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Endangered and Threatened Wildlife and Plants; 12-Month Finding on a Petition To Delist the Idaho Springsnail; 12-Month Finding on a Petition To List the Jackson Lake Springsnail, Harney Lake Springsnail, and Columbia Springsnail; and Proposed Rule To Remove the Idaho Springsnail From the List of Threatened and Endangered Wildlife
Note: EPA no longer updates this information, but it may be useful as a reference or resource.
[Federal Register: September 28, 2006 (Volume 71, Number 188)]
[Proposed Rules]
[Page 56938-56948]
From the Federal Register Online via GPO Access [wais.access.gpo.gov]
[DOCID:fr28se06-42]
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DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 17
RIN 1018-AU66
Endangered and Threatened Wildlife and Plants; 12-Month Finding
on a Petition To Delist the Idaho Springsnail; 12-Month Finding on a
Petition To List the Jackson Lake Springsnail, Harney Lake Springsnail,
and Columbia Springsnail; and Proposed Rule To Remove the Idaho
Springsnail From the List of Threatened and Endangered Wildlife
AGENCY: Fish and Wildlife Service, Interior.
ACTION: Notice of two 12-month petition findings and a proposed rule to
delist the Idaho springsnail (Pyrgulopsis idahoensis).
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SUMMARY: We, the U.S. Fish and Wildlife Service (USFWS, Service, or
we), under the Endangered Species Act of 1973, as amended (Act),
announce combined 12-month findings on a petition to delist the
endangered Idaho springsnail (Pyrgulopsis idahoensis) and a petition to
list the Jackson Lake springsnail (P. robusta), Harney Lake springsnail
(P. hendersoni), and Columbia springsnail (P. species A (unnamed)).
Evidence collected subsequent to the December 14, 1992, listing (USFWS
1992, pp. 59244-59527 (57 FR 59244)) of the Idaho springsnail indicates
it no longer constitutes a distinct species. It is now described as the
Jackson Lake springsnail (P. robusta), a single taxon, composed of four
previously distinct springsnail species (Idaho, Jackson Lake, Harney
Lake, and Columbia springsnails), and therefore we are proposing to remove
[[Page 56939]]
the Idaho springsnail from the Federal List of Endangered and
Threatened Wildlife. We evaluated the best available scientific and
commercial information regarding the status of, and threats to, the
newly described P. robusta, and determined that the threats to the
species do not warrant its listing at this time. Additionally, based on
our status review of P. robusta, we also find that listing the Jackson
Lake springsnail, Harney Lake springsnail, and Columbia springsnail as
separate species is not warranted.
DATES: The 12-month findings on the delisting and listing petitions
announced in this notice were made on September 28, 2006. We request
that new information be submitted to us concerning the status of, or
threats to, Pyrgulopsis robusta, whenever it becomes available.
We will accept comments from all interested parties regarding the
proposal to delist the Idaho springsnail until November 27, 2006. We
must receive requests for public hearings on or before November 13, 2006.
ADDRESSES: Comments may be submitted on the proposed rule to delist the
Idaho springsnail by any of the following methods. Please include RIN
1018-AU66 in any subject line.
? E-mail: fws1srbocomments@fws.gov.
? Fax: (208) 378-5262.
? Hand carry, Postal Delivery, or Courier: Snake River Fish
and Wildlife Office, U.S. Fish and Wildlife Service, 1387 S. Vinnell
Way, Room 368, Boise, ID 83709.
? Federal Rulemaking Portal: http://www.regulations.gov.
Follow the instructions for submitting comments.
Please see the Public Comments Solicited section below for file
format and other information about electronic filing.
FOR FURTHER INFORMATION CONTACT: The Snake River Fish and Wildlife
Office by mail at the above address; by telephone at 208/378-5243; by
facsimile at 208/378-5262; or by electronic mail at:
fw1srbocomment@fws.gov.
SUPPLEMENTARY INFORMATION:
Public Comments Solicited
We intend that any final action resulting from this proposal will
be as accurate and effective as possible. Therefore, comments or
suggestions from the public, other concerned governmental agencies,
Native American Tribes, the scientific community, industry, or any
other interested party concerning this proposed rule are hereby
solicited. Please note that comments merely stating support or
opposition to the actions under consideration without providing
supporting information, although noted, will not be considered in
making a determination, because section 4(b)(1)(A) of the Act directs
that determinations as to whether any species is a threatened or
endangered species shall be made ``solely on the basis of the best
scientific and commercial data available.''
You may submit materials concerning this proposal by any one of
several methods (see ADDRESSES section). Please submit Internet
comments to fws1srbocomments@fws.gov in ASCII file format and avoid the
use of special characters or any form of encryption. Please also
include ``RIN 1018-AU66'' in your e-mail subject header and your name
and return address in the body of your message. If you do not receive a
confirmation from the system that we have received your Internet
message, contact us directly (see ADDRESSES). Please note that the
Internet address fws1srbocomments@fws.gov will be unavailable at the
termination of the public comment period.
Our practice is to make comments, including names and home
addresses of respondents, available for public review during regular
business hours. Individual respondents may request that we withhold
their home addresses from the rulemaking record, which we will honor to
the extent allowable by law. There also may be circumstances in which
we would withhold from the rulemaking record a respondent's identity,
as allowable by law. If you wish us to withhold your name and/or
address, you must state this prominently at the beginning of your
comment, but you should be aware that the Service may be required to
disclose your name and address pursuant to the Freedom of Information
Act. However, we will not consider anonymous comments. We will make all
submissions from organizations or businesses, and from individuals
identifying themselves as representatives or officials of organizations
or businesses, available for public inspection in their entirety.
Comments and other information received, as well as supporting
information used to write this rule, will be available for public
inspection, by appointment, during normal business hours at the above
address. In making a final decision on this proposal, we will take into
consideration any additional information we receive. Such communications
may lead to a final regulation that differs from this proposal.
Background
Section 4(b)(3)(B) of the Endangered Species Act of 1973, as
amended (Act) (16 U.S.C. 1531 et seq.) requires that, for any petition
to revise the List of Threatened and Endangered Species that contains
substantial scientific and commercial information that suggests a
change in status may be warranted, we make a finding within 12 months
of the date of the receipt of the petition on whether the petitioned
action is: (a) Not warranted; (b) warranted; or (c) warranted, but the
immediate proposal of a regulation implementing the petitioned action
is precluded by other pending proposals to determine whether a species
is threatened or endangered, and expeditious progress is being made to
add or remove qualified species from the List of Threatened and
Endangered Species. Such 12-month findings are to be promptly published
in the Federal Register. In addition, section 4(b)(3)(C) of the Act
requires that a petition for which the requested action is found to be
warranted but precluded shall be treated as though resubmitted on the
date of such finding (i.e., requiring a subsequent finding to be made
within 12 months).
Previous Federal Action
We published the final rule listing the Idaho springsnail as
endangered on December 14, 1992 (57 FR 59244). In that rule, we
described range reduction, continued adverse habitat modification,
deteriorating water quality from multiple sources, and the appearance
of the invasive New Zealand mudsnail (Potamopyrgus antipodarum) as the
major threats to the species. We have not designated critical habitat
for the Idaho springsnail.
On June 28, 2004, we received a petition from the Idaho Office of
Species Conservation and the Idaho Power Company (IPC) requesting that
the Idaho springsnail be delisted based on a recent taxonomic revision
of the species. The petitioners also provided new Idaho springsnail
scientific information, and contrasted this new information with
information used in the 1992 Idaho springsnail listing decision (57 FR
59244). The petitioners stated that most, if not all, threats to Idaho
springsnail identified in the 1992 listing rule have been eliminated,
are being actively addressed by State and private entities, or are not
relevant, based on new scientific information.
On August 5, 2004, we received a petition from Dr. Peter Bowler,
the Biodiversity Conservation Alliance, the Center for Biological
Diversity, the Center for Native Ecosystems, the
[[Page 56940]]
Western Watersheds Project, and the Xerces Society, requesting that the
Jackson Lake springsnail, Harney Lake springsnail, and Columbia
springsnail be listed as either threatened or endangered species, and
as either individual species or combined as the new species,
Pyrgulopsis robusta. This listing petition cited habitat loss and
degradation from development impacting springs, domestic livestock
grazing, and groundwater withdrawal, among other factors, as threats to
the continued existence of these three springsnail species. The listing
petition also discussed the recent springsnail taxonomic revision and
acknowledged that the Jackson Lake springsnail, Harney Lake
springsnail, Columbia springsnail, and Idaho springsnail may be one
species (P. robusta), but contended that, whether considered
individually or as one species, all four springsnails warranted the
protection of the Act.
On April 20, 2005, we published combined 90-day petition findings
(USFWS 2005, pp. 20512-20514 (70 FR 20512)), stating that both
petitions provided substantial information suggesting that delisting of
the Idaho springsnail, or listing of Jackson Lake springsnail, Harney
Lake springsnail, and Columbia springsnail, may be warranted.
Species Information
The Idaho springsnail (Pyrgulopsis idahoensis; Hydrobiidae) was
first described by Pilsbry (1933, pp. 11-12) and placed in the genus
Amnicola. Greg and Taylor (1965, pp. 103-110) established the new genus
Fontelicella and then placed P. idahoensis in the subgenus Natricola,
created in 1965 (Greg and Taylor 1965, pp. 108-109). Natricola
contained the Idaho springsnail, the Harney Lake springsnail (P.
hendersoni), and the Jackson Lake springsnail (P. robusta). After
several taxonomic revisions, the subgenus Natricola was placed in
synonymy with the genus Pyrgulopsis by Hershler and Thompson (1987, p.
29). Pyrgulopsis is the largest genus of freshwater mollusks in North
America, comprised of over 120 described species (Liu and Hershler
2005, p. 284). The greatest diversity of the genus occurs in the Great
Basin of the western United States (Hershler and Sada 2000, p. 367;
Hershler and Sada 2002, p. 255).
In 2004, Hershler and Liu (2004, pp. 78-79) revised the taxonomic
status of four springsnails Pyrgulopsis idahoensis, P. hendersoni, P.
robusta, and the Columbia springsnail (P. species A (unnamed)), by
placing all four springsnails into the oldest available taxon of the
four revised species, P. robusta (Jackson Lake springsnail, Walker
1908, p. 97). All four species were considered members of the subgenus
Natricola. Members of the subgenus Natricola are very similar in size
and shape, being distinguished primarily by the morphology of the
shell. The authors reviewed morphological characters, mitochondrial DNA
sequences, and nuclear DNA sequences to establish the need for
taxonomic status change.
Several morphological metrics, including the position of the callus
(thickened portion) on the operculum (serves as a cover for the opening
in the shell); the shape of the central cusp of the central teeth; the
number of cusps on central teeth; notching of inner marginal teeth;
number of cusps on outer marginal teeth; the male penile features; and
female genitals, did not differ significantly among the four
springsnail species (Hershler and Liu 2004, pp. 70-75). Five shell
parameters were significantly heterogeneous in a comparison of the four
springsnail species. In only one case did a single springsnail species
differ significantly from the other three; the Idaho springsnail
differed significantly from the other three springsnail species for the
ratio of shell height to height of body whorl (Hershler and Liu 2004,
p. 71).
To construct species topologies, Hershler and Liu (2004, pp. 67-69)
sequenced selected genes of four springsnail species, Pyrgulopsis
robusta, P. idahoensis, P. hendersoni, and P. species A (unnamed), as
well as congeners P. imperialis, P. intermedia, P. kolobensis, and P.
species B (unnamed). The mitochondrial DNA data revealed little
difference in the partial CO1 gene among the four springsnail species.
Differences ranged from 0.0 to 0.8 percent (0 to 5 base pairs) among
the four springsnail species and 2.6 to 6.9 percent (16 to 43 base
pairs) with congeners. Nuclear DNA data revealed differences in the
ITS-1 sequences within the four springsnail species that were
substantially smaller (0.0 to 0.6 percent) than differences among other
congeners (5.9 to 20.4 percent) (see Figure 8 in Hershler and Liu 2004,
pp. 73-75). These two lines of evidence show that DNA sequence
differences among the four springsnail species are very small compared
to differences with other recognized taxa within the genus Pyrgulopsis.
Hershler and Liu (2004, p. 77) concluded ``three independent data
sets (morphology, mitochondrial, and nuclear DNA sequences) congruently
suggest that these four Natricola snails do not merit recognition as
distinct species according to various currently applied concepts of
this taxonomic rank.'' The methods employed by Hershler and Liu (2004,
pp. 67-70) are considered contemporary in the field of genetics and are
consistent with those used by numerous authors reconstructing
phylogenies based on molecular evidence in general (Raahauge and
Kristensen 2000, pp. 87-89; Jones et al. 2001, pp. 281; Attwood et al.
2003, pp. 265-266), and with western hydrobiid snails in particular
(Hershler et al. 2003, pp. 358-359; Liu et al. 2003, pp. 2772-2775;
Hurt 2004, pp. 1174-1177; Liu and Hershler 2005, p. 285). Further, it
is the position of the American Malacological Society that the Hershler
and Liu (2004) revised taxonomy sets the standard for understanding
this group of springsnails (Leal 2004). Hershler and Liu (2004, pp. 66-
81) represents the best available scientific and commercial data on the
taxonomic status of the four petitioned springsnails, and we therefore
will refer to the four former springsnail species as Pyrgulopsis
robusta for the rest of this document.
Biology
Pyrgulopsis robusta shells are large for the genus, usually ovate
(oval) to narrow-conic (cone shaped), rarely subglobose (not quite
rounded), with whorls weakly to moderately convex (curving outward).
The shell is clear-white and the periostracum (outer layer of the shell
matrix) is tan. The aperture is ovate and weakly angled above. The
inner lip is complete in larger specimens. The penial lobe and filament
are about equal in length. The dorsal proximal lobule is well
developed, usually overlapping the base of the filament and often borne
on a weak proximal swelling. The terminal gland is elongate and
transverse. The dorsal distal lobule is well developed and is usually
bearing one or a series of small glands. The ventral lobule is well
developed and bears a large gland (Hershler and Liu 2004, p. 79).
Information available to describe the life history of Pyrgulopsis
robusta varies widely. The species is hypothesized to primarily feed on
periphyton (i.e., diatoms and algae), which covers the surface of most
benthic (submerged bottom) substrates. Although little specific
information exists regarding reproductive strategies of P. robusta,
members of the genus Pyrgulopsis are generally dioecious (i.e., male
and female individuals) (Dillon 2000, pp. 102-103; Lysne 2003, p. 80).
Pyrgulopsis robusta is hypothesized to
[[Page 56941]]
reproduce once in an annual life cycle, and laboratory studies estimate
average survival to be 382 days (Lysne 2003, p. 82). However, field
data show that not all P. robusta die within a year (Finni 2003a, pp.
3-5), a life history pattern suggested by Dillon (2000, p. 162) to be
exhibited by many populations, allowing extended survivorship and
multiple reproductive events. Additional P. robusta life history
information regarding reproduction and growth rates can be found in the
following references: Finni 2003a, pp. 3-5; Lysne 2003, pp. 24, 36, 38,
79-81; Riley et al. 2003, p. 33; Dillon 2000, p. 103; and, Hershler
1994, pp. 1-119.
Habitat
Species in the genus Pyrgulopsis require permanent fresh waters
(Taylor 1985, pp. 265, 276; Hershler 1998, p. 1; Hershler and Sada
2002, p. 255). Pyrgulopsis robusta utilizes a wide range of flow
conditions and habitats. For example, P. robusta has been found in the
mainstem Snake River, Idaho, in various habitats; in C.J. Strike and
Swan Falls Reservoirs, Idaho (Clark 2005); and in two springs that flow
through Yellowstone National Park and John D. Rockefeller National
Parkway in Wyoming: Marmot Spring, a relatively stable groundwater-fed
spring, and Polecat Creek, a geothermal spring (Riley 2005a, pp. 1, 8;
Hall et al. 2003, p. 408). In southeastern Oregon, P. robusta primarily
occurs in cold springs and spring pools of variable size (Frest and
Johannes 1995, p. 196), but is also found in the South Fork Malheur
River (Hershler and Liu 2004, p. 67). Although P. robusta evolved in
prehistoric Lake Idaho (Taylor 1982, p. 2; Taylor 1985, pp. 288, 309),
the species presently occurs more frequently and abundantly in river
habitat than in lake or reservoir habitat (Clark 2005).
Pyrgulopsis robusta is found on a wide range of substrates in the
Snake and Columbia Rivers, from silt and pebbles to cobbles and
boulders, but in the Snake River the species achieves highest density
on gravel to cobble substrates (Stephenson et al. 2004, A3 pp. 1-4, A4
pp. 1-4). In Southeastern Oregon, the species is generally found on
coarse sand to cobble substrates but may also be associated with the
submerged aquatic plant genus Rorippa (Frest and Johannes 1995, p. 196).
Field and laboratory information indicate Pyrgulopsis robusta has a
wide temperature tolerance (Stephenson and Bean 2003, pp. A1, A2;
Stephenson et al. 2004, A3 pp. 1-4, A4 pp. 1-4; Lysne 2003, p. 27).
Pyrgulopsis robusta has been documented to survive and grow at
temperatures that exceeded the State of Idaho's water temperature
criteria for cold-water life of 66 degrees Fahrenheit (F) (19 degrees
Celsius (C)) mean daily and 72 degrees F (22 degrees C) maximum daily
water temperatures (Lysne 2003, pp. 27-29). Pyrgulopsis robusta have
been routinely collected in the Snake River at water temperatures
greater than 68 degrees F (20 degrees C) (Stephenson and Bean 2003, pp.
A1, A2; Stephenson et al. 2004, A3 pp. 1-4, A4 pp. 1-4). In Wyoming,
high numbers of P. robusta have been collected in Polecat Creek, a
geothermal spring creek with temperatures ranging from approximately
57.2 degrees F (14 degrees C) in winter to 75.2 degrees F (24 degrees
C) in summer (Hall et al. 2003, p. 408). Other variables that
potentially influence P. robusta habitat selection and use have not
been well documented.
Range and Distribution
Pyrgulopsis robusta is now comprised of four geographically
isolated populations that include the northwestern Wyoming population,
the Snake River population in Idaho, the Columbia River population in
Oregon and Washington, and the Oregon closed-basin population (Hershler
1994, p. 91; Hershler 1998, p. 99; Riley et al. 2003, p. 6; Frest
2005a; Riley 2005b). In Wyoming, P. robusta is currently known from
only two locations in Yellowstone National Park and John D. Rockefeller
National Parkway. There have been past collections at other sites, and
P. robusta may be found at additional locations in the future. Recent
surveys have failed to locate the species in Jackson Lake (Riley
2005b), the type locality of P. robusta as described by Walker in 1908.
In southeastern Oregon, Pyrgulopsis robusta occurs in few locations
(six or fewer) in the Oregon Interior Basin, in isolated cold springs
and spring pools (Frest and Johannes 1995, p. 196), and in the South
Fork Malheur River, a tributary to the Snake River (Hershler and Liu
2004, p. 67), in Harney and Lake Counties. Pyrgulopsis robusta was
historically found along the shores of Malheur and Harney Lakes (Frest
and Johannes 1995, p. 196) and was associated with open water habitats
(as opposed to wetland habitats with emergent vegetation) 8,000 to
10,000 years ago (Wriston 2003, p. 28). Pyrgulopsis robusta is not
known to currently exist in Harney or Malheur Lakes, and it is
uncertain when P. robusta last existed there (Frest and Johannes 1995,
p. 196). Many isolated springs and other aquatic habitats of Utah,
Nevada, and Idaho in the Great Basin, including parts of southeastern
Oregon, have been surveyed specifically for springsnails, but no
additional P. robusta have been located (Hershler 1998, p. 3; Hershler
and Sada 2002, p. 259).
In the Snake River, Pyrgulopsis robusta is known to occur at
numerous locations along a stretch of 214 river miles (344 kilometer
(km)) between river mile (rm) 340 (river kilometer mile (rkm) 547) and
rm 554 (rkm 892). There have been at least 174 collections from this
reach of river and the extent of P. robusta is believed to be well
defined and relatively abundant. The distribution of P. robusta in the
Columbia River is less well known than in the Snake River, particularly
in the Hanford Reach below Priest Rapids Dam. In the Columbia River, P.
robusta is known from 17 locations, beginning at approximately rm 20
(rkm 32) and continuing for nearly 400 miles (649 km) upstream to just
below Priest Rapids Dam (Frest 2005a). Although there have been several
hundred invertebrate samples collected in the Columbia River over the
past several years, P. robusta has been found only in a few of these
samples (Frest 2005a).
Status Review Process
On April 20, 2005, we initiated combined 12-month status reviews
(70 FR 20512) of the petitioned springsnails, as well as a 5-year
review of the Idaho springsnail under section 4(c)(2)(A) of the Act,
and solicited additional information from the public on the biology,
ecology, distribution and status, threats affecting the petitioned
springsnail species, and any ongoing or planned conservation measures.
During the 60-day public comment period, we contacted numerous
Federal and State resource agencies, interested Tribal governments, and
County governments. On June 7, 2005, we attended an information
exchange meeting with the State of Idaho Office of Species
Conservation, Idaho Department of Fish and Game (IDFG), Idaho
Department of Environmental Quality (IDEQ), U.S. Bureau of Reclamation
(BOR), U.S. Bureau of Land Management (BLM), and others. After this
information exchange meeting, our staff assimilated and analyzed all
the new information submitted during the 60-day public comment period,
along with the existing information already obtained from published
scientific literature, unpublished technical documents, and written and
personal communications. As part of our routine Status Review process,
we took this synthesized information and created a document titled:
Draft Best Available Biological Information for Four Petitioned
Springsnail Species from
[[Page 56942]]
Idaho, Oregon, Washington, and Wyoming (Draft BAI). The Draft BAI
represented our comprehensive, best available scientific and commercial
information on the petitioned springsnails.
On August 3, 2005, through a widely distributed outreach effort
that included a news release, Dear Interested Party letter, posting on
the Service's Web site, and a request for peer review, we opened an
additional 30-day public and peer review comment period on the Draft
BAI. After the public and peer review, Service staff incorporated the
additional information and technical corrections received, and wrote
Version 2.0 Best Available Biological Information for Four Petitioned
Springsnail Species from Idaho, Oregon, Washington, and Wyoming (BAI).
The revised BAI constituted the peer-reviewed state of knowledge with
regard to the taxonomy, biology, ecology, distribution, and status of
the four petitioned springsnail species, now combined as Pyrgulopsis
robusta, and was used throughout the remainder of the Status Review
process as the primary source of best available scientific and
commercial data.
The Service utilized a structured decision making model to assess
the available data. Based on an early assessment of the degree of
uncertainty surrounding the population trends and conservation status
of Pyrgulopsis robusta, the Service used two panels to inform our
recommended course. The first panel (Expert Panel) was made up of six
scientists from outside the Service with expertise in relevant fields,
including snail biology and ecology, community ecology, population
ecology, stream ecology, aquatic ecotoxicology, and regional water
quality. This Expert Panel met on October 18-19, 2005, to discuss the
strengths and weaknesses of the various data, hypotheses, and opinions
relative to the current status of P. robusta. The Expert Panel only
addressed the scientific aspects of risk and threats, and estimated the
probable extinction risk to P. robusta. A second ``Managers Panel'' of
five Service managers and senior biologists met on October 20-21, 2005,
to consider the Expert Panel's input and all other information
necessary to conduct an extinction risk assessment of P. robusta.
Information generated from these two Panels was used in the Service's
status review to assess threats to, and evaluate the listing status of,
P. robusta. Further details about the structured decision making
process used by the two panels are documented in our administrative
record for this proposed rule.
Inspection of the petition to delist the Idaho springsnail, the
petition to list the Jackson Lake, Harney Lake, and Columbia
springsnails, and the supporting information, administrative finding,
and other relevant materials may be made in person, by appointment, at
the address listed above (see ADDRESSES).
Summary of Factors Affecting the Species
Section 4 of the Act and regulations (50 CFR Part 424) promulgated
to implement the listing provisions of the Act set forth the procedures
for listing, reclassifying, and delisting species. A species may be
listed as threatened or endangered if one or more of the five factors
described in section 4(a)(1) of the Act threaten the continued
existence of the species. A species may be delisted, according to 50
CFR 424.11(d), if the best scientific and commercial data available
substantiate that the species is neither endangered nor threatened
because of: (1) Extinction; (2) recovery; or (3) error in the original
data, or the data analysis, used for classification of the species. For
species that are being considered for delisting, the analysis of
threats must include an evaluation of threats that existed at the time
of listing and those that currently exist or that could, with a
reasonable degree of likelihood, potentially affect the species in the
foreseeable future after its delisting and the consequent removal of
the Act's protections.
A. The Present or Threatened Destruction, Modification, or Curtailment
of Its Habitat or Range
The 1992 final listing rule (57 FR 59244) described activities such
as proposed large hydroelectric dam developments, peak-loading
operations of existing hydroelectric water projects, small
hydroelectric developments, water pollution, and water diversions whose
cumulative effects threatened the habitat and fragmented populations of
the Idaho springsnail (Pyrgulopsis idahoensis). After reviewing the
best available scientific and commercial information regarding present
or threatened destruction, modification, or curtailment of the habitat
or range of P. robusta, we determined that the principal habitat-
related threats are not proceeding at a rate that will threaten the
continued existence of the species within the foreseeable future.
Dams and Reservoirs
Our 1992 listing of the Idaho springsnail was based on information
that indicated that the species was found only in permanent flowing
waters of the mainstem Snake River, and that its historic range had
been reduced nearly 80 percent, in large part by dam and reservoir
development and operations.
Populations of Pyrgulopsis robusta have been collected from various
habitats, including springs, river reaches, and both lake and reservoir
locations (Bickell 1977, p. 33; Hershler 1998, p. 99; Richards and
Lester 2002, pp. 6-7; Stephenson et al. 2004, pp. 11, 21). In the Snake
River in Idaho, where P. robusta occurs over a range of 214 river miles
(344 km), the greatest number of live collections and the highest
percentages of P. robusta occurrence are generally found in flowing
waters influenced by reservoirs (Clark 2005). While extensive surveys
conducted in downstream reaches (i.e., below Hells Canyon) of the Snake
River (Shinn et al. 2001, pp. 80-82; Finni 2003b, p. 1; Richards et al.
2005, pp. 4-5) and Columbia River basins (Frest and Johannes 1995, p.
203) have not documented the presence of springsnails, springsnails
have been known to persist in habitats associated with reservoirs
(i.e., C.J. Strike and Swan Falls). At the upstream end of their range
in C.J. Strike Reservoir, abundant numbers of springsnails are located
at the mouth of a small tributary (i.e., main-pool) and on the gravel
shores of the Bruneau River Arm, where comparatively cool and flowing
waters (i.e., relative to the Snake River) of the Bruneau River run
into C.J. Strike Reservoir (Stephenson et al. 2004, p. 21). In Swan
Falls Reservoir, P. robusta are found in the headwaters (i.e., the
nebulous upstream end of a reservoir and downstream end of free-flowing
river) of the reservoir, but only one snail has been collected (at rm
460; rkm 740) in the main pool from the dam to 7 miles (11.2 km)
upstream of the dam (Clark 2005).
At the downstream end of Pyrgulopsis robusta's range in Idaho, the
species' known distribution ends immediately above the Hells Canyon
Complex at the headwaters of Brownlee Reservoir (approximately rm 340
(rkm 547)). The Hells Canyon Complex includes three large reservoirs
(Brownlee, Oxbow, and Hells Canyon) that are deep (two have very steep
sides) and whose waters fluctuate on both a daily and annual basis
(Esch 2005). Surveys by the IPC in and below the Hells Canyon Complex
have not yielded P. robusta (Finni 2003b, pp. 9, 19; Meyers and Foster
2003, pp. 17-18; Richards et al. 2005, pp. 71-78, 103-149). The
particular habitat conditions of these reservoirs may not be able to
support P. robusta and may also prevent successful
[[Page 56943]]
downstream migration to suitable habitat below the Hells Canyon Complex
(Shinn et al., 2001, p. 20; Meyers and Foster 2003, pp. 18-20).
In Oregon and Washington, Pyrgulopsis robusta has been documented
in the lower Columbia River below Dalles and John Day Dams and in their
pools (Frest 2005a). These collections were in areas where the flow is
greater and the river is shallower than in the reservoir (Frest 2005a).
In southeastern Oregon, P. robusta was found in the south fork of the
Malheur River (Hershler and Liu 2004, p. 79; Frest 2005a). These
collections were reported to have been taken 60 miles upstream of Warm
Springs Dam in an area of spring up-welling from the hyporheic zone
(area below the streambed where water passes through spaces between the
rock and cobble) (Frest 2005a, b).
Our current status review indicates that Pyrgulopsis robusta is not
restricted to permanent free-flowing water; the species also occurs in
slower moving reservoir reaches and also in areas with and without
spring inflow or upwelling occurrences. Our previous concern, as stated
in the 1992 listing rule, regarding the historic range of the species
in the Snake River having been reduced nearly 80 percent by dams and
reservoirs, does not apply to P. robusta. New information collected on
the Idaho springsnail population's life history, distribution, and
status has been incorporated into this status review, together with
information about the three other P. robusta populations (Jackson Lake,
Harney Lake, and Columbia River). Much of this information has been
collected during aquatic and mollusk surveys conducted by the IPC in
the Snake River and Frest (2005 a, b) for the Columbia River and
southeast Oregon populations. The IPC has been collecting information
on Idaho springsnail populations throughout the Snake River since 1995.
Based on the results of these surveys and laboratory studies, we now
have a much better understanding of the basic life history as well as
current distribution and status of P. robusta in the Snake River. These
surveys have documented that P. robusta is more widely distributed in
the Snake River than originally described in the 1992 listing rule. IPC
biologists have surveyed over 400 river miles (644 km) in the Snake
River and have documented the species at over 174 known locations over
214 river miles (344 km), between rm 340 (rkm 547) and rm 554 (rkm 892)
(Clark 2005), a nearly 500 percent increase, or 179 river miles (292
km), of its known range. In summary, P. robusta has been determined to
be more widely distributed and to occur on a much wider diversity of
substrate types and sizes, and in a greater variety of aquatic habitats
than was known at the time of the Idaho springsnail's listing in 1992.
The species occurs throughout long reaches of the Snake River and
Columbia Rivers in areas that are influenced by dams and reservoirs.
The 1992 listing rule discussed ``peak-loading, the practice of
artificially raising and lowering river levels to meet short-term
electrical needs by local run-of-the-river hydroelectric projects,'' as
a threat that ``may adversely affect three known populations of the
Idaho springsnail'' (57 FR 59252). Certain hydroelectric power
generating operational scenarios (e.g., water storage, diversion, and
peak-loading) have been documented to have adverse impacts on aquatic
communities (Armitage 1984, pp. 141-143; Brusven 1984, p. 167; Vaughn
and Taylor 1999, pp. 915-916; Watters 2000, p. 1). C.J. Strike Dam is
the primary peak-loading hydroelectric facility in the Snake River, yet
Pyrgulopsis robusta persists in the peak-loading-affected area (Clark
2005). For example, the largest monitored colony of P. robusta exists
in the Snake River approximately 3 river miles (4.8 km) downstream of
C.J. Strike Dam (Stephenson et al. 2004, p. 14). The Expert Panel and
Service's Manager Panel both acknowledged that because colonies of P.
robusta are widespread and known to occur over a 214-mile (344-km)
stretch of the Snake River that is subject to long-term, recurring
peak-loading and fluctuating flows, these colonies are resilient and
will likely continue to persist into the foreseeable future.
The effects of dams and reservoirs have been suggested as barriers
to dispersal for Pyrgulopsis robusta. Species that have limited
distributions and/or smaller, isolated populations may have a higher
risk of local extirpations due to various threats and demographic
stochasticity (variability) (Meffe et al. 1997, pp. 284-299; Vaughn and
Taylor 1999, p. 916; Fagan et al. 2002, p. 3250). Both the Expert
Panelists and Service's Manager Panelists acknowledged this risk for
springsnails, but did not expect these populations to become extirpated
due to possible barriers to dispersal in the foreseeable future.
Groundwater Pumping
Groundwater pumping is only a concern for Pyrgulopsis robusta
populations in southeast Oregon. Groundwater pumping for domestic use,
agriculture, and industry may deplete flows from groundwater-fed spring
systems by altering, modifying, or curtailing habitats dependent on
those groundwater sources (Sada and Vinyard 2002, pp. 277-278).
The Oregon Water Resources Department (OWRD) regulates water
development (OWRD 2005a), but very little information is available for
the Malheur Basin or the Abert Lake Basin, where the Harney Lake
population of Pyrgulopsis robusta is found. While spring development
and/or destruction have been implicated in native species declines in
southeastern Oregon (Frest and Johannes 1995, p. 196), we are not aware
of spring alterations, modifications, or conservation efforts that are
affecting P. robusta in southeastern Oregon. Although at least one
location previously containing P. robusta in southeastern Oregon no
longer has springsnails (Hershler 1994, p. 41; Frest and Johannes 1995,
p. 196), groundwater pumping can not be explicitly linked to the
springsnail's absence. In two OWRD observation wells in the Malheur
Basin, groundwater levels seem to have been relatively stable since
1960 (OWRD 2005b). We acknowledge that diversion of springwater flows
and groundwater pumping can represent barriers to dispersal and
potentially isolate populations of P. robusta. However, these effects
are limited to populations only in southeast Oregon, and not elsewhere
in the species' range.
Water Quality--Temperature, Nutrients, and Chemical Stressors
The 1992 listing rule (57 FR 59244) stated, ``The quality of water
in these habitats has a direct effect on the species survival. The
species requires cold, well-oxygenated unpolluted water for survival.
Any factor that leads to a deterioration in water quality would likely
extirpate these taxa.''
Numerous reaches of the Snake and Columbia Rivers are classified as
water-quality-impaired due to the presence of one or more pollutants
(e.g., total phosphorous, sediments, total coliforms) in excess of
State or Federal guidelines. Nutrient-enriched waters primarily enter
the Snake and Columbia Rivers via springs, tributaries, fish farm
effluents, municipal waste treatment facilities, and irrigation returns
(U.S. Environmental Protection Agency (USEPA) 2002, pp. 4-20 to 4-22;
USFWS 2004, p. 1; U.S. Geological Survey (USGS) 2005, p. 5). Irrigation
water returned to rivers is generally warmer, contains pesticides or
pesticide byproducts, has been enriched with nutrients from agriculture
(e.g., nitrogen
[[Page 56944]]
and phosphorous), and frequently contains elevated sediment loads.
Pollutants in fish farm effluent include nutrients derived from
metabolic wastes of the fish and unconsumed fish food, disinfectants,
bacteria, and residual quantities of drugs used to control disease
outbreaks. Recent research found elevated levels of fine sediments and
nitrogen as well as elevated levels of trace elements, including zinc,
copper, cadmium, lead, and chromium, immediately downstream of
aquaculture discharges (Falter and Hinson 2003, p. 53). Additionally,
concentrations of lead, cadmium, and arsenic were detected in snails
collected during a research study in the Snake River (Richards 2002).
Researchers at the USGS (1998, p. 15) detected concentrations of some
pesticides in fish tissues, streams, irrigation canals, and irrigation
returns in the Snake River Basin in concentrations exceeding the
aquatic-life criteria established by the USEPA. While some effects of
pollutants, including metals and organic compounds in stream organisms,
are documented in the literature (Naimo 1995, pp. 351-352; Clements
1999, pp. 1076-1078; Courtney and Clements 2002, pp. 1770-1773), the
potential impact of these contaminants on Pyrgulopsis robusta has not
been studied and is unknown. However, P. robusta has been documented to
occur downstream in these stretches of the Snake River where municipal,
aquaculture, and agricultural discharges occur.
In the upper Snake River Basin in Wyoming, very low levels of
ammonia, nitrite and nitrate, phosphorus, trace metals, and pesticides
have been detected in water quality assessments (USGS 2004, p. 39).
Polecat Creek, which contains Pyrgulopsis robusta (Riley et al. 2003,
p. 6), was included in Wyoming's section 303(d) of the Clean Water Act
list of impaired waterbodies due to fecal coliform contamination (WDEQ
2004, pp. 1-91). However, water quality in the upper Snake River Basin
in Wyoming is generally described as good (USGS 2004, p. 38).
Changes in a river's flow and depth as a result of dams lead to
changes in sediment deposition dynamics and thermal characteristics
(Poff et al. 1997, p. 773; Platts 1992, p. 2). Water-transported
sediments that would be flushed downstream and deposited in pools,
eddies, and other still water environments under normal river flows now
settle in slow moving reservoir waters (Poff et al. 1997, p. 773;
Simons 1979, pp. 96, 100-104). Additionally, drops in water velocity in
reservoirs may result in elevated surface water temperatures and
reductions in dissolved oxygen (USGS 2005, p. 11). Pyrgulopsis robusta
has adapted to, and survives in, a relatively wide range of
temperatures within the Snake River (Lysne 2003, p. 27). The IPC has
collected P. robusta in water temperatures ranging from near freezing
to 80 degrees F (27 degrees C) (Clark 2005). While high temperatures
may be of concern for some aquatic snail species, we are not aware that
water temperature limits growth, reproduction, or survival of P.
robusta in any portion of its range. Pyrgulopsis robusta is widespread
and abundant, occurring in a variety of water quality, flow, and
temperature ranges. Expert and Manager Panels noted that water quality
has not significantly modified or curtailed the habitat or range of P.
robusta to an extent that threatens the continued existence of the species.
Grazing
Grazing by cattle has been suggested to be a threat to Pyrgulopsis
robusta habitat in southeastern Oregon (Frest and Johannes 1995, p.
196), but not in other areas. However, little information exists
regarding the impact of livestock grazing on the P. robusta in
southeastern Oregon. Since the mid 1980s, cattle have been excluded
from riparian areas, springs, and spring creeks in both the Harney and
Malheur Lakes region (Burnside 2004). The Expert and Manager panels
agreed that grazing does not appear to constitute a threat to the
continued existence of the species since it is limited only to portions
of the southeastern Oregon populations.
Summary of Factor A
In summary, Pyrgulopsis robusta is distributed over a wide
geographic area and a wide range of aquatic habitats in Idaho, Oregon,
Washington, and Wyoming. Based on new information, previous concerns
about the species being restricted to permanent free flowing water and
a reduction in range limiting its distribution or threatening its
existence are no longer valid. For example, since the 1992 listing, P.
robusta in the Snake River has been collected at 174 locations over 214
river miles (342 km). We are not aware that water temperature limits
growth, reproduction, or survival of P. robusta in any portion of its
range. Dam-induced changes to large river habitats in the Snake River
or Columbia River may create conditions that likely represent barriers
to P. robusta migration; however, the species persists throughout long
reaches of these two river systems in areas influenced by dams and
hydroelectric operations. Barriers to dispersal (i.e., isolated and
fragmented populations) were considered a threat factor by the Expert
Panel for the southeastern Oregon populations, but were considered
relatively insignificant in both the Snake and Columbia Rivers. The
fact that P. robusta is often locally abundant, resilient, and
adaptable to a range of extrinsic factors, contributes to the
determination that P. robusta is not in danger of extinction within the
foreseeable future. Thus, based on the best scientific and commercial
data, we conclude that the present or threatened destruction,
modification, or curtailment of P. robusta's habitat or range is not a
factor that threatens or endangers the species throughout all or a
significant portion of its range.
B. Overutilization for Commercial, Recreational, Scientific, or
Educational Purposes
Overutilization of Pyrgulopsis robusta for commercial,
recreational, or scientific purposes was not considered to be an
applicable threat at the time of the 1992 listing (57 FR 59242), and is
still not considered by the Expert Panel and Service's Manager Panel to
be a threat to P. robusta throughout all or a significant portion of
its range.
C. Disease or Predation
We have no information on the actual effects of disease or
parasites on Pyrgulopsis robusta.
At the time of the 1992 listing, fish predation was not considered
to be a major threat (57 FR 59242). There is currently no information
regarding the threat of predation on the continued existence of
Pyrgulopsis robusta. Predation on snails, in general, is documented and
is a natural occurrence (Merrick et al. 1992, p. 231; McCarthy and
Fisher 2000, p. 387), but information on the effects of predation on P.
robusta is limited. In the only known account of predation by fish on
P. robusta, Beetle (1957, p. 17) reported shells were found in the
digestive tract of a Roseyside sucker (Catostomus fecundus) near
Jackson Lake Dam, Wyoming. A recent study of predation ecology with
Pyrgulopsis species failed to observe predation by native crayfish
(Pacifasticus spp.) (Lysne and Koetsier 2001, p. 6).
The Expert Panel did not identify disease or predation as a
significant threat, but information is lacking to draw any definitive
conclusions about risks to Pyrgulopsis robusta due to predation. Based
on the best scientific and commercial data available, we conclude that
disease and predation are
[[Page 56945]]
not factors that endanger or threaten P. robusta throughout all or a
significant portion of its range.
D. The Inadequacy of Existing Regulatory Mechanisms
In the 1992 Idaho springsnail listing rule (57 FR 59244), nutrient
loading and pollution in the middle Snake River were identified as
areas of concern. We stated that it was unlikely that the downward
trend in water quality would be reversed any time soon, because it
would take several years before any recommendations to improve water
quality, as outlined in comprehensive resource management plans for the
Snake River, were fully implemented through local, State, and Federal
programs and efforts. However, since the 1992 listing rule, some water
quality improvements have been realized in localized reaches of the
Snake River, primarily with regard to sediment and phosphorus reduction
(Buhidar 2005). These improvements are more fully discussed in the
Water Quality Management section below.
Based on our status review, we describe various regulatory
mechanisms implemented by State and Federal resource agencies to
protect Pyrgulopsis robusta and its habitat. Federal agency regulations
are generally consistent across States, but State regulations may
differ considerably with regard to similar natural resource issues.
Analogous State natural resource agencies exist in Idaho, Oregon,
Washington, and Wyoming.
Wildlife Conservation Statutes and Plans
Washington has the comprehensive statutory authority and mandate to
``preserve and protect'' all wildlife, including invertebrates such as
Pyrgulopsis robusta, within its borders (Revised Code of Washington
77.04.012). The Idaho Department of Fish and Game (IDFG) developed a
Comprehensive Wildlife Conservation Strategy (Idaho Strategy) that
lists P. robusta as a ``species of greatest conservation need'' (IDFG
2005, p. 413). For example, Pyrgulopsis robusta conservation will be
considered when IDFG engages other States, Federal agencies, and other
conservation partners on proposed activities affecting Snake River
habitats (e.g., boat ramp construction). The Idaho Natural Heritage
Program lists Idaho springsnail as a species of concern, the Oregon
Natural Heritage Program lists Columbia and Harney Lake springsnails as
species of concern (ODFW 2005, p. 354), and in Wyoming, the Jackson
Lake springsnail is also listed as a species of concern (WGFD 2005, p.
15). These State wildlife conservation strategies and plans are useful
to land managers because they provide the best available information
for species of greatest conservation need and allow these managers to
make informed decisions about land use changes.
Water Quality Management
There are various State-managed water quality programs within the
range of Pyrgulopsis robusta in Idaho, Washington, Wyoming, and Oregon.
These programs are tiered off of the Clean Water Act (CWA), which
requires States to establish water quality standards that provide for
the protection and propagation of fish, shellfish, and wildlife, and
recreation in and on the water (``fishable/swimmable''). In addition,
as part of the CWA, States must also include an antidegradation policy
that protects waterbody uses, and high-quality waters. In Idaho,
Washington, Wyoming, and Oregon, point source discharges are regulated
through the National Pollutant Discharge Elimination System (NPDES)
program. These NPDES permits are written to meet all applicable water
quality standards established for a waterbody to protect human health
and aquatic life.
Idaho has established water quality standards (e.g., water
temperature and dissolved oxygen) for the protections of cold-water
biota (e.g., invertebrate species) in many reaches of the Snake River.
Although conditions within the river periodically exceed these limits
during the summer months (USGS 2005, pp. 7-12), Pyrgulopsis robusta has
been collected in water temperatures ranging from near freezing to 80
degrees F (27 degrees C) (Clark 2005). While high temperatures may be
of concern for some aquatic snail species, water temperature does not
seem to limit growth, reproduction, or survival of P. robusta in any
portion of its range.
Waters that do not meet standards due to point- and non-point
source pollution are listed on USEPA's 303(d) list of impaired water
bodies. States must submit to USEPA a 303(d) list (water quality-
limited waters) and a 305(b) report (status of the State's waters)
every two years. Water quality improvements with regard to point and
non-point sources have been realized in localized reaches of the Snake
River where P. robusta occurs (Buhidar 2005), primarily with regard to
sediment and phosphorus criteria. The IDEQ, under authority of the
State Nutrient Management Act, is coordinating efforts to identify and
quantify contributing sources of pollutants (including nutrient and
sediment loading) to the Snake River basin via the Total Maximum Daily
Load (TMDL) approach. TMDLs are developed, adopted, and implemented
within State Agricultural Water Quality Program, CWA section 401
Certification, BLM Resource Management Plans, the State Water Plan, and
local ordinances.
In Oregon, point- and non-point source pollution is managed by
Oregon's Department of Environmental Quality (ODEQ). TMDLs for several
stream reaches are in development for the Malheur River Basin where
Pyrgulopsis robusta exists. TMDLs establish mechanisms to address point
and non-point sources to bring these reaches into compliance with water
quality standards.
In Washington, the State's Department of Ecology (WECY) has a
mandate to manage point and non-point sources of pollution entering
Washington's waters (WECY 2005). Non-point sources of pollution are
regulated by numerous State of Washington statutes (WECY 2005), and
managed primarily through Washington's Water Quality Management Plan to
Control Non-point Source Pollution (Plan), published in 2000.
Pyrgulopsis robusta is found in the Columbia River, and the Plan may
indirectly benefit the springsnails that occur there.
In Wyoming, Pyrgulopsis robusta exists within waters that occur in
National Parks and are designated as Class 1 or ``outstanding waters''
by the Wyoming Department of Environmental Quality. Maintaining this
designation is one of the National Park Service's highest priorities
(USGS 2004, p. 2). We are not aware of any proposals to modify these
designations or of activities that would impair these water bodies.
Federal Land Management
Many large scale Federal management plans (e.g., U.S. Forest
Service Land and Resource Management Plans, U.S. Bureau of Land
Management (BLM) Resource Management Plans, National Wildlife Refuge
Comprehensive Conservation Plans, and Interior Columbia Basin Ecosystem
Management Plan) promote conservation of aquatic and terrestrial
habitats, including those on which Pyrgulopsis robusta depends.
Much of the Federal lands adjacent to the Snake River in Wyoming,
Idaho, Oregon, and Washington are managed by the BLM. Resource
Management Plans (RMPs) that guide BLM resource management include
provisions to protect water quality and riparian habitats. The Service
and the BLM in Idaho have finalized a Conservation
[[Page 56946]]
Agreement (USBLM 2006, pp. 1-11) that commits the BLM to carry out
specific actions to assess status and distribution of P. robusta in
areas affected by management actions and also to modify those actions
to avoid and minimize impacts to the species in the Snake River. In
addition, BLM has completed Endangered Species Act section 7
consultations for some actions that may affect P. idahoensis, now known
as P. robusta. The BLM's Boise and Twin Falls Districts have completed
a joint section 7 consultation for ongoing livestock grazing activities
in allotments adjacent to P. robusta habitats in the Snake River. Under
that consultation, the BLM and grazing permitees have implemented
actions to reduce the amount of shoreline grazing and grazing-related
sediment, thereby reducing the risk of take of P. robusta resulting
from livestock management.
Water Rights and Operations
In Idaho, there have been improvements in Snake River water
management since the time of listing the Idaho springsnail in 1992 (57
FR 59244). Portions of the Snake River are temporarily protected from
further allocation of consumptive use water rights (Barker et al. 2005)
by order of the Director of the Idaho Department of Water Resources,
although this does not preclude future water diversion or consumption
projects within the range of Pyrgulopsis robusta in the Snake River of
Idaho. For the other geographic areas where P. robusta occurs, we are
not aware of any State-sponsored programs restricting allocation of
consumptive use water rights.
The U.S. Bureau of Reclamation (BOR) operates numerous water
projects in the Snake River basin and is involved in a variety of fish
and wildlife conservation efforts through a number of different
programs in Oregon, Washington, and Idaho (USBOR 2005). The BOR has
conducted numerous surveys for sensitive mollusks for several years
(USBOR 2002, p. 2; 2003, p. 2; 2004, p. 2). Pyrgulopsis robusta has not
been found in the upper reaches of the Snake River. The BOR has
developed 10-year Resource Management Plans designed to create a
balance of resource development, recreation, and protection of natural
and cultural resources for the lands and waters they manage. These
plans outline resource management policies and actions that will be
implemented to protect natural resources (e.g., sensitive mollusk
species) over each plan's 10-year life (USBOR 2005).
The U.S. Army Corps of Engineers (USACE) operates several
hydroelectric projects on the Columbia River within the known range of
Pyrgulopsis robusta, including John Day, Dalles, and Bonneville Dams.
Since passage of the National Environmental Policy Act of 1969,
environmental protection has been an important mission for the
Northwestern Division of the Corps (USACE 2005). Since legislation
passed in 1990 establishing environmental protection as one of the
primary missions of water resource projects, the Corps has taken steps
to ensure that projects meet Federal, State, and local environmental
requirements (USACE 2005).
A Settlement Agreement between the IPC and Service concerning the
relicensing of IPC's mid-Snake and C.J. Strike hydroelectric projects
(IPC and USFWS 2004) requires IPC to implement studies to assess
effects on two listed Snake River aquatic snails, including Pyrgulopsis
robusta, from operation of hydroelectric dams. The 1992 listing rule
stated that proposals for numerous small hydroelectric projects to be
developed on remaining free-flowing portions of the middle Snake River
within the species' range, threatened the Idaho springsnail. However,
those proposals have subsequently been withdrawn or were not approved
by the Federal Energy Regulatory Commission (FERC) (Barker et al.
2005), reducing the likelihood of new FERC licensed hydroelectric
projects impacting P. robusta.
Summary of Factor D
A wide variety of regulatory mechanisms managed by State and
Federal resource agencies are in place to manage and protect
Pyrgulopsis robusta and the habitats upon which it depends. Federal
land management plans address conservation of P. robusta habitats, and
Federal and State agencies are managing water projects to minimize
impacts on P. robusta and protect the water quality where the species
occurs. Water withdrawals for the allocation of consumptive water use
in the Snake River basin have been halted through a temporary
moratorium by the State of Idaho. Additionally, IPC hydroelectric
projects on the Snake River in Idaho have begun to address P. robusta
management needs via specific commitments in recent Settlement
Agreements. Given that P. robusta occurs as multiple populations
distributed over a wide geographic area, and a wide range and variety
of habitat types, the variety of State and Federal regulatory
mechanisms that directly and indirectly provide conservation benefits
for P. robusta are generally considered adequate.
E. Other Natural or Manmade Factors Affecting Its Continued Existence
Numerous non-native and invasive species have become established
throughout the range of Pyrgulopsis robusta, and others threaten to
become established; however, their impacts on native species and
ecosystems have not been well studied or understood. (Frest and Johannes
2000, p. 1; Anderson 2004, pp. 15-18; Sytsma et al. 2004, pp. 33-34).
In the 1992 listing rule (57 FR 59244) for the Idaho springsnail,
we stated that the New Zealand mudsnail (Potamopyrgus antipodarum) was
a potential threat to the Idaho springsnail. The New Zealand mudsnail
was discovered in North America in 1987 in the Snake River, and has
spread rapidly (Bowler 1991, p. 175; Richards and Lester 2003, p. 1;
Richards et al. 2004, p. 114). The New Zealand mudsnail appears to
flourish in warm waterbodies in Wyoming and Montana on substrates of
silt to cobbles (Hall et al. 2003, p. 407; Cada 2004, p. 29), but is
also reported to reach high densities within the much cooler waters of
the Snake River (Clark et al. 2005, p. 17). The wide physical and
physiological tolerances of the New Zealand mudsnail allow it to thrive
in various habitats (Richards et al. 2001, pp. 375, 378; Hall et al.
2003, p. 408). The ability of the New Zealand mudsnail to occupy
numerous habitat types, including those typically occupied by native
snails (Richards et al. 2001, pp. 375, 378; Richards 2004, pp. 137-
139), does not always provide a competitive advantage for the New
Zealand mudsnail in interactions with native species (Cowie 2004).
In the Greater Yellowstone Ecosystem, researchers found evidence
that New Zealand mudsnails limit the colonization of, and may influence
the large-scale distribution of, other macroinvertebrates (Kerans et
al. 2005, p. 135). Research in Wyoming has demonstrated that New
Zealand mudsnails have reduced densities of Pyrgulopsis robusta in
Polecat Creek in Yellowstone National Park, but P. robusta and New
Zealand mudsnails continue to co-exist (Riley et al. 2003, pp. 16-18;
Gustafson 2005, pp. 7-8). The threat the New Zealand mudsnail poses to
P. robusta remains uncertain. However, the New Zealand mudsnail does
not appear to currently endanger or threaten P. robusta throughout all
or a significant portion of its range.
The Expert Panel and Service's Manager Panel identified the threat
of non-native species, including the New Zealand mudsnail, to
Pyrgulopsis robusta's survival as low. Both panels
[[Page 56947]]
identified the lack of information about non-native species
interactions with P. robusta as an area of uncertainty. However, direct
cause and effect information that non-native species are endangering or
threatening P. robusta populations does not exist.
Thus, based on the best scientific and commercial data available,
we have concluded that other natural and manmade factors do not
endanger or threaten Pyrgulopsis robusta throughout all or a
significant portion of its range.
Summary of Threats Section
Evidence collected since the Idaho springsnail was listed in 1992
as endangered (57 FR 59244) indicates Pyrgulopsis idahoensis no longer
constitutes a distinct species. The revised species, Pyrgulopsis
robusta, is a combined taxon composed of four previously regarded as
taxonomically distinct springsnails--the Idaho, Jackson Lake, Harney
Lake, and Columbia River springsnails.
Pyrgulopsis robusta populations in the Columbia and Snake Rivers
have relatively high abundance and occur as multiple populations
distributed over a wide geographic area. The Columbia River population
of P. robusta is currently known from 17 locations starting from river
mile 20 (rkm 32) and continuing for nearly 400 river miles (644 rkm)
upstream to just below Priest Rapids Dam. In the Snake River, P.
robusta is more widely distributed than originally cited in the 1992
listing rule and has been documented at over 174 known locations, over
214 river miles (344 km). The species occurs in a range of habitat
types, and is resilient to changes in flow and water quality. Extant
populations occur in various habitats, including springs, and river
reaches characterized by a wide range of flow conditions, and both
occur in lake and reservoir locations. Pyrgulopsis robusta has adapted
to, and survives in, a relatively wide range of temperatures.
Fluctuating water temperatures likely do not limit growth,
reproduction, or survival of P. robusta in any portion of its range.
Adequate existing regulatory mechanisms contributing to P. robusta
conservation include water quality regulations and FERC hydropower
Settlement Agreements. At this time P. robusta exists in multiple
populations in the States of Oregon, Washington, Idaho, and Wyoming and
is expected to persist into the future. We evaluated the best available
scientific and commercial data regarding status of and threats to the
newly described P. robusta, and determined that the species is not in
danger of extinction, nor is it likely to become endangered in the
foreseeable future throughout all or a significant portion of its range,
and therefore does not meet the definition of threatened or endangered.
Finding
We have carefully assessed the best scientific and commercial
information available regarding the past, present, and future threats
faced by this species. We reviewed the petitions, available published
and unpublished scientific and commercial information, and information
submitted to us during the public comment period following our 90-day
petition findings. This finding reflects and incorporates information
we received during the public comment period and responds to
significant issues (i.e., incorporates appropriate information raised
in comments regarding P. robusta taxonomy, life history, distribution,
status, and threats). We also consulted with recognized springsnail
experts and Federal and State resource agencies. Based on this review,
we find that (1) Based on a change in taxonomic status, the Idaho
springsnail is no longer considered a listable entity, and therefore
its delisting is warranted; (2) based on a change in taxonomic status,
the Jackson Lake, Harney Lake, and Columbia springsnails are no longer
considered listable entities, and therefore their listing is not
warranted; and (3) listing of the combined taxon, P. robusta, is not
warranted because P. robusta is distributed over a wide geographic area
and range of aquatic habitats, is often locally abundant, and appears
to be resilient and adaptable to a range of factors affecting it,
including varying water temperatures, flow conditions, and water
chemistry, and is therefore not threatened with endangerment throughout
all or a significant portion of its range.
In making this determination, we have followed the procedures set
forth in section 4(a)(1) of the Act and regulations implementing the
listing provisions of the Act (50 CFR part 424). While the finding
reflects the analyses conducted to fulfill our responsibilities under
sections 4(b)(3)(A) (status review) and 4(c)(2) (5-year review) of the
Act, we request that you submit any new information, whenever it
becomes available, for this species concerning status and threats. We
intend that any action for the P. robusta be as accurate as possible.
Therefore, we will continue to accept additional information and
comments from all concerned governmental agencies, the scientific
community, Native American Tribes, industry, or any other interested
party concerning this finding.
Delisting Proposal
Section 4(a)(1) of the Act and regulations (50 CFR part 424) issued
to implement the listing provisions of the Act set forth the procedures
for adding species to, or removing them from, Federal lists. The
regulations at 50 CFR 424.11(d) state that a species may be delisted
if: (1) The species is extinct or has been extirpated from its previous
range; (2) the species has recovered and is no longer endangered or
threatened; or (3) investigations show that the best scientific or
commercial data available when the species was listed, or the
interpretation of such data, were in error. Since the time of the Idaho
springsnail listing, additional study has shown that Pyrgulopsis
idahoensis is not a distinct species, but is now part of a combined
taxon (Pyrgulopsis robusta) composed of springsnails occurring in the
States of Wyoming, Oregon, Idaho, and Washington. Our evaluation of P.
robusta status and threats indicates it does not qualify for protection
under the Act. After a review of the best available scientific and
commercial data, we are proposing to remove Pyrgulopsis idahoensis from
the List of Endangered and Threatened Wildlife in 50 CFR 17.11.
Effects of the Proposed Rule
This action proposes to remove Pyrgulopsis idahoensis from the List
of Endangered and Threatened Wildlife. If this proposed rule is
finalized, the prohibitions and conservation measures provided by the
Act would no longer apply to P. robusta, with which P. idahoensis has
been combined. Interstate commerce, import, and export of this species
would not be prohibited under the Act. In addition, Federal agencies
would no longer be required to consult under section 7 of the Act on
actions which may affect this species. There is no designated critical
habitat for this species, and therefore the proposed rule has no effect
on critical habitat.
Public Hearing
The Act provides for one or more public hearings on this proposal,
if requested. Requests must be filed by the date specified in the DATES
section. Such requests must be made in writing and addressed to the
Field Supervisor, Snake River Fish and Wildlife Office, 1387 S. Vinnell
Way, Room 368, Boise, ID 83709.
Peer Review
In accordance with our peer review policy published in the Federal
Register on July 1, 1994 (59 FR 34270), we will seek expert opinions of
at least three
[[Page 56948]]
appropriate and independent specialists regarding this proposed rule.
The purpose of such review is to ensure that our delisting proposal is
based on scientifically sound data, assumptions, and analyses. We will
send copies of this proposed rule to these peer reviewers immediately
following publication in the Federal Register. We will consider all
peer review comments received during preparation of a final rulemaking.
Accordingly, the final decision may differ from this proposed rule.
Clarity of the Rule
Executive Order 12866 requires each agency to write regulations and
notices that are easy to understand. We invite your comments on how to
make this proposed rule easier to understand, including answers to
questions such as the following: (1) Are the requirements in the
proposed rule clearly stated? (2) Does the proposed rule contain
technical jargon that interferes with the clarity? (3) Does the format
of the proposed rule (grouping and order of the sections, use of
headings, paragraphing, and so forth) aid or reduce its clarity? (4) Is
the description of the notice in the SUPPLEMENTARY INFORMATION section
of the preamble helpful in understanding the proposed rule? (5) What
else could we do to make this proposed rule easier to understand?
Send a copy of any comments on how we could make this proposed rule
easier to understand to: Office of Regulatory Affairs, Department of
the Interior, Room 7229, 1849 C Street, NW., Washington, DC 20240. You
may e-mail your comments to this address: Exsec@ios.doi.gov.
Paperwork Reduction Act of 1995 (44 U.S.C. 3501 et seq.)
Office of Management and Budget (OMB) regulations at 5 CFR 1320
implement provisions of the Paperwork Reduction Act (44 U.S.C. 3501 et
seq.), which requires that interested members of the public and
affected agencies have an opportunity to comment on agency information
collection and recordkeeping activities (5 CFR 1320.8(d)). The OMB
regulations at 5 CFR 1320.3(c) define a ``collection of information''
as the obtaining of information by or for an agency by means of
identical questions posed to, or identical reporting, recordkeeping, or
disclosure requirements imposed on, 10 or more persons. Furthermore, 5
CFR 1320.3(c)(4) specifies that ``10 or more persons'' refers to the
persons to whom a collection of information is addressed by the agency
within any 12-month period. This proposal does not contain any new
collections of information that require OMB approval under the
Paperwork Reduction Act.
National Environmental Policy Act
The Service has determined that Environmental Assessments and
Environmental Impact Statements, as defined under the authority of the
National Environmental Policy Act of 1969, need not be prepared in
connection with actions adopted under section 4(a) of the Act. We
published a notice outlining our reasons for this determination in the
Federal Register on October 25, 1983 (48 FR 49244). This assertion was
upheld in the courts of the Ninth Circuit (Douglas County v. Babbitt,
48 F.3d 1495 (9th Cir. Ore. 1995), cert. denied 116 S. Ct. 698 (1996).
Government-to-Government Relationship With Tribes
In accordance with the President's memorandum of April 29, 1994,
``Government-to-Government Relations With Native American Tribal
Governments'' (59 FR 22951), Executive Order 13175, and the Department
of the Interior's manual at 512 DM 2, we readily acknowledge our
responsibility to communicate meaningfully with recognized Federal
Tribes on a government-to-government basis. Therefore, we will solicit
information from Native American Tribes during the comment period to
determine potential effects on them or their resources that may result
from the delisting of the Idaho springsnail, and we will fully consider
their comments on the proposed rule submitted during the public comment
period.
References
A complete list of all references cited is available on request
from the Snake River Fish and Wildlife Office (see ADDRESSES).
Author
The authors of this document are staff of the U.S. Fish and
Wildlife Service, Snake River Fish and Wildlife Office, Boise, Idaho.
List of Subjects in 50 CFR Part 17
Endangered and threatened species, Exports, Imports, Reporting and
recordkeeping requirements, Transportation.
Proposed Regulation Promulgation
Accordingly, we hereby propose to amend part 17, subchapter B of
chapter I, title 50 of the Code of Federal Regulations, as set forth below:
PART 17--[AMENDED]
1. The authority citation for part 17 continues to read as follows:
Authority: 16 U.S.C. 1361-1407; 16 U.S.C. 1531-1544; U.S.C.
4201-4245; Pub. L. 99-625, 100 Stat. 3500; unless otherwise noted.
Sec. 17.11 [Amended]
2. Amend Sec. 17.11(h) by removing the entry ``Springsnail, Idaho
(Fontelicella idahoensis)'' under SNAILS from the List of Endangered
and Threatened Wildlife.
Dated: September 20, 2006.
Marshall Jones,
Acting Director, Fish and Wildlife Service.
[FR Doc. E6-15915 Filed 9-27-06; 8:45 am]
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