Western Watersheds Project v. U.S. Fish and Wildlife Service et al
MEMORANDUM DECISION AND ORDER denying 7 Motion for Preliminary Injunction; denying 43 Motion to Strike; denying 49 Motion to Strike. Signed by Judge B. Lynn Winmill. (caused to be mailed to non Registered Participants at the addresses listed on the Notice of Electronic Filing (NEF) by (cjm)
IN THE UNITED STATES DISTRICT COURT
FOR THE DISTRICT OF IDAHO
WESTERN WATERSHEDS PROJECT,
Case No. 4:13-CV-176-BLW
U.S. FISH AND WILDLIFE SERVICE and
U.S. FOREST SERVICE,
The Court has before it a motion for preliminary injunction filed by plaintiff
WWP. The Court heard oral argument on June 19, 2013, and took the motion under
advisement. For the reasons explained below, the Court will deny the motion.
WWP alleges that grazing in the Little Lost River watershed is harming bull trout,
a species listed as threatened under the Endangered Species Act (ESA). In its original
motion, WWP sought to enjoin grazing on two allotments in that watershed, contained
within the Salmon-Challis National Forest: (1) Mill Creek and (2) Pass Creek.
Later, WWP withdrew its request as to Mill Creek, relying on the Forest Service’s
representation that no grazing will be permitted on that allotment until the Fish &
Wildlife Service (FWS) issues a new Biological Opinion. Thus, the only allotment at
issue is the Pass Creek allotment.
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The Pass Creek allotment is governed by the Forest Service and lies on the
southwest side of the Little Lost River valley. It straddles the Lost River Range, with the
southern portion draining south into the Big Lost River watershed and the northern
portion draining into Wet Creek, which flows into the Little Lost River. Bull trout have
occupied both Wet and Big Creeks on the allotment, although they have not been
documented in Big Creek since 1998. The population in Wet Creek is small, with less
than 10 individuals observed in recent years.
In 2010, the Forest Service initiated consultation with the FWS over the impacts of
grazing on bull trout within the allotment. To start the process, the Forest Service
prepared a Biological Assessment for the FWS’s review.
At that time, the Forest Service was proposing to authorize grazing 1660 cow/calf
pairs between July 15 and October 10 on the allotment. After reviewing the poor
condition of much of the allotment, and the predicted impacts of maintaining the same
level of grazing as in the past, the Forest Service concluded in its BA that the proposed
grazing will “likely limit the ability of the habitat to support Bull Trout.”
The FWS reviewed the BA in light of its recovery plan designed to increase
populations of the bull trout. Bull trout need cold stream temperatures, clean water free
of sediment, plant growth along the bank to shade the water, and well-connected
migratory pathways. Recognizing regional variations in the bull trout recovery process,
the FWS has grouped different regions into Interim Recovery Units (IRU) for
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management purposes. The bull trout in this case are part of the Columbia River IRU,
which in turn is divided into 90 Core Areas. The bull trout in the Pass Creek allotment
are contained in the Little Lost River Core Area.
Within this Core Area, there are ten “local populations” all of which are identified
as essential for bull trout recovery. A local population is a group of bull trout that spawns
within a particular stream or portion of a stream and is the smallest interacting
reproductive unit of bull trout. To recover populations of Columbia River bull trout, the
FWS’s recovery plan was designed to do the following: (1) maintain or expand the
current distribution of the bull trout within Core Areas; (2) maintain stable or increasing
trends in bull trout abundance; (3) maintain/ restore suitable habitat conditions for all bull
trout life history stages and strategies; and (4) conserve genetic diversity and provide
opportunities for genetic exchange.
After reviewing the Forest Service’s 2010 BA, the FWS issued a Biological
Opinion (BO) in September of 2010. The BO noted that the bull trout population in the
Pass Creek allotment has been “trending down over the last 15 years,” and that a 2009
survey found no bull trout in Wet Creek. See 2010 Pass Creek BO at p. 13. The BO
found that “[h]abitat in most of this Allotment . . . does not adequately support essential
biological behaviors of bull trout. Most conditions are below objectives for healthy and
robust populations.” Id. at p. 29. The BO estimated that the Forest Service’s grazing plan
– especially the grazing proposed during August along the Wet Creek spawning sites in
the Pine Creek pasture – could trample one redd and affect two adult bull trout. Id. at p.
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The FWS concluded that “these local populations are important to maintaining
overall production and distribution of bull trout in the Little Lost river Core Area.” Id.
Nevertheless, the FWS found that the trampling of a single redd, and the potential impacts
to two bull trout, were “unlikely to be incompatible with sustaining the two local
populations as viable populations of bull trout.” Id. at p. 29. On a broader scale, the
FWS concluded that there was no threat to the “coterminous U.S. population” because (1)
the Little Lost River Core Area is “not geographically connected to the rest of the
Columbia River Recovery unit,” and (2) the small numbers of bull trout affected in Wet
Creek were insignificant in comparison with the total numbers of bull trout in Idaho. Id.
at pp. 29-30.
With this approval from the FWS, the Forest Service proceeded to implement its
grazing plan on the Pass Creek allotment in 2010. In addition, to boost the numbers of
bull trout, the Forest Service transplanted 161 bull trout into Wet Creek in 2010. See
Gamett Declaration (Dkt. No. 49-1) at p. 4.
Since that time, the Forest Service has been monitoring both the numbers of bull
trout in Wet Creek and the condition of the allotment in general. Monitoring has revealed
that some conditions on the allotment have improved while others have deteriorated. For
example, in 2012, the Forest Service found that livestock were getting through fences
designed to keep them out of spawning areas of Wet Creek, and concluded that these
trespasses have “likely impacted the ability of habitat within the exclosure to support Bull
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Trout.” At the same time, the bank stability along Wet Creek shows “a generally
improving trend at [monitoring] locations since 2009.” See Forest Service BA (Dkt. No.
38-1) at p. 3. The bull trout found in Wet Creek have increased from zero in 2009 to 4 in
2012. Id. at figure 1.
Due to these changed circumstances on the allotment, the Forest Service reinitiated
consultation with the FWS in May of 2013. The Forest Service is preparing a new
Biological Assessment to be submitted to the FWS once the 2013 grazing season is over.
The Forest Service states that it intends to propose a different grazing management
strategy for the FWS to evaluate after the 2013 grazing season but prior to the 2014
In the meantime, the Forest Service has adjusted grazing on the two pastures – or
“units” – within the Pass Creek allotment that contain bull trout habitat. On one of those
units – the Wet Creek unit – no grazing will be permitted. On the other – the Pine Creek
unit – grazing will be limited to 5 days of livestock trailing through a quarter-mile section
of Wet Creek.
One day of trailing has already occurred on June 1, 2013. Trailing is also planned
for July 15, 2013, and August 8-10, 2013. The trailing is intended to occur before the
mid-August spawning season begins. During the July 15th trailing, 231 cow/calf pairs
will be trailed. During the August trailing, 1471 pairs will be trailed. To ensure that the
cattle do not stray off course, the Forest Service requires that an additional two riders
accompany the trailing.
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On May 30, 2013, the Forest Service made a finding under § 7(d) of the ESA that
the newly proposed grazing plan would not jeopardize the continued existence of bull
trout. See § 7(d) Determination (Dkt. No. 38-1). To reach that conclusion, the Forest
Service reasoned that (1) the trailing will occur before August 15th, the typical start of
spawning; (2) the requirements for habitat health – measured by stubble height, woody
browse, and stream bank stability – will be enhanced and strictly enforced; (3) two extra
riders will accompany the trailing to ensure that cattle do not stray off the planned route,
and (4) the quarter-mile crossing site constitutes just 5% of the total length of Wet Creek
in the allotment. Given this, the Forest Service concluded that the impact on bull trout
would be “insignificant” and “will not reach a level considered to be adverse.” Id. at p. 9.
WWP claims that the Forest Service violated § 7 and § 9 of the ESA when it
authorized the trailing of cattle over Wet Creek. Section 7(d) prevents agencies, while
consulting with the FWS, from making “any irreversible or irretrievable commitment of
resources with respect to the agency action which has the effect of foreclosing the
formulation or implementation of any reasonable and prudent alternative measures which
would not violate subsection (a) (2) of this section.” See 16 U.S.C. § 1536(d). “Section
7(d) was enacted to ensure that the status quo would be maintained during the
consultation process, to prevent agencies from sinking resources into a project in order to
ensure its completion regardless of its impacts on endangered species.” Washington
Toxics Coalition v. EPA, 413 F.3d 1024, 1034-35 (9th Cir. 2005). Section 9 of the ESA
makes it unlawful for any person to “take” a listed species. See 16 U.S.C.§
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1538(a)(1)(B). The term “take” is defined to mean “harass, harm, pursue, . . . or collect,
or to attempt to engage in any such conduct.” See 16 U.S.C. § 1532(19). WWP claims
that the trailing violates both § 7(d) and § 9 by disrupting bull trout spawning on Wet
Creek as nearly 3,000 cattle trample the spawning grounds just days prior to the start of
spawning. In the motion now before the Court, WWP seeks to enjoin the trailing.
The Ninth Circuit recently considered a request for injunctive relief as a remedy
for alleged ESA violations. See, Conservation Congress v. U.S. Forest Service, 2013 WL
2631449 (9th Cir. June 13, 2013). The Circuit, citing Winter v. Natural Res. Def. Council,
Inc., 555 U.S. 7 (2008), held that a preliminary injunction is an “extraordinary remedy,”
requiring the movant to show that: (1) it is likely to succeed on the merits; (2) it is likely
to suffer irreparable harm if the preliminary injunction is not granted; (3) the balance of
equities tips in its favor; and (4) an injunction is in the public’s interest. Id. at *4.
The Circuit did not cite or discuss a line of Circuit authority – predating Winter –
holding that the “traditional preliminary injunction analysis does not apply to injunctions
issued pursuant to the ESA.” Nat. Wildlife Fedn. v. NMFS, 422 F.3d 782, 793 (9th
Cir.2005). For example, those cases held that the courts need not “balance interests in
protecting endangered species against the costs of the injunction when crafting its scope,”
because the balance of hardships always favors the threatened species. Wash. Toxics
Coalition, 413 F.3d at 1035. Those cases also put the threshold burden on the agency to
show that their action would not likely cause harm to the listed species. Id. (holding that
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“[p]lacing the burden on the acting agency to prove the action is non-jeopardizing is
consistent with the purpose of the ESA . . .”). Because the Circuit did not discuss this line
of case law in Conservation Congress, and merely cited Winter’s injunction test, it
remains unclear whether that line survived Winter. In the absence of any express
overruling, however, the Court will assume that line of cases is still good law, and will
apply it here.
WWP brings its claims under the ESA’s citizen suit provisions, which authorize
any person or private entity to bring suit to enjoin violations of the ESA. See 16 U.S.C. §
1540(g). The standard of review, and the scope of review, were both discussed in
Western Watersheds Project v Kraayenbrink, 632 F.3d 472 (9th Cir. 2011). Because the
ESA does not establish a standard of review, the courts have borrowed the “arbitrary and
capricious” standard from the APA. Id. at 496. But the courts have not similarly
borrowed the APA’s scope of review that prohibits consideration of material outside the
administrative record: “[B]ecause the ESA provides a citizen suit remedy . . . we may
consider evidence outside the administrative record for the limited purpose of reviewing
plaintiffs’ ESA claim.” Id. at 497.
Bringing all these standards together, the Forest Service has the burden of showing
that the trailing over Wet Creek is not likely to jeopardize the bull trout. The Court
evaluates that showing under the APA’s arbitrary and capricious standard. “A decision is
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, or offered an
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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.”
Conservation Congress, 2013 WL 2631449 at *4. “Agency action is valid if the agency
considered the relevant factors and articulated a rational connection between the facts
found and the choices made.” Id. Moreover, when reviewing scientific judgments and
technical analyses within the agency’s expertise, the reviewing court must be at its “most
Initially, the Court rejects the Forest Service’s argument that the case is moot. The
agency has authorized grazing that WWP alleges will jeopardize a threatened species
under the ESA. The agency has taken action with consequences that have not abated, and
hence this case is not moot. See Center for Biological Diversity v U.S. Forest Service,
820 F.Supp. 2d 1029 (D. Ariz. 2011) (rejecting Forest Service mootness argument where
plaintiff alleged grazing violated ESA).1
The key issue is whether the Forest Service has carried its burden of showing that
the trailing is not likely to jeopardize bull trout. In its § 7(d) determination, as discussed
earlier, the Forest Service found no jeopardy because the quarter-mile of Wet Creek to be
crossed by the cattle constitutes only 5% of the total length of the Creek in the allotment.
The Forest Service also argues that WWP was not diligent in filing this action. The
Court disagrees, finding persuasive the showing of diligence by WWP’s counsel in her
Declaration. See Ruether Declaration (Second)(Dkt. No. 47).
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But while this section of Wet Creek is short, it is contained within the 1.2 mile stretch of
Wet Creek that the FWS identified in its 2010 BO as potential bull trout spawning
grounds. AR at 8349, 8382; see also Gamett Declaration (Dkt. No. 49-1) at ¶ 7 (“the
section of Wet Creek where livestock trail across is within the 2010 [BO] potential
spawning reach”). In its § 7(d) determination, the Forest Service did not discuss the
potential impact of trailing nearly 3,000 cattle over these spawning grounds just days
before spawning would begin on August 15th.
Recognizing that gap in the record, the Forest Service filed the Declarations of (1)
Bart Gamett, the agency’s Fisheries Biologist for the Salmon-Challis National Forest, (2)
Diane Weaver, the District Ranger for the Lost River Ranger District in the Forest, and
(3) Lee Jacobson, the Program Manager for the Region’s listed species and the author of
the § 7(d) determination.
In addressing the trailing over these spawning grounds, Gamett points out that
surveys in 2010 and 2012 found no bull trout redds in this stretch of Wet Creek. Id. at
¶ 6. Moreover, a fish population assessment conducted on July 25, 2011, found no bull
trout in that stretch of Wet Creek. Id. The spawning that does take place on Wet Creek
occurs a mile upstream from the trailing site, according to Gamett. Id. at ¶ 8. With
respect to the trailing site, Gamett concludes that “no spawning actually occurs within this
section of Wet Creek” and thus the trailing “will likely not impact bull trout spawning or
spawning habitat . . . .” Id. at ¶ 7. Even if some bull trout do decide to spawn there, the
trailing will occur prior to spawning and any bull trout in the area “can seek out cover or
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move out of the trailing area and return to normal activity once the livestock trailing is
completed. Since bull trout avoid large animals wading through the stream the likelihood
of livestock stepping on bull trout is extremely small.” Id. at ¶ 9. Gamett concludes that
the trailing will have no adverse impact on the bull trout. Id.
The author of the Forest Service’s § 7(d) determination – Lee Jacobson – agrees
with Gamett. Jacobson states that “few, if any, bull trout are expected at the Wet Creek
stream crossing area” during the July and August crossings. See Jacobson Declaration
(Dkt. No. 34) at ¶ 8. From this, he concludes that it is “unlikely” that bull trout will be
“disturbed” or “trampled” during the trailing. Id.
WWP disagrees. To show the historic numbers of bull trout, and to highlight the
deterioration of conditions, WWP filed a 1996 monitoring study finding 27 bull trout in
this stretch of Wet Creek. See Fishery Management Annual Report (Dkt. No. 53-1) at p.
11. In addition, a monitoring study in 1999 found three bull trout at the trailing site on
August 6, 1999, a date just two days before the August trailing will begin. See Pass AR
9499 at 9502.
WWP also filed the Declaration of Laurence Zuckerman who worked as a
Fisheries Biologist for the FWS, among other agencies. See Zuckerman Declaration
(Dkt. No. 10) at ¶ 2. He states that bull trout will “stage” in the spawning area up to a
month before August 15th at the females dig “test redds” to determine if the substrate is
adequate. See Zuckerman Declaration (Second)(Dkt. No. 46) at ¶ 8. He concludes that
trailing nearly 3,000 cattle over this area in early August “would make it very likely that
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any staging bull trout would be disturbed to such extent that it would abandon the area,
undergo significant stress that would impair its spawning and reproductive success, or
even be harmed or killed directly by cattle hooves.” Id. at ¶ 9. He is also concerned
about grazing on other pastures within the allotment along tributaries that flow into Wet
Creek. That grazing dumps sediment into the tributaries that eventually finds its way into
Wet Creek, and can also result in drying up the tributaries.
The Forest Service takes issue with these conclusions about grazing on other
pastures. While the Forest Service did authorize essentially the same number of cattle on
the allotment in 2013 as 2012, it also imposed more restrictive use standards to govern
criteria such as stubble height, woody browse, and stream bank alteration. See Weaver
Declaration (Second)(Dkt. No. 49-2) at ¶¶ 6. These use standards should be the focus,
rather than the total head of cattle, according to District Ranger Diane Weaver. Id. She
concludes that the use standards will protect the allotment because “[o]nce these specified
levels of use are reached, livestock must be removed from the area . . . .” Id. at ¶¶ 6, 8.
She predicts that these standards, in combination with the drought, will mean that cattle
will be moved “more quickly” through the pastures and be removed early. Id. at ¶ 6.
With regard to the effect of grazing on tributaries to Wet Creek, Weaver concludes that
Basin Creek will probably not flow all the way to Wet Creek in 2013 because of the
drought, not because of any grazing-caused problems. Id. at ¶ 9. Gamett likewise
concludes that while grazing in these other units may have some impact on tributaries,
“the small size of many of these tributaries and their relative distance from Wet Creek
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[makes] it is unlikely that these impacts will adversely affect bull trout or occupied bull
trout habitat in Wet Creek.” Gamett Declaration, supra, at ¶ 15.
The Court is faced with conflicting expert opinions. Both sides support their
opinions with well-reasoned analysis and monitoring data. Under these circumstances,
the Court’s role is not to select the outcome it deems “best.” Lands Council v. McNair,
537 F.3d 981, 996 (9th Cir.2008) (en banc), overruled in part on other grounds by Winter,
supra. The standard of review “requires [the Court] to defer to an agency’s determination
in an area involving a ‘high level of technical expertise.’” Id.; see also Sierra Forest
Legacy v. Sherman, 646 F.3d 1161, 1185 (9th Cir. 2011) (holding that “Forest Service is
entitled to rely on the reasoned opinions of its experts”). Under the arbitrary and
capricious standard, the agency’s decision must be upheld if “there is a rational
connection between the facts found and the conclusions made,” and the determination
was “not so implausible that it could not be ascribed to a difference in view or the product
of agency expertise.” Id. at 987.
Obviously, trailing nearly 3,000 cattle over Wet Creek will have a substantial
impact on that stretch of Wet Creek. The trampling will crush anything underfoot, raising
sediment levels along with water temperatures. But the Forest Service experts conclude
that the bull trout will not be put in jeopardy because (1) the trailing occurs prior to
spawning, (2) no spawning takes place in that stretch of Wet Creek, (3) the spawning
takes place about a mile upstream and so will not be affected by the trampling, and (4) the
grazing on other units will not affect Wet Creek.
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The destruction of an insignificant portion of habitat for a listed species does not
necessarily support injunctive relief. See Conservation Congress, 2013 WL 2631449 at
*8 (rejecting injunctive relief where plaintiff “fail[ed] to explain how the alteration to 68
acres of the Owl’s foraging habitat will appreciably diminish the Owl's broader foraging
habitat”); Butte Environmental Council v. U.S. Army Corp of Engineers, 620 F.3d 936,
948 (9th Cir. 2010) (holding that “[a]n area of a species’ critical habitat can be destroyed
without appreciably diminishing the value of critical habitat for the species’ survival or
The opinions of the Forest Service experts that the effects of trailing will be
insignificant are reasoned and supported by some of the monitoring data; there is a
rational connection between the facts and their conclusions. The opinions are not so
implausible that they must be the result of something other than the application of agency
It is true that the required rational connection was not made in the § 7(d)
determination, which ignored the FWS’s earlier designation of this stretch of Wet Creek
as spawning grounds. But the connection was made in the Declarations submitted to the
Court, and discussed above, demonstrating that spawning is unlikely in the trailing area.
The Court may rely on such extra-record material in this proceeding. Kraayenbrink, 632
F.3d at 497 (holding that the courts “may consider evidence outside the administrative
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record for the limited purpose of reviewing plaintiffs’ ESA claim”).2
For all of these reasons, the Court will deny WWP’s motion for preliminary
In accordance with the Memorandum Decision set forth above,
NOW THEREFORE IT IS HEREBY ORDERED, that the motion for preliminary
injunction (docket no. 7) is DENIED.
IT IS FURTHER ORDERED, that the motions to strike (docket nos. 43 & 49) are
DATED: June 26, 2013
Honorable B. Lynn Winmill
Chief U. S. District Judge
The Forest Service filed two motions to strike extra-record material submitted by WWP. The
Court has examined the material and relied on it in this decision, finding that extra-record material may be
examined. In addition, the Court has relied upon the extra-record material submitted by the Forest
Service. At any rate, the Court will deny both motions.
Memorandum Decision & Order - 15
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