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ESAblawg is an educational effort by Keith W. Rizzardi. Correspondence with this site does not create a lawyer-client relationship. Photos or links may be copyrighted (but used with permission, or as fair use). ESA blawg is published with a Creative Commons License.

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florida gators... never threatened!

If you ain't a Gator, you will be, because gator blood looks like our pharmaceutical future. Click here to read the relevant ESA musing.gatorlogo2.gif

Follow the truth.

"This institution will be based on the illimitable freedom of the human mind. For here we are not afraid to follow truth wherever it may lead, nor to tolerate any error so long as reason is left free to combat it." -- Thomas Jefferson to William Roscoe, December 27, 1820.

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Thanks, Kevin.

KEVIN S. PETTITT helped found this blawg. A D.C.-based IT consultant specializing in Lotus Notes & Domino, he also maintains Lotus Guru blog.

Contributors

PETE DAVID (Albuquerque, NM). Pete is a Certified Wildlife Biologist with 25 years experience with land stewardship and natural resources programs. He previously worked with the South Florida Water Management District, Florida Department of Environmental Regulation, U.S. Department of Defense, U.S. Forest Service, and U.S. Fish and Wildlife Service (FWS). His project experience includes reintroducing the federally endangered red-cockaded woodpecker to South Florida, and the Middle Rio Grande Endangered Species Act Collaborative Program in New Mexico. Today, Pete continues to work on endangered species issues as a Senior Project Manager for SWCA Environmental Consultants in Albuquerque.

YELIZAVETA BATRES (West Palm Beach, FL). Liz is currently clerking at the Florida Fourth District Court of Appeal, after graduating from the University of Florida Levin College of Law, where she was a senior research editor of the Law Review. Liz also interned at the U.S. Department of Justice, Environment and Natural Resources Division.

Bulk petitions: breaking the Endangered Species Act, a few hundred species at a time? (Updated)

08/31/2010

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With each new petition to list a few hundred more species as threatened or endangered, environmental advocates risk the destruction of one of their most beloved statutes.  By overburdening federal agencies, and outraging opponents, excessive petition and litigation tactics threaten something else: the rewriting of the Endangered Species Act (ESA).

Some scholars have estimated that the ESA currently protects less than nineteen percent of plant and animal species at risk of extinction.  See, K. Mollie Smith. That frustration, in turn, has helped create enormous pressure to litigate over the ESA, and to use its citizen participation tools in an effort to force greater species conservation.  For example, in recent years, environmental groups sent petitions to list hundreds of species to the biologists at the U.S. Fish & Wildlife Service (FWS) and the National Marine Fisheries Service (NOAA Fisheries).  The Center for Biological Diversity sent FWS a Petition to List 404 Aquatic, Riparian and Wetland Species from the Southeastern United States (see ESA blawg) and sent NOAA Fisheries a separate petition to list 83 species of coral (again, see ESA blawg).  WildEarth Guardians sent FWS a petition to list 475 imperiled plant and animal species across the American Southwest, (see Federal Register) and sent a separate petition seeking Federal Protection for 681 Western Species (see press release and Federal Register.)  Four petitions, one thousand six hundred forty three species.  

Raw numbers aside, these tactics -- call them "bulk petitions" -- generate substantive, procedural and economic consequences.

First, the petitions create substantive burdens for the agencies.  In the easiest of cases, the regulatory agencies will be able to respond in a systematic manner, rejecting the listing of many or all of the petitioned species because the petition fails to meet certain procedural thresholds. For example, the petition might rely upon an inapplicable international standard or unreliable or outdated information, or it might contain insufficient information on many of the species, enabling the FWS or NOAA Fisheries to reject the petition because it does not "present substantial information indicating that the petitioned action may be warranted." See ESA Sec. 4(b)(3)(B), and FWS flow chart.  Such petitions waste agency time and resources simply to make a point.  But in other cases,the petitions might contain sufficient information to overcome that initial standard, thereby triggering a duty to review whether each species is threatened or endangered.  That analysis, in turn, requires review of the best scientific available information available (and a notice and comment process!) to determine how each of the five factors for listing apply: (1) present or threatened destruction, modification, or curtailment of its habitat or range; (2) overutilization for commercial, recreational, scientific, or educational purposes; (3) disease or predation; (4) inadequacy of existing regulatory mechanisms; and (5) other natural or man-made factors affecting its continued existence.  This type of substantive analysis is difficult for a single species; but when 1643 species are involved, for 5 factors, mistakes and inadequacies will occur.

Second, compounding the substantive problems, the petitions create procedural burdens, because FWS and NOAA Fisheries lack discretion to prioritize the petitions (nevermind attending to the needs of already listed species!)  The petitioners had as long as they wanted to create their petition.  But once the FWS or NOAA Fisheries receives the petition, it must respond, within no more than twelve months, based on the deadlines in the ESA Sec. 4(b)(3)(B).  See also, Petition Management Guidance (1996).  For each and every species in the petition, one of three outcomes must occur: either the petition is rejected for a species as inadequate, the species is listed, or the listing of the species is considered warranted but precluded.  The clock ticks relentlessly, and no matter what other competing priorities exist, the expert discretion of our agency biologists gives way to the demands of intemperate petitioners.  Worse yet, with petitions offering lists of hundreds of species, the agency's face a terrible choice: take time to do it right, and get sued for taking too long, or rush to make decisions, and face the potential risk of being sued for making errors.

Third, pursuant to the ESA's citizen suit provision, the lawsuits that follow the unanswered petitions have economic consequences.  The taxpayer already pays for the FWS and NOAA review (whether late or not.)  And of course, once the litigation begins, the taxpayer pays for the Justice Department and the judiciary, too.  But adding insult to injury, Congress has created a process where the taxpayer pays the petitioners for filing their lawsuits.  Most of the time, under the "American rule," litigants pay for themselves.  But some statutes, including the ESA, have "fee-shifting" provisions.   As explained in the ESA, Sec. 11, the court "may award costs of litigation (including reasonable attorney and expert witness fees) to any party, whenever the court determines such award is appropriate."  And unfortunately, through case law, the courts have decided that payment is "appropriate" whenever a litigant achieves even just a partial victory, or merely serves as a "catalyst" for action.  In theory, these types of statutes and legal doctrines were created to help individual taxpayers act as "citizen attorney generals" to help ensure that the government does its job, enabling them to be compensated when they were proven right.  But the multi-million dollar litigation organizations such as the Center for Biological Diversity and Pacific Legal Foundation do not deserve taxpayer funding for their lawsuits.  (In 2008, CBD had $9.1 million in revenues and net assets of $6.4 million, PLF had $10.1 million in revenues and $10.2 million in net assets. See Charity Navigator.)  The fee shifting process adds nothing, except debt, to the national dialogue. See, ESA blawg (2010).

These three concerns aside, some members of the environmental community justify these bulk petition tactics, and their consequences, by labeling the President, Secretary or decision maker (or anyone else who disagrees with them) as unenlightened, ignorant, or worse.  They profess that the government fails to act in times of biological crisis, insist that the extinction of countless species is imminent, and declare that without their push for action, nothing at all happens.  See CBD and Newsweek. Their opponents, in turn, deem the environmental advocates to be irresponsible extremists, deluded into "sky-is-falling" worry without sufficient facts, and otherwise unwilling to acknowledge property rights or the economic consequences of the green agenda.  See PLF.  The environmentalists then respond to their naysayers, tarnishing them as rich or selfish polluters and resource exploiters who only want to preserve the status quo. And so on, and so on. To some degree, everyone may even be right.  But none of the rhetoric, none of the posturing, none of the fundraising, and none of the litigation will change the realities.  The advocates have taken over the priorities, the agencies have lost control, and the taxpayers -- as well as the species -- suffer.  The state of the Endangered Species Act is precarious, because lawsuits have become a business model. See ESA blawg (2008).  

In response to all these concerns, some future Congress might decide that enough is enough.  As a starting point, some lawmakers might even encourage the end of bulk petitions by limiting petitioners to a single species at a time.  But sadly, the consequence of such a rule would be predictable: in lieu of the four petitions discussed above, 1643 "separate" petitions would be filed (maybe even by 1643 "separate" people).  Meanwhile, worthy multi-species petitions would be needlessly inhibited.  So, with that sad truth swallowed, I suggest that whenever ESA reform does finally happen, five changes should occur to the petition process.  First, twelve month deadlines for agency review should only apply to the decision as to whether or not a species warrants emergency  listing -- and the need for an emergency listing could be expressly defined, creating a higher standard that dissuades litigation over insufficiently detailed bulk petitions, and that enables the agency to quickly reject inadequate petitions.  Second, any right to sue for inaction should apply only when the inaction exceeds a much longer period: perhaps five years (one year before the statute of limitations might otherwise apply.)  This longer period of time would allow the agencies to create internal priorities -- and yes, even to acknowledge political influences.)  Third, no matter how long the agency delays its review of a petition, the deadline should not create strict liability for a deadline violation; the ESA should allow the agency to explain any reasonable delay.  (For example, in Telecommunications Research & Action v. F.C.C., 750 F.2d 70, 79-80 (D.C.Cir.1984) the court described a six-factor test for evaluating unreasonable delay.)  Fourth, the litigation incentive should be removed, and the right to be compensated by fee-shifting provisions should be severely curtailed (with a capped dollar amount) or eliminated. (See ESA blawg (2010)).  Fifth, and last, but certainly not least, with the agency discretion to control the process restored, and far less money spent on litigation, Congress should ensure that the listing process is adequately funded.

Although the Endangered Species Act protects over 1900 species, the statute is certainly not perfect.  Its protections for listed species can be insufficient, and its many requirements consume the implementing agencies' time and attention.  But these limitations demonstrate the value of a workable listing petition process, because knowledgeable citizens and qualified scientists can play an important role in the identification of threatened species and the establishment of needed statutory protections -- before it's too late for the species.  The bulk petition process, however, goes much too far.  Thoughtful environmental advocates should recognize that a moderately and partially helpful ESA is better than no ESA at all.

***

Postscript.  The abuses of the listing petition process is hardly a new topic.  It was the subject of U.S. Senate hearings in 2004, see Environment and Public Works, and the National Governors Association also called for reform.  See The Heartland Institute.   And sadly, all of that Congressional dialogue came from anti-regulation industry advocates.  Nevertheless, the recent petitions are elevating an old concern to new plateaus, and will expand opposition to the perceived abuses of the ESA.  At its June 2010 meeting, the federal Marine Fisheries Advisory Committee addressed this issue, including the petition to list 83 coral species.  The group, consisting of a broad array of stakeholders, including fishermen, academics, environmental groups (and me, the author of this blawg), unanimously adopted the following statement: "MAFAC notes that a thorough scientific analysis takes time, and expresses its concern that some petitions to list species -- such as a recent petition to list 83 species of coral -- may not be adequately responded to within the statutory timeframes of 90 days (for an initial determination) or twelve months (for a final determination). MAFAC also notes its concerns that the deadlines associated with this petition process, as well as the associated litigation and court orders, can, at times, limit the full exploration and exercise of NMFS' scientific expertise and also renders NMFS unable to meet its existing priorities. For example, deadlines associated with listing petitions for new species can interfere with existing efforts to develop and implement recovery plans for species already listed. To the extent that the ESA petition process requires a deadline for NMFS to respond, MAFAC encourages NOAA to ask Congress to consider whether alternatives such as an “unreasonable delay” standard, as included in the Federal Administrative Procedure Act, would be more appropriate."  

One final note: In August 2010, the Center for Biological Diversity filed a more restrained petition, seeking to list four mountainous species based on the alleged effects of climate change, including the ‘I‘iwi (or scarlet Hawaiian honeycreeper, pictured below), the Bicknell’s thrush, the White-tailed ptarmigan, and the San Bernardino flying squirrel.  

ScarletHawaiianHoneyCreeper.jpeg
The I'iwi or Scarlet Hawaiian Honeycreeper (Vestiaria coccinea) is a Hawaiian "hummingbird-niched" species, of the Hawaiian honeycreepers, subfamily, Drepanidinae, and the only member of the genus Vestiaria. The I'iwi is a highly recognizable symbol of Hawai'i. The I'iwi is the third most common native land bird in the Hawaiian Islands.  Altogether, the remaining populations add up to a total of 350,000 birds.  There are large colonies of I'iwi on the islands of Hawai'i and Kaua'i, and smaller colonies on Moloka'i and O'ahu; I'iwi were extirpated from Lāna'i in 1929. It was formerly classified as a Near Threatened species by the IUCN, but recent research has proven that it was rarer than previously believed. Consequently, it was uplisted to Vulnerable status in 2008.  Caption and photo from wikipedia.

***

READER CORRESPONDENCE: Earlier today, I received the following insightful comment from Elizabeth Ellis, an Environmental Planner who works for the Washington State Department of Natural Resources.  Our dialogue deserves reproduction here...

Hi Keith,

I really appreciate your insight into the ESA, although sometimes I think you may be a bit critical. I used to work for NMFS doing section 7(a)(2) ESA consultations on the Columbia River. While petitions may seem like they are a burden, they are also a tool if completed correctly. They allow multiple species to be submitted and reviewed at once, which saves the agencies time, reduces their workload, and saves their money.  Let's not overlook the reductions in the staff and funding the services have had to endure. To remove a tool meant to streamline may do more harm than good.  Yes, some folks may be misusing it, but as you point out correctly, what could happen if it is removed? Single-species petitions (again?)? Now THAT is a burden.

Let's look at the real issues - why are the petitions coming in so quickly, Keith? Are people just mad at the services? Are they anarchists? Are they bored?  No, the reality of it is, there is science supporting species decline as our population increases. Many people want to conserve and protect these species and their habitat before it is too late and see the ESA as a tool to do that. Perhaps we need to develop more mandatory protections for species and their habitat in every state to ease the burden on the ESA, so that it can be used correctly - as an emergency room for species in in dire straits.

To quote Professor Emeritus Gorden H. Orians, University of Washington, the ESA is just a "finger in the dike" of biodiversity. It is not the answer.  We must build better dikes, as Professor Orians to rightly reminds us, in order to protect the future of species and their habitats. Not rely on the emergency room.

Sincerely,

Liz

***

MY REPLY:  I support the petition process, and do not advocate its elimination. I simply believe that the inevitable litigation over all these petitions is a waste of intellect, and money. Yes, some petitions may have merit, but those merits compete with the needs of existing listed species, and the needs of other petitioned species. Under the current system, two litigious non-profit organizations can force FWS and NOAA to drop every other priority and address their petitions.  Other discretionary activities, like recovery planning, stop dead.  I say let the agencies limp along, and give them sufficient discretion to sort out the priorities by eliminating the much too rigid 12-month deadline.  I also agree that the ESA cannot continue to serve as the only tool regulating biodiversity, and have repeatedly emphasized the point that the ESA is drowning under the weighty risk of extinction created by climate change and sea level rise.  Sadly, we need to make room for triage, at least until we build those additional dikes that Professor Orians espouses. Indeed, perhaps the intellect spent on lawsuits can be redirected to building those new dikes -- climate change legislation, anyone?  The economic and intellectual savings from less litigation can be reinvested in agency resources and species protection.  See also, ESA blawg postings in 2008(has climate change jeopardized the ESA?) and 2008(the preservation predicament) and 2009(climate change and the 5-factor analysis) and 2009(polar bear listing shows need for climate legislation) and 2010 (listing of the van Rossem’s gull-billed tern, now what?).  

9th Circuit upholds NOAA Fisheries distinct treatment of Steelhead and Rainbow trout

08/31/2010

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Modesto Irrigation District v. Gutierrez, No. 09-15214, 2010 WL 3274499 (9th Cir. Aug. 20, 2010)(Judges Mary M. Schroeder, Consuelo M. Callahan, and Barbara M. Lynn)

This Endangered Species Act (“ESA”) case is a challenge to the decision of the National Marine Fisheries Service (“NMFS”) to list the steelhead, a type of Pacific salmon, as a threatened species in California's Central Valley. In listing the steelhead, NMFS defined it as a distinct species under the ESA, separate from rainbow trout, another type of Pacific salmon that breeds with and looks like the steelhead. The separate listing was a departure from the prior NMFS policy of classifying interbreeding Pacific salmon as a single species.  Plaintiffs are irrigation districts in California's Central Valley, (including  Modesto Irrigation District (MID)) whose operations are impeded by the listing. They contend that the listing violated the ESA because steelhead and rainbow trout interbreed, and the statute therefore requires NMFS to treat them as a single species. Plaintiffs also contend that NMFS violated the Administrative Procedure Act (“APA”) by failing adequately to explain its decision to adopt a new policy for classifying the fish. We agree with the district court that under the ESA, interbreeding is not alone determinative of whether organisms must be classified alike where, as here, they develop and behave differently. We also find that NMFS' explanation for its change of policy satisfies the standards set forth in the Supreme Court's recent decision in F.C.C. v. Fox Television Stations, Inc.,129 S.Ct. 1800 (2009). We therefore affirm.

steelheadTroutSalmon.jpg
This case turned upon the distinctions between the steelhead (above from AlaskaSalmon.com) and rainbow trout, (below from oldtrout.ca) types of Pacific salmon that comprise the Oncorhyncus mykiss (“O.mykiss ”) species as scientifically defined. The fish are born in fresh water, but the steelhead migrate to the ocean anywhere from hours to years after their birth. To transition from fresh water to salt water, steelhead undergo a “smolt” stage, and then after one to five years in the sea, return to the original stream to spawn. Because of their migration pattern, steelhead are known as the anadromous form of O. mykiss. The rainbow trout, on the other hand, remain in fresh wa-ter their entire lives and are commonly known as the resident form of the O. mykiss species.  While the two fish grow to differing sizes as adults and have different predators and prey, they do inter-breed to some extent, and the offspring can take on the form of either. An excess of steelhead can regen-erate the population of rainbow trout, but the reverse does not seem to be the case.
RainbowTrout.jpg

BACKGROUND: Previously,NOAA Fisheries had sought to apply its evolutionary significant unit (“ESU”) policies to these species.  See, e.g. Proposed Listing Determinations for 27 ESUs of West Coast Salmonids, 69 Fed.Reg. 33,102, 33,115 (June 14, 2004); Final Listing Determinations for 10 Distinct Population Segments of West Coast Steelhead, 71 Fed.Reg. 834, 836 (Jan. 5, 2006).  Under these policies, NOAA determined that an ESU was the functional equivalent of a "Distinct Population Segment."  Under the ESU Policy, a salmon stock had to satisfy two main criteria before NMFS could place the stock in a distinct ESU: (1) It must be substantially reproductively isolated from other nonspecific population units; and (2) It must represent an important component in the evolutionary legacy of the species.  On November 4, 2005, NMFS proposed to abandon the ESU Policy with respect to O. mykiss. NMFS proposed using the DPS Policy instead to classify O. mykiss so the steelhead and rainbow trout could be treated separately under the ESA. See 70 Fed.Reg. at 67,131. In support of the change in policy, NMFS stated:

"It is appropriate that we consider departing from our past practice of applying the ESU Policy to O. mykiss stocks, and instead apply the DPS Policy in determining “species” of O. mykiss for listing consideration. Such an approach would also be consistent with use of the DPS Policy by the agencies in defining DPSs of Atlantic salmon ... The primary difference in the application of the two policies is that the ESU Policy relies on “substantial reproductive isolation” as the primary factor in delineating a group of organisms, while the DPS Policy relies on “marked separation” to delineate the group. Within a discrete group of O. mykiss populations, the resident and anadromous life forms of O. mykiss remain “markedly separated” as a consequence of physical, physiological, ecological, and behavioral factors. Despite the apparent lack of reproductive isolation between the two forms within a given population or group of populations, under the DPS Policy anadromous and resident O. mykiss may not warrant delineation as part of the same DPS."

EXCERPT: NMFS changed its policy when it applied the DPS Policy to O. mykiss after it had previously applied the ESU Policy, and it is undisputed that such a policy change requires an explanation. See F.C.C. v. Fox Television Stations, Inc., 129 S.Ct. 1800, 1810-11 (2009). MID questions whether NMFS provided sufficient explanation for the change. We hold that the record reflects that NMFS engaged in a careful decision-making process and provided a sufficient explanation for its decision to apply the DPS Policy...  This record thus contains ample support for the reasons NMFS stated when it decided to use the DPS Policy. The final rule stated that the ESU Policy was no longer appropriate for classifying O. mykiss because it is “a type of salmonid with characteristics not typically exhibited by Pacific salmon.” 71 Fed.Reg. at 834. The final rule may not explicitly describe why and how O. mykiss differ from other species of Pacific salmon, but the rule does provide an extensive discussion of the similarities and differences between steelhead and rainbow trout that are not shared by other Pacific salmon. It “may reasonably be discerned,” then, that NMFS determined that O. mykiss is distinct from other types of Pacific salmon. See Fox, 129 S.Ct. at 1811.  In light of the evolving understanding of the differences between the fish, the desire for a flexible policy, and the depth of consideration that NMFS has given the issue over close to two decades, we conclude that the agency was not arbitrary or capricious in changing its policy in order to protect the steelhead. We therefore affirm the district court's holding that the explanation for the policy change was sufficient. Its ruling was fully consistent with the Supreme Court's subsequent decision in Fox.

KEITHINKING: The opinion ended on a discomforting pragmatic point, reminding us about the tensions between good law and bad facts: "We are aware of the practical difficulties the classification decision creates for management of the Irrigation and Water Districts. The two types of fish look and behave the same during their early years in the rivers and streams in the area, and the practical effect of our decision is that plaintiffs may have to protect both the steelhead and rainbow trout, even though only the steelhead is threatened. The flexibility to make policy changes in response to such concerns, however, remains in the agencies administering the provisions of the ESA and not with the courts."

Interpreting plant provisions of the ESA, 9th Circuit shows restraint, encourages FWS to adopt rules

08/31/2010

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Northern California River Watch v, Wilcox, No. 08-15780,(August 25, 2010)(Dorothy W. Nelson, William A. Fletcher, and Richard A. Paez, Circuit Judges).

SUMMARY:
   Robert Evans and Northern California River Watch (“River Watch”) appeal the district court’s grant of summary judgment to the Schellinger defendants and three employees of the California Department of Fish and Game (collectively “Defendants”). River Watch contends that Defendants violated the Endangered Species Act (“ESA”), codified at 16 U.S.C. § 1531 et seq. Specifically, River Watch argues that Defendants dug up and removed the endangered plant species, Sebastopol meadowfoam (Limnanthes vinculans) and, therefore, violated § 9 of the ESA, which makes it unlawful for anyone to “take” a listed plant on areas under federal jurisdiction. See 16 U.S.C. § 1538(a)(2)(B).
   The district court granted Defendants’ motion for summary judgment, concluding that River Watch could not establish, as a matter of law, that the areas in which the Sebastopol meadowfoam plants were growing were “areas under Federal jurisdiction.” On appeal, we consider the meaning of the term “areas under Federal jurisdiction” as used in ESA § 9. River Watch argues that the term encompasses privately-owned wetlands adjacent to navigable waters that have been designated as “waters of the United States” by the Army Corps of Engineers. The United States, representing the interests of the Department of the Interior’s Fish and Wildlife Service as amicus curiae, argues that § 9 is ambiguous, that we must apply the deference principles set forth in Chevron, U.S.A., Inc. v. Natural Resources Defense Counsel, Inc., 467 U.S. 837 (1984), and that under Chevron the privately-owned land at issue in this case is not an “area under Federal jurisdiction.”
   Although we agree that the term “areas under Federal jurisdiction” is ambiguous, we are not convinced that the U.S. Fish and Wildlife Service (“FWS”), the agency with rule making authority, has interpreted the term. Nonetheless, for the reasons set forth in this opinion, we hold that “areas under Federal jurisdiction” does not include the privately-owned land at issue here. We therefore agree with the district court’s ultimate legal conclusion in this case and affirm the grant of summary judgment to Defendants.

FACTUAL BACKGROUND:
   William and Frank Schellinger are brothers and business partners who seek to develop 21 acres of private property in Sebastopol, California. These 21 acres (“the Site”) are comprised of grasslands containing seasonal vernal pools, wetlands, seasonal creeks, vernal pools, and vernal swales.  After learning of the discovery of Sebastopol meadowfoam, California Department of Fish & Game (CDFG) Habitat Conservation Manager Carl Wilcox, CDFG biologist Gene Cooley, and Project Manager for the Site’s development Scott Schellinger, visited the Site in order to further investigate the presence of the plants. Wilcox, 547 F. Supp. 2d at 1073. Wilcox confirmed that the vegetation was the endangered plant species Sebastopol meadowfoam. (Photo below from USDA Natural Resources Conservation Service).  In examining the plants to determine whether they were rooted in the soil and thus naturally occurring, Wilcox lifted the plants, along with their substrates, out of the wetland. Because the CDFG employees suspected that the plants were not naturally occurring, Cooley later returned to the Site to gather evidence. Wilcox, 547 F. Supp. 2d at 1073. Upon his return visit, he removed the Sebastopol meadowfoam plants, placed them in plastic bags, and transported them to the local CDFG office, where he placed most of the plants in an evidence locker. Id. at 1073, 1079.

SebastMeadowfoam.jpg
Limnanthes vinculans, or Sebastopol meadowfoam, is an endangered species of meadowfoam found only in the Laguna de Santa Rosa in Sonoma County, California, USA and an area slightly to the south in the Americano Creek and Washoe Creek watersheds. Like the other meadowfoams, it is a small annual herb, with multiple stems growing up to 30 centimeters (12 inches) in height; white flowers occur singly at the ends of stems.  This species is only known from approximately 30 locations in the laguna de Santa Rosa and southern Cotati Valley of Sonoma County, in these areas it occurs in wet meadows and around vernal pools at elevations of under 300 meters. Photo credit: Mark W. Skinner @ USDA-NRCS PLANTS Database

EXCERPT RE: CHEVRON STEP ONE:
   The prohibitions at issue here are found at § 9(a)(2)(B), which states that it is unlawful to: remove and reduce to possession any endangered species of plants from areas under Federal jurisdiction; maliciously damage or destroy any such species on any such area; or remove, cut, dig up, or damage or destroy any such species on any other area in knowing violation of any law or regulation of any State or in the course of any violation of a State criminal trespass law. Id. § 1538(a)(2)(B) (emphasis added). The meaning of “areas under Federal jurisdiction” is not immediately clear, nor is it explicitly defined in the ESA. “Jurisdiction, it has been observed, is a word of many, too many, meanings.” Steel Co. v. Citizens for a Better Env’t, 523 U.S. 83, 90 (1998)
   Therefore, we conclude that the meaning of the statutory text “areas under Federal jurisdiction” is not plainly clear from the text of the ESA, nor does the ESA’s legislative  history elucidate Congress’ intent in using the term. We agree with the district court’s conclusion that “Congress did not explain what it meant by ‘areas under Federal jurisdiction,’ ” and we proceed to examine whether the FWS’s interpretations offered in the United States’ amicus brief satisfy the requirements set forth in United States v. Mead Corp., 533 U.S. 218, 226-27 (2001).

EXCERPT RE: CHEVRON STEP TWO:
   The United States cites three rules, which were promulgated by the FWS using formal rule-making authority, as evidence of the FWS’s interpretation of the phrase “areas under Federal jurisdiction.” The three rules designate certain plant species as endangered or threatened. None of these rules, however, interprets “areas under Federal jurisdiction;” instead, the rules use the phrase in passing and somewhat interchangeably with the term “federal lands.” Thus, the three rules do not provide an agency interpretation to which we could defer under Chevron...
   The United States also urges us to give Chevron deference to an “interpretation” of “areas under Federal jurisdiction” found in the Habitat Conservation Planning And Incidental Take Permit Processing Handbook, an FWS guidance manual for conducting the  Incidental take permit program under ESA § 10. Habitat Conservation Planning And Incidental Take Permit Processing Handbook (1996).  The Handbook states that “the ESA does not prohibit the incidental take of federally listed plants on private lands unless the take or the action resulting in the take is a violation of state law (which in most cases eliminates the need for an incidental take permit for plants).” Id. at 3-17. Although issued after public notice and comment, see 61 Fed. Reg. 63,854 (Dec. 2, 1996); 59 Fed. Reg. 65,782 (Dec. 21, 1994), the Handbook is not deserving of Chevron deference. First, “interpretations contained in policy statements, agency manuals, and enforcement guidelines, all of which lack the force of law-do not warrant Chevron-style deference.” ...  Finally, the 300+ page Handbook does not discuss “areas under Federal jurisdiction” other than in one paragraph where it restates the statute. In sum, the focus of the Handbook is the § 10 incidental take permit program, and any interpretation one might glean from the Handbook is attenuated at best.
   we hold that contrary to the United States’ arguments, the FWS has not yet interpreted “areas under Federal jurisdiction.”

EXCERPT RE: JUDICIAL CONSTRUCTION OF SECTION 9(a)(2)(B):
   Without any agency interpretation of “areas under Federal jurisdiction” to which we must defer, we proceed to interpret the term. We agree with the district court that River Watch’s proposed construction of § 9(a)(2)(B) is not tenable. The potential for overbreadth posed by interpreting “areas under Federal jurisdiction” as including all “waters of the United States” is simply too large...
  ...We hold that River Watch has not established that the plain language of the ESA mandates that “waters of the United States” are “areas under Federal jurisdiction.” We agree with the United States that the term is ambiguous, but we conclude that, thus far, the FWS has not promulgated regulations or offered any guidance materials specifically addressing this issue to which we must defer. We thus interpret “areas under Federal jurisdiction” as not including all of the “waters of the United States” as defined by the CWA and its  regulations. Although our ruling will constitute “binding law,” we recognize that under Brand X Internet Servs., 545 U.S. 967, 986 (2005)., we are not the “authoritative interpreter” of “areas under Federal jurisdiction.” See 545 U.S. at 983. The FWS might have good reason to issue regulations or guidance that more thoroughly addresses this issue at some later date, and our decision does not foreclose the possibility that the FWS might adopt some version of the statutory construction set forth by River Watch. See id. After all, the objective of the ESA, to provide a program and means to conserve endangered species and their ecosystems, 16 U.S.C. § 1531(b), is surely intertwined with that of the CWA, “to restore and maintain the chemical, physical, and biological integrity of the Nation’s waters.” 33 U.S.C. § 1251(a).

KEITHINKING: Seems as though Chevron deference is becoming increasingly less deferential...  This case also involved a sinister subplot, as revealed in footnote 6, which states: "In the district court, the Schellingers alleged that the plants were illegally
transplanted to the Site in an effort to delay their development plans. Although this issue is disputed by the parties, it is irrelevant to our review."

NOAA extends comment period for 5-year status review on Steller's sea lion

08/31/2010

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75 Fed. Reg. 53272 / Tuesday, August 31, 2010 / Notices
DEPARTMENT OF COMMERCE National Oceanic and Atmospheric Administration
RIN 0648–XY36
Endangered and Threatened Species; Initiation of 5–Year Review of the Eastern Distinct Population Segment of the Steller Sea Lion
SUMMARY: NMFS published a notice in the Federal Register on June 29, 2010, announcing the initiation of a 5–year review of the eastern Distinct Population Segment (DPS) of the Steller Sea Lion (Eumetopias jubatus) under the Endangered Species Act of 1973, as amended (ESA) and requesting information related to that review. A notice correcting the email address and fax number to which comments and information should be sent was published July 7, 2010. Written comments were due by August 30, 2010. NMFS has decided to reopen the public comment period for an additional 45 days, to October 14, 2010. DATES: The public comment period for this action has been reopened for an additional 45 days, to October 14, 2010. Written comments and information must be received no later than October 14, 2010.  See also, NOAA's prior notice, 75 Fed. Reg. 37385 (Tuesday, June 29, 2010), and the Steller's sea lion management information pages published by NOAA's Alaska Regional Office. Photo below by JJ Vollenweider, NOAA Fisheries.

StellerSeaLions.jpg
In 2001-2003, a complex suite of regulations to manage Steller sea lion and various groundfish fishery interactions were enacted, and a description of these regulations can be found on the National Marine Fisheries Service/Alaska Region website.

NOAA rejects petition to list tiger rockfish and China rockfish

08/30/2010

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75 Fed. Reg. 52929 / Monday, August 30, 2010 / Notices
DEPARTMENT OF COMMERCE / National Oceanic and Atmospheric Administration
Docket No. 100813341–0341–01 / RIN 0648–XX56
Endangered and Threatened Wildlife and Plants; Notice of 90–Day Finding for a Petition to List Georgia Basin Populations of China Rockfish and Tiger Rockfish as Endangered or Threatened
SUMMARY: We (NMFS) received a petition to list Georgia Basin populations of China rockfish (Sebastes nebulosus) and tiger rockfish (S. nigrocinctus) as endangered or threatened species under the Endangered Species Act (ESA). We  determine that the petition does not present substantial evidence to indicate that the petitioned action may be warranted.

TigerRockfish.jpg
Tiger rockfish are solitary, sometimes territorial, and are known to prey upon caridean shrimp, crabs (particularly rock crabs), amphipods and small fishes like herring and juvenile rockfish in the Gulf of Alaska . This species is a generalized feeder that depends on currents bringing food items near its home territory -- often associated with "wall" habitat..  Tiger rockfish are commonly found in caves along undersea cliffs or on the sea floor, generally in high relief areas with strong currents.  Photo from the Northwest Fisheries Science Center.

EXCERPT: The petition points to the fact that there are few observations of China rockfish and tiger rockfish in these surveys. The petition provides no analysis to explain how these surveys can be interpreted to indicate either a low abundance level or a declining trend in abundance, either of which might be evidence of risk to the species. To the contrary, the petitioner acknowledges that adults of these two species tend to remain hidden in rocky habitats, which could make them difficult for SCUBA divers to observe...  We agree with the petitioner’s assertion that China rockfish and tiger rockfish typically utilize a small home range and experience low productivity. However, as the petitioner acknowledges, a small home range causes individuals to remain hidden in rocky habitat, where they may experience lower mortality, as a result of less frequent exposure to predators. Low productivity can be a risk factor in some instances. However, low productivity is not an indication of declining abundance (another risk factor) since it reflects a life history trade-off between fecundity and life span.


FWS announces draft ocelot recovery plan

08/30/2010

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75 Fed. Reg. 52547 / Thursday, August 26, 2010 / Notices
DEPARTMENT OF THE INTERIOR / Fish and Wildlife Service
FWS–R2–ES–2010–N167; 20124–1113–0000–C2
Endangered and Threatened Wildlife and Plants; Draft Ocelot (LEOPARDUS PARDALIS) Recovery Plan, First Revision
SUMMARY: We, the U.S. Fish and Wildlife Service (Service), announce the availability of the Draft Ocelot (Leopardus pardalis) Recovery Plan, First Revision. We request review and comment from the public on this draft revised recovery plan. We will also accept any new information on the status of the ocelot throughout its range to assist in finalizing the revised recovery plan. DATES: To ensure consideration, we must receive any comments no later than October 25, 2010.

OcelotEsperanza.JPG
The ocelot requires dense vegetation (more than 75 percent canopy cover), with 95 percent cover preferred in Texas. Habitats used by the ocelot throughout its range vary from tropical rainforest, pine forest, gallery forest, riparian forest, semideciduous forest, and dry tropical forest, to savanna, shrublands, and marshlands. Contiguous areas of vegetation are necessary for ocelot dispersal. In south Texas, 2 remaining ocelot populations of less than 25 total known individuals inhabit dense thornscrub communities on the Lower Rio Grande Valley and Laguna Atascosa National Wildlife Refuges, as well as on private lands. Its prey consists primarily of rabbits, rodents, birds, and lizards.  In November 2009, an ocelot was documented in Arizona with the use of camera traps for the first time since 1964, when the last known ocelot in Arizona was legally shot.  For more information, visit the link above, or the 1990 recovery plan. Photo above of Esperanza, the first female on the Laguna Atascosa National Wildlife Refuge ever be photographed with a kitten!.  According to Friends of South Texas National Wildlife Refuges, she's actually had three kittens since Refuge biologists first captured her in February 2008.



FWS proposes experimental population of whooping cranes in Louisiana

08/25/2010

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75 Fed. Reg. 51223 / Vol. 75, No. 160 /Thursday, August 19, 2010 / Proposed Rules
DEPARTMENT OF THE INTERIOR Fish and Wildlife Service
50 CFR Part 17 / Docket No. FWS–R4–ES–2010–0057 / 92220–1113–0000–C3 / RIN 1018–AX23
Endangered and Threatened Wildlife and Plants; Establishment of a Nonessential Experimental Population of Endangered Whooping Cranes in Southwestern Louisiana

SUMMARY: We, the U.S. Fish and Wildlife Service (Service), propose to reintroduce whooping cranes (Grus americana), a federally listed endangered species, into habitat in its historic range in southwestern Louisiana with the intent to establish a nonmigratory flock that lives and breeds in the wetlands, marshes, and prairies there. We propose to classify the flock as a nonessential experimental population (NEP) according to section 10(j) of the Endangered Species Act of 1973 (Act), as amended. Releases will be within the historic breeding area in southwestern Louisiana near White Lake in Vermilion Parish. This proposed rule provides a plan for establishing the NEP and provides for allowable legal incidental take of whooping cranes within the defined NEP area. The objectives of the reintroduction are to advance recovery of the endangered whooping crane. No conflicts are envisioned between the reintroduction and any existing or anticipated Federal, State, Tribal, local government, or private actions such as oil/gas exploration and extraction, aquacultural practices, agricultural practices, pesticide application, water management, construction, recreation, trapping, or hunting. DATES: We request that you send us comments on the proposed rule and the draft environmental assessment by the close of business on October 18, 2010, or at the public hearings. We will hold public informational open houses from 6 p.m. to 7 p.m., followed by public hearings from 7 p.m. to 9 p.m., on September 15 and 16, 2010, at the locations within the proposed NEP area identified in the ADDRESSES section.

WhoopingCraneFWS.jpg
The whooping crane is a member of the family Gruidae (cranes). It is the tallest bird in North America; males approach 1.5 meters (m) (5 feet (ft)) tall. Adults are potentially long-lived. Current estimates suggest a maximum longevity in the wild of 32 years. Mating is characterized by monogamous lifelong pair bonds.   Whooping cranes historically occurred in Louisiana in both a resident, nonmigratory flock and a migratory flock that wintered in Louisiana. Establishing a Louisiana nonmigratory flock has become a species recovery priority.  Image courtesy  of Whooping Crane Eastern Partnership founding member Operation Migration Inc., available at North Florida Ecological Services Office.

EXCERPT RE: SPECIES STATUS: Whooping cranes currently exist in three wild populations and within a captive breeding population at 12 locations. The first population, and the only self-sustaining natural wild population, nests in the Northwest Territories and adjacent areas of Alberta, Canada, primarily within the boundaries of Wood Buffalo National Park...   Another population of wild whooping cranes is referred to as the Eastern Migratory Population (EMP). The EMP has been established through reintroduction and currently numbers 97. During the 2009 spring breeding season, all 12 first nests of the season were abandoned, as have all first nests during the previous years. From 2005–2009, there have been a total of 41 nests (including 7 renests); only 2 renests have hatched chicks, and only 1 chick has been successfully fledged...  The (third) population, the Florida nonmigratory population, is found in the Kissimmee Prairie area of central Florida. Between 1993 and 2004, 289 captive-born, isolation reared whooping cranes were released into Osceola, Lake, and Polk Counties in an effort to establish this nonmigratory flock. The last releases took place in the winter of 2004–2005. Since the first nest attempt in 1999, there have been a total of 72 nest attempts, 33 chicks hatched and only 10 chicks successfully fledged. Problems with survival and reproduction, both of which have been complicated by drought, are considered major challenges for this flock...  In 2008, scientists from Florida FWC and major project partners conducted a workshop to assess the current status and potential for success of establishing the resident, nonmigratory population of whooping cranes in Florida. The Recovery Team used the workshop findings and other considerations, and in 2009 recommended there be no further releases into the Florida flock. The water regimes produced by periodic droughts in Florida make it extremely unlikely that reproduction in wildhatched Florida whooping cranes will ever achieve production rates adequate for success.

EXCERPT RE: REINTRODUCTION: We propose to initially gentle-release four to eight juvenile whooping cranes in the White Lake Wetlands Conservation Area in Vermilion Parish, Louisiana. These birds will have been captive-reared at one of the captive rearing facilities, then transferred to facilities at the Louisiana release site, and conditioned for wild release to increase post-release survival and adaptability to wild foods. Before release, the cranes will be banded for identification purposes, tagged with radio and/or GPS solar-powered satellite transmitters at release, and monitored to discern movements, habitat use, other behavior, and survival. Numbers of birds available for release will depend on production at captive-propagation facilities and the future need for additional releases into the EMP. The Species Survival Center in New Orleans has received Federal funding to construct a hatchery and chick- rearing facility so that whooping cranes produced for release in this project could be hatched and reared in Louisiana.




FWS will not delist the Stephen's Kangaroo Rat

08/25/2010

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51204 Federal Register / Vol. 75, No. 160 / Thursday, August 19, 2010 / Proposed Rules
DEPARTMENT OF THE INTERIOR Fish and Wildlife Service
50 CFR Part 17 / Docket No. FWS–R8–ES–2010–0052; 92220–1113–0000C5
Endangered and Threatened Wildlife and Plants; 12-Month Finding on a Petition To Remove the Stephens’ Kangaroo Rat From the Federal List of  Endangered and Threatened Wildlife

SUMMARY: We, the U.S. Fish and Wildlife Service (Service), announce a 12-month finding on a petition to remove the Stephens’ kangaroo rat (Dipodomys stephensi) from the Federal List of Endangered and Threatened Wildlife under the Endangered Species Act of  1973, as amended. After a review of the best available scientific and commercial information, we find that delisting the Stephens’ kangaroo rat is not warranted at this time. However, we  ask the public to submit to us any new information that becomes available concerning the threats to the Stephens’ kangaroo rat or its habitat at any time. This information will help us monitor and encourage the conservation of this species. DATES: The finding announced in this document was made on August 19, 2010.

StephensKangarooRat.jpeg
Kangaroo rats are burrow-dwelling, seed-eating animals that inhabit arid and grassy habitats in western North America. They are characterized by furlined, external cheek pouches used for transporting seeds; large hind legs for rapid, bi-pedal, saltatorial (leaping) locomotion; relatively small front legs; long tails; and large heads. Stephens’ kangaroo rat typically occurs at lower elevations in flat or gently rolling grasslands of the dry inland valleys west of the Peninsular Ranges of southern California, in western Riverside and northern and central San Diego Counties.  Photo by Nicole Peltier from Paw-Talk.

EXCERPT: The primary threats identified in the 1988 listing rule (53 FR 38465), habitat destruction from urban and agricultural development resulting in isolated habitat patches, has been largely ameliorated through the implementation and design of the core reserve system (through an HCP), through ongoing land acquisitions and easements, and with other conservation plans and efforts. Significant areas of habitat have been protected in western Riverside County and San Diego Counties since the species was listed. Populations in San Diego County that are on privately held lands may enhance the survival and recovery of the species, including some habitat under permanent conservation supporting the Ramona Grasslands population. The Stephens’ kangaroo rat population at Camp Pendleton/Detachment Fallbrook in San Diego County is covered by active INRMPs that include actions to provide for the long-term conservation of the Stephens’ kangaroo rat on Federal military lands. In spite of these conservation gains, significant threats to Stephens’ kangaroo rat in Riverside and San Diego Counties remain.
   There has been loss,fragmentation, and degradation of Stephens’ kangaroo rat habitat in the past, and we have identified information indicating that Stephens’ kangaroo rat habitat continues to be threatened by fragmentation and degradation associated with urban development (see Factor A) in western Riverside and San Diego Counties. This habitat degradation is associated with the lack of boundary security at some of the core reserves, which allows trespass, OHV use, and trash dumping, and the lack of appropriate management (such as fire suppression) to prevent invasive species or succession to shrub-dominated communities. Lands currently or historically dedicated to agricultural activities likely continue to serve as a source of invasive, nonnative plants. Encroachment of nonnative grasses and succession to more shrubdominated communities threaten Stephens’ kangaroo rat habitat throughout the species’ range by filling open spaces and reducing the presence of forbs (Factor A).
   While existing data are not adequate to estimate population size, within the existing core reserves in western Riverside County or in San Diego County, surveys indicate that the amount of Stephens’ kangaroo rat occupied habitat may be in decline in localities within both counties. Latest survey data indicate that Camp Pendleton, Detachment Fallbrook, and Lake Henshaw, in addition to previous declines in habitat populations, may have suffered declines in the amount of Stephens’ kangaroo rat occupied habitat. Predation (Factor C) and rodenticide (Factor E) continue to threaten the species and may contribute additively to other threats affecting this species. Existing regulatory mechanisms, absent the protections of the Act, provide insufficient certainty (Factor D) that efforts needed to address long-term conservation of the species will be implemented or that they will be effective in reducing the level of threats to the Stephens’ kangaroo rat throughout its range. Therefore, we find that, in absence of the Act, the existing regulatory mechanisms are not adequate to conserve Stephens’ kangaroo rat throughout its range in the foreseeable future.
   In conclusion, we have carefully assessed the best scientific and commercial information available regarding the past, present, and future threats faced by this species. Our review of the information pertaining to the five threat factors does not support a conclusion that the threats have been sufficiently removed or their imminence, intensity, or magnitude have been reduced to the extent that the species no longer requires the protections of the Act. Therefore, we find the Stephens’ kangaroo rat is in danger of extinction, or likely to become so within the foreseeable future, throughout all or a significant portion of its range and does not warrant delisting at this time.

KEITHINKING: The decision was disappointing for the Pacific Legal Foundation, which has been engaged in years of litigation to force a decision on its petition to delist the species.  In a press release, PLF stated: "Keeping the rat on the endangered list can only endanger jobs and the economy, because it imposes unnecessary restrictions on productive land use.   We'll be reviewing this troubling decision to determine whether more litigation should be the next step in PLF's fight for jobs, the economy and a prudent, balanced approach to environmental regulations." For more on their perspective, visit PLF Sentry.  Alternatively, the Center for Biological Diversity emphasized the continued loss of species habitat, and the need to protect the species from PLF's vision of economic development. See CBD Press Release.

FWS removes listed status of Utah valvata snail in light of new data showing species abundance

08/25/2010

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75 Fed. Reg. 52272 / Vol. 75, No. 164 / Wednesday, August 25, 2010 / Rules and Regulations
DEPARTMENT OF THE INTERIOR Fish and Wildlife Service
50 CFR Part 17 / Docket No. FWS–R1–ES–2008–0084; 92220–1113–0000–C6 / RIN 1018–AW16
Endangered and Threatened Wildlife and Plants; Removal of the Utah (Desert) Valvata Snail From the Federal List of Endangered and Threatened Wildlife

SUMMARY: Under the authority of the Endangered Species Act of 1973, as amended (Act), we, the U.S. Fish and Wildlife Service (Service), are removing the Utah (desert) valvata snail (Valvata utahensis) from the Federal List of Endangered and Threatened Wildlife (List). Based on a thorough review of the best available scientific and commercial data, we determined that the Utah valvata snail is more widespread and occurs in a greater variety of habitats in the Snake River than known at the time of listing in 1992. We now know the Utah valvata snail is not limited to areas of cold-water springs or spring outflows; rather, it persists in a variety of aquatic habitats, including cold-water springs,  spring creeks and tributaries, the mainstem Snake River and associated  tributary stream habitats, and reservoirs influenced by dam operations. Given our current understanding of the species’ habitat requirements and threats, the species does not meet the definition of an endangered or threatened species under the Act. Therefore, we are removing the Utah valvata snail from the List, thereby removing all protections provided by the Act.

EXCERPT: As required by the Act, we considered potential threat factors to assess whether the Utah valvata snail is endangered or threatened throughout its range. Information collected since the species’ listing in 1992 indicates that the Utah valvata snail is widely distributed and occurs in a variety of ecological settings over a 255-mile range of the Snake River. Much of the Snake River within the range of the Utah valvata is influenced by seasonal dam operations for hydroelectric or agricultural purposes, yet the species persists in these varied mainstem Snake River systems, including impounded reservoir habitats (e.g., Lake Walcott and American Falls reservoirs). None of the  threats that we identified in the 1992 listing determination appear to be significant to the species (individually or in combination) in light of our current understanding of its distribution and life history; nor have we identified  any significant new threats to the species. Therefore, we find that the Utah valvata snail is not in danger of extinction throughout its range, nor is it likely to become so in the foreseeable future. The Service has determined that the original data for classification of the Utah valvata snail used in 1992 were in error. However, it is important to note that the original data for classification constituted the best scientific and commercial data  available at the time and were in error only in the sense that they were incomplete when viewed in context of the data now available.

In response to petition, FWS considering listing of Oklahoma grass pink orchid

08/25/2010

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75 Fed. Reg. 51969 / Vol. 75, No. 163 / Tuesday, August 24, 2010 / Proposed Rules
DEPARTMENT OF THE INTERIOR Fish and Wildlife Service
50 CFR Part 17 / Docket No. FWS-R3-ES-2010-0034 / MO 92201-0-0008
Endangered and Threatened Wildlife and Plants; 90-Day Finding on a Petition to List the Oklahoma Grass Pink Orchid as Endangered or Threatened

SUMMARY: We, the U.S. Fish and Wildlife Service (Service), announce a 90–day finding on a petition to list Calopogon oklahomensis (Oklahoma grass pink orchid) as endangered or threatened under the Endangered Species Act of 1973, as amended (Act). Based on our review, we find that the petition presents substantial scientific or commercial information indicating that listing the plant species, C. oklahomensis, as endangered or threatened may be warranted. Therefore, with the publication of this notice, we are initiating a review of the status of the species to determine if listing C. oklahomensis as endangered or threatened is warranted. To ensure that this status review is comprehensive, we are requesting scientific and commercial data and other information regarding this species. Based on the status review, we will issue a 12–month finding on the petition, which will address whether the petitioned action is warranted, as provided in section 4(b)(3)(B) of the Act.

CalopogonOklahomensis.jpg
Calopogon oklahomensis has a forked corm (a modified underground stem), with the new corm at the base of the leaf and the inflorescence (a branching stem with flowers) rapidly growing distally at the time of anthesis (the period from flowering to fruiting). The flower buds are deeply grooved longitudinally, waxy and shiny, with elongated acuminate apices (narrowing to a point at the tip). The flowers are fragrant and open in succession.  Calopogon oklahomensis occupies moist, loamy prairies, savannas, and sandy woodlands from central Minnesota southward to Texas, including the States of Wisconsin, Iowa, Illinois, Indiana, Kansas, Missouri, Tennessee, Arkansas, Oklahoma, Mississippi, Louisiana, and Florida, with a few scattered populations further east in South Carolina, Georgia, and Alabama. C. oklahomensis appears to prefer moist to seasonally dry-mesic prairies, prairiehaymeadows, savannas and open woodlands, avoiding the wetter habitats preferred by other species of Calopogon. This species appears to thrive under a frequent burning regime or haymeadow management where most or all of the above ground vegetation is effectively removed once every 1 to 2 years, with  subsequent flowering within a year after the last burn or haymowing.  Plant photo taken at at Roth Prairie in
central Arkansas, available online from Tennessee Native Plant Society

FWS lists foreign bird species, but not Utah's Brian Head Mountain Snail

08/19/2010

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75 Fed. Reg. 50814 / Vol. 75, No. 158 / Tuesday, August 17, 2010 / Rules and Regulations
DEPARTMENT OF THE INTERIOR Fish and Wildlife Service
50 CFR Part 17 / Docket No. FWS–R9–ES–2009–0092; 90100–16601–FLA–B6 / RIN 1018–AV76
Endangered and Threatened Wildlife and Plants; Listing Three Foreign Bird Species From Latin America and the Caribbean as Endangered Throughout Their Range

SUMMARY: We, the U.S. Fish and Wildlife Service (Service), determine endangered status for three species of birds from Latin America and the Caribbean—the Andean flamingo  (Phoenicoparrus andinus), the Chilean woodstar (Eulidia yarrellii), and the St. Lucia forest thrush (Cichlherminia lherminieri sanctaeluciae)—under the Endangered Species Act of 1973, as amended (Act). DATES: This final rule is effective September 16, 2010.

AndeanFlamingoReichie.jpg
The Andean flamingo’s entire life cycle relies on the  availability of networks of shallow saline wetlands (salars and lagunas) at low, medium, and high altitudes that are characteristic throughout its range in Argentina, Bolivia, Chile, and Peru.  Photo by Steffen Reichlefrom Exploring Bolivia's Biodiversity.

EXCERPT:
   Status Determination for the Andean Flamingo.  The Andean flamingo is colonial, feeding and breeding in flocks, and is the rarest of all six flamingo species worldwide. Experts consider that the more dispersed nature of the species at smaller nesting sites has inhibited reproduction in the species. The Andean flamingo underwent a severe population decline in the last few decades, from a conservative estimate of 50,000 to 100,000 in the early 1980s to a current estimate of 34,000. In the past 20 years, nesting sites and breeding has declined with increased habitat alteration (Factor A), overutilization (Factor B), disease and predation (Factor C), as well as increased human disturbance and an ongoing drought (Factor E)... Several manmade and natural factors are having a negative impact on the flamingo’s persistence in the wild. These factors include mining activities and resultant pollution, increasing human population and water usage, hunting and egg collection, tourism, predation, human disturbance, and drought conditions. Mining occurs at many of the wetlands that the Andean flamingo depends upon for habitat. The threats from mining include direct habitat destruction, water pollution, water extraction, and disturbance (Factors A and E). Hunting and egg collecting reduce the number of individuals in the population and exacerbate the species’ poor breeding success and low recruitment rate (Factor B). In combination with these habitat threats, the altiplano region is undergoing a long-term drought, which is impacting the availability and quality of wetlands for feeding, breeding, and overwintering (Factor E). Increased tourism at the wetlands is taxing limited water supplies, causing further water contamination from trash and sewage, and increasing habitat disturbance from human presence (Factors A and B). Infrastructure to support mining and tourism destroys and increases access to Andean flamingo habitats, facilitating hunting, egg collecting, and human influx, along with increased pollution, water use, and disturbance (Factors A, B, and E). Predation removes potentially reproductive adults  from the breeding pool, disrupts mating pairs, and exacerbates the species’ already poor breeding success and is facilitated by increased access to wetlands and the ongoing drought (Factors A, B, and E). Many wetlands within protected areas continue to undergo activities that destroy habitat or remove individuals from the population (including hunting and egg collecting), such that the regulatory mechanisms are inadequate to mitigate the threats to the species and its habitat (Factor D). The magnitude of the threats is exacerbated by the species’ recent and drastic reduction in numbers, poor breeding success and recruitment, and the species’ reliance on only a few wetlands for the majority of its reproductive output.
   Status Determination for the Chilean Woodstar.  The species is currently at risk throughout  all  of its range due to a number of immediate and ongoing threats. The Chilean woodstar is restricted to two river valleys, where there has been extensive modification of its primary habitat. It is threatened by agricultural practices, in particular the use of pesticides and, to  a lesser extent, high-pressure spraying of olive trees to remove mold, as well as competition from the more aggressive Peruvian sheartail. The magnitude of these threats is exacerbated by the species’ restricted range, only one known breeding site, low recruitment rate, and extremely small population size. An insect outbreak causing increased use of toxic pesticides in agricultural fields, a series of catastrophic events, or other detrimental interactions between environmental and demographic factors could result in the rapid extinction of the Chilean woodstar.
   Status Determination for the St. Lucia Forest Thrush.  The subspecies is currently at risk throughout all of its range due to ongoing threats of habitat destruction and modification (Factor A), lack of near- and long-term viability associated with the thrush’s presumed small population size (Factor E), and random, naturally occurring events such as volcanic activity, tropical storms, and hurricanes (Factor E).

***

75 Fed. Reg. 50739 / Vol. 75, No. 158 / Tuesday, August 17, 2010 / Proposed Rules
DEPARTMENT OF THE INTERIOR / Fish and Wildlife Service
50 CFR Part 17 / Docket No. FWS-R6-ES-2010-0058 / MO 92210-0-0008
Endangered and Threatened Wildlife and Plants; 90-Day Finding on a Petition to List Brian Head Mountainsnail as Endangered or Threatened with Critical Habitat

SUMMARY: We, the U.S. Fish and Wildlife Service (Service), announce a 90–day finding on a petition to list the Brian Head mountainsnail (Oreohelix parawanensis) as endangered or  threatened under the Endangered Species Act of 1973 (Act), as amended. Based on our review, we find that the petition does not present substantial information indicating that listing the  species may be warranted. However, we ask the public to submit to us any new  information that becomes available concerning the status of, or threats to, the mountainsnail or its habitat at any time. This information will help us monitor and encourage the conservation of this species. DATES: The finding announced in this document was made on August 17, 2010.

BrianHeadMountainSnail.jpg
The Brian Head mountainsnail is reported from Iron County, Utah. The species exists as a localized population at a rock slide on the southwest slope of Brian Head Peak, above timberline at approximately 3,350 meters (11,000 feet).  The rock slide is located within a mountain shrub habitat type that is the focus of conservation by the State of Utah.  Photo by Bill Bosworth, available at Utah Division of Wildlife Resources.


Two plants, two stories: sole specimen of soon-to-be-listed San Francisco manzanita left the Golden Gate Bridge for the Presido, but once rare Tennessee Purple Coneflower now recovering and soon to be delisted

08/12/2010

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75 Fed. Reg. 48294 / Vol. 75, No. 153 / Tuesday, August 10, 2010 / Proposed Rules
DEPARTMENT OF THE INTERIOR Fish and Wildlife Service
50 CFR Part 17 / Docket No. FWS-R8-ES-2010-0049 / MO-92210-0-0008-B2
Endangered and Threatened Wildlife and Plants; 90-Day Finding on a Petition to List Arctostaphylos franciscana as Endangered with Critical Habitat

SUMMARY: We, the U.S. Fish and Wildlife Service (Service), announce a 90-day finding on a petition to list Arctostaphylos franciscana (Franciscan manzanita or San Francisco manzanita) as endangered under the Endangered Species Act of 1973, as amended, (Act) and to designate critical habitat. Based on our review, we find that the petition presents substantial scientific or commercial information indicating that listing this species may be warranted. Therefore, with the publication of this notice, we are initiating a review of the status  of the species to determine if listing the species is warranted. To ensure that the status review is comprehensive, we are requesting scientific and commercial data and other information regarding this species. Based on the status review, we will issue a 12–month finding on the petition, which will address whether the petitioned action is warranted, as provided in section 4(b)(3)(B) of the Act.

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Arctostaphylos franciscana is a low, spreading to ascending evergreen shrub in the heath family (Ericaceae) that may reach 2 or 3 feet in height when mature. Arctostaphylos franciscana is endemic (native and restricted) to the San Francisco peninsula, California, and historically occurred in areas with serpentine soils and bedrock outcrops.  The species has been reduced to the single remaining wild plant because of loss of its original habitat at all other known locations, and that single plant was recently relocated to the Presidio.  Photo by Michael Chasse / National Park Service, available online at Bay Nature.

EXCERPT RE: RELOCATING A ONE-OF-A-KIND.  Prior to October, 2009, Arctostaphylos franciscana had not been seen in the wild since 1947.  It was originally known from three locations: the Masonic and Laurel Hill Cemeteries in San Francisco’s Richmond district, and Mount Davidson in the south-central part of San Francisco...  In October 2009, an ecologist identified a plant growing in a concrete bound median strip along Doyle Drive in the Presidio as Arctostaphylos franciscana. The plant’s location was directly in the footprint of a roadway improvement project designed to upgrade the seismic and structural integrity of the south access to the Golden Gate Bridge. The identification of the plant as A. franciscana has since been confirmed with 95 percent confidence based on morphological characteristics. Additional tests of ploidy level indicate that the plant is diploid, consistent with A. franciscana.  Preliminary results from molecular genetic data also increase the confidence that the plant belongs to A. franciscana, although genetic analysis shows evidence that the plant is a descendant of a distant hybridization event, a situation that is thought to be quite common in the genus. Based on the best available scientific information we consider the species to be A. franciscana.

Several agencies, including the Service, established an MOA and conservation plan for the species. The conservation partners concluded it was not feasible to leave the plant undisturbed at its original site, due to impacts on public safety and to cultural resources related to a potential curtailment or redesign of the roadway improvement project.  The conservation plan recommended that the plant be moved to a new site within the Presidio. The plan included measures to take cuttings from the plant, both from non-rooted stems and from layering stems (stems which have rooted at their leaf nodes), for vegetative propagation.  The plan also called for collection and eventual propagation of seeds (including seeds in the soil around the plant’s original location), and for genetic testing of resulting plants (since seeds fertilized in the wild would likely produce hybrids). Additionally, because the roots of most Arctostaphylos individuals establish a mutually beneficial association with species of mycorrhyzal fungus living in the soil, the conservation plan established means by which the soil for propagating cuttings and seeds should be inoculated with spores from such fungi. The plan also evaluated potential translocation sites, established procedures for preparation of the new site and for the translocation itself, and called for management and monitoring (both short- and long-term) of the translocated plant and all newly propagated plants, with the goal of eventually establishing self-sustaining populations of the species in the wild.  The translocation of the Arctostaphylos franciscana plant to an active native plant management area of the Presidio was accomplished, apparently successfully and according to plan, on January 23, 2010. Subsequent monitoring reports indicate the plant continues to do well at its new location

LINKS: "The Presidio's Miracle Manzanita" by Bay Nature

***

75 Fed. Reg. 48896 / Vol. 75, No. 155 / Thursday, August 12, 2010 / Proposed Rules
DEPARTMENT OF THE INTERIOR Fish and Wildlife Service
50 CFR Part 17 / Docket No. FWS–R4–ES–2010–0059; 92220–1113–0000–C6 / RIN 1018–AW26
Endangered and Threatened Wildlife and Plants; Removing the Tennessee Purple Coneflower From the Federal List of Endangered and Threatened Plants

SUMMARY: Under the authority of the Endangered Species Act of 1973, as amended (Act), we, the U.S. Fish and Wildlife Service (Service), propose to remove the plant Echinacea tennesseensis (Tennessee purple coneflower) from the Federal List of Endangered and Threatened Plants due to recovery. This action is based on a thorough review of the best available scientific and commercial data, which indicate that this species’ status has improved to the point that E. tennesseensis is not likely to become endangered within the foreseeable future throughout all or a significant portion of its range. Our review of the status of this species shows that all of the threats to the species have been eliminated or significantly reduced, adequate regulatory mechanisms exist, and populations are  stable. We also announce the availability of the draft post-delisting monitoring plan. This proposed rule completes the 5-year status review for the species, initiated on September 21, 2007.  

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A member of the sunflower family (Asteraceae), Echinacea tennesseensis is a perennial herb with a long and fusiform (i.e., thickened toward the middle and tapered towards either end), blackened root. In late summer, the species bears showy purple flower heads on one-to-many hairy branches.  The flowers of this plant  nearly always face east, and the plant prefers full sun and well–drained average soil.  Photo from Tennessee DOT

EXCERPT: The Service first approved the Tennessee Coneflower Recovery Plan on February 14, 1983 and revised it on November 14, 1989.  According to the recovery plan, Echinacea tennesseensis will be considered recovered when there are at least five secure wild populations, each with three self-sustaining colonies of at least a minimal size. A colony will be considered self-sustaining when there are two juvenile plants for every flowering one. Minimal size for each colony is 15 percent cover of flowers over 669 square meters. Downlisting (reclassification from endangered to threatened) will be considered when each of the five secure wild populations has two colonies.  There were an estimated total of 146,000 individual plants in 1989. Recovery efforts have secured habitat for 19 colonies that are self-sustaining and distributed among six geographically defined populations. All but 1 of the 19 introduced colonies have greater than 100 flowering stems, and the estimated total number of plants in these colonies ranged from 866 to 52,997.  These 19 secured, self-sustaining colonies accounted for an estimated 761,055 individual plants in 2005, or approximately 83 percent of the total species’ distribution; colonies that we do not consider secure accounted for 159,224 individual plants, or approximately 17 percent of the total species’ distribution.  



Humans vs. species? Hunting of tigers prevents delisting, while wind farm striking of Indiana bats necessitates permits

08/12/2010

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75 Fed. Reg. 48914 / Vol. 75, No. 155 / Thursday, August 12, 2010 / Proposed Rules
DEPARTMENT OF THE INTERIOR Fish and Wildlife Service
50 CFR Part 17 / FWS–R9–IA–2008–0121; 96100–1671–0000–B6
Endangered and Threatened Wildlife and Plants; 90–Day Finding on a Petition to Delist the Tiger (Panthera tigris)

SUMMARY: We, the U.S. Fish and Wildlife Service (Service), announce a 90-day finding on a petition to remove the tiger (Panthera tigris) from the List of Endangered and Threatened Wildlife under the Endangered Species Act of 1973, as amended. We find that the petition does not present substantial scientific or commercial information indicating that removing the species from the List of Endangered and Threatened Wildlife may be warranted. Therefore, we will not initiate a status review in response to this petition. We ask the public to submit to us any new information that becomes available concerning the status of the tiger or threats to it or its habitat at any time. This information will help us monitor and encourage the conservation of this species.

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Tigers originally ranged from eastern Turkey to southeastern Siberia and the Malay Peninsula, Sumatra, Java, and Bali. The current geographic distribution is greatly reduced, and tigers have been exterminated from most of their former geographic range. At the end of the 19th century, there may have been as many as 100,000 tigers in the wild. Currently, tiger populations are smaller, increasingly more isolated, and progressively more fragmented than before. Based on estimates by species experts, extant tiger populations total about 7,700 individuals in the wild and occupy only about 7 percent of their original range. Photo from Wikimedia.

EXCERPT RE: HUMANS AS PREDATORS: Tigers, which hunt primarily at night, mainly prey upon larger mammals, especially ungulates. Domestic livestock, such as cattle, water buffalos, goats, and dogs, are also frequently taken by tigers. These attacks are a major cause of conflicts with local farmers. Tigers also attack and kill humans, especially in India. Conservation threats to tigers include being poisoned, shot, trapped, and snared, as well as loss or modification of habitat and reductions to natural prey populations.  These threats are widespread and ongoing. Recent reports suggest that natural mortality of tigers is being replaced by mortality due to man. Historically, bears, wild pigs, and other large mammals were major predators of tigers; today, tigers increasingly are being killed by human hunters. As a result, tiger populations in most areas are greatly reduced due to human activities.
    International trade in tigers has been a source of concern to conservationists and species experts for many years. Big cats already showed signs of becoming rare in the 1960s. Three tigers were imported into the United States in 1968. During 1968–1972, 17 living tigers were imported into the United States. Following the ratification of CITES in the United States, during 1979–1980, a total of 103 live tigers were imported according to Service records. Overall, a total of 317 live Appendix I tigers were reported in international trade during 1979–1980.  More recently in the United States, more than 130 live tigers were either imported, exported, or re-exported legally during 2004–2006 (purpose of  transaction: zoos, circuses and traveling exhibitions, and breeding in captivity. About 6,000 illegally obtained items during that same time period were either abandoned at the port of entry or seized by U.S. law enforcement officials (primarily skins, teeth, trophies, and articles used for traditional medicine).

***

75 Fed. Reg. 48359 / Vol. 75, No. 153 / Tuesday, August 10, 2010 / Notices
DEPARTMENT OF THE INTERIOR Fish and Wildlife Service
FWS–R3–ES–2010–N140; 30120–1113–0000–F6
Endangered and Threatened Wildlife and Plants; Indiana Bat; Notice of Intent To Prepare an Environmental Impact Statement on a Proposed Habitat Conservation Plan and Incidental Take Permit

SUMMARY: We, the U.S. Fish and Wildlife Service (Service), intend to prepare an Environmental Impact Statement (EIS) on a proposed Habitat Conservation Plan (HCP) and Incidental Take Permit (ITP) for the Indiana Bat (Myotis sodalis) at a wind power project in Adair, Sullivan, and Putnam Counties, Missouri (Project). Construction and operation of the Project has the potential to cause the take of Indiana bat, an endangered species, protected by the Endangered Species Act (ESA). We provide this notice to advise other agencies, tribes, and the public of our intentions, and to obtain suggestions and information on the scope of review under NEPA (National Environmental Policy Act), as well as issues to consider during the planning process.

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The range of the Indiana bat extends from eastern Vermont, western Oklahoma, southern Wisconsin, and northern Florida. Indiana bats migrate between their summer forested ranges and winter hibernacula, which typically are climatically stable caves and mines. During summer months, they forage for insects along streams, in riparian forests and floodplains, and in upland forests and low open areas. Males roost individually or in small groups throughout the range, preferring areas near hibernacula. Females, forming larger maternity colonies of 50 to 100, roost in dead or dying trees or living trees with broken and flaking bark.  Photo above of a cluster of Indiana bats hibernating on a cave ceiling, by USFWS; Andrew King

EXCERPT: There are no known hibernacula in the Project area or nearby. However, maternity roosts and maternity colonies have been identified proximate to and within the Project area. The Service and the Applicant have determined that the development and operation of the Project, in proximity to summer maternity colonies and spring and fall migratory flight paths, may affect the Indiana bat and their habitat, possibly resulting in the involuntary take of Indiana bats.

KEITHINKING: Wind farms are becoming big business for rural Missouri.  Enough so that the wind industry is developing regional HCPs.  Clearly, this applicant has learned its lesson from the decision in Animal Welfare Institute v. Beech Ridge Energy LLC, Case No. 09-1519-RWT, (D. Md.), where a wind energy company failed to obtain an ITP, and the West Virginia project was stopped because of concerns over Indiana bats.  See, windaction.org or read the actual opinion.

Federal Judge, reversing FWS rule, says Northern Rocky Mountain wolves are one population, so Wyoming cannot be managed differently from Idaho and Montana

08/10/2010

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Defenders of Wildlife v. Salazar, CV 09-77-M-DWM, CV 09-82-M-DWM (consolidated)(D. Montana, Aug. 10, 2010)(Judge Donald Molloy)

RULING: After reviewing the Final Rule, the administrative record, the arguments submitted by the parties, the statutes and relevant case law, the Court finds:
-- The Endangered Species Act does not allow the U.S. Fish & Wildlife Service to list only part of a "species" as endangered, or to protect a listed distinct population segment only in part as the Final Rule here does; and
-- The legislative history of the Endangered Species Act does not support the Service's new interpretation of the phrase "significant portion of its range." To the contrary it supports the historical view that the Service has always held, the Endangered Species Act does not allow a distinct population segment to be subdivided.
Accordingly, the rule delisting the gray wolf must be set aside because, though it may be a pragmatic solution to a difficult biological issue, it is not a legal one.

EXCERPT: The record in this case implies that the Service tried to find a pragmatic solution to the legal problem raised by the inadequacy of Wyoming's regulatory mechanisms, and Wyoming's choices about meaningful participation in a collective delisting agreement like that engaged in by Montana and Idaho. Even if the Service's solution is pragmatic, or even practical, it is at its heart a political solution that does not comply with the ESA. The northern Rocky Mountain DPS must be listed, or delisted, as a distinct population and protected accordingly. The issues of the adequacy of the regulatory mechanisms of Montana and Idaho, population size, connectivity and genetic exchange are subsumed by the determination that the Final Rule is contrary to the law and as such are not decided here.

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The gray wolf is the largest wild member of the dog family. 74 Fed. Reg. 15,123,15,123 (April 2, 2009). Wolves generally live in packs of 2 to 12 animals and have strong social bonds. Id. Wolf packs consist of a breeding pair (the alpha male and alpha female), their offspring from previous years, and an occasional unrelated wolf. Id. Generally, only the alpha male and alpha female breed. Id. Litters are born in April and average around 5 pups. Id. Normally, 4 pups survive until winter. Id. Wolves can live up to 13 years, but in the northern Rocky Mountains 4 years is the average lifespan. Id. Packs typically occupy territories from 200 to 500 square miles, which they defend against other wolves and wolf packs. Id.  Wolf pack image above from Howling for Justice (Blogging for the Gray Wolf).

KEITHINKING: This month marked yet another turning point in the wolf litigation -- but then again, there have been ALOT of turning points.  As Lauren Himiak noted in her National & State Parks Blog "wolves were on the list in 1974, off the list in 2008, on the list in late 2008, off the list 2009, and back on the list now."  This time, the wolf is back on the list thanks to District Court Judge Donald Molloy and his ruling that the entire Rocky Mountain wolf population must be managed together.  In other words, Idaho and Montana could not have its own policies allowing wolf hunts while the listed wolves in Wyoming were regulated differently. See coverage in the Missoulian.  The ruling might seem inconsistent with the usual notion that Congress bestowed flexibility upon federal wildlife managers for "experimental populations" pursuant to Section 10(j) of the Endangered Species Act (ESA) -- but as the opinion explains, the problem is that Congress did not, in fact, provide that much flexibility.  Sure, critical habitat and consultation requirements might be different pursuant to ESA Section 10(j), but a "species" is still a species. (Or, more precisely, a Distinct Population Segment of a species cannot be further subdivided by state boundaries.)  Idaho Fish & Game declared the ruling a mess, see KLEW-TV, hunters called for legislation, see AmmoLand.com and Sen. Max Baucus vowed legislation.  Sadly, the decision scuttled plans for the settlement talks -- the one path that might actually produce a solution.  See Salt Lake Tribune.   In fact, what the Rocky Mountain wolves really need is a reasonable settlement, in turn codified through legislation, to end the litigation once and for all.  As Judge Molloy held, "Even if the (FWS) solution is pragmatic, or even practical, it is at heart a political solution that does not comply with the ESA."  That sentence sums up the problem.  The law is intolerant of politics (and all too often, politics are intolerant of the law.)  In a editorial published in the Casper Star-Tribune, the Greater Yellowstone Coalition proposed a long-term solution: (1) determine a baseline population figure used to set management policies (they propose using the exist population size), (2) develop policies to protect ranchers, and (3) allow fair-chase hunting for population control. The concept sounds workable, but #1 might prove to be the tricky one.  Reasonable minds, and scientists, will disagree about the "right" population figure.  Inevitably, even if a broad consensus is reached, a handful of persistent environmentalists might want more wolves than the baseline number, and an equally determined group of strong-willed ranchers and hunters will want fewer.  High low, high low, it's back to court we'll go...?

P.S.  In the colorful first page of the opinion, the Court wrote: "The fight about wolves, steeped in stentorian agitprop, ignores the two different mandates of the act: the risk assessments, whether listing or delisting, are designed to prevent extinction of a species, and secondly {whether} they are intended to promote recovery of that species."  FYI: stentorian agitprop = extremely loud propaganda.

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Evincing the silver lining in the disaster, FWS issues an emergency permit for sea turtle rehabilitation.

08/09/2010

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75 Fed. Reg. 47825 / Vol. 75, No. 152 / Monday, August 9, 2010 / Notices
DEPARTMENT OF THE INTERIOR Fish and Wildlife Service
FWS–R2–ES–2010–N138; 20124–1113–0000–F5
Emergency Exemption; Issuance of Emergency Permit to Rehabilitate Sea Turtles Affected by the Deepwater Horizon Oil Spill, Gulf of Mexico

SUMMARY: On April 20, 2010, a massive oil spill occurred as a result of the Deepwater Horizon drilling rig explosion in the Gulf of Mexico. The oil spill continues to threaten the Gulf of Mexico environment and its inhabitants, including five sea turtle species. We, the U.S. Fish and Wildlife Service have authorized Texas State Aquarium, under an Endangered Species Act (ESA) permit, to aid sea turtles affected by the oil spill.

EXCERPT: Rehabilitation may include the following activities: Examine and document stranded sea turtles; aid with holding/restraining live turtles while others permitted rush to the scene, examine tags, apply tags, collect data/specimens, or attach satellite transmitters; examine for tags and tag live sea turtles; transport live and dead sea turtles to rehabilitation facilities, satellite transmitter attachment sites, and necropsy sites and necropsy dead sea turtles and collect samples; examine gut contents from dead sea turtles; attach satellite transmitters to nesting Kemp's ridley turtles; locate egg chambers and retrieve eggs for protected incubation; provide care for incubating sea turtle eggs; release hatchling sea turtles; examine unhatched eggs and collect tissue/gonad samples; capture juvenile sea turtles in nets and collect associated data; collect blood samples from stranded, nesting, and captured sea turtles; and collect small tissue samples from live stranded, nesting, and captured sea turtles.

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Image of an oiled sea turtle from Sea Turtle Restoration Project

KEITHINKING: The impacts of oil on sea turtles have been a tragedy.  See Defenders of Wildlife.  And the need to protect sea turtles from these types of disastrous oil spills have been understood for years.  See NOAA response information.  But we should all remember that out of crisis came opportunities for on-the-job training.  One of the silver linings in the Deepwater Horizon tragedy is the significant growth in sea turtle awareness and rescue capabilities.  Consider, for example, the following:
No, it should not have happened, and yes, we need to avoid it ever happening again (but it will....)  Still, for the moment, I'm choosing to be an optimist, and to celebrate one of the success stories.  For more links on sea turtle rehab efforts, visit the Huffington Post and New York Times.

Keith Who?

Keith W. Rizzardi, a Florida lawyer, is board certified in State & Federal Administrative Practice. A former U.S. Dept. of Justice attorney, Keith represents the South Florida Water Management District, serves on NOAA's Marine Fisheries Advisory Committee, and chaired The Florida Bar Government Lawyer Section.

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16 U.S.C. §1531 et. seq.

"The Congress finds and declares that -

(1) various species of fish, wildlife, and plants in the United States have been rendered extinct as a consequence of economic growth and development untempered by adequate concern and conservation;

(2) other species of fish, wildlife, and plants have been so depleted in numbers that they are in danger of or threatened with extinction;

(3) these species of fish, wildlife, and plants are of aesthetic, ecological, educational, historical, recreational, and scientific value to the Nation and its people."

16 U.S.C. §1531(a)

The purpose of the Endangered Species Act is "to provide a means whereby the ecosystems upon which endangered species and threatened species depend may be conserved."

16 U.S.C. §1531(b)

Reasons for the ESA

1. ECOLOGICAL: Species have a role in the web of life. Who knows which missing link causes the collapse?

2. ECONOMICAL: Species have actual, inherent, and potential value -- some as food, others as tourist attractions. As Congress said, these species have "aesthetic, ecological, educational, historical, recreational, and scientific value to the Nation." 16 U.S.C. §1531(a).

3. MEDICAL: Although perhaps a subset of economics, medical reasons for the ESA deserve special note, because today's listed species could be tomorrow's cure for cancer.

4. MORAL: With each extinction, we take something from others. We must prevent "the tragedy of the commons."

5. THEOLOGICAL: Even the Bible instructed Noah to save God's creatures, male and female, two by two.

"Every species is part of an ecosystem, an expert specialist of its kind, tested relentlessly as it spreads its influence through the food web. To remove it is to entrain changes in other species, raising the populations of some, reducing or even extinguishing others, risking a downward spiral of the larger assemblage." An insect with no apparent commercial value may be the favorite meal of a spider whose venom will soon emerge as a powerful and profitable anesthetic agent. That spider may in turn be the dietary staple of a brightly colored bird that people, who are notoriously biased against creepy crawlers and in favor of winsome winged wonders, will travel to see as tourists. Faced with the prospect that the loss of any one species could trigger the decline of an entire ecosystem, destroying a trove of natural and commercial treasures, it was rational for Congress to choose to protect them all. -- Alabama-Tombigbee Rivers Coalition v. Kempthorne, 477 F.3d 1250, 1274-75 (11th Cir.2007), cert. denied, 128 S.Ct. 8775 (2008), quoting Edward O. Wilson, The Diversity of Life 308 (1992).

Reasons for ESA Reform

1. ECOSYSTEM (MIS)MANAGEMENT. The ESA encourages selective review of individual species needs, even though nature pits species needs against one another. Furthermore, the ESA's single-species focus detracts from efforts to achieve environmental restoration and ecosystem management.

2. SCIENTIFIC UNCERTAINTY: While the ESA requires consideration of the "best available science," sometimes the best is not enough, forcing decisions under great uncertainty. The ESA, however, is generally proscriptive, regulatory, and absolute; as a result, it insufficiently allows for adaptive management.

3. LITIGATION: ESA implementation is at the mercy of the attorneys. Cases involving one listed species can serve as a proxy for hidden agendas, especially land use disputes, and regardless of actual species needs, litigation and judicial orders set agency priorities. In the end, realistic solutions disappear amidst court-filings, fundraising, and rhetoric.

4. PRIVATE LANDS: Up to 80% of ESA-listed species habitat is on privately owned lands. While the ESA can place reasonable restrictions on private property rights, there are limits. But the best alternatives have limits too, such as Federal land acquisition and the highly controversial "God Squad" exemptions.

5. FUNDING: Protecting species is expensive, but resources appropriated by Congress are limited. An overburdened handful of federal agency biologists cannot keep pace with the ESA's procedural burdens, nor court-ordered deadlines (see #3 above). Provisions requiring agencies to pay attorney's fees to victorious litigators -- who challenge the hastily written documents prepared by overworked bureaucrats -- simply exacerbate the problem.

"This case presents a critical conflict between dual legislative purposes, providing water service for agricultural, domestic, and industrial use, versus enhancing environmental protection for fish species whose habitat is maintained in rivers, estuaries, canals, and other waterways that comprise the Sacramento-San Joaquin Delta… This case involves both harm to threatened species and to humans and their environment. Congress has not nor does TVA v. Hill elevate species protection over the health and safety of humans... No party has suggested that humans and their environment are less deserving of protection than the species. Until Defendant Agencies have complied with the law, some injunctive relief pending NEPA compliance may be appropriate, so long as it will not further jeopardize the species or their habitat." -- The Consolidated Delta Smelt Cases, 2010 WL 2195960 (E.D.Cal., May 27, 2010)(Judge Wanger)(addressing the need for further consideration of the human consequences of ESA compliance).

Notable quotables

"A nation, as a society, forms a moral person, and every member of it is personally responsible for his society." – Thomas Jefferson (1792)

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"The destruction of the wild pigeon and the Carolina parakeet has meant a loss as sad as if the Catskills or Palisades were taken away. When I hear of the destruction of a species, I feel as if all the works of some great writer had perished."

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"Conservation means development as much as it does protection. I recognize the right and duty of this generation to develop and use the natural resources of our land; but I do not recognize the right to waste them, or to rob, by wasteful means, the generations that come after us." – Theodore Roosevelt (Aug. 31, 1910)

Noah's orders

GENESIS, Chapter 6: [v 20] "Of the birds according to their kinds, and of the animals according to their kinds, of every creeping thing of the ground according to its kind, two of every sort shall come in to you, to keep them alive. [v 21] Also take with you every sort of food that is eaten, and store it up; and it shall serve as food for you and for them."

GENESIS, Chapter 9: [v12] "And God said, This is the token of the covenant which I make between me and you and every living creature that is with you, for perpetual generations"

"The power of God is present at all places, even in the tiniest leaf … God is currently and personally present in the wilderness, in the garden, and in the field." – MARTIN LUTHER

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