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Declining
Amphibian Task Force (DAPTF)California-Nevada Working Group Meeting
2004 :
January 15 and 16,
2004
University of Nevada, Reno
PRESENTATIONS
Factors Implicated
in Amphibian Population Declines: A National Perspective
Dave Bradford, US Environ. Protection Agency, Las Vegas, CA. (pdf
file)
Aspects
of the reproductive ecology of Rana boylii: implications
for species conservation and management Clara Wheeler,
US Forest Service, Arcata, CA. (pdf
file)
Video Files of
Rana boylii:
- Aggression
- Oviposition
(1)
- Oviposition
(2)
An
Experimental Approach to Managing Rare Ranids in Southern California
Cindy Hitchcock, USGS, Biol. Resources Division, San Diego,
CA. (pdf file)
Population
Status, Threats, and Conservation Efforts for the Amargosa Toad
(Bufo nelsoni) Brian Hobbs, Nevada Dept. of
Wildlife, Las Vegas, NV. (pdf
file)
Amphibian
Conservation Planning in Nevada: The Efficacy of Conservation Agreements
and Strategies Jon Sjoberg, Nevada Dept. of Wildlife,
Las Vegas, NV. (pdf
file)
AGENDA
David Bradford, Chair
Anita Cook, Eric Simandle, Tom Skiles: Local Committee
Thursday,
January 15, 2004
10:00-10:10 am Introduction
and Announcements. David Bradford, US Environmental Protection
Agency, Las Vegas, NV
DISEASE, MALFORMATIONS,
AND AMPHIBIAN POPULATION DECLINES
Moderator: David Bradford, US Environmental Protection Agency, Las
Vegas, NV
10:10-10:30 am Amphibian
Diseases! Why Didn't We Think of This Before? Gretchen
Padgett-Flohr, Rana Resources, Davis, CA.
10:30-11:10 am Chytridiomycosis
in the Mountain Yellow-Legged Frog. Cheryl Briggs*,
Lara Rachowicz*, and John Parker*, Univ. of Calif., Berkeley, CA.
11:10-11:30 am Amphibian
Chytridiomycosis and California Herpetofauna. Gretchen
Padgett-Flohr, Rana Resources, Davis, CA.
11:30-11:40 am Larval
Diseases, Should We Be Concerned? Nathan Nieto, Humboldt
State Univ., Arcata, CA.
11:40-11:50 am Amphibian
Malformations at Three National Wildlife Refuges in California.
Jamie Bettaso, US Fish & Wildlife Service, Arcata, CA.
11:50-1:20 pm Lunch
Moderator: Amy Lind,
US Forest Service, Sacramento, & Univ. Calif., Davis, CA.
INVASIVE SPECIES
AND NATIVE AMPHIBIANS
1:20-1:40 pm
Synopsis of Current Amphibian Projects Supported
or Conducted by the California Department of Fish and Game.
Betsy Bolster, CA Dept. Fish & Game, Sacramento, CA
1:40-2:00 pm Negative
Effects of Introduced Trout on Ambystoma macrodactylum in
the Sierra Nevada, California: Results from "Historic Site" Surveys,
Watershed Surveys, and Experimental Data. Karen Leyse,
Univ. of Calif., Davis, CA. 2:00-2:10
pm Community Response to Experimental Fish Removals in
Wilderness Basins in Northern California. Karen Pope, Univ.
of Calif., Davis, CA.
2:10-2:25 pm
Foothill Yellow-Legged Frog (Rana boylii)
Predation by the Introduced Signal Crayfish (Pacifasticus leniusculus)
in the North Fork Feather River, CA. Kevin Wiseman,
Garcia & Assoc., San Francisco, CA.
ROLE OF CHEMICAL
CONTAMINATION IN AMPHIBIAN DECLINES
2:25-2:30 pm
Summary of Ongoing Projects Addressing Effects of Airborne Contaminants
on Amphibians in California Mountains. Dave Bradford, US
Environmental Protection Agency, Las Vegas, NV.
2:30-2:50 pm
The Role of Contaminants in California Amphibian Declines.
Gary Fellers, USGS, Biological Resources Division, Pt. Reyes, CA.
2:50-3:35 pm Break
Moderator: Betsy Bolster,
Calif. Dept. Fish & Game, Sacramento, CA.
LEGAL ACTIONS
3:35-3:45 pm
Legal Status Summary. Deanna Spooner, Pacific Rivers Council,
Eugene, OR.
3:45-3:55 pm
Status of Two Lawsuits Against the U.S. Environmental Protection
Agency and California Department of Pesticide Regulation.
Michael Graf, private attorney, El Cerrito, CA.
ECOLOGY, POPULATION
GENETICS, AND ACTIVE MANAGEMENT - BUFONID TOADS
MOSTLY
3:55-4:15 pm
Amphibian Conservation Planning in Nevada: The
Efficacy of Conservation Agreements and Strategies. Jon
Sjoberg, Nevada Dept. of Wildlife, Las Vegas, NV.
4:15-4:35 pm
Metapopulation Structure in Two Species of Rare Toads (Bufo
nelsoni and Bufo exsul) with Implications for Conservation.
Eric Simandle* and C. Richard Tracy, Univ. of Nevada, Reno, NV.
4:35-4:55 pm Use
of Habitat by Adult Amargosa Toads (Bufo nelsoni).
Denise Jones* and C. Richard Tracy, Univ. of Nevada, Reno,
NV.
POSTERS
All Day Imperiled
Amphibians of the West.Pacific Rivers Council, Eugene, OR.
All Day Metapopulation
Processes or Infinite Dispersal?: Habitat Patch Occupancy by Toads
(Bufo punctatus) in a Naturally Fragmented Desert Landscape.
David F Bradford1, Anne C Neale1, Maliha S
Nash1, Donald W Sada2, and Jef R Jaeger3.1U.S.
Environ. Protection Agency, Las Vegas, NV; 2Desert Research
Institute, Reno, NV; 3Univ. of Nevada, Las Vegas, NV.
Friday,
January 16, 2004
Moderator: Roland Knapp,
Univ. of Calif., Sierra Nevada Aquatic Research Lab, Mammoth Lakes,
CA
ECOLOGY, POPULATION
GENETICS, AND ACTIVE MANAGEMENT - BUFONID TOADS
MOSTLY (continued)
8:30-8:50 am Population
Status, Threats, and Conservation Efforts for the Amargosa Toad
(Bufo nelsoni). Brian Hobbs, Nevada Dept.
of Wildlife, Las Vegas, NV.
8:50-9:10 am Using
the ARMI (Amphibian Research and Monitoring Initiative) Metric,
Percent Area Occupied, for Monitoring Arroyo Toads in Southern California.
Cheryl Brehme, USGS, Biol. Resources Division, San Diego,CA.
ECOLOGY, POPULATION
GENETICS, AND ACTIVE MANAGEMENT - RANID FROGS MOSTLY
9:10-9:30 am
Status of the Relict Leopard Frog (Rana onca):
Our Limited Understanding of the Distribution, Size, and Dynamics
of Extant and Recently Extinct Populations. Jef Jaeger1*,
David Bradford2, Randy Jennings3, and Brett
Riddle1. 1Univ. of Nevada, Las Vegas, NV;
2US Environ. Protection Agency, Las Vegas, NV; 3Western
New Mexico Univ., Silver City, NM.
9:30-9:45 am
Conservation Activities and Plans for the Relict Leopard Frog,
Rana onca. Ross Haley, Lake Mead Nat. Recreation Area,
Boulder City, NV.
9:45-9:55 am
Population Survey and Inventory Results for the Columbia Spotted
Frog, Rana luteiventris, in Elko County, Nevada for 2003.
Chris Drake, Nevada Dept. of Wildlife.
9:55-10:40 am Break
Moderator: Gary Fellers,
USGS, Biological Resources Division, Pt. Reyes, CA
10:40-11:00 am An
Experimental Approach to Managing Rare Ranids in Southern California.
Cindy Hitchcock, USGS, Biol. Resources Division, San Diego,
CA.
11:00-11:10 am Overview
of Amphibian Projects at the USFS Redwood Sciences Lab. Don
Ashton, US Forest Service, Arcata, CA.
11:10-11:20 am Spatial
Dynamics of a Montane Frog (Rana cascadae) in Response
to Resource Availability. Justin Garwood, Humboldt State
Univ., Arcata, CA.
11:20-11:30 am Aspects
of the reproductive ecology of Rana boylii: implications
for species conservation and management. Clara
Wheeler, US Forest Service, Arcata, CA.
11:30-11:50 am Reintroduction
of a Declining Amphibian: Determining an Ecologically Feasible Approach
Through Analysis of Decline Factors, Genetic Structure, and Habitat
Associations. Amy Lind, US Forest Service, Sacramento,
& Univ. Calif., Davis, CA.
11:50-1:05 pm Lunch
(Note: Lunch today is shorter than yesterday)
Moderator: Anita Cook,
Nevada Department of Wildlife, Reno, NV
1:05-1:25 pm
Re-establishment of California Red-legged Frog Populations
at Pinnacles National Monument. Paul Johnson1*,
Norman Scott2, and Amy Fesnock. 1Pinnacles
Nat. Monument, Paicines, CA; 2Creston, CA.
1:25-1:45 pm
Population Studies on the Declining Amphibians: Rana aurora,
R. muscosa, and Bufo boreas. Gary Fellers,
USGS, Biol. Resources Division, Pt. Reyes, CA.
1:45-1:55 pm
Restoration of Mountain Yellow-legged Frogs in Kings
Canyon National Park. Danny Boiano, Sequoia & Kings
Canyon Nat. Parks, Three Rivers, CA.
1:55-2:05 pm
Restoration of Mountain Yellow-legged Frog Populations in Humphreys
Basin. Roland Knapp, Univ. of Calif., Sierra Nevada Aquatic
Research Lab, Mammoth Lakes, CA.
2:05-2:20 pm
Updates on the US Forest Service's Amphibian Conservation Assessments
and Sierra Nevada Amphibian Monitoring Program. Cathy Brown1
or Amy Lind2. 1US Forest Service, Albany,
CA; 2US Forest Service, Sacramento
OTHER IMPORTANT
TOPICS
2:20-2:30 pm
Update on the Forest Reptile and Amphibian Working Group's (FRAWG)
Consideration of Seeps, Springs, Wet Meadows, and Wet Areas in California's
Forest Practice Rules and Habitat Conservation Plans. Don
Ashton, US Forest Service, Arcata, CA.
2:30-2:50 pm
Factors Implicated in Amphibian Population Declines:
A National Perspective. Dave Bradford, US Environ.
Protection Agency, Las Vegas, CA.
2:50-3:10 pm
Demonstration and Discussion of the New CA/NV DAPTF Website. Amy
Lind. US Forest Service, Sacramento, and Univ. Calif., Davis, CA.
3:10-3:15 pm
Next meeting date and place.
ABSTRACTS
Restoration of Mountain
Yellow-legged Frogs in Sequoia and Kings Canyon National Parks
To help reverse the decline
of the mountain yellow-legged frog (Rana muscosa), Sequoia
and Kings Canyon National Parks (SEKI) began removing introduced
trout in 2001 from six lakes and adjacent streams using gill nets
and backpack electrofishers. Over 1,700 introduced trout were removed
from these sites in 2003, and a total of over 7,700 introduced trout
have been removed since the project inception in 2001. Complete
eradication of introduced trout is expected from five of the six
lakes by the middle of the 2004 season. To assess frog recovery,
shoreline visual encounter surveys also were conducted in the restoration
areas. The average number of frogs and tadpoles detected per restoration
lake was 16 times greater in 2003 versus 2001. The change observed
in the strongest responding frog population was 33 times greater
in 2003 versus 2001. SEKI recently received a funding award to
hire an additional frog restoration crew for three seasons. As
a result, removal of introduced will begin in five additional SEKI
lakes in 2004. A programmatic environmental document is also being
planned that will guide management of all threats to mountain yellow-legged
frogs across the entire park.
BOIANO, DANNY
Sequoia &
Kings Canyon National Parks, Division of Natural Resources, 47050
General Highway, Three Rivers, CA, 93271; E-mail: danny_boiano@nps.gov
Synopsis
of Current Amphibian Projects Supported or Conducted by the California
Department of Fish and Game
During 2003, the California
Department of Fish and Game (CDFG) supported or conducted a variety
of activities that benefited native amphibians. CDFG sampled 1,984
waters during its third year of amphibian/fish surveys in the Sierra
Nevada. Of these waters, 989 contained amphibians - 195 with Rana
muscosa and 32 with Bufo canorus. Six sites contained
R. muscosa and trout. CDFG conducted habitat restoration
(trout removal) for R. muscosa in ten lakes on the east side
of the Sierra Nevada, and in one stream in southern California.
CDFG sponsored three research contracts including R. muscosa
monitoring in southern California (Fisher USGS), R. muscosa
habitat use and movement in northern Sierra Nevada (esp. stream
habitats) (Vredenberg, UC Berkeley), and responses of R. cascadae
and other wildlife to changes in fishery management in the Trinity
Alps (Pope UC Davis). CDFG continued work on aquatic biodiversity
basin management plans to guide amphibian conservation and angling
opportunities. Basin plans provide long-term aerial fish stocking
criteria; interim short-term criteria, developed in 2001, are based
on presence of R. muscosa and evaluating stocking need based
on sound fishery management practices. CDFG began working with
the State Water Resources Control Board to develop and implement
amphibian survey protocols and requirements for FERC relicensing.
CDFG and the USFWS produced a joint, interim survey guidance for
the California tiger salamander.
BOLSTER, BETSY
California Department
of Fish & Game, Habitat Conservation Planning Branch, Sacramento,
California 95814; bbolster@dfg.ca.gov
Factors
Implicated in Amphibian Population Declines in the United States
Factors known or suspected
to be adversely affecting native amphibian populations in the US
were identified using information from 267 species accounts written
in a standardized format by multiple authors in the forthcoming
book, "Status and Conservation of U.S. Amphibians." Specific adverse
factors were identified for 53 (58%) of 91 anurans and 93 (53%)
of 176 caudates. Land use was the most frequently implicated adverse
factor for both anurans and caudates. The predominant land use
factors were agriculture, urban development, and timber harvest/silviculture,
followed by road construction/use, livestock grazing, altered fire
regime, recreational use/development, and mining. Exotic animal
species were the second most frequently implicated adverse factor
for anurans, and third for caudates. Exotic taxa implicated consisted
of a number of introduced fishes, American bullfrogs, crayfish,
defoliating insects, and other amphibians. Chemical contamination
ranked third for anurans and second for caudates, and included acid
precipitation, pesticides/herbicides, and mine water pollution.
A regional analysis revealed that exotic species were implicated
significantly more frequently among anurans in the western US than
elsewhere, whereas chemical contamination was implicated significantly
more frequently among caudates in the non-western US. Less frequently
implicated factors were disease, water source modification, collecting/harvesting,
and UV-B radiation.
BRADFORD, DAVID
F.
U.S. Environmental
Protection Agency, P.O. Box 93478, Las Vegas, NV 89193-3478; bradford.david@epa.gov.
Metapopulation
Processes or Infinite Dispersal?: Habitat Patch Occupancy by Toads
(Bufo punctatus) in a Naturally Fragmented Desert Landscape
(Poster)
Amphibians
are often thought to have a metapopulation structure, which may
render them vulnerable to habitat fragmentation. The red‑spotted
toad (Bufo punctatus) in the southwestern USA and Mexico
commonly inhabits wetlands that have become much smaller and fewer
since the late Pleistocene. This study tests two predictions based
on metapopulation theory --- the incidence of habitat patch occupancy
is directly related to patch size and inversely related to patch
isolation --- and a third, potentially competing hypothesis that
patch occupancy is influenced by local environmental conditions.
In a 20,000 km2 area of the eastern Mojave Desert, 128
potential habitat patches (primarily springs) were identified and
surveyed for local environmental characteristics and presence/absence
of B. punctatus. Patch isolation metrics were based on nearest-neighbor
distances, calculated both as Euclidian distance and distance via
connecting drainage channels. B. punctatus was found at
73% of the sites, including all of the 15 historic (pre-1970) sites.
Based on stepwise multiple logistic regression, the incidence of
patch occupancy increased significantly with patch size, and was
also significantly related to elevation, latitude, and four metrics
that were associated with rocky terrain, periodic scouring water
flows, and ephemeral water. In contrast, incidence of patch occupancy
was not significantly related to patch isolation. These findings
are consistent with a "patchy population" model, rather than the
classical equilibrium metapopulation model, implying frequent dispersal
among patches and virtually no local extinctions. Implicated dispersal
distances of many kilometers are large for an amphibian.
BRADFORD,
DAVID F.
NEALE. ANNE C.
NASH, MALIHA S.
U.S. Environmental
Protection Agency, P.O. Box 93478, Las Vegas, NV 89193-3478; bradford.david@epa.gov.
SADA, DONALD
W.
Desert Research
Institute, 2215 Raggio Pkwy., Reno, Nevada 89512.
JAEGER, JEF
R.
Department of
Biological Sciences, University of Nevada, 4505 Maryland Parkway,
Las Vegas, Nevada 89154-4004
Using
the ARMI Metric, Proportion Area Occupied, for Monitoring Arroyo
Toads in Southern California
ARMI
(Amphibian Research and Monitoring Initiative) has adopted proportion
of area occupied (PAO, MacKenzie et al. 2002) as a standardized
metric for midlevel monitoring of amphibian populations. In 2003,
we implemented a new monitoring program using this metric for the
endangered arroyo toad (Bufo californicus) on Marine Corps
Base Camp Pendleton (MCBCP). Using the PAO approach, we are tracking
the presence of breeding arroyo toads over 89 km of potential habitat.
Because they have a much higher probability of detection, we are
using the presence of tadpoles to document the presence of adult
breeding populations. We implemented the first year of a 5 year
rotating panel design by comprehensively surveying 120 randomly
stratified survey lengths (250 km each). The survey lengths were
visited from 1 to 4 times throughout the breeding season. We then
used the loglinear modeling program PRESENCE to model the data and
correct for imperfect detection probabilities. In 2003, 87.4% (se
= 9.5) of wet habitat was occupied by breeding arroyo toads. We
also evaluated over 14 habitat and survey specific variables in
the models. These included landscape variables, environmental variables,
and the presence of nonnative plant and aquatic vertebrate species.
Results showed that the absence of crayfish was the single most
significant predictor of the presence of arroyo toad tadpoles. At
this time, we do not know if this relationship is causative or correlative.
BREHME,
CHERYL S.
Western Ecological
Research Center, US Geological Survey, 5745 Kearny Villa Road, San
Diego, CA 92123, cbrehme@usgs.gov.
Chytridiomycosis
in Mountain Yellow-Legged Frogs (Rana muscosa)
A
collaborative project is underway at the University of California,
Berkeley to study the impact of chytridiomycosis on Rana muscosa
populations. The project includes large scale surveys of distribution
and temporal progression of the disease through the Sierra, laboratory
and field experiments studying transmission and the disease process,
genetic work investigating the origin and spread of the disease,
and dispersal studies to parameterize spatially-explicit models
aimed at understanding the dynamics of the disease.
Laboratory
and field mesocosm experiments were performed to estimate the mortality
rate of post-metamorphic Rana muscosa and to test if infected
tadpoles retain their infection as they metamorphose. In the lab
at 17<C, 100% of infected tadpoles metamorphosed and died of
chytridiomycosis, and 100% of uninfected tadpoles metamorphosed
successfully with no mortality. Mesocosm experiments during the
summer of 2003 at four infected lakes and three uninfected lakes
in the Sierra Nevada, California followed tadpoles through metamorphosis.
Field results mimicked lab results; infected tadpoles metamorphosed
and experienced very high mortality, and uninfected experienced
very low mortality.
In
attempt to characterize the disease processes involved with chytridiomycosis,
two factors, ambient temperature and hydration status, were found
to contribute to morbidity and mortality of frogs infected with
Batrachochytrium. Laboratory experiments conducted at UCB
support previous findings of ambient temperature affects on survival
rate. In Rana muscosa, temperatures of 22<C result in
a 50% mortality rate while temperatures of 17<C result in 100%
mortality. Furthermore, observational evidence collected at UCB
support dehydration and hypovolemia to be present during, and contribute
to, the ultimate demise of infected animals.
BRIGGS,
CHERYL*
Department of
Integrative Biology, University of California, Berkeley, CA 94720-3140;
cbriggs@socrates.berkeley.edu
RACHOWICZ,
LARA*
Department of
Integrative Biology, University of California, Berkeley, CA 94720-3140;
larar@socrates.berkeley.edu
PARKER,
JOHN*
Department of
Integrative Biology, University of California,Berkeley, CA 94720-3140;
jparker@olac.berkeley.edu
Population
Status, Threats, and Conservation Efforts for the Amargosa Toad
(Bufo nelsoni)
The
Amargosa toad is an amphibian endemic to the Oasis Valley in Nye
County, Nevada. Due to the cooperation and efforts of several agencies,
organizations and local residents, placing the toad on the Endangered
Species Act list was found to be "not warranted" by the U.S. Fish
and Wildlife Service in 1994. The Conservation Agreement for the
Amargosa Toad (Bufo nelsoni) and co-occurring species in
Oasis Valley, Nye County, Nevada was signed in 2000. An intensive
mark and recapture survey, using PIT tags, began at various sites
throughout the valley in 1998. These surveys have resulted in estimates
for groups or complexes of survey sites using the computer program
MARK. Valley-wide, the population estimates over the past 6 years
have ranged from 1774 to 2401 toads. Based on these annual visits,
the cooperators have been able to assess and address habitat needs
at each survey site or complex of sites. Such needs include rehabilitation
and maintenance of spring sites and non-native species removal and/or
control. Upcoming projects include a pond restoration at the Harlan/Keal
site and habitat rehabilitation in the Amargosa River just north
of town.
Status
of the Relict Leopard Frog (Rana Onca): Our Limited Understanding
of the Distribution, Size, and Dynamics of Extant and Recently Extinct
Populations
The
relict leopard frog (Rana onca) was once thought to be extinct,
but has recently been shown to comprise a valid taxon with extant
populations. Here, we discuss research from several studies, conducted
between 1991 and 2001, that represent the basis for our understanding
of the distribution, size, and dynamics of extant and recently extinct
relict leopard frog populations. We review phylogeographic findings
that have been used to identify this taxon, discuss the delineation
of a minimum historical range, report the findings from mark-recapture
studies and visual encounter surveys, and describe the extinction
of 2 of 7 populations extant in the 1990s and speculate on the causes
for these extinctions. A minimum historical range for this taxon
was based on records from 24 localities (> 1 km apart) along
the Virgin and Muddy River drainages and adjacent portion of the
Colorado River drainage in southern Nevada, northwestern Arizona,
and southwestern Utah. These frogs currently exist naturally at
only 5 spring sites distributed in 2 general areas: near the Overton
Arm of Lake Mead, and in Black Canyon along the Colorado River below
Lake Mead, Nevada. The loss of populations in the 1990's greatly
reduced the extant distribution of this frog. These population
extinctions occurred concomitantly with encroachment of emergent
vegetation into pools. A rough estimate for the total number of
frogs at all sites in 2001 was approximately 1100 adults (range
693-1833). Annual adult survivorship from a mark-recapture study
at one site was estimated at 0.27. The limited number and distribution
of populations, the low estimated total population size, the high
estimated population turnover, and the observations of recent population
extinctions are reasons for concern about the continued existence
of the relict leopard frog.
JAEGER,
J. R. *
Department of
Biological Sciences, University of Nevada, 4505 Maryland Parkway,
Las Vegas, Nevada 89154-4004; jaeger@ccmail.nevada.edu
BRADFORD,
D. F.
U.S. Environmental
Protection Agency, Landscape Ecology, Branch, P.O. Box 93478, Las
Vegas, Nevada 89193-3478
JENNINGS,
R. D.
Department of
Natural Science, Western New Mexico University, P.O. Box 680, Silver
City, New Mexico 88062
RIDDLE,
B. R.
Department of
Biological Sciences, University of Nevada, 4505 Maryland Parkway,
Las Vegas, Nevada 89154-4004
Re-Establishing
California Red-Legged Frogs to Their Historic Range Within Pinnacles
National Monument
California
red-legged frogs (Rana aurora draytonii) were once abundant
in the streams and reservoir at Pinnacles National Monument, California.
In the early 1980's they were extirpated from the reservoir due
to an infestation of exotic catfish and the draining of the reservoir.
By the late 1990's the remaining stream-breeding populations had
reached very low levels. We believe that the reservoir supported
the primary source population in the area, and that the stream may
not provide adequate habitat to maintain self-sustaining populations.
We began a project in 2001 to re-establish a breeding population
at the reservoir, which is currently free of exotic predators. We
moved portions of egg masses, just prior to hatching, from streams
into secured holding pens in the reservoir. The holding pens were
designed to protect tadpoles from predation while providing adequate
food supply and water circulation. After tadpoles had reached sufficient
size, they were released into the reservoir at large and their numbers
were tracked using minnow traps. At the end of the third year of
the project, there were at least 7 one-year-old and 20 two-year-old
frogs at the reservoir. Over 400 metamorphs were produced in the
third year, indicating that frogs may have already begun breeding
in the reservoir. Without this project, we believe the status of
California red-legged frogs in our watershed to be precarious at
best. Specific methodology will be presented.
JOHNSON,
PAUL G., II*
National Park
Service, Pinnacles National Monument, Paicines, CA 95043; paul_johnson@nps.gov
SCOT,
NORMAN
P.O. Box 307,
Creston, California 93432
FESNOCK,
AMY
Use
of habitat by Adult Amargosa Toads (Bufo nelsoni)
The
Amargosa toad (Bufo nelsoni) is narrowly a precinctive species
to the Oasis Valley in Nye County, NV. This species occupies the
riparian areas of the ephemeral Amargosa River, and associated springs
in the Oasis Valley. Using radio telemetry, adult toads were tracked
over the course of one year to determine how they use available
habitat. Approximately 10 males and 10 females were tracked at two
study sites. Home range sizes did not differ between male and female
toads. Distances moved by individuals varied by sex and month of
the year. Movements were significantly larger after rain. The frequency
of animal movements declined during the fall and winter. The relative
distance toads were found relative to water differed by gender,
with males observed closer to water than were females. Toads were
rarely found greater than 50 m from the water.
JONES,
DENISE*
University of
Nevada, Reno, Dept. of Biology, Reno, NV 89557; djones@biodiversity.unr.edu
TRACY,
C. RICHARD
University of
Nevada, Reno, Biological Resources Research Center, Reno, NV 89557;
dtracy@biodiversity.unr.edu
Negative
Effects of Introduced Trout on Ambystoma macrodactylum in
the Sierra Nevada, California: Results from "Historic Site"
Surveys, Watershed Surveys, and Experimental Data
Ambystoma
macrodactylum sigillatum, the long-toed salamander, is thought
to be experiencing local declines in areas with fish but is still
common in the Sierras. I combined three methods to assess the effects
of introduced trout on Ambystoma presence in California's
Sierra Nevada. I surveyed 20 lakes that historically supported these
salamanders, comparing sites with and without introduced trout to
see if local extinctions were correlated with trout introductions.
I also completed multiple surveys of 57 lakes and ponds in two watersheds
to assess landscape patterns of amphibian and trout occurrence.
Finally, I used experimental enclosures to quantify trout impacts
on salamander recruitment. Failure to detect A. m. sigillatum
larvae in sites where they were historically present was correlated
with trout introductions. In the watershed survey, trout presence
was negatively correlated with presence of A. m. sigillatum
larvae. To supplement surveys, I tested trout effects on larval
A. m. sigillatum in a lake, using eight 5 m by 5 m enclosures.
Trout negatively affected larval survival and body size. In high
elevation lakes and ponds, A. m. sigillatum larvae are known
to overwinter before reaching metamorphosis. Surveys suggest that
larvae are negatively affected by trout presence and are seldom
present in lakes with trout. A. m. sigillatum populations
may persist at the watershed scale because some larvae reach metamorphosis
in one season when small ponds dry during drought conditions. A
comparison of survey methods highlights the importance of using
methods such as seining in addition to visual surveys.
LEYSE,
KAREN E.
University of
California, Ecology Graduate Group, Davis, One Shields Avenue, Davis
CA, 95616; keleyse@ucdavis.edu
Reintroduction
of a Declining Amphibian: Determining an Ecologically Feasible
Approach Through Analysis of Decline Factors, Genetic Structure,
And Habitat Associations
Species
reintroductions provide a model for integrating practical and theoretical
aspects of conservation biology and developing suitable sets of
analytical tools. Reviews have suggested that research is needed
in several areas to improve the success of reintroductions: (1)
causes of species declines, (2) genetic relationships of source
populations, (3) social dynamics, (4) habitat associations, and
(5) monitoring designs. Amphibians present distinct challenges
due to unique ecological, genetic, and demographic characteristic
such as low mobility and patchy distributions. This study focuses
on a declining amphibian in California (the foothill yellow-legged
frog, Rana boylii) and includes three components: (1) spatial
analysis to determine the primary causes of decline, (2) description
of range-wide genetic variation, and (3) quantification of habitat
associations. One recent study suggests that agricultural chemicals
and climatic factors may be involved in the decline. My work includes
more detailed analyses of these threats and adds information on
dams and water flow modifications - key influences on this stream-dwelling
frog. Initial study of habitat associations shows that a narrow
set of stream conditions are necessary for reproduction. Genetic
data also indicate low variation throughout the range. I propose
a model for integrating this and other information into reintroduction
programs.
LIND,
AMY J.
Department of
Evolution and Ecology, One Shields Avenue, University of California,
Davis, CA 95616 and Sierra Nevada Research Center, USDA Forest Service,
Pacific Southwest Research Station, Davis, CA 95616; ajlind@ucdavis.edu
Amphibian
Diseases! Why Didn't We Think Of This Before?
Potential
factors in the worldwide decline of amphibians have been hot topics
for the last 25 years. Disease has now been implicated in a number
of amphibian declines on 6 continents and it is likely that this
is just the beginning of our understanding. Amphibian chytridiomycosis
and Iridoviruses have been the primary culprits identified so far,
but other diseases are also present and acting on amphibian populations.
Educating ourselves as professional biologists about a variety of
amphibian diseases, what to be aware of when in the field and how
to minimize the risk of spreading disease pathogens need to be
our primary concerns, as we continue to investigate the causes of
declines in our amphibians on local and global levels.
PADGETT-FLOHR,
GRETCHEN E.
5082 Yellowstone Park Drive, Fremont, CA 94538;
GPadgettflohr@aol
Amphibian
Chytridiomycosis and California Herpetofauna
Amphibian
chytridiomycosis has been detected in over 13 species of amphibians
in the State of California. Batrachochytrium dendrobatidis
is species-specific in its effects and even these effects can be
influenced by environmental conditions. The primary order of business
is determining which species are mortally affected and across which
geographic ranges the mortality occurs; and also which species can
be carriers and across which geographic range this occurs. Amphibians
generally occur as a suite of species which will interact with each
other at various points of their life history. My study site at
Grant County Park, San Jose, California has 7 species of amphibians
with aquatic life stages within the park boundaries. Three species
are currently special status. Amphibian chytridiomycosis has been
detected in 3 species, including one special status species and
further monitoring over the next 5 years will assist in determining
how widespread the disease is both geographically and taxonomically
and what the overall effects of the pathogen is on the diverse amphibian
populations within the park.
PADGETT-FLOHR,
GRETCHEN E.
5082 Yellowstone Park Drive, Fremont, CA 94538;
GPadgettflohr@aol
Metapopulation
Structure in Two Species of Rare Toads (Bufo nelsoni and
Bufo exsul) with Implications for Conservation.
Recognizing
metapopulation structure in amphibian populations is tremendously
important to conservation efforts as it significantly alters our
expectations with respect to population and species persistence.
At the same time, misidentifying populations as metapopulations
can have dire results. We review the metapopulation concept as it
applies to amphibian populations, and present applications of this
concept to the conservation of two species of toads (Bufo nelsoni
and Bufo exsul). We used both direct and indirect methods
to determine that both species meet stringent criteria as metapopulations.
There are many differences in the metapopulation processes (e.g.
migration rates, levels of differentiation, etc.) in each species.
These differences may be best explained by the differences in the
degree of physical isolation among subpopulations, and differences
in climate, between the ranges of the two species. The differences
in metapopulation dynamics also have implications for our expectations
with respect to conservation of these rare toads.
SIMANDLE,
ERIC T.*
University of
Nevada, Reno, Ecology, Evolution and Conservation Biology, Reno,
NV 89557;
simandle@unr.edu
TRACY,
C. RICHARD
University of
Nevada, Reno, Biological Resources Research Center, Reno, NV 89557;
dtracy@biodiversity.unr.edu
Amphibian
Conservation Planning in Nevada: The Efficacy of Conservation Agreements
and Strategies
Three
of Nevada's endemic amphibians, the Amargosa toad Bufo nelsoni,
Columbia spotted frog Rana luteiventris and relict leopard
frog Rana onca are species of concern classified as protected
amphibians under Nevada Administrative Code. These species have
been the subject of recent listing petitions and the US Fish and
Wildlife Service has determined that listing under the ESA for Great
Basin populations of the Columbia spotted frog is warranted but
precluded. Effective conservation for these species is challenging
because of limited resources, complex agency jurisdictions and land
ownerships, gaps in biological knowledge and limited understanding
of potential threats.
Cooperative
inter-agency efforts to implement conservation actions for these
species in Nevada have focused on the development of species-specific
Conservation Agreements and Strategies (CAS) which commit signatory
participants to the implementation of adaptive conservation actions
and the maintenance of field-level, collaborative working groups
that coordinate on-ground activities, evaluate the efficacy of conservation
actions and can adaptively modify initial conservation strategies
based on findings, changed conditions and new information. A key
element for success of this conservation approach has been the aggressive
participation of the species working groups, which have identified
and implemented interim conservation actions during the frequently
tedious CAS development processes.
The
first CAS, for Amargosa toad, was developed over a five-year period
and implemented beginning in October 2000. Because the Columbia
spotted frog in Nevada occurs in two distinct, geographically disparate
population segments, and conservation planning and implementation
for each population segment involves unique participants, two separate
but associated CASs have been developed and were implemented in
September 2003. A relict leopard frog CAS, which also involves
the states of Arizona and Utah, is under development and should
be completed by mid-year 2004.
SJÖBERG,
JON C.
Nevada Department
of Wildlife, 4747 Vegas Drive, Las Vegas NV 89108;
sjoberg@ndow.org
Foothill
Yellow-Legged Frog (Rana boylii) Predation by the Introduced
Signal Crayfish (Pacifasticus leniusculus) in the North Fork
Feather River, CA
As
part of ongoing monitoring of foothill yellow-legged frog (Rana
boylii) populations on the North Fork Feather River (Butte and
Plumas Co., CA) for Pacific Gas and Electric's FERC relicensing
projects, we employed an underwater video camera to document potential
predation of R. boylii embryos and tadpoles. Between
16 and 27 June 2003, we operated an Aqua-Vu® underwater
video camera at two known R. boylii breeding sites. Analysis
of over 92 hours of videotape revealed that the introduced signal
crayfish (Pacifasticus leniusculus) prey upon the egg masses
of R. boylii. Five other species were also observed
around egg masses and tadpole groups including four species of fish
(two non-native species) and Sierra garter snakes (Thamnophis
couchii). Results of visual encounter surveys suggested that
P. leniusculus also prey upon larval stages of R. boylii,
based upon observations of tail injuries. Pacifasticus leniusculus
is present in large numbers in this drainage and has been observed
in other systems where R. boylii are found, including the
Pit and Stanislaus Rivers. Although the extent of predation upon
R. boylii by crayfish is not known, other studies demonstrate
that crayfish can have devastating impacts upon all life stages
of native amphibians. Further research is needed to explore both
the indirect and direct effects of signal crayfish on R. boylii
populations in order to assess the potential impact this exotic
species may have on the ecology and distribution of the foothill
yellow-legged frog.
WISEMAN,
KEVIN
Garcia and Associates,
2601 Mission St. San Francisco, CA 94110; kwiseman@garciaandassociates.com
* Denotes speaker in multi-authored presentations
Updated: May 27, 2004
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