Abstract:Food acquisition is a fundamental process that drives animal distribution and abundance, influencing how species respond to changing environments. Disturbances such as fire create significant shifts in available dietary resources, yet, for many species, we lack basic information about what they eat, let alone how they respond to a changing resource base. In order to create effective management strategies, faunal conservation in flammable landscapes requires a greater understanding of what animals eat and how t… Show more
“…This has led to molecular scatology studies that have focused on the diet of target wildlife species (e.g. Anderson et al., 2018 ; Berman & Inbar, 2022 ; Henger et al., 2022 ; Jorns et al., 2020 ; Khalatbari et al., 2022 ; King & Schoenecker, 2019 ; Klure et al., 2022 ; McLennan et al., 2022 ; Mitchell et al., 2022 ; Nelms et al., 2019 ; O'Rourke et al., 2021 ; Roffler et al., 2021 ; Wanniarachchi et al., 2022 ). In parallel, other molecular scatology studies continue to focus on the behaviour, gene flow and space‐use patterns of the target species itself (e.g.…”
Next‐generation sequencing technology has enabled accurate insights into the diet of wildlife species. The protocols for faecal sample collection and DNA extraction for diet analysis have differed from those focusing on target species, even in most studies combining questions on both aspects. We designed an experiment to evaluate two protocols using 11 parameters and select a single one that will generate both target species (Asiatic wild ass, Equus hemionus, in Israel) and diet DNA, as an effective strategy to minimise time, effort, and cost without hampering efficiency. In Protocol A, we swabbed the outer surface of faecal boluses and extracted DNA using a Stool Kit, while for Protocol B, we homogenised faecal matter from inside the bolus followed by extraction using a Powersoil Kit. Protocol A performed significantly better for four parameters, which included, for the target species, microsatellite amplification success and the quantity of the GAPDH gene; and for its diet, the number of exact sequence variants (ESVs) obtained at genus level and plant genus richness. However, there was no significant difference in the amplification success of sex‐linked and plant markers, total reads at genus level, number of genera obtained and plant genus composition. Although we chose Protocol A, both protocols yielded results for the target species and its diet, demonstrating that one single protocol can be used for both purposes, although a pilot study is recommended to optimise the protocol for specific systems. This strategy may also be useful for studies combining target species and their gut microbiome and parasitic load.
“…This has led to molecular scatology studies that have focused on the diet of target wildlife species (e.g. Anderson et al., 2018 ; Berman & Inbar, 2022 ; Henger et al., 2022 ; Jorns et al., 2020 ; Khalatbari et al., 2022 ; King & Schoenecker, 2019 ; Klure et al., 2022 ; McLennan et al., 2022 ; Mitchell et al., 2022 ; Nelms et al., 2019 ; O'Rourke et al., 2021 ; Roffler et al., 2021 ; Wanniarachchi et al., 2022 ). In parallel, other molecular scatology studies continue to focus on the behaviour, gene flow and space‐use patterns of the target species itself (e.g.…”
Next‐generation sequencing technology has enabled accurate insights into the diet of wildlife species. The protocols for faecal sample collection and DNA extraction for diet analysis have differed from those focusing on target species, even in most studies combining questions on both aspects. We designed an experiment to evaluate two protocols using 11 parameters and select a single one that will generate both target species (Asiatic wild ass, Equus hemionus, in Israel) and diet DNA, as an effective strategy to minimise time, effort, and cost without hampering efficiency. In Protocol A, we swabbed the outer surface of faecal boluses and extracted DNA using a Stool Kit, while for Protocol B, we homogenised faecal matter from inside the bolus followed by extraction using a Powersoil Kit. Protocol A performed significantly better for four parameters, which included, for the target species, microsatellite amplification success and the quantity of the GAPDH gene; and for its diet, the number of exact sequence variants (ESVs) obtained at genus level and plant genus richness. However, there was no significant difference in the amplification success of sex‐linked and plant markers, total reads at genus level, number of genera obtained and plant genus composition. Although we chose Protocol A, both protocols yielded results for the target species and its diet, demonstrating that one single protocol can be used for both purposes, although a pilot study is recommended to optimise the protocol for specific systems. This strategy may also be useful for studies combining target species and their gut microbiome and parasitic load.
“…A large amount of evidence highlights their use as food (e.g. Wanniarachchi et al 2022 for some small mammal species) and shelter by many invertebrate and vertebrate species. In a review with a focus on two Queensland species, Borsboom (2005) determined that this evidence concerned over 315 invertebrate species and nearly 100 vertebrate species.…”
Context The iconic grass-trees (Xanthorrhoea semiplana) of Australia are used by many animal species, but their role as shelters against weather extremes is poorly known. The severe contribution of the fungal pathogen Phytophthora cinnamomi to grass-tree deaths and current burning practices could affect small animal conservation by exacerbating impacts of weather extremes. Aims We examined the buffering role of X. semiplana canopies against extreme weather at four sites in the Mount Lofty Ranges, South Australia. Methods We measured ambient temperature, temperatures under grass-tree canopies, and 2 m away at random locations in summer (>35°C) and in winter (<13°C) over 24-h periods at each study site. We scored soil dryness under the canopies during and after heavy rainfall. Key results Temperatures under grass-tree canopies were more stable and with smaller ranges than other temperatures, and showed dramatic differences in summer when conditions were up to 20°C cooler than ambient. Temperatures were higher under grass-trees at night in winter. The soil under the largest canopies was completely dry during and after heavy rainfall. Conclusions Xanthorrhoea semiplana buffers ground-dwelling animals against temperature extremes and rain so that the animals maintain their thermal resistance. Animals may choose foraging times based on grass-tree availability. The largest grass-trees provide the best shelter. Implications Considerable grass-tree deaths from P. cinnamomi infestation, together with removal or burning, can have dramatic detrimental consequences for their habitat value and the survival of wildlife using them as shelter.
The only population of the endangered blue racer (Coluber constrictor foxii) in Canada occurs on Pelee Island, Ontario. The species is threatened by multiple factors including habitat degradation and loss, road mortality, persecution, and potentially predation. We designed and evaluated the performance of an eDNA ddPCR assay that can be used for multiple facets of conservation of this species. We tested the assay in silico and in vitro using DNA of blue racers and co-occurring snake species, and estimated the LOD and LOQ using synthetic DNA. As wild turkey predation has been suggested to negatively affect racers, we tested the assay on eight wild turkey fecal samples. Our assay is specific, can detect the target species at very low levels of concentration (0.002 copies/μL) and can accurately quantify the copy number ≥0.26 copies/μL. We detected no racer DNA in any wild turkey fecal sample. More fecal samples collected at strategic locations during snake peak activity would enable a more thorough assessment of the possibility of turkey predation. Our assay should be effective for other environmental samples and can be used for investigating other factors negatively affecting blue racers, for example helping to quantify blue racer habitat suitability and site occupancy.
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