep 20, 2006
No. Civ. S-06-1908 FCD/GGH (E.D. Cal. Sep. 20, 2006)
Case details for

Baykeeper v. U.S. Army Corps of Engineers

Case Details

Full title:BAYKEEPER and its Deltakeeper Chapter, and NATURAL RESOURCES DEFENSE…

Court:United States District Court, E.D. California

Date published: Sep 20, 2006

Citations

No. Civ. S-06-1908 FCD/GGH (E.D. Cal. Sep. 20, 2006)

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