Sierra Club, Etc. v. Clayton K. Yeutter, Etc.

926 F.2d 429, 21 Envtl. L. Rep. (Envtl. Law Inst.) 20755, 1991 U.S. App. LEXIS 3522
CourtCourt of Appeals for the Fifth Circuit
DecidedMarch 4, 1991
Docket88-6041
StatusPublished
Cited by53 cases

This text of 926 F.2d 429 (Sierra Club, Etc. v. Clayton K. Yeutter, Etc.) is published on Counsel Stack Legal Research, covering Court of Appeals for the Fifth Circuit primary law. Counsel Stack provides free access to over 12 million legal documents including statutes, case law, regulations, and constitutions.

Bluebook
Sierra Club, Etc. v. Clayton K. Yeutter, Etc., 926 F.2d 429, 21 Envtl. L. Rep. (Envtl. Law Inst.) 20755, 1991 U.S. App. LEXIS 3522 (5th Cir. 1991).

Opinion

GARWOOD, Circuit Judge:

Defendants-appellants Clayton Yeutter, et al. (the government) appeal two injunc-tive orders of the district court in favor of plaintiff-appellees Sierra Club, et al.

Facts and Proceedings Below

This litigation concerns the red-cockaded woodpecker (RCW), a species of woodpecker that has garnered a position on the endangered species list, as provided by the Endangered Species Act of 1973 (ESA), 16 U.S.C. §§ 1531-43; see also 50 C.P.R. § 17.11 (1989) (listing endangered species). The RCW lives mainly in isolated areas of national forests in the southern regions of the United States, extending from Virginia to Florida and westward to East Texas. 1

The RCW nests and forages in several species of Southern pine trees, creating cavities in live trees that serve as nests. The resin flow in live pine trees that forms around the cavity opening provides the cavity a protective barrier against predators. Because older trees have softer wood as a result of age and, often, redheart disease and hence are easier to excavate, the bird prefers trees that range in age from roughly 60-120 years.

The survival of the species has long been at risk, coincident with the dwindling range of the coastal Southern pine forests and the destruction of the species’ natural habitat. Infestation of the Southern pine beetle has compounded the problem by denying the RCW old-growth pines. In fact, on April 17, 1985, the Sierra Club, Wilderness Society, and Texas Committee on Natural Resources (TCONR) filed this action originally to challenge the United States Forest Service’s (USFS) policy of cutting trees in Texas wilderness areas to control the pine beetle infestation. The plaintiffs alleged that the beetle-control-tree-cutting policy violated the Wilderness Act, 16 U.S.C. §§ 1131-36, as well as the ESA and the National Environmental Policy Act (NEPA), 42 U.S.C. §§ 4321-47. See Sierra Club v. Block, 614 F.Supp. 134 (E.D.Tex. 1985). Pending a trial on the merits, the court denied TCONR’s request to halt all timber cutting in East Texas national forests, but granted it limited relief. Id. at 139-41.

The nature of the litigation changed dramatically, however, in late 1987 when two United States Forest Service (USFS) scientists documented a dramatic forty to fifty percent decline in active RCW colonies in three of four national forests in Texas from 1983-87. As a result only 113 of the birds existed in Texas in 1987.

The USFS, an agency of the Department of Agriculture, manages the national forests and is authorized to sell timber to industry. The revenues raised help finance the agency and provide economic assistance to adjacent rural counties. Since 1964 the Forest Service has conducted “even-aged” harvesting of its lumber resources. Under this method, entire sections of forest are cut, on a rotational basis, and then allowed to regenerate for the next sixty to eighty years. Three alternative methods for achieving regeneration exist.

First, if an area has been clearcut, i.e., all the trees have been cut, it may be regenerated artificially by planting seeds or seedlings. Second, rather than clearcut an area, a few trees may be left to seed the area naturally. This is called seed-tree cutting. Finally, under the shelterwood cut method, an even greater density of trees, compared to the seed-tree cutting method, is left to provide regeneration. Under the latter two regeneration schemes, however, the salvaged trees are cut a few years later, in a second phase, to provide unimpeded growth for the new stand of trees. Consequently, the maximum tree age is determined by the rotational schedule for such lumbering. An alternative to even-aged harvesting is uneven-aged manage *432 ment or “selection” harvesting. Under this scheme, in contrast to even-aged management, an area will contain a mix of trees of different ages, as trees to be harvested are selected individually.

As a consequence of the RCW’s federal listing as an endangered species, under the ESA, the Secretary of the Interior, who operates through an agency of the Department, the United States Fish and Wildlife Service (USFWS), is charged with managing recovery of the species. See 16 U.S.C. § 1533(f). All federal agencies, including the USFS, must “consult” with the USFWS to ensure that agency action “is not likely to jeopardize the continued existence of any endangered species or threatened species or result in the destruction or adverse modification of the habitat of such species....” § 1536(a)(2). If the USFWS finds that the habitat is in jeopardy or subject to adverse modification, it “shall suggest those reasonable and prudent alternatives” to the federal agency to protect the listed species by issuing a “biological opinion.” See § 1536(b)(3)(A); 50 C.F.R. § 402.02 (1989). If new information becomes available pertaining to the harmful effects of previously approved agency action, the consultation process must be repeated with the USFWS. See 50 C.F.R. § 402.16 (1989).

The USFS published a wildlife management handbook in 1979 concerning silvicul-tural practices in relation to the RCW’s habitat. The handbook endorsed a two hundred foot buffer zone — to be free of pine tree cutting — for active RCW colonies, coupled with a hardwood management program. Beyond the buffer zone, even-aged logging could continue on a sixty to eighty year rotational cycle, depending on the species of pine tree. The USFWS recommended a longer rotational cycle, but otherwise endorsed the USFS’s RCW management handbook in a subsequent biological opinion. In 1984-85, the USFS again consulted with the USFWS concerning republication of the handbook for the RCW. On February 15, 1985, the USFWS issued a biological opinion approving the handbook. When the decline in the RCW population became publicly known in 1987, reconsultation between the USFS and the USFWS was interrupted when the TCONR filed an amended complaint in this case on October 22, 1987, alleging, among other things, that the USFS’s timber management practices harmed the RCW in violation of sections 7 and 9 of the ESA, 16 U.S.C. §§ 1536(a)(2), 1538(a)(1)(B). This amended complaint challenged the USFS’s general timber management and even-aged harvesting practices — not simply the beetle control cutting program, as had the original April 1985 complaint (although the amended complaint also included the earlier ESA and other attacks on the beetle control cutting) —as harmful to the RCW and thus in violation of the ESA. The TCONR at the same time sought a temporary restraining order halting all even-aged harvesting in the East Texas national forests, but the court denied this request.

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926 F.2d 429, 21 Envtl. L. Rep. (Envtl. Law Inst.) 20755, 1991 U.S. App. LEXIS 3522, Counsel Stack Legal Research, https://law.counselstack.com/opinion/sierra-club-etc-v-clayton-k-yeutter-etc-ca5-1991.