OREGON ENVIRONMENTAL COUNCIL, Citizens for the Safe Control
of the Gypsy Moth, Elaine Olsen and Glen Olsen,
Plaintiffs-Appellants,
and
Friends of the Earth; National Coalition Against the Misuse
of Pesticides, Plaintiffs/Intervenors-Appellants,
v.
Leonard KUNZMAN, Director, State of Oregon, Department of
Agriculture, State of Oregon, Department of Agriculture,
United States Department of Agriculture, John R. Block,
Secretary, United States Department of Agriculture, et al.,
Defendants-Appellees,
and
Oregonians for Food and Shelter, Inc., Defendant/Intervenor-Appellee.
Nos. 85-4266, 85-4308 and 86-3779.
United States Court of Appeals,
Ninth Circuit.
Argued and Submitted Sept. 4, 1986.
Decided May 12, 1987.
Michael Axline and John E. Bonine, Eugene, Or., and Larry Sokol, Portland, Or., for plaintiffs-appellants.
Ralph A. Bradley, Eugene, Or., for plaintiffs/intervenors-appellants.
Dorothy R. Burakreis, Peter R. Steenland, Jr., and Albert M. Ferlo, Jr., F. Henry Habicht, II, Dirk D. Snel, Washington, D.C., for defendants-appellees.
John DiLorenzo, Jr., and Brendan Stocklin-Enright, Portland, Or., for defendant/intervenor-appellee.
Appeal from the United States District Court for the District of Oregon.
Before WRIGHT, GOODWIN and NELSON, Circuit Judges.
NELSON, Circuit Judge:
In these consolidated appeals, we review (1) a ruling that an environmental impact statement ("EIS") for an insecticide spraying program to combat infestations of gypsy moths satisfies the National Environmental Policy Act of 1969 ("NEPA"), 42 U.S.C. Sec. 4332(C) (1982), and its implementing regulations, 40 C.F.R. Secs. 1500-1508 (1986), and (2) the denial of attorneys' fees under the Equal Access to Justice Act ("EAJA"), 28 U.S.C. Sec. 2412(d)(1)(A) (Supp.III 1985), for certain parts of this litigation. We affirm on the adequacy of the EIS. On the attorneys' fees issues, we affirm in part and vacate and remand in part.
I. PROCEDURAL BACKGROUND
This litigation commenced in 1982, when Oregon Environmental Council, Citizens for the Safe Control of the Gypsy Moth, and two Oregon residents (collectively "OEC") brought suit to enjoin various state and federal officials, including the U.S. Secretary of Agriculture ("the Secretary"), from performing or authorizing aerial spraying of carbaryl, a chemical insecticide, in a federally assisted state program to eradicate gypsy moths in a populated, residential area of South Salem, Oregon. OEC challenged the adequacy of a Programmatic Environmental Impact Statement ("the 1982 PEIS") that had been developed for spraying in forested areas of the northeastern United States and a three-page environmental assessment ("EA") describing the South Salem spraying program. The litigation progressed in four phases.
Phase I ended in 1983, when the Ninth Circuit held that the 1982 PEIS and EA did not satisfy NEPA's requirements for the South Salem spraying program. Oregon Environmental Council v. Kunzman,
Phase II began in March 1984 with the issuance of a new EIS ("the 1984 EIS"), which OEC challenged on numerous grounds. Two national environmental organizations, Friends of the Earth and the National Coalition Against the Misuse of Pesticides (collectively "FOE"), filed a complaint in intervention. Trial was scheduled for September 25, 1984, and a pretrial conference was set for August 31, 1984. On August 20, 1984, the federal defendants withdrew the contested 1984 EIS in order to supplement it. Because no final agency action then existed, the court dismissed OEC's challenge to the 1984 EIS, but granted its request for injunctive relief based on the Secretary's representation that no action would be taken until the EIS was supplemented. The court again retained jurisdiction to review the sufficiency of a final EIS.
Phase III commenced in March 1985 with the issuance of the final EIS, as supplemented ("the 1985 EIS"), which OEC and FOE again challenged. This EIS recommended "integrated pest management" to control gypsy moths, a program that permitted the use of chemical and/or biological insecticides. After trial, the district court found that the main text of the 1985 EIS was legally adequate, but that the worst case analysis in Appendix F violated 40 C.F.R. Sec. 1502.8, which requires that an EIS be written in "plain language." The court enjoined the use of carbaryl and three other chemical insecticides (trichlorfon, acephate, and diflubenzuron) in Oregon effective immediately and on a nationwide basis effective January 1, 1986. Oregon Environmental Council v. Kunzman,
OEC and FOE sought attorneys' fees under the EAJA for their work in Phases II and III. On October 4, 1985, the district court denied fees for both phases, holding that in Phase II the plaintiffs were not "prevailing parties" under the EAJA and that in Phase III, although the plaintiffs were prevailing parties, the government's position was "substantially justified." OEC and FOE both appealed (Nos. 85-4266, 85-4308).
Phase IV began in early 1986 with the issuance of an addendum to the 1985 EIS ("the 1986 Addendum"), which included a "plain language version" of the worst case analysis. In April 1986, the district court found that the worst case analysis met the readability and other requirements, and lifted the injunction. Oregon Environmental Council v. Kunzman,
II. THE 1985 EIS AND THE 1986 ADDENDUM
A few words are in order on the documents that are the focal point of the latest round of this strenuously and well litigated controversy. The 1985 EIS includes an 8-page summary, a 78-page main text, lists of preparers and 145 references, an index, and a glossary defining 90 terms. Eight appendices include EPA reports on N-nitrosocarbaryl and carbaryl; data on the history of gypsy moth eradication; comments on the draft documents and responses; a 134-page worst case analysis (Appendix F); a 43-page "plain language version" of Appendix F (Appendix H); and further information on Appendices F and H (Appendix I).
The EIS's statement of purpose and need for action describes the history of the gypsy moth in the United States and the attempts to control it. The gypsy moth, Lymantria dispar L., native to Europe, Asia, and Africa, was accidentally released in Massachusetts in 1869. From 1889, when an outbreak of gypsy moth larvae first threatened severe tree defoliation, until the late 1950s, state and federal agencies used a variety of compounds, including dichloro-diphenyl-trichloroethane (DDT), to control infestations in New England. With the phasing out of DDT in the 1960s and 1970s, new compounds were developed--carbaryl, trichlorfon, acephate, and diflubenzuron. Almost two million pounds of carbaryl were used in gypsy moth programs in the northeastern United States between 1962 and 1977.
Despite these efforts, the gypsy moth spread to the mid-Atlantic states by the 1970s and has appeared as far south as South Carolina, in certain mid-western states, and in California and Oregon. The EIS reports that gypsy moths defoliated 11,955,486 acres between 1924 and 1969, 11,640,705 acres between 1970 and 1979, and 29,425,328 acres between 1980 and 1984. It estimates that, as of 1980, economic losses to home owners, forest industries, and recreation areas have totaled $272 million.
The EIS evaluates four alternatives for the gypsy moth problem: (1) no action, (2) the four chemical insecticides, (3) the biological insecticide Bacillus thuringiensis, to which appellants do not object, and (4) the selected alternative, integrated pest management, which permits the use of both chemical and biological insecticides. The EIS identifies mitigating measures and the affected environment--tree species susceptible to gypsy moths, nontarget organisms that the insecticides would affect,1 and geographical areas. The analysis of the environmental consequences concludes that realistic dose levels (and certain worst case dose exposures) for the four chemical insecticides are below the acceptable daily intake level and estimates that certain worst case risks of human cancer and heritable mutations range from the order of 1 in 100,000,000 to the order of 1 in 1,000,000. The highest worst case cancer risk (for acephate) is on the order of 1 in 100,000.
The 1985 EIS and 1986 Addendum have the outward indicia of comprehensiveness. See 40 C.F.R. Sec. 1502.10 (1986) (setting forth EIS format). At trial several witnesses testified to the thoroughness of the documents; one stated that he had "never seen a greater effort made to identify all possible avenues of exposure and all reasonably possible exposure contingencies." If the EIS is inadequate, it is not for lack of substantial effort on the part of its preparers. Yet OEC and FOE assign numerous errors in this lengthy document. We address their principal arguments.
III. JURISDICTION IN THE DISTRICT COURT
As a preliminary matter the Secretary argues that, because the State of Oregon has indicated an intention to forgo the use of chemical insecticides, OEC lacks standing. We disagree. The plaintiffs alleged numerous violations of NEPA's procedural requirements. See Trustees for Alaska v. Hodel,
The Secretary argues that to allow anyone to bring an action to enforce compliance with NEPA would allow even individuals in states without gypsy moths to bring this action. This case does not present such a situation. In Coleman, we held that a plaintiff had standing to challenge the failure to prepare an EIS if he has "a sufficient geographical nexus to the site of the challenged project that he may be expected to suffer whatever environmental consequences the project may have." Id. at 671. In this case, OEC's members reside in a state with an actual gypsy moth problem and thus may challenge a nationwide EIS that is applicable to them.
This analysis comports with the traditional requirements for standing. Injury sufficient to meet the standing requirement may be actual or threatened, Heckler v. Mathews,
IV. SUBSTANTIVE CHALLENGES
The purpose of NEPA is to ensure that federal agencies are fully aware of the impact of their decisions on the environment. Friends of Endangered Species, Inc. v. Jantzen,
A. Standard of Review
NEPA is essentially a procedural statute. Trustees for Alaska,
This circuit employs a "rule of reason" that asks whether an EIS contains a " 'reasonably thorough discussion of the significant aspects of the probable environmental consequences.' " Id. (quoting Trout Unlimited v. Morton,
Appellants argue that the district court applied an erroneous standard of review when it characterized its task as one of determining "whether the agency made a 'good faith effort' to take environmental concerns into account." OEC III,
We review findings of fact underlying the district court's decision for clear error. Northwest Indian Cemetery,
B. The Readability or Understandability Requirement
In order to achieve the purpose of informing decisionmakers and the public of potential environmental consequences of a proposed agency action, the CEQ regulations require:
Environmental impact statements shall be written in plain language and may use appropriate graphics so that decisionmakers and the public can readily understand them. Agencies should employ writers of clear prose or editors to write, review, or edit statements, which will be based upon the analysis and supporting data from the natural and social sciences and the environmental design arts.
40 C.F.R. Sec. 1502.8 (1986); see also id. Sec. 1500.2(b) (stating that an EIS "shall be concise, clear, and to the point"); id. Sec. 1502.1 (same); id. Sec. 1502.2(a) (stating that an EIS "shall be analytic rather than encyclopedic"); id. Sec. 1500.4(e) ("clear format"); id. Sec. 1502.10 ("clear presentation"). Appellants argue that neither the main text of the 1985 EIS nor the worst case analysis in the 1986 Addendum meets this requirement.
This circuit has not defined the level of readability that Sec. 1502.8 requires. The district court stated that an EIS "must translate technical data into terms that render it an effective disclosure of the environmental impacts of a proposed project to all of its intended readership." OEC II,
We hold that Sec. 1502.8 imposes a requirement that an EIS must be organized and written so as to be readily understandable by governmental decisionmakers and by interested non-professional laypersons likely to be affected by actions taken under the EIS. The main text of an EIS will routinely include some scientific data and reasoning necessary to apprise decisionmakers and the public of potential environmental consequences. The more complicated the science underlying those consequences is, the more challenging the preparer's task will be to convey the information clearly. Overly technical material and supporting data, however, should ordinarily appear in appendices. See 40 C.F.R. Sec. 1502.18 (1986).
In this inquiry, we adhere to the general principle that the reviewing court must make a pragmatic judgment as to the adequacy of an EIS. If so inclined, the parties may introduce evidence concerning the reading level of the affected public and expert testimony on any indicia of the inherent readability of an EIS, as was done in this case. See OEC III,
We have reviewed the evidence and read the 1985 EIS. The district court's reasons for finding the main text of the 1985 EIS readable are given in OEC II,
The worst case analysis in the 1986 Addendum presents an additional question. We agree with the district court that the readability requirement of Sec. 1502.8 applies to the worst case analysis. When required, a worst case analysis is central to a full understanding of potential environmental impacts of proposed agency action. Clearly conveying that information to decisionmakers and to the public is as important as the identification of known adverse environmental impacts. As noted above, an EIS may include appendices to provide technical material that supports or amplifies a worst case analysis for the benefit of specialists, see 40 C.F.R. Secs. 1502.18, 1502.24 (1986), and such supplemental technical material may be exempt from the readability requirement. But an agency may not circumvent its obligation to provide a clear assessment of environmental impacts simply by placing a worst case analysis in an appendix.
As with the main text of the 1985 EIS, the district court's finding on the readability of the worst case analysis in Appendix H is not clearly erroneous. The district court's reasoning amply supports its conclusion. See OEC III,
C. Use of a Worst Case Analysis
The CEQ regulations provide that an EIS must include a worst case analysis when an agency is faced with incomplete or unavailable information. 40 C.F.R. Sec. 1502.22 (1985).4 The regulation thus "requires disclosure and analysis of the 'cost[s] of uncertainty--i.e., the costs of proceeding without more and better information.' " Southern Oregon Citizens Against Toxic Sprays, Inc. v. Clark,
The 1985 EIS justified its decision to forgo additional independent research and to prepare a worst case analysis principally on the ground that the costs would be exorbitant.5 It cites estimates ranging from tens of thousands to hundreds of thousands of dollars per study for each of several dozen studies that might be carried out. The EIS also indicates that completion of such studies would require several years, thus implicitly recognizing the harm to the environment that might be caused by infestations of gypsy moths during that period without chemical insecticides. The EIS, however, explains only that "[b]ecause of the cost and time involved, a worst case analysis was done."
Appellants correctly point out that the EIS does not explicitly evaluate the cost of the studies "in light of the size of the project and/or the possible harm to the environment." A more thorough EIS might well have done so. We believe, however, that the EIS implicitly embodies such a calculus. Despite some evidence introduced by appellants that indicated that the costs of research might be somewhat lower, we believe that the district court did not clearly err in finding that the costs were in fact exorbitant. The omission of an explicit exposition of the agency's determination of exorbitance does not warrant deeming this EIS legally inadequate. To do so in this case would impermissibly "fly speck" the EIS.6
D. Other NEPA Claims
Appellants charge that the EIS and worst case analysis are insufficient under NEPA on numerous other grounds. These challenges principally fall in two categories: (1) the EIS does not adequately disclose the cumulative effects associated with the program, and (2) the EIS manipulates and ignores data to conceal health risks.
We have considered the numerous contentions. Many concern the use of particular scientific methodologies, decisions to rely on certain scientific studies instead of others, and the use and application of Acceptable Daily Intake (ADI) and No Observable Effect Levels (NOELs) in various risk assessments. We are convinced that the district court's treatment of these challenges is sufficient and does not warrant restating here. See OEC III,
E. Conclusion on the Merits
Although we have noted a few areas in which the 1985 EIS and 1986 Addendum might have been improved, we hold that under the "rule of reason" these documents contain a "reasonably thorough discussion of the significant aspects of the probable environmental consequences." Trout Unlimited,
V. ATTORNEYS' FEES
The EAJA provides that a court shall award attorneys' fees to a "prevailing party" in a civil action brought against the United States unless the government's position was "substantially justified" or "special circumstances make an award unjust." 28 U.S.C. Sec. 2412(d)(1)(A) (Supp. III 1985). We review a decision denying attorneys' fees under the EAJA for abuse of discretion. Merrell v. Block,
A. Phase II: "Prevailing Party"
Appellants contend that the district court erred in holding that they were not prevailing parties in Phase II, which witnessed the Secretary's withdrawal of the 1984 EIS several weeks prior to the scheduled trial. In its request for fees, appellants argued that "but for" its challenge, the 1984 EIS would not have been withdrawn and supplemented. The government countered that it withdrew the 1984 EIS because of "the availability of new information from various sources." The district court concluded:
I find that although this litigation certainly had some effect on the government's decision to supplement the 1984 EIS, it was not the cause for the supplementation. The government drafted a document it thought complied with NEPA standards. Thereafter, it received information from various sources outlining the deficiencies of the document and it then withdrew that EIS in order to correct those shortcomings. Thus, I find that plaintiffs are not prevailing parties for this portion of the litigation, and decline to award them attorney's fees for phase II.
A party need not obtain formal relief on the merits to be deemed a prevailing party. McQuiston I,
The efforts of prevailing parties have been labelled variously as "at least a 'contributing ... factor' in the bringing about of [the desired] procedural changes," although not the "sole cause", as a "material factor in bringing about the defendant's action", and as contributing "in a significant way."
American Constitutional Party,
The district court seems to have applied a legal standard that required a higher degree of causation, perhaps because of the way in which the appellants initially framed their position. Its decision does not discuss the appropriate legal standard of whether the litigation was a "material factor" or played a "catalytic role" in the Secretary's action. Cf. McQuiston II,
Although it appears that the district court most likely did not apply the material factor/catalytic role test, we pretermit our discussion of this issue. Even if we were to conclude that the appellants were prevailing parties, we would have to remand to determine whether the government's position on the adequacy of the 1984 EIS was substantially justified. See Lummi Indian Tribe,
B. Phase III: "Substantially Justified"
The district court held that the appellants were prevailing parties in Phase III because the worst case analysis in Appendix F did not satisfy the readability requirement. It denied attorneys' fees, however, on the ground that the government's position was substantially justified. The district court must consider the totality of the circumstances present prior to and during litigation. Hill,
This court has long applied a test of reasonableness in determining whether the government's position was substantially justified. League of Women Voters v. FCC,
Several courts have held correctly that "substantial justification" means more than merely reasonable. Because in 1980 Congress rejected a standard of "reasonably justified" in favor of "substantially justified," the test must be more than mere reasonableness.
H.R.Rep. No. 120, 99th Cong., 1st Sess. 9, reprinted in 1985 U.S. Code Cong. & Admin. News 132, 138 (footnote omitted); see also Spencer v. NLRB,
The district court stated that the defendant's position on the adequacy of the worst case analysis was substantially justified because "no court had previously invalidated an EIS on the[ ] grounds" that it did not satisfy Sec. 1502.8. We do not affirm on this broad ground. Although the absence of adverse precedent on an issue is relevant to the determination of the "substantially justified" question, it is not dispositive. Hill,
We find merit in a narrower position. We do not decide whether the Secretary's position that Sec. 1502.8 did not apply to a worst case analysis was substantially justified. Cf. SOCATS,
CONCLUSION
The appeal on the merits in No. 86-3779 is affirmed. The appeal on the attorneys' fees in Nos. 85-4266 and 85-4308 is affirmed in part and vacated and remanded in part. The parties shall bear their own costs on this appeal.
AFFIRMED IN PART, VACATED AND REMANDED IN PART.
Notes
The EIS states that carbaryl is toxic to honeybees, some aquatic insects, and shellfish; that trichlorfon is toxic to flies; that acephate is toxic to honeybees; and that diflubenzuron is toxic to some aquatic organisms. It further states that the expected doses of these pesticides should not adversely affect fish, wildlife, livestock, or domestic animals
Members of the nationally based Friends of the Earth and the National Coalition Against the Misuse of Pesticides reside in states in which chemical spraying has been proposed or conducted
The text of the EIS did not, as appellants suggest, exceed the length limitations. See 40 C.F.R. Sec. 1502.7 (1986)
The applicable regulation provides in pertinent part:
When an agency is evaluating significant adverse effects on the human environment in an environmental impact statement and there are gaps in relevant information or scientific uncertainty, the agency shall always make clear that such information is lacking or that uncertainty exists.
(a) If the information relevant to adverse impacts is essential to a reasoned choice among alternatives and is not known and the overall costs of obtaining it are not exorbitant, the agency shall include the information in the environmental impact statement.
C.F.R. Sec. 1502.22(a) (1985) (amended 1986)
At trial, the Secretary justified forgoing research on one issue, the risks from heritable human mutations, as beyond the state of the art. Appellants do not contest this assertion
Appellants also argue that the failure to list the source of the information on the costs of such studies (a personal communication with an employee of Dow Chemical) violated 40 C.F.R. Sec. 1502.21 (1986), which provides that an EIS may not incorporate material "unless it is reasonably available for inspection by potentially interested persons within the time allowed for comment." In the face of the comprehensiveness of the EIS, however, we believe that the omission is a "fly speck."
Counsel for the government conceded at oral argument that the government was "not oblivious" to the litigation and that, in view of several recent adverse decisions on herbicide spraying in this court, the government was being "cautious."
