Drought

Freshwater wetlands provide critical habitat for a diverse array of organisms including many amphibians. Yet, under the continued impacts of water diversions and drought, these habitats are among the most imperiled ecosystems on Earth. Drought has the potential to alter many sources of water critical to the habitats amphibians need, especially those associated with breeding and development. Potential changes include: timing and availability of water from glacier melt, snow and rain timing and amount; persistence of vernal pools and seasonal wetlands; altered evapotranspiration rates; reduced stream flows, and groundwater recharge rates.

Other ecosystem components likely to change in response to drought include the timing and frequency of fires, the spread of invasive plants and animals, and microclimates in which the animals live.

Lake Shasta Feb-Oct 2014 comparison.
Lake Shasta Feb-Oct 2014 comparison.

Drought - ARMI Papers & Reports

Papers & Reports Using life history traits to assess climate change vulnerability in understudied species
Authors: Ross K Hinderer; Blake R Hossack; Lisa A Eby
Outlet: Integrative Zoology
Climate change is a primary threat to biodiversity, but for many species, we still lack information required to assess their relative vulnerability to changes. Climate change vulnerability assessment (CCVA) is a widely used technique to rank relative vulnerability to climate change based on species characteristics, such as their distributions, habitat associations, environmental tolerances, and life-history traits. However, for species that we expect are vulnerable to climate change yet are understudied, like many amphibians, we often lack information required to construct CCVAs using existing methods. We used the CCVA framework to construct trait-based models based on life history theory, using empirical evidence of traits and distributions that reflected sensitivity of amphibians to environmental perturbation. We performed CCVAs for amphibians in 7 states in the north-central USA, focusing on 31 aquatic-breeding species listed as species of greatest conservation need by at last 1 state. Because detailed information on habitat requirements is unavailable for most amphibian species, we used species distributions and information on traits expected to influence vulnerability to a drying climate (e.g., clutch size and habitat breadth). We scored species vulnerability based on changes projected for mid-century (2040?2069) from 2 climate models representing “least-dry” and “most-dry” scenarios for the region. Species characteristics useful for discriminating vulnerability in our models included small range size, small clutch size, inflexible diel activity patterns, and smaller habitat breadth. When projected climate scenarios included a mix of drier and wetter conditions in the future, the exposure of a species to drying conditions was most important to relative rankings. When the scenario was universally drier, species characteristics were more important to relative rankings. Using information typically available even for understudied species and a range of climate projections, our results highlight the potential of using life history traits as indicators of relative climate vulnerability. The commonalities we identified provide a framework that can be used to assess other understudied species threatened by climate change.
Papers & Reports Assessing amphibian richness, rarity, threats, and conservation prospects for U.S. national park network [UPDATE TITLE]
Authors: Benjamin Lafrance; Andrew M Ray; Michael T Tercek; Robert N Fisher; Blake R Hossack
Date: 2024-11 | Outlet: npj Biodiversity
We assessed amphibian diversity, rarity, and threats across the U.S. National Park System, which covers 3.5% of the U.S. and 12% of federal lands. At least 230 of 354 (65%) amphibian species native to the U.S. occur in parks. Of the species documented in parks, 17% are considered at-risk globally and 20% are uncategorized, reflecting still-widespread data deficiencies. Parks in the Northwest and Northeast accumulated species most quickly (i.e., steepest species?area relationships). Non-native crayfishes and amphibians occur within 50 km of 60% and 25% of parks, respectively, illustrating the broad threat of non-native predators. Projected mid-century (2040–2069) changes in climatic water deficit, based on 25 climate futures, produced an expected 34% increase in dryness across all parks in the contiguous U.S. territory. Our analyses highlight the extent and regional differences in current and future threats and reveal gaps in species protection, but also reveal opportunities for targeted expansion and active management.
Papers & Reports Unburned habitat essential for amphibian breeding persistence following wildfire.
Authors: Larissa L Bailey; Richard Henderson; Wendy A Estes-Zumpf; Charles Rhoades; Ellie Miller; Dominique Lujan; Erin Muths
Date: 2025 | Outlet: Global Ecology and Conservation, 57, p.e03389.
Wildfire regimes are changing rapidly with widespread increase in the intensity, frequency, and duration of fire activity, especially in the western United States. Limited studies explore the impacts of wildfires on aquatic taxa and few focus on lentic habitats that are essential for amphibians, many of which are of conservation concern. We capitalized on existing pre-fire surveys for anuran species and resurveyed a random subset of wetlands across a gradient of soil burn severity to investigate the short-term effects of wildfire on a relict population of wood frogs in the southern Rocky Mountains. We also investigated whether maps created to support rapid post-fire emergency response activities (i.e., USFS BAER program) accurately characterize soil burn severity around small habitat features (i.e., ponds) that serve as important amphibian breeding and rearing habitat. We found that wood frog breeding persistence following fires was strongly influenced by the percentage of their terrestrial habitat (100m buffer surrounding breeding ponds) that was burned. Wood frog colonization probability of previously unoccupied ponds was low (~ 0.10) and unaffected by soil burn severity. Importantly, we found that remotely sensed data typically produced to predict flooding and erosion at broad (catchment) scales is a poor representation of the amount and variation in soil burn severity surrounding small habitat features (e.g., ponds), suggesting that additional field sampling is necessary to understand wildfire responses for species that rely on small habitat features. Understanding short-term geographic- and species-specific variation in response to wildfires provides the basis to explore time to recovery (e.g., when wood frogs return to burned breeding sites) or to determine if declines in breeding distributions intensify over time.
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