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News & Stories New WV vernal pool community science program collaborates with ARMI scientists
ARMI scientists have been collaborating with West Virginia’s Department of Environmental Protection and WV Division of Natural Resources to inform development of a Vernal Pool Mapping and Monitoring initiative which aims to engage community volunteers in wetland science. Startup and initial costs were funded by a grant received by WVDEP, and the program aims to mirror success of the WV Save Our Streams volunteer-based program and expand knowledge of vernal pools in the state. The program objectives are to increase public understanding of wetlands functions and values, improve knowledge of the location and extent of wetlands, and engage public participation in wetland policy, conservation, and restoration. Starting in 2023, volunteers will visit pools 1-3 times per year, submit photos of the pool and any observed amphibians to the WV iNaturalist project, and complete datasheets to document habitat conditions, species observed, and water levels at their assigned pools. ARMI scientists will continue to collaborate with the program to advise on data collection protocols, site selection, and provide opportunities for volunteers to engage with ARMI science occurring in wetlands across the northeast.
News & Stories Decision makers collaborate to address multiple threats to endemic salamander
Salamanders in the US are at risk from the impending arrival of a novel chytrid fungus Batrachochytrium salamandrivorans (Bsal). In New Mexico, the state’s Department of Game and Fish and the US Forest Service are concerned about the risk this emerging pathogen poses to the state-threatened, endemic Sacramento Mountain salamander – Aneides hardii. Drought, warming temperatures, and increased risk of stand-replacing fires are a compounding and critical factors for the persistence of A. hardii populations. Wildlife disease problems are complex and require purposeful thinking and directed application of science to best optimize manger decision making. Since fall 2021, ARMI researchers E. Grant, M. Bletz have been leading a series of structured decision-making workshops with state, US Forest Service and Mescalero tribe decision makers and science experts in amphibian ecology and disease, including ARMI scientist E. Muths. They are working with this group to frame the problem, identify management objectives and possible management actions and to identify where and how science can reduce critical uncertainties pertinent to the manager’s decision to, in turn, identify the best course of action for the salamander threatened by disease and increased fire.
Papers & Reports Keeping the Heat On: Weighted Surveillance for Chytrid Fungus in Dixie Valley Toads
Papers & Reports Abiotic and biotic factors reduce the viability of a high-elevation salamander in its native range
2. We use field data to estimate population demographic parameters for an exemplary high-elevation amphibian species, the federally endangered Shenandoah salamander (Plethodon shenandoah). These parameters were entered into a Markov projection model which we used to forecast the future population status of the Shenandoah salamander.
3. We found that if the population maintains its current site colonization and persistence rates, it is at risk of extinction that could be exacerbated by both climate and interspecific competition.
4. Synthesis and applications. Managers have a fundamental objective directed by official policy of maintaining the species ‘for the foreseeable future (Grant et al., 2014).’ Our evaluation of multiple hypotheses about population drivers reveals that extinction is projected for this species. Our analysis suggests that considering active management need not depend on resolving the uncertainty.
Data Release Calculations of BioLake climate data
These BioLake raster data provide global estimates (~10.0 x 12.4 km resolution) of twelve bioclimatic variables based on estimated lake temperature. Eleven of these twelve variables (BioLake01 - BioLake11) are estimated for each of three lake strata: lake mix (surface) layer, lake bottom, and total lake water column. These eleven variables correspond to CHELSA (Climatologies at high resolution for the earth's land surface areas) bioclimatic variables BIO1 - BIO11, except that these BioLake variables are based on lake water temperature and CHELSA BIO1 - BIO11 variables are based on air temperature. CHELSA BIO is also calculated a finer spatial resolution (~1 x 1 km). The twelfth variable (BioLake20; months with non-zero ice cover) does not correspond to any CHELSA bioclimatic variable. The data are supplied as a multi-layer raster (.grd) file in the World Mollweide projection, accompanied by a header file (.gri) with layer names.
For BioLake layer download, see https://doi.org/10.5066/P96QLN5Y
Data Release BioLake bioclimatic variables based on ERA5-Land lake temperature estimates 1991-2020
Papers & Reports Complex life histories alter patterns of mercury exposure and accumulation in linked aquatic-terrestrial food webs: an amphibian example
Papers & Reports Disentangling direct and indirect effects of extreme events on coastal wetland communities
2. We extended static structural equation modeling approaches to incorporate system dynamics in a multi-year multispecies occupancy model to quantify the effects of extreme weather events on a coastal freshwater wetland system.
3. We used data from an 8-year study (2009 to 2016) on St. Marks National Wildlife Refuge in Florida, USA, to quantify species-specific and community-level changes in amphibian and fish occupancy associated with two flooding events in 2012 and 2013. We examine how physical changes to the landscape, including potential changes in salinity and increased wetland connectivity, may have contributed to or exacerbated the effects of these extreme weather events on the biota of isolated coastal wetlands.
4. We provide evidence that the primary effects of flooding on the amphibian community were through indirect mechanisms via changes in the composition of the sympatric fish community that may have had lethal (i.e., through direct predation) or non-lethal (i.e., through direct or indirect competitive interactions) effects. In addition, we shown that amphibian species differed in their sensitivity to direct flooding effects and indirect changes in the fish community and wetland specific conductance, which led to variable responses across the community. These effects led to the overall decline in amphibian species richness from 2009 to 2016, suggesting that wetland-breeding amphibian communities on St. Marks may not be resilient to predicted changes in coastal disturbance regimes as a result of climate change.
5. Understanding both direct and indirect effects, as well as species interactions, is important for predicting the effects of a changing climate on individual species, communities, and ecosystems.
News & Stories ARMI biologists released captive-bred Mountain Yellow-legged Frogs to the San Gabriel Mountains
On Thursday, Sept. 9th, 2022, ARMI biologists Adam Backlin and Elizabeth Gallegos led two teams on a release of captive-bred southern California mountain yellow-legged frogs. Each team hiked to a remote canyon with spring-fed creek in the San Gabriel Mountains. These sites have been assessed and monitored through out the year to ensure they would be suitable for the frogs. This batch of frogs were bred at the Los Angeles Zoo and Botanical Gardens and head started by the Santa Ana Zoo and the Aquarium of the Pacific in Long Beach, CA. Thanks to their effort, these 200 sub-adult yellow-legged frogs will have a chance to restore their population in these mountains, where they once thrived for thousands of years.
More coverage of this release can be found at the LA Times website.
News & Stories ARMI Scientists participate in first Global Amphibian and Reptile Disease Conference
The first Global Amphibian and Reptile Disease Conference was held in Knoxville, Tennessee in July 2022. ARMI scientists E. Muths and B. Hossack presented a synthesis of efforts to understand amphibian disease in the Greater Yellowstone Ecosystem, and B. Hardy and L. Bailey, a PhD student and ARMI affiliate (respectively) at Colorado State University, presented a paper on the potential for demographic compensation in amphibian populations challenged by disease. These presentations were among the few field-based papers at the conference. ARMI scientists E. Grant and M. Bletz led one of the conference workshops to discuss and design conceptual disease models for major herpetofaunal pathogens. The aim of this workshop was to identify differences in knowledge, processes, and possible management strategies among host-pathogen systems. In addition, M.C. Hopkins, Wildlife Disease Coordinator, USGS Ecosystems Mission Area, was a member of the Scientific Committee for the conference.
The goal of the GARD conference was to engage a wide range of people, from scientists and students to veterinarians, natural resource managers, and policy makers, in sharing knowledge about various amphibian and reptile diseases and in working to identify disease management strategies that are applicable to herpetofauna conservation. This hybrid meeting hosted scientists from 25 countries, with presentations ranging from the research reports, including the roles of biodiversity and climate change in amphibian disease risk and amphibian disease immunogenetics, to broad keynotes, such as “Comparative ecology and evolution of reptile pathogens” and “Ranaviruses: four things we (mostly) know and three we (largely) do not”.
Papers & Reports Compensatory recruitment unlikely in high elevation amphibian populations challenged with disease
2. We use long-term mark-recapture data from five populations of boreal toads (Anaxyrus boreas boreas ), across an elevational gradient in Colorado, before and after pathogen arrival to assess whether populations can persist with Batrachochytrium dendrobatidis (Bd) via compensatory recruitment.
3. Prior to pathogen arrival, we found a life history tradeoff between survival and recruitment across elevations, where high elevation toads have high survival but lower recruitment and vice versa at lower elevations.
4. Pathogen arrival had a strong negative effect on apparent annual survival and recruitment leading to negative population growth rates and dramatically reduced host abundances. The data did not support the occurrence of compensatory recruitment.
5. Synthesis and applications. Our unique dataset indicates that demographic responses to pathogens may be environmentally (i.e., elevationally) context-dependent and highlights the value of long-term monitoring. We recommend that practitioners verify that potential persistence mechanisms occur across multiple populations and relevant environmental gradients to counter any assumptions of the mechanism existing species-wide. Quantifying variation in population responses to disease will aid in understanding the bounds of such persistence mechanisms and identify particularly vulnerable populations where mechanisms are non-existent.
Papers & Reports Captivity, reintroductions, and the rewilding of the amphibian microbiome
Data Release Water level data from select depressional wetlands at Saint Marks National Wildlife Refuge: July 2010 - May 2019 (ver. 2.0, August 2022)
1. water level monitoring site Locations (tabular data)
2. wetland perimeters (GIS vector data)
3. water level and water temperature data for 59 select wetlands (tabular data)
4. revision history text file that describes the changes from the original release to version 2.0.
Papers & Reports Revisiting conservation units for the endangered mountain yellow-legged frog species complex (Rana muscosa, Rana sierrae) using multiple genomic methods
Papers & Reports Winter severity affects occupancy of spring- and summer-breeding anurans across the eastern United States
News & Stories ARMI scientists lead analysis of factors linked with long-term reintroduction success for a threatened frog
Reintroduction programs are growing in use to help recover imperiled species. However, there is still little information on the long-term success of these programs or factors linked with successful establishment of populations. ARMI scientists collaborated with partners from the US Fish and Wildlife Service, Arizona Game and Fish Department, Turner Endangered Species Fund, and university scientists to analyze 25 years of reintroductions for the Chiricahua Leopard Frog in Arizona and New Mexico. The reintroduction program stocks larvae and frogs reared in several captive and semi-captive facilities in the region, as well as egg masses and frogs moved from wild sources. The results from the study can help improve reintroduction success and speed recovery for the Chiricahua Leopard Frog and other species with similar life histories.
Citation
Hossack and others. 2022. Identifying factors linked with population persistence: Lessons learned from 25 years of amphibian translocations. Global Ecology and Conservation 35: e02078. https://doi.org/10.1016/j.gecco.2022.e02078
Papers & Reports Cryptic declines of small, cold-water specialists highlight potential vulnerabilities of headwater streams as climate refugia
including cold-water specialists. Montane areas and cold streams are often considered climate refugia that buffer
communities against change. However, climate refugia are often species-specific, and despite growing awareness
that life histories and habitat requirements shape responses to change, small or non-game species are often
under-represented in monitoring and planning programs. A recent study in Montana, USA, revealed much larger
warming-related declines in occupancy for small, non-game slimy sculpin (Cottus cognatus) between 1993 and
1995 and 2011–2013 than for two socially valued salmonid fishes that shape regional conservation efforts. To
broaden insight into climate change vulnerabilities of headwater stream communities, we analyzed data for
Rocky Mountain tailed frogs (Ascaphus montanus) that were collected during those same electrofishing surveys
for fishes from 241 stream reaches. Tailed frogs occupy small, cold streams and have several life-history traits
that make them sensitive to environmental change. We used a Bayesian framework to estimate occupancy,
colonization, and extinction dynamics relative to forest canopy, estimated stream temperature, and wildfire
effects. Tailed frog occupancy decreased by 19 % from 1993 to 1995 to 2011–2013. Changes in occupancy were
linked with increased extinction and reduced colonization where there were fire-driven reductions in canopy
cover, and reduced colonization of stream reaches that warmed on average 0.8 ?C during the study. Our results
highlight extensive extirpations for oft-overlooked species and emphasize the importance of including species
with diverse habitat requirements and life histories in conservation planning.
Papers & Reports Empirical evidence for effects of invasive American Bullfrogs on occurrence of native amphibians and emerging pathogens
threats to biodiversity. American Bullfrogs (Rana [Lithobates] catesbeiana),
which have been introduced to many parts of the world, are often linked with
declines in native amphibians via predation and the spread of emerging pathogens
such as amphibian chytrid fungus (Batrachochytrium dendrobatidis [Bd])
and ranaviruses. Although many studies have investigated the potential role of
bullfrogs in the decline of native amphibians, analyses that account for shared
habitat affinities and imperfect detection have found limited support for
clear effects. Similarly, the role of bullfrogs in shaping the patch-level distribution
of pathogens is unclear. We used eDNA methods to sample 233 sites in the southwestern USA and Sonora, Mexico (2016–2018) to estimate how
the presence of bullfrogs affects the occurrence of four native amphibians,
Bd, and ranaviruses. Based on two-species, dominant-subordinate occupancy
models fitted in a Bayesian context, federally threatened Chiricahua Leopard
Frogs (Rana chiricahuensis) and Western Tiger Salamanders (Ambystoma
mavortium) were eight times (32% vs. 4%) and two times (36% vs. 18%), respectively,
less likely to occur at sites where bullfrogs occurred. Evidence for the
negative effects of bullfrogs on Lowland Leopard Frogs (Rana yavapaiensis)
and Northern Leopard Frogs (Rana pipiens) was less clear, possibly because of
smaller numbers of sites where these native species still occurred and because
bullfrogs often occur at lower densities in streams, the primary habitat for
Lowland Leopard Frogs. At the community level, Bd was most likely to occur
where bullfrogs co-occurred with native amphibians, which could increase the
risk to native species. Ranaviruses were estimated to occur at 33% of bullfrogonly
sites, 10% of sites where bullfrogs and native amphibians co-occurred,
and only 3% of sites where only native amphibians occurred. Of the 85 sites
where we did not detect any of the five target amphibian species, we also did
not detect Bd or ranaviruses; this suggests other hosts do not drive the distribution
of these pathogens in our study area. Our results provide landscape-scale
evidence that bullfrogs reduce the occurrence of native amphibians and
increase the occurrence of pathogens, information that can clarify risks and
aid the prioritization of conservation actions.