Opinion
21-cv-05407-VKD
04-22-2024
OCEANA, INC., Plaintiff, v. GINA RAIMONDO, et al., Defendants.
ORDER ON CROSS-MOTIONS FOR SUMMARY JUDGMENT
RE: DKT. NOS. 43, 44
VIRGINIA K. DEMARCHI UNITED STATES MAGISTRATE JUDGE
Plaintiff Oceana, Inc. (“Oceana”), a non-profit ocean conservation and advocacy organization, sues Secretary of Commerce Gina Raimondo, the National Oceanic and Atmospheric Administration (“NOAA”), and the National Marine Fisheries Service (“NMFS”), challenging defendants' management of the Pacific sardine under the Magnuson-Stevens Fishery Conservation and Management Act (“MSA”), 16 U.S.C. § 1801 et seq., and the National Environmental Policy Act (“NEPA”), 42 U.S.C. § 4321 et seq.
After proceedings regarding completion of the administrative record, the parties filed cross-motions for summary judgment. Dkt. Nos. 43, 44. On July 11, 2023, the Court held a hearing on the motions. Dkt. No. 48. After the hearing, the parties stipulated to allow Oceana to file an amended complaint adding a challenge to NMFS's 2023-2024 annual specifications for the Pacific sardine. See Dkt. Nos. 47, 50. They also agreed that defendants would file a supplemental administrative record regarding the annual specifications and that the parties would file supplemental briefs in support of their respective motions. Id.
In its operative complaint, Oceana claims that NMFS's plan to rebuild the Pacific sardine's population after it was declared overfished in 2019 violates the MSA because NMFS: (1) failed to *This order corrects non-substantive typographical errors on pages 2, 3, 5, 8, and 31. set a reasonable rebuilding target for the sardine population based on the best available science (claim 1); (2) failed to demonstrate, based on the best available science, that the plan will rebuild the sardine population (claim 2); (3) failed to demonstrate, based on the best available science, that the plan will prevent overfishing (claim 3); (4) failed to consult regarding the plan's impact on essential fish habitat (claim 7); and (5) failed to demonstrate, based on the best available science, that the 2023-2024 annual specifications will prevent overfishing or rebuild the sardine population (claim 8). Dkt. No. 51 ¶¶ 140-161, 182-191. Oceana also claims that NMFS's approval of the plan violates NEPA because they: (1) failed to analyze the impacts of the authorized action (claim 4); (2) failed to take a hard look at the plan's impacts on sardine population and marine predators (claim 5); and (3) failed to prepare an environmental impact statement for the plan, even though the plan will have significant impacts on the environment (claim 6). Id. ¶¶ 162-181.
Having considered the parties' briefing and oral arguments, the Court grants Oceana's motion in part and denies it in part, and grants defendants' cross-motion in part and denies it in part.
I. BACKGROUND
A. Statutory and Regulatory Background
1. The Magnuson-Stevens Fishery Conservation and Management Act
After overfishing threatened the survival of some fish species, Congress enacted the Magnuson-Stevens Fishery Conservation Act in 1976 to conserve and manage the fisheries off the coasts of the United States. See 16 U.S.C. § 1801(a), (b). The MSA establishes eight regional fishery management councils, each of which is charged with developing a “fishery management plan” (“FMP”) for the fisheries in its region. 16 U.S.C. § 1852(a)(1), (h)(1). The regional councils are assisted in the work of developing and amending fishery management plans by scientific and statistical committees (“SSCs”) whose members must have “strong scientific or technical credentials and experience.” 16 U.S.C. § 1852(g)(1)(A), (C).
FMPs must contain the conservation and management measures “necessary and appropriate for the conservation and management of the fishery, to prevent overfishing and rebuild overfished stocks, and to protect, restore, and promote the long-term health and stability of the fishery.” 16 U.S.C. § 1853(a)(1)(A). FMPs must also comply with ten national standards, including the requirements that conservation and management measures must “prevent overfishing while achieving, on a continuing basis, the optimum yield from each fishery for the United States fishing industry” (National Standard 1), and must “be based upon the best scientific information available” (National Standard 2). 16 U.S.C. § 1852(a)(1), (2). The Secretary of Commerce has promulgated regulations in the form of “advisory guidelines” based on these national standards “to assist in the development and review of FMPs, amendments and regulations” prepared by the regional councils. See 16 U.S.C. § 1851(b); 50 C.F.R. § 600.305 et seq.
Among many other requirements, FMPs must “establish a mechanism for specifying annual catch limits . . . at a level such that overfishing does not occur in the fishery, including measures to ensure accountability.” 16 U.S.C. § 1853(a)(15). FMPs must also “specify objective and measurable criteria for identifying when the fishery . . . is overfished . . . and, in the case of a fishery which [has been determined to be] overfished, contain conservation and management measures to prevent overfishing or end overfishing and rebuild the fishery.” 16 U.S.C. § 1853(a)(10). In addition, they must also “describe and identify essential fish habitat [(“EFH”)] for [a] fishery” and “minimize to the extent practicable adverse effects on such habitat caused by fishing.” 16 U.S.C. § 1853(a)(7).
NMFS, an agency of the United States Department of Commerce, has primary responsibility for ensuring that the requirements of the MSA are followed and enforced. See Pac. Dawn LLC v. Pritzker, 831 F.3d 1166, 1170 (9th Cir. 2016).
The Secretary of Commerce is ultimately responsible for overseeing the proper administration and implementation of the MSA. See 16 U.S.C. §§ 1802(39), 1851-1855. The Secretary has delegated responsibility for ensuring compliance with the MSA to NMFS, an agency within NOAA. See Pac. Dawn LLC, 831 F.3d at 1170.
2. National Environmental Policy Act
NEPA establishes a national policy to “encourage productive and enjoyable harmony between man and his environment” and to “promote efforts which will prevent or eliminate damage to the environment and biosphere and stimulate the health and welfare of man.” 42 U.S.C. § 4321. NMFS, as a federal agency, is bound by NEPA and its implementing regulations. 42 U.S.C. § 4332; 40 C.F.R. § 1500.3.
An agency must take a “hard look” at the environmental effects of a proposed action, including considering all foreseeable direct and indirect impacts as well as cumulative impacts. Ctr. for Biological Diversity v. Salazar, 695 F.3d 893, 916-17 (9th Cir. 2012); Robertson v. Methow Valley Citizens Council, 490 U.S. 332, 350 (1989); see also 42 U.S.C. § 4321. However, NEPA “imposes only procedural requirements on federal agencies” and “‘does not mandate particular results.'” Dep't of Transp. v. Pub. Citizen, 541 U.S. 752, 756 (2004) (quoting Robertson, 490 U.S. at 350).
Under NEPA, a federal agency must prepare an environmental impact statement (“EIS”) for any major federal action significantly affecting the human environment. 42 U.S.C. § 4332(C); 40 C.F.R. § 1501.3(a)(3). If an action is not likely to have a significant impact on the environment or if the environmental impact is unknown, the agency must prepare an environmental assessment (“EA”). 40 C.F.R. § 1501.3(a)(2). An EA is a “concise, public document” providing “sufficient evidence and analysis” for the agency to determine “whether to prepare an environmental impact statement.” 40 C.F.R § 1508.1(h). If the EA demonstrates that the action is likely to significantly impact the environment, then the agency must prepare an EIS. 40 C.F.R. § 1501.5(c)(1). If the EA demonstrates that the action is not likely to significantly impact the environment, then the agency must prepare a finding of no significant impact. 40 C.F.R. §§ 1501.6(a), 1501.5(c)(1).
B. Management of the Pacific Sardine
The northern subpopulation of Pacific sardine (“Pacific sardine”) is a small pelagic fish that travels in large schools. AR 12. This subpopulation is found off the west coast between southeast Alaska and the northern portion of Baja California in Mexico. AR 12. The Pacific sardine is an important source of forage for larger fish, marine mammals, and seabirds. AR 24. Multiple fisheries take the Pacific sardine, including (1) the primary directed commercial fishery, which directly targets sardine at a large scale, (2) the live bait fishery, which harvests sardines for bait, (3) the minor directed fishery, comprised of small-scale fishing that directly targets sardines, (4) the tribal fishery, which includes directed fishing by Native American tribes, and (5) fisheries that target other fish species, but catch sardines incidentally. AR 16-19.
A different subpopulation, the southern subpopulation of Pacific sardine, is found off the coast of southern California and the Baja California peninsula and overlaps with the northern subpopulation in southern California. AR 12. The southern subpopulation sardine is not managed by the NMFS under the MSA. See AR 12; Dkt. No. 44 at 5.
In addition, some sardine fishing is exempt from regulation and is permitted for scientific purposes. See AR 5462.
The Pacific sardine population naturally fluctuates in abundance and productivity over time. AR 12. Overfishing can occur at any time, but fishing during a period of low abundance and productivity may contribute to the rapid decline of the population and delay its recovery- although scientists disagree regarding the extent to which fishing impacts sardine population fluctuations. AR 15, 5823, 6323, 6339, 6371. For example, scientists agree that a natural decline in sardine population, combined with overfishing, led to the sudden collapse of the Pacific sardine fishery in the 1950s. AR 15-16, 6320, 6339. More recently, the population of Pacific sardine peaked in 2006 with an estimated biomass of over 1.5 million metric tons (“mt”), after which it declined significantly over the next several years to an estimated biomass of only 28,276 mt in 2020. AR 15-16; AR 28 (graph showing sardine biomass 2005-2019).
Sardine populations may be described in terms of metric tons of biomass. There are two different ways to measure biomass. “Spawning biomass” measures sardines two years or older, when the fish become old enough to reproduce, while “1+ biomass” measures sardines one year or older. Dkt. No 43 at 13 n.4; Dkt. No. 44 at 20 n.7; AR 6150. Unless otherwise stated, this order uses “biomass” to refer to the “1+ biomass” measure.
The Pacific Fishery Management Council (“the Council”) is the regional council responsible for fisheries off the coasts of California, Oregon, and Washington. 16 U.S.C. § 1852(a)(1)(F). Effective January 1, 2000, the Council amended its Coastal Pelagic Species Fishery Management Plan (“CPS FMP”) to cover the Pacific sardine. AR 12, 1939, 5442. Like all FMPs, the CPS FMP must “prevent overfishing” while also achieving the “optimum yield” from the fishery on a sustained basis. See 16 U.S.C. § 1851(a)(1).
The MSA defines “overfishing” as a “rate or level of fishing mortality that jeopardizes the capacity of a fishery to produce the maximum sustainable yield on a continuing basis.” 16 U.S.C. § 1802(34). The “optimum yield” of a fishery is “the amount of fish” that “will provide the greatest overall benefit to the Nation, particularly with respect to food production and recreational opportunities,” while “taking into account the protection of marine ecosystems.” 16 U.S.C. § 1802(33)(A). The optimum yield is meant to be “the maximum sustainable yield from the fishery, as reduced by any relevant social, economic, or ecological factor.” 16 U.S.C. § 1802(33)(B). The “maximum sustainable yield” or “MSY” is defined by regulation as “the largest long-term average catch” that can be taken from a stock “under prevailing ecological, environmental conditions and fishery technological characteristics.” 50 C.F.R. § 600.310(b)(2)(i), (e)(1)(i)(A). If a fishery is “overfished,” the optimum yield means “the amount of fish” that “provides for rebuilding to a level consistent with producing the maximum sustainable yield in such fishery.” 16 U.S.C. § 1802(33)(C).
Closely related to MSY are exploitation rate at maximum sustainable yield (“EMSY”), which is “the fishing mortality rate that, if applied over the long term, would result in MSY,” and biomass at maximum sustainable yield (“BMSY”), which is “the long-term average size of the stock or stock complex . . . that would be achieved by fishing at [EMSY.]” 50 C.F.R. § 600.310(e)(1)(i)(B)-(C) (emphasis added).
To prevent overfishing, an FMP must “specify objective and measurable criteria for identifying when the fishery to which the plan applies is overfished.” 16 U.S.C. § 1853(a)(10). One such measure is an overfishing limit (“OFL”), which is the annual amount of catch “above which overfishing is occurring.” 50 C.F.R. § 600.310(e)(2)(i)(C), (D). To prevent overfishing, regulators set annual catch limits below the OFL, using two additional measures: the acceptable biological catch and annual catch limits. Acceptable biological catch (“ABC”) reflects an adjustment to OFL “to account for scientific uncertainty in the estimate of OFL.” 50 C.F.R. § 600.310(f)(1)(ii). The annual catch limit (“ACL”) is the maximum amount of fish that may be caught each year for the fishery and serves as the trigger for invoking accountability measures. 50 C.F.R § 600.310(f)(1)(iii); 16 U.S.C. § 1853(a)(15). The ACL “cannot exceed” the ABC and may be set lower because of “ecological, economic, and social factors” to ensure the optimum yield from a fishery. 50 C.F.R. § 600.310(f)(1)(iii), (f)(4)(i), (f)(4)(iv); see also 16 U.S.C. § 1851(a)(1). To account for uncertainty and ensure that catch does not exceed the ACL, an annual catch target (“ACT”) may also be set. 50 C.F.R. § 600.310(g)(4).
In addition to requiring calculation of catch limits using these measures, the CPS FMP adopts two different management approaches for the Pacific sardine depending on whether the sardine population is above or below a “cutoff” biomass level of 150,000 mt. AR 8-9, 5475-76. If the stock has an estimated biomass of more than 150,000 mt, NMFS uses a “harvest guideline” to set the catch limit for the year, which is based on the stock's estimated biomass, reduced by 150,000 mt. AR 5474-76. Typically, the harvest guideline will produce a lower catch limit than the limit calculated using the OFL/ABC measures. AR 5474-76. If the stock has an estimated biomass at or below the 150,000 mt cutoff, NMFS automatically closes the primary directed commercial fishery, which eliminates the main source of Pacific sardine removals, and then sets an annual catch limit for the remaining fisheries using the OFL/ABC measures. AR 5443, 547476.
C. Overfishing and Development of the Pacific Sardine Rebuilding Plan
In 2015, Pacific sardine biomass fell below 150,000 mt. AR 7. As required by the CPS FMP, NMFS closed the primary directed commercial fishery. AR 7, 16. Although the live bait, minor directed, and tribal fisheries remained open, and the incidental harvest of sardines by fisherman targeting other species continued, AR 16-18, the closure of the primary directed commercial fishery had a substantial impact on the amount of catch, AR 20. The annual Pacific sardine catch fell from 19,440 mt in the 2014-2015 fishing year to 2,329 mt in the 2015-2016 fishing year. AR 7, 20. Over the next several years, while the primary directed commercial fishery remained closed, the annual catch averaged approximately 2,200 mt. AR 20.
These figures include all sardine catch in the United States, of which the northern subpopulation sardine is only a portion. See AR 13, 15.
As required by the MSA, the CPS FMP specifies a threshold for determining when the Pacific sardine is overfished-here, 50,000 mt. AR 5476; 16 U.S.C. § 1853(a)(10). An April 2019 stock assessment showed that Pacific sardine biomass had fallen below 50,000 mt. AR 6, 3118. In June of 2019, NMFS declared the Pacific sardine overfished, triggering NMFS's and the Council's obligation under the MSA to prepare and implement a rebuilding plan. AR 6101-02; see also 16 U.S.C. § 1854(e).
Once the NMFS identifies a fishery as overfished, the responsible regional council is given two years to “prepare and implement a fishery management plan, plan amendment, or proposed regulations” to prevent or end the overfishing. 16 U.S.C. § 1854(e)(3). The plan must “specify a time period for rebuilding the fishery” that is “as short as possible, taking into account the status and biology of any overfished stocks of fish, the needs of fishing communities, . . . and the interaction of the overfished stock of fish within the marine ecosystem.” 16 U.S.C. § 1854(e)(4)(i). This period may “not exceed 10 years, except in cases where the biology of the stock of fish [or] other environmental conditions . . . dictate otherwise.” 16 U.S.C. § 1854(e)(4)(ii); see also Nat. Res. Def. Council, Inc. (“NRDC”) v. NMFS, 421 F.3d 872, 879-81 (9th Cir. 2005) (describing 16 U.S.C. § 1854(e)(4)'s requirements).
To ensure that its rebuilding plan complied with 16 U.S.C. § 1854(e), the Council first had to set a rebuilding target-i.e. the level of sardine population at which rebuilding would be deemed a success. The Council's SSC used a model called “Rebuilder” to estimate the Pacific sardine's BMSY under low and moderate productivity levels, drawing on sardine recruitment data from 2005 to 2018. AR 36, 48, 50-51. Under low productivity conditions, modeled on data from 2010 to 2018, the SSC estimated a BMSY of 38,112 mt spawning biomass (which is roughly equivalent to 48,994 mt 1+ biomass). AR 36. Under moderate productivity levels, modeled on data from 2005 to 2018, the SSC estimated a BMSY of 137,812 mt spawning biomass (which is roughly equivalent to 169,929 mt 1+ biomass). AR 36. The SSC recommended that the Council set the rebuilding target at the median of the two values, a BMSY of 116,374 mt spawning biomass (which is roughly equivalent to 143,495 mt 1+ biomass). AR 37. The Council chose a target of 150,000 mt 1+ biomass, equivalent to 121,650 mt spawning biomass, explaining that it was slightly above the SSC's recommendation and consistent with the cutoff threshold already used in the FMP. AR 37.
For these calculations, the Court assumes that the ratio of spawning biomass to +1 biomass approximates that reported at ¶ 37.
After setting the rebuilding target, the Council formulated and analyzed three potential rebuilding plans for the Pacific sardine. AR 6-7. Alternative 1 (“Status Quo Management”) would adopt and maintain all existing management measures and rules already in place for the Pacific sardine. AR 8. Alternative 2 (“Zero U.S. Harvest Rate”) would eliminate all Pacific sardine fishing under U.S. jurisdiction, including complete closure of the remaining fisheries that target Pacific sardine. AR 9. Alternative 3 (“Five Percent Fixed U.S. Harvest Rate”) would set the annual catch limit for the Pacific sardine at 5% of the stock's biomass for the year, bypassing the other formulas in the CPS FMP. AR 9.
To predict the effects the alternative proposals would have on the Pacific sardine population over time, the Council again used the Rebuilder model. AR 10. The SSC modeled how long it would take each proposal to rebuild the sardine, defined as the point at which there was a 50% or greater probability that sardine biomass would exceed the target. See AR 14, 45-56. Each proposal was modeled under both moderate and low productivity conditions. AR 10-11. The model did not eliminate the uncertainty caused by sardine's natural fluctuations in population. As the Council noted, because “Pacific sardine recruitment and productivity are largely driven by environmental conditions, which cannot be accurately predicted, . . . the modeling results [] have limitations in informing realistic rebuilding timelines.” AR 10. Even so, the SSC endorsed the use of the Rebuilder model to analyze the sardine's recovery. AR 3667.
For Alternative 2, where no fishing was allowed, the model predicted rebuilding would require 12 years. AR 14. For Alternative 3, where the annual catch was limited to 5% of biomass, the model predicted rebuilding would require 16 years, assuming that the full amount of catch permitted was taken each year. AR 14-15. For Alternative 1, which contemplated the level of catch currently permitted under the CPS FMP would be allowed to continue, the model predicted rebuilding would never occur, assuming the full ABC would be taken each year. AR 14. However, the Council decided to model Alternative 1 a second time using a different assumption; rather than assuming an annual catch up to the limit of ABC, it assumed the annual catch would be 2,200 mt per year, consistent with the actual average catch for the proceeding five years, which was significantly below the ABC. AR 14, 20. This time, the model predicted rebuilding would require 17 years. AR 14. Comparing the revised rebuilding timeline for Alternative 1 with the timelines for the two other alternatives, the Council reasoned that it was “unclear” whether Alternative 3 “would allow the stock to realistically rebuild any faster” than Alternative 1, noting that there was only a one-year difference between the projected rebuilding timelines for these two alternatives. AR 15. The Council observed that “the rebuilding timeline under Alternative 3 is expected to be longer than the 12 years for Alternative 2, but potentially shorter than the 16 years initially modeled.” AR 15. But, it ultimately concluded that “no management alternative is expected to significantly impact the ability of the Pacific sardine resource to rebuild in the near or long term, as fishing mortality is not the primary driver of stock biomass.” AR 15.
Having modeled the rebuilding timelines for the three alternatives, the Council then considered the impact of each alternative on the fishing industry. Because the primary directed commercial fishery would remain closed until the rebuilding target was reached under all three plans, the Council focused its analysis on the smaller fisheries that had remained open after the cutoff was reached in 2015, most notably the live bait fishery, the minor directed fishery, and the incidental harvest of sardines by other fisheries. See AR 16. According to the Council, under Alternative 1, these fisheries would experience “minimal” negative impacts; under Alternative 2, they would be “severely and adversely impacted,” until sardine biomass was rebuilt and fishing was permitted again; and under Alternative 3, “there would inevitably be negative economic impacts to the smaller-scale fishery sectors when biomass is at 50,000 mt and below.” AR 19-21. Weighing these considerations, the Council determined that “Alternative 3 would impose unnecessary economic impact to the industry with minimal change in the rebuilding timeline.” AR 23.
Of the three fisheries, the live bait fishery is the largest, catching an average of 2,522 mt of sardines per year between 2005 and 2015. AR 17-18.
As required by NEPA, the Council also considered the environmental impacts of the three alternative proposals. It noted that Pacific sardine is prey for “several commercially important marine fishes,” including salmon and tuna. AR 24. It also acknowledged that sardines are forage for two endangered species, the marbled murrelet and the humpback whale. AR 24. However, the Council concluded that “none of the proposed management alternatives are expected to significantly affect forage availability, as most Pacific sardine predators are generalists that are not dependent on the availability of a single species but rather on a suite of species, any one (or more) of which is likely to be abundant each year.” AR 27.
Based on these analyses, in September 2020 the Council selected Alternative 1 as its preferred alternative. AR 4911. The Council then a proposed an amendment, Amendment 18, to the CPS FMP incorporating Alternative 1, and transmitted the proposed amendment to NMFS for approval in January of 2021. AR 4324. NMFS solicited public comment on the proposed amendment. AR 3113; 86 Fed.Reg. 14,401. Oceana urged the agency not to approve it, arguing that Amendment 18 violated the MSA and the APA. See AR 5279. Several fishing industry groups filed comments in support of the amendment. See AR 4877, 4881, 4904. NMFS approved the amendment on June 14, 2021. AR 4910, 4883. Along with its approval, the agency issued a finding of no significant impact under NEPA. AR 158-63.
D. 2023-2024 Annual Specifications
The CPS FMP requires the Council and NMFS to set annual specifications, including the OFL, ABC, ACL, and accountability measures, for the Pacific sardine. AR 5479. Annual specifications are set after a rulemaking process including consultation with the SSC, a public meeting, and an opportunity for public comment. AR 5479-80.
On June 23, 2023, NMFS published in the Federal Register annual specifications “based on the annual specification framework, control rules, and management guidelines in the [CPS] FMP” for the Pacific sardine during the 2023-2024 fishing year. Dkt. No. 53-2 at 12-15; 88 Fed.Reg. 41,040-43. Based on a biomass estimate of 27,369 mt, the specifications included an OFL of 5,506 mt, an ABC of 3,953 mt, an ACL of 3,953 mt, and an ACT of 3,600 mt. Dkt. No. 53-2 at 13. The primary directed commercial fishery remained closed. Id. The 2023-2024 annual specifications also included the following management measures to limit live bait and incidental catch fishing: “(1) If landings in the live bait fishery reach 2,500 mt of Pacific sardine, then a 1mt per-trip limit of sardine would apply to the live bait fishery. (2) An incidental per-landing limit of 20-percent (by weight) Pacific sardine applies to other CPS primary directed fisheries (e.g., Pacific mackerel). (3) If the ACT of 3,600 mt is attained, then a 1-mt per-trip limit of Pacific sardine would apply to all CPS fisheries (i.e., (1) and (2) would no longer apply). (4) An incidental per-landing allowance of 2 mt of Pacific sardine applies to non-CPS fisheries until the ACL is reached.” Id.
The fishing year runs from July 1st of one year to June 30th of the next. See Dkt. No. 53-2 at 12.
II. STANDARD OF REVIEW
Judicial review of agency decisions under the MSA and NEPA is governed by the APA's standard of review. 16 U.S.C. § 1855(f)(1); Oregon Trollers Ass'n v. Gutierrez, 452 F.3d 1104, 1116 (9th Cir. 2006) (MSA); Native Ecosystems Council v. Dombeck, 304 F.3d 886, 891 (9th Cir. 2002) (NEPA). Agency action must be set aside if it is “arbitrary, capricious, an abuse of discretion, or otherwise not in accordance with law,” or if the agency acts without observing “procedure required by law.” 5 U.S.C. § 706(2)(A), (D). Agency action is arbitrary and capricious if “the agency has relied on factors which Congress has not intended it to consider, entirely failed to consider an important aspect of the problem, offered an explanation for its decision that runs counter to the evidence before the agency, or is so implausible that it could not be ascribed to a difference in view or the product of agency expertise.” Motor Vehicle Mfrs. Ass'n v. State Farm Mutual Auto. Ins. Co., 463 U.S. 29, 43 (1983) (“State Farm”).
While a court must “conduct a ‘searching and careful' inquiry” into the agency's decision, Native Ecosystems Council v. Weldon, 697 F.3d 1043, 1050 (9th Cir. 2012) (quoting Marsh v. Oregon Nat. Res. Council, 490 U.S. 360, 378 (1989)), the scope of this review is narrow and “a court is not to substitute its judgment for that of the agency.” Snoqualmie Valley Pres. All. v. U.S. Army Corps of Eng'rs, 683 F.3d 1155, 1159 (9th Cir. 2012) (quoting State Farm, 463 U.S. at 43). The court looks only to whether the agency “examined ‘the relevant data' and articulated ‘a satisfactory explanation' for [its] decision, ‘including a rational connection between the facts found and the choice made.'” Dep't of Com. v. New York, 139 S.Ct. 2551, 2569 (2019) (quoting State Farm, 463 U.S. at 43).
A court must defer to the expert agency in factual disputes, particularly “when the analysis requires a high level of technical expertise.” Selkirk Conservation All. v. Forsgren, 336 F.3d 944, 954 (9th Cir. 2003). However, “the deference accorded an agency's scientific or technical expertise is not unlimited” and can be rebutted “when its decisions, while relying on scientific expertise, are not reasoned.” Brower v. Evans, 257 F.3d 1058, 1067 (9th Cir. 2001).
Although courts routinely resolve APA challenges to an agency's administrative decisions by summary judgment, they need not conduct the traditional search for genuine disputes of material fact, because “there are no disputed facts that the district court must resolve.” Occidental Eng'g Co. v. INS., 753 F.2d 766, 769 (9th Cir. 1985). Rather, “the function of the district court is to determine whether or not as a matter of law the evidence in the administrative record permitted the agency to make the decision it did.” Id.
III. DISCUSSION
A. Whether Disputed Agency Action Is Subject to Judicial Review
In their motion for summary judgment, defendants initially contended that this Court lacks jurisdiction to decide Oceana's claims. See Dkt. No. 44 at 12-15. Citing Alaska Factory Trawler Association v. Baldridge, 831 F.2d 1456, 1464 (9th Cir. 1987), defendants argued that (1) the MSA provides for judicial review only of regulations and “actions” taken to “implement a fishery management plan,” and not FMPs themselves, see id. at 12-13 (quoting 16 U.S.C. § 1855(f)(1)-(2)), and (2) judicial review is unavailable under the APA because an FMP is not a “final agency action,” see id. at 13-15. Oceana responded that Amendment 18 is a regulation, or alternatively an agency action, reviewable under the MSA and the APA. Dkt. No. 45 at 3-9.
However, the parties agree that the annual specifications implementing the FMP are subject to judicial review, and defendants concede that if Oceana challenges the annual specifications, that challenge may encompass the FMP amendment on which the specifications are based. Dkt. No. 46 at 2, 6; see also Oregon Trollers, 452 F.3d at 1113 (“[A timely] petition . . . of an action may challenge both the action and the regulation under which the action is taken.”); Gulf Fishermen's Ass'n v. Gutierrez, 529 F.3d 1321, 1323 (11th Cir. 2008) (same). Pursuant to the parties' stipulation, Oceana filed an amended complaint that includes a challenge to the 2023-2024 annual specifications. See Dkt. Nos. 50, 51. The parties agree that the amendment “eliminate[s] any dispute as to whether the Court has jurisdiction over this suit.” Dkt. No. 50 at ECF 2.
B. Magnuson-Stevens Act Claims
Oceana claims that in approving Amendment 18 and the 2023-2024 annual specifications implementing the amendment, NMFS violated the MSA in five ways: (1) it failed to set a reasonable rebuilding target for the sardine population (claim 1); (2) it failed to demonstrate that the rebuilding plan will rebuild the sardine population in the statutory timeframe (claim 2); (3) it failed to demonstrate that the plan will prevent overfishing (claim 3); (4) it failed to consult regarding the plan's impact on essential fish habitat (claim 7); and (5) it failed to demonstrate that the 2023-2024 annual specifications will prevent overfishing or rebuild the sardine population (claim 8). Dkt. No. 51 ¶¶ 140-161, 182-191.
1. Claim 1: Rebuilding Target
Oceana claims that NMFS failed to use the best available science to set a rebuilding target for the Pacific sardine. Id. ¶¶ 140-147; Dkt. No. 43 at 12-15. It argues that the rebuilding target in Amendment 18 conflicts with the agency's own scientific estimates of the long-term biomass necessary to support MSY. Specifically, Oceana contends that “the rebuilding target must reflect the long-term average BMSY,” and because the sardine population fluctuates over a period of about 60 years, NMFS must estimate BMSY using data from a 60-year population cycle or at least periods of both low and high productivity. See Dkt. No. 43 at 13-14 (citing 50 C.F.R. § 600.310(e)(1)(i)(C)). Oceana faults NMFS for calculating a BMSY value based on data from a “shorter timeframe of 14 years (from 2005-2018) that only included years when sardine productivity was low,” when the agency had superior data for longer periods of time. Id. at 14.
Defendants respond that NMFS relied on the best available science when setting the rebuilding target at 150,000 mt biomass. Dkt. No. 44 at 20-22. They note that NMFS has never specified a single BMSY for the Pacific sardine because its population is subject to dramatic, natural fluctuations. Id. at 20 (citing AR 3062). They also argue that the older BMSY estimates proffered by Oceana are “inconsistent with current conditions,” id. at 21, and that the applicable regulations direct that MSY should be estimated “under prevailing ecological, environmental conditions,” Dkt. No. 46 at 10 (citing 50 C.F.R. § 600.310(1)(i)(A)); see also AR 4928 (“[W]hen developing a rebuilding plan it is important to consider the current environmental and/or reproductive conditions the stock is experiencing.”). Finally, defendants emphasize that the BMSY estimates and the Rebuilder model used to calculate the estimates were reviewed and endorsed by the SSC, reflect the best available science, and are therefore entitled to deference. Dkt. No. 44 at 20, 22 (citing AR 3667).
Once a fishery becomes overfished, the MSA requires NMFS to implement an FMP, FMP amendment, or regulation to end overfishing immediately and rebuild the stock “to a level consistent with producing the maximum sustainable yield in such fishery”-i.e. BMSY. 16 U.S.C. §§ 1802(33)(C), 1851(a)(1), 1854(e); 50 C.F.R. § 600.310(j)(3)(i); see also AML Int'l, Inc. v. Daley, 107 F.Supp.2d 90, 98 (D. Mass. 2000) (“The primary purpose of a rebuilding program for overfished stock is to rebuild the stock to produce MSY on a continuing basis.”). NMFS's MSA regulations provide guidelines for “specifying MSY.” See 50 C.F.R. § 600.310(e)(1)(v). “Ecological and environmental information should be taken into account,” when estimating MSY or BMSY and these values “should be re-estimated as required by changes in long-term environmental or ecological conditions, fishery technological characteristics, or new scientific information.” 50 C.F.R. § 600.310(e)(1)(v)(A), (B). These estimates “must be based on the best scientific information available.” 50 C.F.R. § 600.310(e)(1)(v)(A); see also 16 U.S.C. § 1851(a)(2). The guidelines also recognize that MSY estimates “will have some level of uncertainty associated with them” and suggest that “[t]he degree of uncertainty in the estimates should be identified, when practicable, . . . and should be taken into account when specifying the ABC Control rule” and “[w]hen data are insufficient to estimate MSY directly, Councils should adopt other measures of reproductive potential that can serve as reasonable proxies for [MSY or BMSY].” 50 C.F.R. § 600.310(e)(1)(v)(B), (D).
“Where scientific and technical expertise is necessarily involved in agency decision- making, a reviewing court must be highly deferential to the judgment of the agency.” Oregon Trollers, 452 F.3d at 1120 (quoting Nat'l Wildlife Fed'n v. U.S. Army Corps of Eng'rs, 384 F.3d 1163, 1174 (9th Cir. 2004). However, no deference is owed if the “agency's decision is without substantial basis in fact” or it “did not consider all the relevant factors and [] there is no rational connection between the facts found and the determination made.” Earth Island Inst. v. Hogarth, 494 F.3d 757, 766 (9th Cir. 2007) (quoting Fed. Power Comm'n v. Fla. Power & Light Co., 404 U.S. 453, 463 (1972) and Pac. Coast Fed'n of Fishermen's Ass'n, Inc. v. NMFS, 265 F.3d 1028, 1034 (9th Cir. 2001)).
The Court concludes that NMFS's decision to set the rebuilding target at 150,000 mt does not violate the MSA or the APA. Oceana is correct that NMFS must set a target that reflects longterm average BMSY, but neither the MSA nor its implementing regulations defines “long-term” to mean the entire productivity cycle of a species. See generally 50 C.F.R. § 600.310. More importantly, neither the MSA nor its implementing regulations specifies whether, for a species with natural productivity fluctuations like the Pacific sardine, the agency must set a target that reflects periods of both low and high productivity, regardless of whether the stock is presently in a natural period of low productivity, or conversely, high productivity. Rather, the guidelines contemplate that current ecological and environmental conditions may be taken account in estimating BMSY. See 50 C.F.R. § 600.310(e)(1)(i), (v).
The rebuilding target adopted by NMFS is based on a rebuilding analysis prepared the SSC, whose members must have “strong scientific or technical credentials and experience.” 16 U.S.C. § 1852(g)(1)(C); see also AR 45-56 (SSC rebuilding analysis). The SSC acknowledged that the results of its rebuilding analysis “are difficult to interpret as the target biomass levels and times to achieve rebuilding are strongly dependent on assumptions of the state of nature.” AR 53. Likewise, the SSC noted that its analysis relies on data “represent[ing] a relatively narrow time frame” and thus provides “a limited snapshot of the long-term population fluctuations.” AR 53. Citing the Pacific sardine's “highly variable recruitment success and related population abundance based primarily on oceanographic factors,” the SSC also concluded that accurate projections of the Pacific sardine's population over a longer period could not be made. See AR 53 (“Detailed
understanding of the relationship between specific environmental drivers and a [small pelagic fish] stock's productivity is generally lacking or at the very least, refuted when evaluated over longer time periods.”). Similarly, the SSC acknowledged that the rebuilding model it adopted also could not accurately project the size of the Pacific sardine stock over a longer period. AR 54 (“[T]he results presented here are likely to be more accurate in capturing short-term projected stock and fishery dynamics as opposed to the longer term since there is an absence of critical environmental data generally believed to be the underlying/overriding factors that influence this species' population dynamics.”); see also AR 4928 (stating in response to Oceana's comment that “[a]lthough history and science have shown that the Pacific sardine population can recover quickly when conditions are favorable . . . it is unknown when those conditions will change.”). In view of these uncertainties, the SSC used data from a period of low and moderate productivity for purposes of setting the rebuilding target, taking into account existing and reasonably anticipated ecological and environmental conditions. Based on the SSC's analysis, the NMFS concluded that the Pacific sardine fishery can support a specified maximum average catch during a sustained period of low productivity when the stock is at 150,000 mt. This reflects a reasoned determination based on scientifically relevant data, rather than a “clear error of judgment,” San Luis & Delta-Mendota Water Auth. v. Jewell, 747 F.3d 581, 601 (9th Cir. 2014) (quoting Citizens to Pres. Overton Park, Inc. v. Volpe, 401 U.S. 402, 416 (1971)).
Oceana argues that 150,000 mt “represents a vulnerable, low sardine population level,” Dkt. No. 43 at 15 (quoting AR 2590), and that by adopting this biomass as the rebuilding target “Amendment 18 keeps the sardine population at levels too low to support either dependent predators or the primary sardine fishery for half a century or more,” id. at 1, 12-15. Nothing in the MSA or its implementing regulations prohibits NMFS from setting the rebuilding target at the 150,000 mt level, even if that is the same level at which NMFS has decided to automatically close the primary directed fishery when biomass is declining. Defendants explain that NMFS adopted the 150,000 mt cutoff as a conservative measure-a “precaution built into [the FMP's] framework”-that is intended to automatically protect the fishery from overfishing in the first instance. Dkt. No. 44 at 22; see also AR 4924, 4928. As such, defendants argue-and the Court agrees-there is no inherent inconsistency arising from the fact that NMFS set the cutoff and the rebuilding target at the same level. See Dkt. No. 44 at 22.
On this record, the Court finds that NMFS did not ignore or disregard the best available science. While NMFS could have rationally relied on different data and/or different models in setting the rebuilding target, the agency has articulated a rational connection between the scientific evidence and its decision to set the rebuilding target at 150,000 mt. See Oregon Trollers, 452 F.3d at 1119 (“[W]e will uphold a regulation against a claim of inconsistency with a ‘national standard' under § 1851 if [NMFS] had a ‘rational basis' for it.”).
Accordingly, the Court concludes that NMFS's rebuilding target does not fail to use the best available science.
2. Claim 2: Failure to Rebuild Within Statutory Timeframe
Oceana claims that defendants have failed to demonstrate that Amendment 18 will rebuild the sardine population. Dkt. No. 51 ¶¶ 148-155. It argues that NMFS's modeling of the plan's effects assumes that only 2,200 mt of sardine will be caught each year, while NMFS has implemented no measures to ensure that catch will not exceed this level. Dkt. No. 43 at 17; Dkt. No. 55 at 3. Defendants respond that the assumptions underlying its modeling are sound because the existing conservation and management measures result in a real-world Pacific sardine catch consistent with these assumptions. Dkt. No. 44 at 16-19; Dkt. No. 54 at 2.
After a fishery has been identified as overfished, the MSA requires the Council to develop a rebuilding plan that specifies a time period for rebuilding that is “as short as possible,” taking into account, among other factors, “the status and biology of any overfished stocks of fish” and “the needs of fishing communities.” 16 U.S.C. § 1854(e)(4)(A)(i). The rebuilding period may not exceed 10 years, unless “the biology of the stock of fish” or “other environmental conditions” dictate otherwise. 16 U.S.C. § 1854(e)(4)(A)(ii). If the rebuilding period must exceed 10 years, NMFS may still take into account the needs of fishing communities “so long as the weight given is proportionate to the weight the Agency might give to such needs in rebuilding periods under 10 years.” NRDC v. NMFS, 421 F.3d at 881. Regulations implementing the MSA require NMFS to estimate the minimum and maximum times required for rebuilding the stock, and to select a time that is within the resulting range. See 50 C.F.R. § 600.310(j)(3)(i). The minimum time period is the amount of time it can be expected, with at least 50% probability, that the stock would reach BMSY with no fishing mortality, while the maximum time is set at a default of 10 years, although it may exceed 10 years if conditions require. 50 C.F.R. § 600.310(j)(3)(i)(A), (B).
In developing the rebuilding plan adopted by NMFS, the Council modeled how long it would take to rebuild the Pacific sardine using three alternative approaches. As explained above, it initially determined that if catch met the limit permitted in Alternative 1 (i.e. ABC, which was calculated as 4,288 mt in 2020-2021), then the Pacific sardine biomass would never reach the rebuilding target. AR 14, 22. By contrast, the Council determined that biomass would reach the rebuilding target in 12 years under Alternative 2 (i.e. no fishing mortality), and in 16 years under Alternative 3 (i.e. an ACL of 5% of biomass, which was calculated as 1,414 mt in 2020-2021). AR. 14, 22. Thereafter, it modeled Alternative 1 again, this time assuming that only 2,200 mt of sardines would be caught each year, consistent with the average sardine catch for the preceding five years, even though the ABCs during those years ranged from 4,514 mt to 15,479 mt. See AR 14, 20. Under this assumption, the model predicted that Alternative 1 would rebuild the sardine population in 17 years. AR 14. Because the Council viewed this 17-year period as “comparable” to the 16-year period estimated for Alternative 3, and because Alternative 1 did not require additional economically disruptive fishery closures, the Council and NMFS ultimately adopted Alternative 1. See AR 23.
The modeling period extended only through 2050, and the model projected the Pacific sardine would not rebuild by that date. AR 14.
The Court agrees with Oceana that NMFS violated the MSA by assuming that the sardine harvest would never reach the ABC or the ACLs authorized by the rebuilding plan. The statute requires FMPs to “establish a mechanism for specifying annual catch limits in the plan (including a multiyear plan), implementing regulations, or annual specifications, at a level such that overfishing does not occur in the fishery, including measures to ensure accountability.” 16 U.S.C. § 1853(a)(15). Specifically, NMFS and the regional councils must set “hard, science-based caps on how many fish could be caught each year” and requires that those caps be backed by “accountability measures [that are] triggered when fishermen exceeded those caps.” Conservation Law Found. v. Pritzker, 37 F.Supp.3d 254, 266 (D.D.C. 2014) (citing Magnuson-Stevens Fishery Conservation and Management Reauthorization Act of 2006, sec. 103, 104, Pub. L. No. 109-479, 120 Stat. 3575, 3580, 3584); see also Oceana v. Locke, 831 F.Supp.2d 95, 119-20 (D.D.C. 2011) (quoting 50 C.F.R. § 600.310(g)(3)) (“The Council must determine as soon as possible after the fishing year if an ACL was exceeded. If an ACL was exceeded, [accountability measures] must be triggered and implemented as soon as possible. . .”) (cleaned up, emphasis in original). The legislative history of the 2006 amendments to the MSA suggests that Congress added this requirement because it was dissatisfied with NMFS's and the regional councils' exercise of discretion in the past and intended to further constrain their ability to exceed the SSC's recommendations. Conservation Law Found. v. Pritzker, 37 F.Supp.3d at 266 (“Congress fundamentally altered American fishing regulation by requiring regional fishing Councils to set hard, science-based caps on how many fish could be caught each year.... [This] system was necessary because the prior regime-which was less data driven-had resulted in continued overfishing.”); see also 16 U.S.C. § 1852(h)(6) (requiring that ACLs not exceed the recommendations of a council's SSC).
Defendants argue that the MSA permits NMFS to rely on conservation and management measures, in addition to annual catch limits, to achieve the agency's rebuilding goals. Dkt. No. 44 at 18; Dkt. No. 46 at 9. They cite 16 U.S.C. § 1853(a)(10), which requires that FMPs “contain conservation and management measures to prevent overfishing or end overfishing and rebuild the fishery.” 16 U.S.C. § 1853(a)(10). According to defendants, management measures, like those implemented in the 2023-2024 annual specifications, “form the core of the rebuilding plan.” Dkt. No. 54 at 1; see also Dkt. No. 53-2 at 13 (2023-2024 management measures). They claim that because “[c]hanges to the OFL and annual catch limits will not have an on-the-ground effect when the management measures are already limiting the fishery to landing only 1% of NSP sardine biomass,” these measures validate the rebuilding timeframe modeled for Alternative 1. Dkt. No. 54 at 3.
However, NMFS may not avoid the “[e]xpress limits set by Congress” in the MSA's ABC/ACL requirement. See Conservation Law Found. v. Pritzker, 37 F.Supp.3d at 266. While the CPS FMP contains conservation and management measures that may have the practical effect of significantly limiting sardine harvest, as Oceana points out, the agency's own regulations make clear that an agency must use ABCs, from which ACLs are derived, to rebuild the fishery, even if other measures are also employed. See Dkt. No. 45 at 13; 50 C.F.R. § 600.310(f)(3)(ii) (“For overfished stocks and stock complexes, a rebuilding ABC must be set to reflect the annual catch that is consistent with the schedule of fishing mortality rates (i.e., Frebuild) in the rebuilding plan.”) (emphasis added). These regulations are entitled to “considerable deference.” Guindon v. Pritzker, 31 F.Supp.3d 169, 198 (D.D.C. 2014). Moreover, defendants' argument that conservation and management measures adequately constrain the fishery does not address the fact that the MSA's ACL requirement is intended to constrain the regulators-i.e. NMFS and the regional councils-as well. See Conservation Law Found. v. Pritzker, 37 F.Supp.3d at 266.
In assessing Alternative 1 the second time, NMFS modeled an annual catch-2,200mt- that was substantially less that the catch limits set in Alternative 1. The FMP does not expressly limit harvest to 2,200 mt nor does the FMP require NMFS to set annual specifications that do not exceed this level. See Dkt. No. 55 at 3; AR 5476; Dkt. No. 53-2 at 6, 13. In effect, NMFS modeled an entirely different alternative and then relied on that modeling as support for Alternative 1. See Dkt. No. 43 at 17. This approach to evaluating Alternative 1-the alternative the agency ultimately adopted as Amendment 18-was arbitrary and capricious and not in accordance with the law. Oceana v. Ross, 483 F.Supp.3d 764, 785 (N.D. Cal. 2020) (rejecting agency's argument that ACLs would prevent overfishing because past harvests fell below the levels authorized by the ACLs); see also Oceana v. Locke, 670 F.3d 1238, 1243 (D.C. Cir. 2011) (“When a statute commands an agency without qualification to carry out a particular program in a particular way, the agency's duty is clear; if it believes the statute untoward in some respect, then it should take its concerns to Congress, for in the meantime it must obey the statute as written.”) (cleaned up).
Accordingly, the Court concludes that Amendment 18 violates the MSA because it does not set catch limits that will rebuild the Pacific sardine population within the statutory timeframe.
3. Claim 3: Failure to Prevent Overfishing
Oceana claims that Amendment 18 will not prevent overfishing, as required by the MSA. Dkt. No. 51 ¶¶ 156-161. Specifically, Oceana argues that the formula NMFS used to calculate EMSY for the Pacific sardine, which is based on a set of ocean temperature measurements made by the California Cooperative Oceanic Fisheries Investigations (“CalCOFI”), is scientifically unsound and overstates the stock's productivity. Dkt. No. 43 at 18-20. According to Oceana, NMFS's use of the CalCOFI data produces artificially high OFLs that do not reliably indicate when overfishing has occurred. Dkt. No. 45 at 19.
Defendants respond that while the current methodology for calculating EMSY is imperfect, NMFS's estimates are nevertheless based on the best scientific information available. See Dkt. No. 44 at 24; Dkt. No. 54 at 2. They acknowledge that “the SSC has recommended additional investigation” into the use of the CalCOFI data to estimate EMSY, but defendants maintain that the SSC “has not . . . found that evidence sufficient to recommend a change for this fishing year.” Dkt. No. 54 at 2 (emphasis in original).
As noted above, overfishing refers to a rate of fishing mortality “that jeopardizes the capacity of a fishery to produce the maximum sustainable yield on a continuing basis.” 16 U.S.C. § 1802(34). “The overfishing limit is the numerical instantiation of this concept”-i.e. catch levels above the limit constitute overfishing. Oceana v. Coggins, 606 F.Supp.3d 920, 933 (N.D. Cal. 2022). EMSY is the maximum rate of fishing that can occur over time without causing overfishing. Id.; 50 C.F.R. § 600.310(e)(1)(i). Like all aspects of an FMP, OFLs must be determined using the best available science. 16 U.S.C. § 1851(a)(1).
Oceana's critique of NMFS's use of the CalCOFI data finds support in the administrative record. In April of 2021, during the process of setting the 2021-2022 annual specifications, both the Council's SSC and the Coastal Pelagic Species Management Team, noted serious concerns regarding the EMSY estimates calculated from the CalCOFI data. The SSC stated: “There are several urgent research priorities to consider revisiting to better inform the next benchmark assessment. The SSC strongly recommends that these issues be addressed in time for the next benchmark assessment.... The value for EMSY based on the CalCOFI temperature index suggests a productive stock but this is not evident from recent assessments, suggesting the need to reevaluate the best way to calculate EMSY for the northern subpopulation sardine stock.” AR S-1618. The Management Team stated: “The CPSMT recommends evaluation of the EMSY term based on the [CalCOFI] temperature index because it no longer appears to adequately reflect sardine productivity.... This environmental proxy was designed to reflect stock productivity, yet it has been near that upper cap for the last five years, while the most recent benchmark assessment stated that actual recruitments have been some of the lowest on record during that same time period.” AR S-498-99. When Oceana raised this issue in a comment on the proposed rebuilding plan that became Amendment 18 in June of 2021, NMFS responded that it was monitoring the situation, but that a change was not yet warranted. AR 4926-27 (“NMFS is aware of the scientific publications and ongoing Council discussions related to EMSY, and is committed to participating in these ongoing discussions about new science, and whether that new science justifies a change for how EMSY is calculated for management purposes.... If a change is determined to be necessary, NMFS will promulgate a new action that will go through the proper Council process and will include public input during the Council process and during NMFS'[s] subsequent rulemaking process.”).
Despite the acknowledged flaws in this methodology, when NMFS calculated EMSY for use in the 2023-2024 annual specifications, it continued to rely on the CalCOFI data. Dkt. No. 53-2 at 60. Defendants point out that the SSC approved the use of this data. Id. at 60. However, the SSC's own comments reflect its continued concerns about NMFS's use of this data, including its recommendations that something be done to address the concerns: “The SSC noted last year that since this [harvest control rule] was revised in 2013, the temperature has suggested an EMSY close to the upper end of the recommended range, despite evidence for low productivity and abundance since that time. The SSC recommends that a workshop be convened to revisit the analysis and assumptions that have been used to inform the NSP Pacific sardine [harvest control rule], as there continues to be evidence that the adopted relationship between sardine productivity and ocean temperatures is not currently valid.” Id. at 60-61. So far, NMFS has not taken the recommended action.
The question presented is whether, in setting an overfishing limit in Amendment 18, NMFS relied on the best available science. Oceana does not propose a specific alternative to NMFS's use of the CalCOFI data to calculate EMSY; instead, it argues that NMFS should set limits that do not rely exclusively on EMSY. Dkt. No. 55 at 2. The Court agrees. While the agency has a statutory obligation to “assess and specify the present and probable future condition of, and the maximum sustainable yield . . . from the fishery,” 16 U.S.C. § 1853(a)(3), neither the MSA nor its implementing regulations require the agency to adopt, without adjustment, the results of its EMSY calculation as the overfishing limit. See 50 C.F.R. § 600.310(e)(2) (guidelines for setting “status determination criteria” for overfishing). Rather, the MSA requires NMFS to “specify objective and measurable criteria for identifying when the fishery to which the plan applies is overfished (with an analysis of how the criteria were determined and the relationship of the criteria to the reproductive potential of stocks of fish in that fishery).” 16 U.S.C. § 1853 (a)(10); 50 C.F.R. § 600.310(e)(2).
The best available science demonstrates that the CalCOFI data does not yield a reliable measure of Pacific sardine productivity in existing or anticipated conditions. It is not that the scientific information is “uncertain” or has “gaps.” Rather, the record reflects that use of the CalCOFI temperature index to calculate EMSY consistently and materially overstates the productivity of the Pacific sardine. The SSC has expressed doubts about use of the CalCOFI data for several years and most recently describes the NMFS calculation that relies on that data as “not currently valid.” Dkt. No. 53-2 at 61. And while the SSC identified this issue as an “urgent research priorit[y]” in 2021, NMFS has made no changes to its EMSY formula. AR S-1618; Dkt. No. 53-2 at 60-61. The Court appreciates that developing a new EMSY model for the Pacific sardine is a time-consuming and resource-intensive endeavor, but there appears to be no reasonable justification for NMFS's continued reliance on an EMSY value without addressing, in any way, the unreliability of its methodology when setting the overfishing limit. See 50 C.F.R. § 600.315(a)(2) (“Scientific information that is used to inform decision making should include an evaluation of its uncertainty and identify gaps in the information. Management decisions should recognize the . . . risks associated with the sources of uncertainty and gaps in the scientific information.”). NMFS “cannot use insufficient evidence as an excuse” when “all of the evidence” before it indicates that its current methodology for calculating sardine EMSY produces directionally incorrect results. See Brower, 257 F.3d at 1071.
NMFS has failed to demonstrate that it relied on the best available science to set the overfishing limits and that Amendment 18 will prevent overfishing.
4. Claim 7: Essential Fish Habitats
Oceana contends that NMFS failed to consult as required regarding Amendment 18's adverse effects on essential fish habits (“EFHs”). Dkt. No. 1 ¶¶ 175-179; Dkt. No. 43 at 20-21. Defendants respond that NMFS determined Amendment 18 would have no adverse effects on EFHs, and thus no consultation was required. Dkt. No. 44 at 24-25; Dkt. No. 46 at 14; see also AR 4915.
The MSA requires that FMPs “minimize to the extent practicable adverse effects on [EFHs] caused by fishing.” 16 U.S.C. § 1853(a)(7). This mandate applies to FMP amendments and extends to EFHs designated under other FMPs. 50 C.F.R. § 600.815(a)(2)(ii). “Adverse effect” means “any impact that reduces quality and/or quantity of EFH” and includes “individual, cumulative, or synergistic consequences of actions.” 50 C.F.R. § 600.810(a). “[A]ctions that reduce the availability of a major prey species . . . may be considered adverse effects on EFH.” 50 C.F.R. § 600.815(a)(7). In addressing adverse effects, an agency may apply its “expertise and discretion in determining how best to manage fishery resources.” Conservation Law Found. v. Ross, 374 F.Supp.3d 77, 91 (D.D.C. 2019) (quoting Conservation Law Found. v. Evans, 360 F.3d 21, 28 (1st Cir. 2004)). NMFS need not adopt measures to minimize effects on EFHs when the available scientific evidence suggests no such measures are required or that sufficient measures are already in place. See Am. Oceans Campaign v. Daley, 183 F.Supp.2d 1, 13 (D.D.C. 2000); Friends of Del Norte v. Cal. Dep't of Transp., No. 18-CV-00129-JD, 2023 WL 2351649, at *11 (N.D. Cal. Mar. 3, 2023).
The MSA also requires federal agencies to consult with NMFS “with respect to any action authorized, funded, or undertaken, or proposed to be authorized, funded, or undertaken” that may “adversely affect” an EFH. 16 U.S.C. § 1855(b)(2); 50 C.F.R. § 600.920. The consultation requirement applies to NMFS, as a federal agency, thereby requiring NMFS to consult with itself regarding any action within the scope of the requirement. See AR 5432; cf. Turtle Island Restoration Network v. NMFS, 340 F.3d 969, 974 (9th Cir. 2003) (noting that NMFS “must consult within its own agency” to fulfil the Endangered Species Act's consultation requirement). When consulting on an action that may adversely affect EFHs, NMFS must provide an assessment that includes an “analysis of the potential adverse effects of the action on EFH and the managed species” as well as “alternatives that could avoid or minimize adverse effects on EFH.” 50 C.F.R. § 600.920(e)(3) (ii), (iv). Consultation under the MSA may be consolidated and coordinated with other review procedures, such as those required by NEPA. 50 C.F.R. § 600.920(f)(1).
Oceana argues that NMFS was required to consult with respect to the impact of Amendment 18 on EFHs but failed to do so. Dkt. No. 43 at 21. Oceana's premise is that Amendment 18, and the annual specifications implementing it, “will keep sardines at low levels for the foreseeable future,” which may adversely affect EFHs for marine predators, like groundfish, tuna, sharks, and salmon, that rely on the Pacific sardine as a key food source. Dkt. No. 45 at 20. Defendants respond that because Amendment 18 and the annual specifications rely on existing management measures for the Pacific sardine, including application of the harvest guidelines and closure of the primary directed commercial fishery, the amendment creates no new fishing pressures and therefore no additional anticipated impacts to EFH. Dkt. No. 44 at 25; Dkt. No. 46 at 14; see also AR 4915, 4929. In addition, defendants point to the results of an EFH consultation in 2013 on which they continue to rely. Dkt. No. 44 at 25; AR 5432. Oceana objects that the 2013 consultation “addresses a single year of fishery removals from a sardine population that was an order of magnitude larger than it is now,” and addresses circumstances that are not at all comparable to the FMP implemented by Amendment 18 and the annual specifications. Dkt. No. 43 at 21.
In determining that adoption of Amendment 18 did not require consultation, NMFS reasoned that because the primary directed fishery would remain closed for the foreseeable future and other existing management measures would remain in place, Amendment 18 would have no new or different adverse impacts on EFHs. See AR 4915-16 (“This action maintains the closure of the primary directed fishery for Pacific sardine; therefore, [NMFS has] determined that this action would have no adverse impact on any areas identified as EFH for U.S. fisheries[.]”). NMFS relied on similar reasoning when it found that the 2023-2024 annual specifications would not adversely impact EFHs. Dkt. No. 53-2 at 21 (“Because this proposed action is prohibiting fishing by the primary directed fishery for sardine, there is no affected area. As such, the proposed action in this context will not have an adverse impact on EFH; therefore, an EFH consultation is not required.”). The rebuilding plan discusses the fact that Pacific sardine are important forage for marine predators, while observing that most such predators are generalists that also rely on other forage species, including some that are presently abundant and likely to be so in the future. AR 24-25; see also 4919-20. The agency also specifically considered that, under the amendment, fishing would remain at minimal levels, as required by the MSA, due to closure of the primary directed commercial fishery, and noted the scientific uncertainty regarding the extent to which fishing impacts natural sardine population fluctuations. AR 12-13, 4915, 4924, 4929. NMFS's assessment that sufficient measures were in place to minimize fishing and protect EFHs because Amendment 18 and the annual specifications implemented existing constraints is rationally connected to the evidence in the record and consistent with the statutory and regulatory requirements.
The Court agrees with Oceana that to the extent defendants rely on the 2013 EFH consultation, their reliance is not supported by the record. No one disputes that fishery conditions in 2013 differed from fishery conditions at the time Amendment 18 was adopted, and there is no indication in the record that the findings reflected in the 2013 memorandum have any relevant bearing on the circumstances presented by Amendment 18. See AR 5432.
In sum, NMFS's determination that Amendment 18 and its annual specifications required no EFH consultation was not arbitrary and capricious, as NMFS did consider whether Amendment 18 may adversely affect EFH and the agency's conclusion that it would not is rationally connected to the factors it considered.
5. Claim 8: 2023-2024 Annual Specifications
In its amended complaint, Oceana challenges NMFS's 2023-2024 annual specifications for the Pacific sardine. Dkt. No. 51 ¶¶ 187-191. These specifications “set annual catch levels for the Pacific sardine fishery based on the annual specifications framework, control rules, and management measures in the FMP.” Dkt. No. 53-2; 88 Fed.Reg. 41,040, 41,041. Oceana argues that the annual specifications fail to rebuild the sardine population and fail to prevent overfishing. Dkt. No. 51 ¶¶ 187-191. As discussed above, the annual specifications implement Amendment 18 and provide Oceana with a vehicle to challenge it. See Oregon Trollers, 452 F.3d at 1115-16. And, as explained above, the Court concludes that NMFS has set a rebuilding target that does not violate the MSA, but that it has failed to demonstrate that the rebuilding plan will rebuild the sardine population in the statutory timeframe and that the plan will prevent overfishing. These conclusions apply equally to Oceana's challenges to the annual specifications in claim 8.
C. NEPA Claims
Oceana claims that NMFS's approval of Amendment 18 violated NEPA in three ways: (1) it failed to analyze the impacts of the authorized action (claim 4); (2) it failed to take a hard look at the plan's impacts on the sardine population and marine predators (claim 5); and (3) it failed to prepare an environmental impact statement (claim 6). Dkt. No. 51 ¶¶ 162-181.
1. Claim 4: Action Analyzed Based on Incorrect Assumptions
Oceana contends that NMFS's environmental assessment (“EA”) failed to analyze the impacts of the actions Amendment 18 authorizes because the agency assumed that only 2,200 mt of sardine would be caught each year under Alternative 1, rather than the higher amount permitted under the plan's ABC or ACLs. Dkt. No. 51 ¶¶ 162-166. Like Oceana's challenge to NMFS's rebuilding plan in claim 2, this challenge relies principally on the agency's assumption that the full ACLs would not be caught under Alternative 1. See Dkt. No. 43 at 22-25. Oceana argues that NMFS applied this assumption inconsistently in its environmental analysis, preventing both the agency and the public from making an informed assessment of the alternative plans. Id. Defendants disagree, arguing that it was reasonable for NMFS to consider what Alternative 1's actual effects would be. Dkt. No. 44 at 26-27.
When reviewing a proposed action, an agency must take a “hard look” at all foreseeable impacts and “may not rely on incorrect assumptions or data.” Env't Def. Ctr. v. Bureau of Ocean Energy Mgmt., 36 F.4th 850, 872 (9th Cir. 2022) (quoting Native Ecosystems Council v. U.S. Forest Serv., 418 F.3d 953, 964 (9th Cir. 2005)); see also 40 C.F.R. § 1502.23 (“Agencies shall ensure the professional integrity, including scientific integrity, of the discussions and analyses in environmental documents.”). The agency's EA must “provide [a] full and fair discussion of significant environmental impacts and inform decisionmakers and the public of the reasonable alternatives which would avoid or minimize adverse impacts or enhance the quality of the human environment.” Klamath-Siskiyou Wildlands Ctr. v. Bureau of Land Mgmt., 387 F.3d 989, 993 (9th Cir. 2004) (quoting 40 C.F.R. § 1502.1) (cleaned up). If the agency “entirely fail[s] to consider an important aspect of the problem,” then its actions are arbitrary and capricious. Idaho Sporting Cong., Inc. v. Rittenhouse, 305 F.3d 957, 973 (9th Cir. 2002) (quoting State Farm, 463 U.S. at 43).
The Court agrees with Oceana that NMFS's analysis of how Alternative 1 compares to the other two alternatives relied on flawed assumptions and therefore was arbitrary and capricious. As explained above, ACLs play a significant role in the MSA regulatory framework, most notably in requiring NMFS and the Council to ensure the catch limits are not exceeded. NMFS cited the “flexibility” to increase harvests if future conditions allowed as a reason to adopt Alternative 1. AR 22. However, it did not consider the effect that such increases, whether intentional or accidental, would have on rebuilding. NMFS's justification for modeling Alternative 1 based on the assumption that annual catch would average 2,200 mt was that it “represent[ed] a more realistic projection of fishery landings” given “the prohibition on primary directed fishing, restrictions on incidental harvest, and to some degree market dynamics.” AR 14. NMFS acknowledged that the same circumstances also could lead to catches below the ACL under Alternative 3, but it made no attempt to adjust for or model this possibility. AR 15, 26. In effect, NMFS compared apples and oranges: predictions of future catches, which had no binding effect, for Alternative 1; and binding ACLs, which might overestimate catch, for Alternative 3.
Defendants point out that the EA made no attempt to mask how NMFS conducted its assessment of the relevant alternative. Dkt. No. 44 at 28 (citing AR 15, 30). However, merely noting a potential issue or discrepancy is not sufficient for the “hard look” required by NEPA. Blue Mountains Biodiversity Project v. Blackwood, 161 F.3d 1208, 1213 (9th Cir. 1998) (“General 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.”). Here, NMFS made no attempt to quantify the differences between its alternative rebuilding plans, beyond observing that “[t]he modeling [for Alternative 3] also does not account for restrictions on incidental catch that might restrict harvest, or the fact that industry may not take the full five percent for other socioeconomic reasons.” AR 15.
NMFS acted arbitrarily and capriciously and failed to take the hard look required by NEPA by relying on inconsistent assumptions and by ignoring important aspects of the proposed rebuilding plans under consideration. See State Farm, 463 U.S. at 43; Env't Def. Ctr., 36 F.4th at 872.
2. Claim 5: Impact on Marine Predators
Oceana contends that defendants also failed to take a hard look at the impact that Alternative 1 would have on the marine predators that rely on the Pacific sardine for food, including specifically the endangered humpback whale. Dkt. No. 43 at 28-30. Defendants respond that the EA concisely noted the sardine's importance to many of these species, consistent with NEPA's requirements. Dkt. No. 44 at 28-29 (citing 40 C.F.R. §§ 1501.5(c)(1)-(2) (“An environmental assessment shall briefly [discuss various factors.]”), 1508.1(h) (“Environmental assessment means a concise public document. . . “)); AR 24. They also argue that the EA acknowledged the possibility of effects on other predators, but concluded that these effects would not be materially different under the other alternatives. Dkt. No. 44 at 28-29.
“To satisfy the ‘hard look' requirement, an agency must provide ‘a reasonably thorough discussion of the significant aspects of the probable environmental consequences.'” 350 Montana v. Haaland, 50 F.4th 1254, 1265 (9th Cir. 2022) (quoting Ctr. for Biological Diversity v. Nat'l Highway Traffic Safety Admin. (“NHTSA”), 538 F.3d 1172, 1194 (9th Cir. 2008)). “A ‘hard look' includes considering all foreseeable direct and indirect impacts [and] should involve a discussion of adverse impacts that does not improperly minimize negative side effects.” N. Alaska Env't Ctr. v. Kempthorne, 457 F.3d 969, 975 (9th Cir. 2006). The agency must also consider reasonably foreseeable cumulative effects of the proposed action, see 40 C.F.R. § 1508.1(g)(2)-(3), and must provide a convincing statement of reasons explaining why the proposed action will have no significant impact on the environment, see Ocean Advocs. v. U.S. Army Corps of Eng'rs, 402 F.3d 846, 865 (9th Cir. 2005). Among the factors agencies are directed to consider in this analysis are the effects on “listed species and designated critical habitat under the Endangered Species Act.” 40 C.F.R. § 1501.3(b).
When reviewing an agency decision to determine whether the hard look standard is met, courts must “employ a ‘rule of reason,'” rather than “fly speck” the agency's analysis or “act[] as a type of omnipotent scientist.” Audubon Soc'y of Portland v. Haaland, 40 F.4th 967, 984 (9th Cir. 2022) (cleaned up). The agency need not affirmatively address every uncertainty-although it must “acknowledge and respond to comments by outside parties that raise significant scientific uncertainties and reasonably support that such uncertainties exist.” The Lands Council v. McNair, 537 F.3d 981, 1001 (9th Cir. 2008). If the agency's decision is “fully informed and well-considered,” then the court must defer to it. N. Alaska Env't Ctr, 457 F.3d at 975.
The record reflects that NMFS did consider the reasonably foreseeable impacts of the proposed alternatives on marine predators generally, including how those impacts would likely be mitigated by the availability of other forage fish species. The agency explained:
[M]ost Pacific sardine predators are generalists that are not dependent on the availability of a single species but rather on a suite of species, any one (or more) of which is likely to be abundant each year. For example, while the biomass of Pacific sardine is currently low, the central population of northern anchovy biomass is high (approximately 800,000 mt in 2019 . . .). Therefore, it is unclear whether there would be any measurable difference in benefits between the rebuilding timelines for Pacific sardine from the aspect of prey availability.
AR 25. For the reasons explained above, see III.B.1, the Court disagrees with Oceana's characterization of Amendment 18 as an action that “keeps” the sardine population at a biomass of 150,000 mt, and further disagrees that NMFS failed to analyze how the rebuilding target and other aspects of the rebuilding plan impact marine predators. See Dkt. No. 43 at 28.
However, Oceana also argues that NMFS failed to consider how Amendment 18 and its annual specifications may impact the endangered humpback whale and its critical habitat, contrary to NEPA regulations. Dkt. No. 51 ¶¶ 10, 121-22; Dkt. No. 43 at 29; see also 50 C.F.R. § 226.227(f); 86 Fed.Reg. 21,082, 21,084 (listing the Pacific sardine among “species that have been recognized and documented as key prey species within the diet of humpback whales”). Oceana specifically raised this issue in public comments submitted in response to NMFS's draft and final rebuilding plans. See AR 148, 5290-91. Defendants' response is limited to the observation that the EA “acknowledged that endangered humpback whales are part of the assemblage of predators that use NSP sardine.” Dkt. No. 44 at 29 (citing AR 24).
NMFS's decision materials refer to “prior ESA consultations on the Pacific sardine fishery.” See AR 159, 4929. However, neither party raised these consultations in their briefs, nor do they appear to be a part of the administrative record.
To comply with NEPA, NMFS need only have “sufficiently considered the issue and arrived at a reasonable conclusion that the effects would not be significant.” WildEarth Guardians v. Provencio, 923 F.3d 655, 675 (9th Cir. 2019). However, neither the EA nor any other environmental document discusses whether or how Amendment 18 may impact the humpback whale's critical habitat. See AR 1-43 (EA), 158-63 (finding of no significant impact), 4910-30 (NMFS decision memorandum). The agency's mere acknowledgment of the humpback whale's endangered status is not enough to satisfy NEPA's “hard look” requirement. See Klamath-Siskiyou Wildlands Ctr., 387 F.3d at 997 (EAs that failed to discuss impact of timber sales on northern spotted owl's critical habitat “[did] not satisfy the requirements of the NEPA”).
Accordingly, while the NMFS prepared an adequate EA regarding the impact of Amendment 18 and its implementing annual specifications on marine predators generally, it failed to take a hard look at the impact on the endangered humpback whale, as required by NEPA. See 40 C.F.R. § 1501.3(b).
3. Claim 6: Failure to Prepare an Environmental Impact Statement
Oceana claims that NMFS violated NEPA by failing to prepare an EIS. Dkt. No. 51 ¶¶ 173-172; Dkt. No. 43 at 30. Defendants disagree that an EIS was required. Dkt. No. 44 at 2930.
A reviewing court must examine an EA “with two purposes in mind: to determine whether it has adequately considered and elaborated the possible consequences of the proposed agency action when concluding that it will have no significant impact on the environment, and whether its determination that no EIS is required is a reasonable conclusion.” Env't Def. Ctr., 36 F.4th at 872 (quoting Ctr. for Biological Diversity v. NHTSA, 538 F.3d at 1215). “An EIS must be prepared if substantial questions are raised as to whether a project may cause significant degradation of some human environmental factor.” Ocean Advocs., 402 F.3d at 864 (cleaned up, emphasis in original). If an agency opts not to prepare one, it must give a “convincing statement of reasons” why the project's environmental impact will not be significant. Id. (quoting Blue Mountains Biodiversity Project, 161 F.3d at 1212). “[C]onclusory assertions that an activity will have only an insignificant impact on the environment” are insufficient. Id. However, “it does not follow that the presence of some negative effects necessarily rises to the level of demonstrating a significant effect on the environment.” Barnes v. Fed. Aviation Admin., 865 F.3d 1266, 1275 (9th Cir. 2017) (quoting Native Ecosystems Council v. U.S. Forest Serv., 428 F.3d 1233, 1240 (9th Cir. 2005)).
“[P]reparation of an EIS is not mandated in all cases simply because an agency has prepared a deficient EA or otherwise failed to comply with NEPA.” Ctr. for Biological Diversity v. NHTSA, 538 F.3d at 1225. If an “EA [is] prepared in reliance” on an erroneous legal conclusion, remand to the agency for the preparation of a new EA may be proper. San Luis Obispo Mothers for Peace v. Nuclear Regul. Comm'n, 449 F.3d 1016, 1035 (9th Cir. 2006); Ctr. for Biological Diversity v. NHTSA, 538 F.3d at 1225.
As described above, NMFS violated NEPA by relying on inconsistent assumptions and failing to take a hard look at the impact of Amendment 18 and the annual specifications on the endangered humpback whale. Because of these errors, the EA was deficient. However, the significance of these deficiencies, and whether they can be remedied, is unclear. As such, “the record is insufficiently complete for [the Court] to order the immediate preparation of an EIS.” Ctr. for Biological Diversity v. NHTSA, 538 F.3d at 1227.
IV. REMEDY
Oceana asks the Court to vacate Amendment 18 and the 2023-2024 annual specifications and remand to NMFS with instructions to promulgate a new rebuilding plan within nine months, as well as regulations implementing it. Dkt. No. 43 at 30; Dkt. No. 55 at 3. Defendants claim that “nine months is not sufficient time to comply with the requirements of the MSA” and requests the opportunity to submit briefing on the question of remedy. Dkt. No. 44 at 30. They also assert that if the 2023-2024 annual specifications are vacated “all the limitations placed on the fishery would be lifted and the management measures would no longer control catch levels.” Dkt. No. 54 at 1.
Where agency action is found to be arbitrary and capricious or not in accordance with the law, a court typically vacates the decision or action and remands to the agency for further proceedings. 350 Montana, 50 F.4th at 1273; Earth Island Institute v. Hogarth, 494 F.3d at 770. However, remand without vacatur is proper in “limited circumstances.” 350 Montana, 50 F.4th at 1273 (quoting Pollinator Stewardship Council v. EPA, 806 F.3d 520, 532 (9th Cir. 2015)). “Whether agency action should be vacated depends on how serious the agency's errors are and the disruptive consequences of an interim change that may itself be changed.” Id. (quoting Nat'l Family Farm Coal. v. EPA, 966 F.3d 893, 929 (9th Cir. 2020)). The Ninth Circuit considers “whether vacating a faulty rule could result in possible environmental harm” and has “chosen to leave a rule in place when vacating would risk such harm.” Pollinator Stewardship Council, 806 F.3d at 532; see also All. for the Wild Rockies v. U.S. Forest Serv., 907 F.3d 1105, 1121 (9th Cir. 2018) (“When equity demands, however, the regulation can be left in place while the agency reconsiders or replaces the action, or to give the agency time to follow the necessary procedures.”).
Given defendants' representations regarding the possible effect of an order vacating Amendment 18 and/or the annual specifications, the Court declines to issue such an order at this time. Instead, the parties must confer regarding what further proceedings are necessary to resolve the question of an appropriate remedy.
V. CONCLUSION
The parties' cross-motions for summary judgment are granted in part and denied in part, as follows:
1. On claim 1 (unlawful rebuilding target under the MSA), defendants' motion is granted and Oceana's cross-motion is denied.
2. On claim 2 (failure to rebuild within statutory timeframe under the MSA), Oceana's motion is granted and defendants' cross-motion is denied.
3. On claim 3 (failure to prevent overfishing under the MSA), Oceana's motion is granted and defendants' cross-motion is denied.
4. On claim 7 (failure to analyze and minimize adverse effects on EFHs under the MSA), Oceana's motion is denied and defendants' cross-motion is granted.
5. On claim 8 (challenge to 2023-2024 annual specifications under the MSA), Oceana's motion is granted and defendants' cross-motion is denied.
6. On claim 4 (incorrect assumptions in environmental analysis under NEPA), Oceana's motion is granted and defendants' cross-motion is denied.
7. On claim 5 (failure to take a hard look at impacts on marine predators under NEPA), Oceana's motion is granted and defendants' cross-motion is denied with respect to Oceana's claim that NMFS failed to consider Amendment 18's effects on the humpback whale's critical habitat. In all other respects, defendants' motion is granted and Oceana's cross-motion is denied.
8. On claim 6 (failure to prepare an EIS under NEPA), Oceana's motion is granted and defendants' cross-motion is denied with respect to Oceana's claim that the EA was deficient. However, defendants' motion is granted and Oceana's cross-motion is denied with respect to Oceana's claim that an EIS is required.
By May 6, 2024, the parties shall jointly submit their agreed or respective proposals for further proceedings regarding the question of an appropriate remedy.
IT IS SO ORDERED.