EDWARD J. LODGE, District Judge.
On July 2, 2010, 731 F.Supp.2d 1028, 2010 WL 3172662, United States Magistrate Judge Ronald E. Bush issued his Report and Recommendation in this matter. (Dkt. 51.) Pursuant to 28 U.S.C. § 636(b)(1), the parties had ten days in which to file written objections to the Report and Recommendation. Defendants Jane Cottrell, Ranotta McNair and the United States Forest Service ("Defendants") filed their objections on July 19, 2010. (Dkt. 52.) Lands Council filed its response to the objections on July 24, 2010. (Dkt. 53.) The applicable federal rules, local rules and statutes do not provide for a reply to be filed.
Pursuant to 28 U.S.C. § 636(b)(1)(C) this Court "may accept, reject, or modify, in whole or in part, the findings and recommendations made by the magistrate judge." Moreover, this Court "shall make a de novo determination of those portions of the report which objection is made." Id. In United States v. Reyna-Tapia, 328 F.3d 1114, 1121 (9th cir.2003) the court interpreted the requirements of 28 U.S.C. 636(b)(1)(C):
See also Wang v. Masaitis, 416 F.3d 992, 1000 & n. 12 (9th Cir.2005). Based on the objections filed in this case, the Court has conducted a de novo review of the record pursuant to 28 U.S.C. § 636(b).
The Court adopts and incorporates by reference the factual background as set forth in the Report and Recommendation, 731 F.Supp.2d at 1032-35,:
This is a civil action seeking review of a decision by the United States Forest service
Plaintiff, the Lands Council, is a nonprofit corporation dedicated to the long-term community and biological stability of the Greater Columbia river Ecosystem. Id. at ¶ 15. Plaintiff's members and staff use and enjoy the IPNF, including the area in which the Project will take place. Id. at ¶ 10. Defendants include: (1) Jane Cottrell, Acting Regional Forester for the Northern Region of the Forest Service; (2) Ranotta K. McNair, the Forest Supervisor for the IPNF; and (3) the USFS, an administrative agency within the Department of Agriculture (collectively referred to hereinafter as "Forest Service") entrusted with management of the national forests.
The Bussel 484 Project Area is located within the Bussel Creek Watershed, a tributary of Marble Creek, and is located eight miles northeast of Clarkia, Idaho, Shoshone County in the IPNF. (AR 3:1). The Project Area covers 14,646 acres, 83% of which is Forest Service land. Id. The remaining 2,454 acres are privately owned. Id.
The Project Area is composed of subalpine fir, spruce, western red cedar, western hemlock, and grand fir forests located entirely within the IPNF's Old Growth Management Unit ("OGMU") Eight. See Second Amended Complaint, ¶ 29 (Docket No. 17); (AR 2:163). Both parties agree that the quality of old growth habitat in the Project Area has degraded over time due to fire and past logging activity. (AR 2:147-48); See First Amended Complaint, ¶¶ 29-34 (Docket No. 17).
From the outset, beginning in August 2003, the Forest Service involved interest groups, individuals, tribes, and agencies in the development of the Project. (AR 3:30, 2:7).
In April 2005, the Forest Service issued a scoping notice and also published in the Federal Register a notice of intent to prepare an environmental impact statement. (AR 3:30, AR 2:7). After several years of work, study, and collaboration, a draft environmental impact statement ("DEIS"), was made available for public comment on the IPNF website on February 21, 2008. (AR 3:30, AR 144). A related Notice of Availability appeared in the Federal Register on March 7, 2008. (AR 3:30, AR 156).
The DEIS identifies three possible alternative actions in the Project Area: Alternative A: no action, Alternative B: proposed logging and related road construction activities, and Alternative C: logging with no road construction. (AR 1:3). In May 2008, the Forest Service issued a final environmental impact statement
Modified Alternative B involves the harvest of approximately 2,137 acres using a variety of silvicultural prescriptions (1,486 acres of commercial thin, 521 acres of group shelterwood, 53 acres of seedtree, and 78 acres of clearcut with reserves). (AR 3:5). The ROD indicates that Alternative B was selected, in part, because "it best meets the need to improve vegetative conditions through reducing stand density, changing species composition, and promoting larger trees in the future." (AR 3:27). By reducing stand density, the Forest Service intends to "decrease the competition for water, nutrients, and sunlight in stands and promote increased growth and yield." (AR 3:27). The goal is to remove the smaller trees and focus growth on the larger diameter, more vigorous trees. (AR 3:28).
To facilitate the harvest activities, Modified Alternative B also involves road construction. The road activity authorized by the Project includes: (1) constructing 4.5 miles of system road and .5 miles of temporary road; (2) improving or reconstructing 5.4 miles of existing road; and (3) removing 10.7 miles of existing roads and placing 20.2 miles of existing roads into "long term storage."
The ROD provides that the Project will not harvest any timber or construct any roads within old growth stands. (AR 3:14, 45). However, it is undisputed that the Project will have an effect on the habitat of old growth dependent species. The FEIS states that the Project will eliminate the following habitat: (1) one of eight home ranges modeled for the pileated woodpecker (AR 2:272); (2) three of 19 nesting stands modeled for the goshawk (AR 2:275); (3) 100 acres of habitat modeled for the threatened Canada lynx (AR 2:279); (4) and 256 acres of habitat modeled for the fisher and marten (AR 2:288). Nevertheless, evaluating the over-all impact of the Project on wildlife habitat, the Forest Service determined that the Project would not contribute towards federal listing or loss of viability for any of the wildlife species in the Project Area. (AR 2:292).
With regard to cumulative impacts, both the DEIS and FEIS identify "fire and fuels" as having an environmental effect on the Project Area. (AR 1:82-88), (AR 2:129-42). The DEIS analyzes the effect of fire under the general direction of Forest Plan. (AR 1:82). The FEIS analyzes the effect of fire under the now-withdrawn forest-wide, 2008 IPNF Fire Management Plan ("2008 Fire Plan"). (AR 129). Consistent with the 2008 Fire Plan, the logging aspect of the Project is intended to mimic the effects of fires of low to moderate intensity. (AR 2:141-42, AR 3:39-40). However, fire itself will be suppressed throughout the Project Area. (AR 2:61) ("Consistent with current policy, efforts will be made to suppress all fires which occur in the project area.").
Plaintiff filed an administrative appeal of the decision approving Modified Alternative B, and the Forest Service denied the
Plaintiff also asserts claims related to a proposed action, the 2008 Fire Plan. On March 18, 2008, the Forest Service implemented a Fire Plan for the IPNF. (AR 1037). At one time, Plaintiff claimed that approval of the 2008 Fire Plan violated NEPA and the Endangered Species Act. First Amended Complaint (Docket No 11). However, when the Forest Service later withdrew the 2008 Fire Plan, Plaintiff withdrew these claims. See Docket No. 16. Nonetheless, Plaintiff continues to contend that the Project EIS is flawed, in part, because the analysis of the cumulative environmental impacts of fire and fire management is based on the implementation of the now-withdrawn 2008 Fire Plan. Second Amended Complaint (Docket No. 17).
Two timber sales authorized as part of the Project, the Bussel Peak and Tole Booth sales, have been awarded. Plaintiff represents that logging activity in the Project area may begin as soon as August 1, 2010.
The Court adopts and incorporates by reference the standard of review as set forth in the Report and Recommendation, 731 F.Supp.2d at 1035-36,:
The APA provides the authority for judicial review of agency decisions under NFMA and NEPA. Pit River Tribe v. U.S. Forest Serv., 469 F.3d 768, 778 (9th Cir.2006). The APA states, in relevant part, that a review court "shall . . . hold unlawful and set aside agency action, findings, and conclusions found to be—arbitrary, capricious, an abuse of discretion, or otherwise not in accordance with law." 5 U.S.C. § 706(2)(A). The arbitrary and capricious standard is deferential and an agency will be reversed as arbitrary and capricious "only if the agency relied on factors Congress did not intend it to consider, entirely failed to consider an important aspect of the problem, offered an explanation 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." Ecology Ctr. v. Castaneda, 574 F.3d 652, 656 (9th Cir.2009) (quotations and citations omitted).
Nevertheless, the Court must review the administrative action to ensure that the agency has "examine[d] the relevant data and articulate[d] a satisfactory explanation for its action including a `rational connection between the facts found and the choice made.'" Motor Vehicle Mfrs. Ass'n v. State Farm Mut. Auto. Ins. Co., 463 U.S. 29, 43, 103 S.Ct. 2856, 77 L.Ed.2d 443 (1983) (quoting Burlington Truck Lines v. United States, 371 U.S. 156, 168, 83 S.Ct. 239, 9 L.Ed.2d 207
The Defendants' argue that Lands Council's action is not ripe for the Court's adjudication. In their objection the Defendants rely primarily on Ohio Forestry Ass'n, Inc. v. Sierra Club, 523 U.S. 726, 118 S.Ct. 1665, 140 L.Ed.2d 921 (1998). In Ohio Forestry the plaintiffs challenged the adoption of logging standards in the forest plan. Id. at 730, 118 S.Ct. 1665. The Supreme Court held that this challenge was not ripe because no projects based on those logging standards had yet been contemplated, the forest plan itself did not authorize the cutting of any trees. Id. at 733-34, 118 S.Ct. 1665. The Defendants argue that the current case is analogous because Lands Council is challenging Forest Plan old growth standards and the species at issue do not exclusively use old growth stands. (Defs.' Obj. at 4.) Unlike Ohio Forestry, however, the present case deals with an actual plan to cut trees. This plan necessarily implicates the Forest Plan's old growth standards, even if Lands Council is not challenging the project on the basis that those standards will not be met. (Report and Recommendation, 731 F.Supp.2d at 1036.) The old growth standards are at issue "because the Forest Service relied upon the old growth standards as a proxy to ensure that it is meeting the species viability and monitoring requirements." Id. at 10. Therefore, given that the decisionmaker has issued its final decision, Lands Council's action is properly before the Court.
Defendants argue that Lands Council's action is collaterally estopped based on Lands Council v. McNair, No. 06-00425-EJL, slip op. at 26-28, 2009 WL 3199641 (D.Idaho Sept. 30, 2009). The Defendants argue that the exact same issues were present in that case and that they were resolved in favor of the Forest Service. (Defs.' Obj. at 4.) The current challenge, however, is in a different area of the forest and presents issues unique to that area. The Ninth Circuit has held that a claim should not be collaterally estopped from proceeding where different timber stands located in different management areas of the same forest with their own unique factual circumstances are at issue. Idaho Sporting Congress, Inc. v. Rittenhouse, 305 F.3d 957, 965 (9th Cir.2002). The Court adopts the Report and Recommendation's analysis that because different project areas are involved with different characteristics, collateral estoppel does not apply. (Report and Recommendation, 731 F.Supp.2d at 1037-38.)
The Forest Service has elected to meet the standard for the maintenance of viable wildlife populations in the project area through a proxy-on-proxy approach. The Forest Plan requires that the Forest Service maintain Management Indicator Species ("MIS") within the area. (AR 942: II-5). This itself is a proxy, the viability of the MIS standing in for the viability of all species in the Project Area. The Forest Service reasons that these MIS are more susceptible to management activities like logging and road building than most species, and so if the impact of the activity on
Directly monitoring the population of the MIS is more difficult than evaluating the status of the MIS' habitat. The Ninth Circuit has consistently held that a second proxy, a proxy for a proxy, may be employed to determine the impact on the MIS. Gifford Pinchot Task Force v. U.S. Fish and Wildlife Serv., 378 F.3d 1059, 1066 (9th Cir.2004); accord Native Ecosystems Council v. U.S. Forest Serv., 428 F.3d 1233, 1250 (9th Cir.2005) (holding that habitat-as-proxy is appropriate "only where both the Forest Service's knowledge of what quality and quantity of habitat is necessary to support the species and the Forest Service's method of measuring the existing amount of that habitat are reasonably reliable and accurate."). In this case the Forest Service chose to evaluate the impact of its proposed activities in the Project Area through the habitat of the MIS in order to determine the impact that the activities would have on the MIS itself. (AR 2: 249). The Forest Service's logic is that if it can properly evaluate the impact of its proposed action on the MIS' habitat, it will be able to effectively determine the impact of the action on the MIS, which will allow it to in turn evaluate the proposed action's impact on species viability as a whole.
An exception to the general validity of the proxy-on-proxy approach is where the existence of a given MIS cannot be confirmed within the proposed project area. While a habitat proxy is allowed, it must be evaluated to determine whether "it `reasonably insures' that the proxy results mirror reality." Gifford Pinchot Task Force, 378 F.3d at 1066 (quoting Idaho Sporting Cong., Inc. v. Rittenhouse, 305 F.3d 957, 972-73 (9th Cir.2002)). In Native Ecosystems Council v. Tidwell, 599 F.3d 926 (9th Cir.2010) the Ninth Circuit addressed a situation where the Forest Service attempted to use habitat as a proxy to determine the impact of its proposed action on an MIS that was absent from the project area. Id. at 933. The Ninth Circuit ultimately rejected the Forest Service's proposed project and held that "[t]he proxy-on-proxy approach's reliability is questionable when the MIS is absent from the project area." Id. at 933. What the Ninth Circuit noted was a missing link in the logical chain that would normally support the use of proxy-on-proxy. Without evidence of the existence of MIS in the project area it becomes a black box, the Forest Service is unable to determine the impact of its proposed action on the viability of the species in that area and the MIS itself.
In their objection to the Report and Recommendation's reliance on NEC the Defendants argue that the Ninth Circuit's earlier en banc decision, Lands Council v. McNair, 537 F.3d 981 (9th Cir.2008), should control in this case. (Defs.' Obj. to Report and Recommendation at 6, Dkt. 52.) The Ninth Circuit took that case en banc in order "to clarify some of our environmental jurisprudence with respect to our review of the actions of the United States Forest Service." McNair, 537 F.3d at 984. In that case, the plaintiffs challenged a Forest Service action in the IPNF on the basis that its scientific analysis of the effects of its action on the MIS flammulated owl and its habitat. Id. at 994. The main thrust of the Ninth Circuit's decision was that when determining that a proposed action would have no impact on a given species "the Forest Service must support its conclusions that a project meets the requirements of the NFMA and the relevant Forest Plan with studies that the agency, in its expertise, deems reliable."
The Ninth Circuit's holding in NEC does not conflict with the en banc decision in McNair. NEC merely identified a situation where the normally valid proxy-on-proxy approach of measuring species viability would be arbitrary and capricious. The NEC outcome is perfectly consonant with the directive from McNair for the courts to defer to the Forest Service's science. Ultimately all that NEC recognizes is that the Forest Service's science speaks only for the propositions that it contains. The Ninth Circuit in NEC had no argument with the Forest Service's science which showed that the proposed action would not negatively impact the MIS, it noted that "there is simply no basis to evaluate the Forest Service's assertion that the sagebrush habitat is sufficient to sustain viable sage grouse populations when sage grouse cannot be found in the project area." NEC, 599 F.3d at 933. In other words, the Forest Service could show conclusively that sage grouse preferred a certain kind of habitat; but if this habitat was maintained and no sage grouse could be found, it could not logically rely on knowledge about what habitat sage grouse preferred to say that maintenance of that habitat guaranteed a viable population of sage grouse. The Ninth Circuit, then, only recognized an exception to the general rule that proxy-on-proxy is a permissible way to assess the impact of a proposed action on an MIS population. In order to qualify for this exception the MIS population must: (1) have trended downward in the area Id. at 930 and (2) be virtually non-existent in the project area. Id. at 933. Even if these two standards are met, the Forest Service might still be able to use proxy-on-proxy if it can demonstrate difficulties in monitoring the MIS. Id. at FN 9.
Because the Court has found that NEC is the controlling standard in the case, it must determine whether the factual elements in the administrative record are sufficient to show the population trend of the MIS and whether the particular MIS at issue are present in the project area. Depending on these factual findings the Court may then consider whether there are sufficient monitoring difficulties to warrant an exception to the NEC standard.
The purpose of assessing population trends is to determine whether habitat-as-proxy is actually successful at tracking the viability of a given species population. NEC, 599 F.3d at 935 ("In applying the proxy-on-proxy approach to evaluate whether the project complied with the Forest Service's duty to ensure wildlife diversity, the Forest Service did not adequately consider evidence that, despite the Forest Service's asserted compliance with the Connelly Guidelines, the sage grouse population continued to trend downward"). If the Forest Service can demonstrate, using the administrative record, that its reliance on habitat-as-proxy in its management decisions generated outcomes consistent with its expectation that maintaining habitat at certain levels
In order to show that the northern goshawk population is on an upward trend the Defendants point towards the Final Environment Impact Statement (FEIS). In turn, the study that the FEIS cites for its conclusion that the short-term viability of the northern goshawk is not at issue is Samson 2006. (AR 2:275) Samson 2006 is also cited by a letter outlining regional direction to foresters on how to evaluate northern goshawk habitat, a letter which the Defendants cite for the same proposition as the FEIS. (AR 494:1) However, Samson simply cannot be read to support any conclusions about population trends. Samson 2006 is similar to the Connolly Guidelines in NEC. It is a review of the best available literature on the availability of habitat, and from this literature gives foresters the tools to evaluate whether such habitat is present in the forest for the purposes of estimating population trends. (AR 901:5). In this sense, Samson is predictive only. It is true that Samson concludes that "[n]o scientific evidence exists that the northern goshawk is decreasing in numbers." Id. at 39. However, Samson 2006 is unable to show that northern goshawk populations are actually increasing and can conclude only that "[s]uppression of natural ecological processes has increased and continues to increase amounts of northern goshawk habitat." Id. at 40. While Samson 2006 appears to be the best available science for the estimation of habitat availability, in light of the Ninth Circuit's decision in NEC, this evidence cannot satisfy the Forest Service's burden to show that population trends are actually increasing.
The Forest Service does indicate that the northern goshawk had, at the time of the final decision, been removed from the sensitive species list. (AR 2:275; AR 494:2). While this would certainly seem to indicate a positive trend in population growth it is not reflected in the Forest Service's other analyses. In the 2003 IPNF Plan Monitoring and Evaluation Report, the northern goshawk's population trend is listed as "unknown." (AR 976:38).
The Defendants make the same citations for the pileated woodpecker as they do for the northern goshawk. The FEIS concludes that there is no evidence that the pileated woodpecker is decreasing in numbers, citing to Samson 2006. (AR 2:272). The Court has already discussed the limitations of the Samson 2006 study, which are just as applicable to the pileated woodpecker as to the northern goshawk. The 2003 report also notes that the population
Defendants cite to Ruggiero 1994 and Coffin et al 2002 to demonstrate that marten populations are increasing. Neither study, however, purports to document marten populations or even the extent of their habitat in the IPNF. Ruggiero 1994 is a general overview of the marten, its habitat and its research needs. (AR 896:7). Coffin et al 2002 is a study of the marten's natural range. (AR 565). Like the northern goshawk and the pileated woodpecker, the 2003 report notes that the population trend of the marten is "unknown". (AR 976:38). There is also no population estimate for 1998 or 2003. (AR 976:38). The Forest Service likewise cannot support its decision to use proxy-on-proxy with the evidence it has presented relating to the marten's population trends.
As a threshold matter Defendants contend that they are not required to determine the presence of the MIS, or indeed evaluate the viability of a species, within a given project area because the IPNF Forest Plan mandates that they "[m]aintain at least minimum viable populations of management indicator species distributed throughout the forest." (AR 942:II-28). Similar language appeared in the Forest Plan at issue in NEC. There the Forest Service instructed that "[v]iable populations of all existing wildlife species will be maintained by providing a diversity of habitats throughout the Forest." NEC, 599 F.3d at 932. Despite the same "throughout the forest" language, the Ninth Circuit nonetheless held that the Forest Service's duty to provide for viable populations required it to determine that an MIS was present in the given project area before it could use proxy-on-proxy. Id. at 933. It is difficult to imagine how the Forest Service could satisfy its burden under the NFMA if it was excused from all site specific analyses of a proposed project's impact, and no known court has ever held that the Forest Service is excused from assessing the impact of a proposed project on a project area.
The Court is cognizant of the fact that the Project Area is just one part of the much larger IPNF, and that its borders are drawn to suit human needs as opposed to a naturally occurring boundary that is a perfect snapshot of the forest as a whole. The Project Area cannot be viewed in complete isolation, nor can its uniqueness serve to completely sever it from the dynamic of the larger forest. Given the imperfect measuring methods available to the Forest Service and the indifference of wildlife to the need to be counted, the Court has struggled with the concept of "presence" as it is defined in NEC. That said, however, the NEC decision is not as rigid as the Defendants claim. The dissent's criticism that reduces the analysis area to the ranger's backyard is answered by the majority which holds that the Forest Service "must indeed analyze that particular site to determine the effects of the proposed action." Id. at 934 (emphasis in original). This does not say that there must be a certain number of species or certain signs in every area, simply that the Forest Service cannot divest itself of its duty to assess the impacts of its proposed actions by reducing the scale of the proposed project site. "Presence" for the purposes of an NEC analysis should be flexible enough not to unduly burden the
The Court also notes that in its reading of the limited holding of NEC that the Forest Service's burden to establish the presence of MIS in the Project Area may be mitigated if the Forest Service can demonstrate that its proxy-on-proxy method is viable. As noted above, evidence that habitat management throughout the forest has produced population trends consistent with what the Forest Service had hoped to achieve through its management decisions would indicate that the necessity of finding MIS in the specific project area is not great. However, if the Forest Service cannot demonstrate that its habitat management practices produce any known effect on species population, its burden to show that the MIS are in the Project Area in sufficient numbers to render habitat-as-proxy analysis meaningful is greater. In the present case the Forest Service is unable to demonstrate that it has any knowledge about the population trends of the MIS. In the 1993 monitoring report the population trends were unknown. (AR 949:33). Ten years later in 2003 the population trends were still unknown. (AR 976:38).
In NEC, the Ninth Circuit rejected a proposed action where the only evidence of actual MIS presence in the project area was a pair of sage grouse taken illegally from the site. Id. at 934. The Ninth Circuit was also not persuaded that a sage grouse lek eleven miles west of the project area could provide constructive presence within the project area itself. Id. at 930. Though the Ninth Circuit has not articulated a firm test for what constitutes "presence", the Court will use these benchmarks to evaluate the evidence offered by the Forest Service to prove that the MIS are within the Project Area.
In order to prove that northern goshawks are present in the Project Area the Forest Service points to the FEIS, which states that "goshawks are occasionally sighted within the wildlife analysis area." (AR 2:274).
The Defendants point out that the northern goshawk has a large range for the proposition that northern goshawk sightings near the Project Area can be deemed to be within the Project Area itself. (Defs.' Obj. at 10.) The Ninth Circuit rejected this very same argument in NEC. In that case, a lek eleven miles away from the project area, even given the wide ranging nature of the sage grouse, was not sufficient to establish that the MIS was present in the project area. NEC, 599 F.3d at 930. Given the scant evidence in the record the Forest Service has failed to show that northern goshawks are present in the Project Area such that the evaluation of the impact of their proposed action on northern goshawk habitat would satisfy the Forest Service's burden under the Forest Plan and the NFMA to ensure the viability of existing species.
The Defendants indicate that the FEIS concluded that the pileated woodpecker was present in the project area. (AR 2:269). The evidence for this presence is contained in two surveys conducted by the Forest Service. The first is the same 2008 survey conducted by Forester Ware that also sighted a pair of northern goshawks. (AR 504). In that survey, Forester Ware sighted a single pileated woodpecker in a stand of trees just outside the Project Area. The second survey was conducted in September of 2006. (AR 462). The forester in that survey identified a number of stands, and eleven of twenty eight of them had pileated woodpecker feeding signs. (Defs. Obj. at 10.) There is no indication in the record as to where these stands are, or how old the feeding signs were. The survey indicates that some signs are old, and some are not.
The Defendants have not carried their burden of demonstrating that the pileated woodpecker is present in the Project Area. Eleven feeding signs of unknown age and the sighting of a single bird rise to the same level of evidence as two actual sage grouse removed from the project area in NEC. This is confirmed by the 1993 and 2003 IPNF Plan Monitoring and Evaluation Reports. In 1993 the pileated woodpecker's population status was unknown and the Forest Service was implementing new methods to survey them. (AR 949:33). Ten years later, in 2003, the population estimate of pileated woodpeckers was unknown. (AR 976:38). Because the Forest Service cannot establish that pileated woodpeckers are present in the Project Area, it was arbitrary and capricious to rely on a habitat-as-proxy approach to determine the potential impact on the Project Area of its proposed action.
The Defendants reiterate the "constructive" presence argument that they raised to argue that the population of marten was not declining; that because marten are wide ranging animals and have been spotted within six miles of the analysis area they can be deemed to be present in the Project Area. (Defs.' Obj. at 10.) The Ninth Circuit in NEC rejected this argument when it did not allow evidence of a lek within eleven miles of the project area to establish the presence of the sage grouse. NEC, 599 F.3d at 930. Because the Forest Service cannot demonstrate that it has any knowledge of the population trend of the marten, it cannot rely on sightings outside the Project Area to establish that the decision to use habitat-as-proxy was not arbitrary and capricious.
The Defendants have failed to demonstrate, based on the evidence in the administrative record, that any of the relevant MIS were present in the Project Area at the time that the decisionmaker made their final decision. The lack of species sightings otherwise ignored and unexplained by the Forest Service undermines the assumption that by taking care of the habitat the IPNF can ensure species viability.
Once the Court has determined that the population trends for the MIS are unknown and that they are not present within the project area, it must assess whether monitoring difficulties exist that would justify the use of proxy-on-proxy as the best possible way to assess the impact of the proposed action. The Defendants cite Samson 2006 and other studies for the proposition that monitoring populations directly is difficult and time consuming. (Defs.' Obj. at 14.)
The limited nature of the Court's finding should be emphasized. The Court is not requiring, and NEC did not mandate, that the Forest Service maintain detailed population trends of MIS. Rather, McNair requires some population evidence sufficient to confirm that habitat-as-proxy results in the viability of MIS. All that NEC stands for, and all that the Court requires now, is that if the Forest Service chooses to rely on a proxy-on-proxy to satisfy its burden under the Forest Plan and NFMA, it must be able to demonstrate the presence of MIS within the project area. The Forest Service cannot evaluate the impact of its proposed action on the MIS' habitat when there is no evidence that the maintenance of that habitat in turn ensures a viable population of MIS as required by the Forest Plan. There is no evidence in the record that monitoring difficulties would preclude this limited finding. Indeed, in the 1993 IPNF Plan Monitoring and Evaluation Report the Forest Service laid out the plans that it would follow to assess the population of the MIS and did not at that time believe monitoring to be too difficult. (AR 949:33). Whether these efforts were too difficult is not for the Court to decide. However, if the Forest Service wishes to use proxy-on-proxy it must have the evidence to show that the method is valid for the proposed Project. Absent a showing of monitoring difficulties above those difficulties which are inherent in the monitoring of species in general, the Defendants should not qualify for the exception to the rule announced in NEC.
Defendants object to the Report and Recommendation's conclusion that they relied solely on habitat-as-proxy in making their decision. (Defs.' Obj. at 11.) Defendants argue that the Forest Service did not rely solely on old growth standards, and that this means that the Forest Service "did not rely only on the habitat as proxy approach in reaching its conclusions regarding population viability." Id. at 12. However, an examination of the methods that the Forest Service claims that it did use, show exactly that. For the pileated woodpecker the Forest Service used Samson 2006's conclusion that "there was an abundance of well-distributed pileated woodpecker nest site habitat [...] and habitat modeling to identify potentially suitable pileated woodpecker habitat and assess potential effects on the species." Id. at 11. For the northern goshawk the Forest Service "relied on the maintenance of suitable habitat and home ranges in the analysis area." Id. For the marten the Forest Service relied on "the percent of the area in mature/old forest structure (i.e. suitable habitat) in comparison with the management guidelines." Id. at 12. All of these approaches are habitat-as-proxy. The essence of habitat-as-proxy is that the Forest Service measures the effect of its actions on the MIS' habitat and uses that as a conclusion about the impact on the MIS itself. All of the methods raised in the Defendants' objection follow the same logic, and none are valid unless the MIS can be shown to be present within the Project Area.
Complete absence of old growth MIS in the Project Area renders implausible the assumption that the habitat-as-proxy approach satisfies the Forest Service's monitoring and viability requirements set forth in the Forest Plan. Stated another way, if the MIS is not present then the assumption
The Court recognizes that "NEPA was passed by Congress to protect the environment by requiring that federal agencies carefully weigh environmental considerations and consider potential alternatives to the proposed action before the government launches any major federal action." Lands Council v. Powell, 395 F.3d 1019, 1026 (9th Cir.2005) (Lands Council I). In addition, NEPA is a procedural statute and does not mandate any particular substantive results. Robertson v. Methow Valley Citizens Council, 490 U.S. 332, 350, 109 S.Ct. 1835, 104 L.Ed.2d 351 (1989). The Report and Recommendation found that the EIS violated NEPA because it contained an incomplete analysis of the project's impact on the viability of MIS. (Report and Recommendation, 731 F.Supp.2d at 1052.) Defendants object to this finding by arguing that there is no logical link in the Report and Recommendation between a substantive violation of the NFMA and a violation of NEPA. (Defs.' Obj. at 16.)
In order to comply with NEPA's requirement that the Forest Service be required to take a "hard look" at the proposed project's effects it "may not rely on incorrect assumptions or data in an EIS." Native Ecosystems Council v. USFS, 418 F.3d 953, 964 (9th Cir.2005) (citing 40 C.F.R. 1500.1(b)). Where, as here, the alleged violation of the NFMA pertains to the procedural requirements that the Forest Service must comply with in order to ensure the viability of species, a NEPA violation can be found based on a violation of the NFMA. Native Ecosystems Council v. Tidwell, 599 F.3d 926, 937 (9th Cir.2010) ("Just as the methodology applied by the Forest Service to measure habitat conditions did not meet the NFMA requirements, its flawed methodology in the complete absence of a sage grouse population does not constitute the requisite `hard look' mandated by NEPA.") (citing NEC, 418 F.3d at 964-65). The Forest Service failed to properly assess the impact of its proposed project on the viability of MIS in the project area, as mandated by the Forest Plan and the NFMA. As such, the EIS failed to "`inform [...] decisionmakers and the public of the reasonable alternatives which would avoid or minimize adverse impacts' on [management species]." NEC, 418 F.3d at 965 (citing Klamath-Siskiyou Wildlands Ctr. v. Bureau of Land Mgmt., 387 F.3d 989, 993 (9th Cir. 2004)). Therefore, the violation of the NFMA serves to establish a violation of NEPA.
The Report and Recommendation found that the when the Forest Service withdrew the present fire plan in favor of the 2008 Fire Plan this shift constituted a "significant new circumstance" which mandated a supplementary EIS to assess the impact of the shift. (Report and Recommendation, 731 F.Supp.2d at 1053-54..) Defendants object to this finding on the grounds that the shift did not result in any on the ground changes that would rise to the level of a significant new circumstance. (Defs.' Obj. at 18.) Specifically, Defendants argue that because both fire plans complied with the Forest Plan and other management
Defendants cite to Swanson v. USFS, 87 F.3d 339 (9th Cir.1996), to support their argument. In Swanson the plaintiff argued that a change in the chinook salmon's listing to a threatened species constituted a significant new circumstance that mandated a supplemental EIS. Id. at 344. Swanson, however, only dealt with a change in legal status and not a change in management plans and the Forest Service had already been required to determine whether the change in status required a change in management. Id. Therefore, Swanson is distinguishable and does not control the present case. The Court adopts the Report and Recommendation's analysis regarding the fire plan. The Court also adopts the Report and Recommendation's remedy, that "to the extent the Forest Service decides to move forward with this Project, any future analysis of the Project's environmental impact must address the cumulative impact of fire and fire management under whatever policy is in place at the time the environmental impact statement is drafted." (Report and Recommendation, 731 F.Supp.2d at 1054,.)
The Supreme Court has established the standard for permanent injunction:
eBay Inc. v. MercExchange, L.L.C., 547 U.S. 388, 391, 126 S.Ct. 1837, 164 L.Ed.2d 641 (2006). In its most recent case discussing the standard for permanent injunction in an environmental case the Supreme Court held that such an injunction is not the automatic remedy in cases where NEPA has been violated. Monsanto Co. v. Geertson Seed Farms, ___ U.S. ___, 130 S.Ct. 2743, 2756-57, 177 L.Ed.2d 461 (2010). Rather, the traditional four factor test must be evaluated to determine whether a permanent injunction is an appropriate remedy given the circumstances of the case. Id. Defendants object to the Report and Recommendation's conclusion that, based on these factors, the Forest Service's decision authorizing the project should be set aside and a permanent injunction issued prohibiting all current and future activity under the time sales. (Report and Recommendation, 731 F.Supp.2d at 1056.) The Court will asses these factors together in order to determine whether a permanent injunction is an appropriate remedy given the Court's finding that the Project violated both the NFMA and NEPA.
The nature of the injury which Lands Council claims will be suffered are environmental harms. By their very nature, environmental harms "can seldom be adequately remedied by money damages and [are] often permanent or at least of long duration, i.e., irreparable." Sierra Club v. Bosworth, 510 F.3d 1016, 1033 (9th Cir.2007) (quoting Amoco Prod. Co. v. Village of Gambell, 480 U.S. 531, 545, 107 S.Ct. 1396, 94 L.Ed.2d 542 (1987)). The Report and Recommendation found that
When determining whether a permanent injunction should issue the Court must weigh potential environment injury against other harms that will result from that injunction. Lands Council v. McNair, 537 F.3d 981, 1005 (9th Cir.2008). The Defendants claim that if the Project is enjoined, the local community will suffer economic hardships and significant management risks like fire danger, insect infestation, drought and disease will go unaddressed. (Defs.' Obj. at 19.) The Court recognizes that these are serious harms. The Court is particularly concerned that the state of the Project Area might continue to deteriorate if management actions are not taken. An injunction might frustrate the ultimate goal of species preservation if the Forest Service is prevented from implementing the Project. However, it would defeat the purpose of NEPA and the NFMA if the Forest Service could fail to adequately assess the impact of its proposed project on a project area and then claim that its actions would be necessary and beneficial to the health of the project area in order to defeat an injunction.
It is for this reason that the Court adopts the Report and Recommendation's position that the agency's decision should be vacated and a permanent injunction on all pending and awarded timber sales be issued. The Court does not foreclose the possibility that the very real economic harms suffered by local communities as a result of environmental litigation might overwhelm even a valid claim that the Forest Service did not follow procedures mandated by NEPA and the NFMA. Weinberger v. Romero-Barcelo, 456 U.S. 305, 313, 102 S.Ct. 1798, 72 L.Ed.2d 91 (1982) ("The grant of jurisdiction to ensure compliance with a statute hardly suggests an absolute duty to do so under any and all circumstances, and a federal judge sitting as chancellor is not mechanically obligated to grant an injunction for every violation of law.") In this case, however, failure to provide for an injunction would undermine the public's interest in ensuring that executive agencies follow the laws that govern their conduct. The NEPA and NFMA violations that the Court has found here are not mere technical deficiencies or oversights, they are failures of procedure that go to the heart of the Forest Service's mission to ensure the viability of species within the national forests.
For these reasons the Court finds that the Lands Council has satisfied its burden to show irreparable harm as a result of the proposed project. In addition these harms are not readily remedied by the tools available at law as they cannot be compensated by money. An equitable remedy is appropriate in this case due to the lack of remedy at law, and because the balance of harms when the public interest is properly considered against the harms alleged by
Lands Council's claim is ripe because it concerns old growth standards in the context of species viability and because the decisionmaker has issued its final decision. Lands Council's claims are not precluded because these claims concern a different project area than the one at issue in Lands Council v. McNair, No. 06-00425-EJL, slip op., 2009 WL 3199641 (D.Idaho Sept. 30, 2009). Because it is undisputed the Project will have a negative impact on the habitats of the pileated woodpecker, northern goshawk and marten, the lack of evidence that the other available habitats will protect MIS populations and keep them from decreasing is unknown. The Forest Service's decision to authorize the Project was arbitrary and capricious because its use of habitat-as-proxy to assess the impact of the Project on the viability of MIS populations was flawed. In the absence of evidence about MIS population trends and where no MIS can be located within the Project Area the Forest Service's reliance on habitat-as-proxy was arbitrary and capricious. Because of this finding the Forest Service's decision to authorize the Project is set aside and remanded to the agency. Whatever fire plan is in effect at the time of any new supplemental EIS must be evaluated in that EIS. A permanent injunction on all pending and approved timber sales for the Project Area is appropriate given the irreparable harm shown by Lands Council and is in the public interest.
1) The Report and Recommendation entered on July 02, 2010 (Dkt. No. 51) be
2) Plaintiff's Motion for Summary Judgment (Dkt. No. 24) be
3) Defendants' Motion for Summary Judgment (Dkt. No. 27) be
4) Plaintiff's Motion for Preliminary Injunction is
5) Counsel for Plaintiff is directed to provided the Court with a proposed Judgment consistent with this Amended Memorandum Order within five (5) days from this date.
