Abstract:Conservation translocations are complex and challenging, but are frequently employed to tackle biodiversity decline. Large predator translocations can be particularly emotive and contentious, in part because they present actual or perceived risks to the safety and livelihoods of people. Understanding the social feasibility of conservation translocations is imperative, and provides opportunities to identify and address these risks.
In Britain, the Eurasian lynx Lynx lynx is the most frequently raised prospect f… Show more
“…For example, the Eurasian lynx has been reintroduced across Europe (Linnell et al., 2009 ) to Poland (Skorupski et al., 2022 ) and Slovenia, from where they were extirpated in the early 20th century (Kos et al., 2012 ). There is also discussion about reintroducing lynx to its former range in Scotland (Bavin et al., 2023 ; Ovenden et al., 2019 ). However, carnivore translocations can face challenges, primarily due to reported anthropogenically caused mortality (Stepkovitch et al., 2022 ), stressing the importance of considering implications for farmers, hunters and the forestry sector (Drouilly & O'Riain, 2021 ).…”
Predicting the effects of global environmental changes on species distribution is a top conservation priority, particularly for large carnivores, that contribute to regulating and maintaining ecosystems. As the most widespread and adaptable large felid, ranging across Africa and Asia, leopards are crucial to many ecosystems as both keystone and umbrella species, yet they are threatened across their ranges. We used intraspecific species distribution models (SDMs) to predict changes in range suitability for leopards under future climate and land‐use change and identify conservation gaps and opportunities. We generated intraspecific SDMs for the three western leopard subspecies, the African, Panthera pardus pardus; Arabian, Panthera pardus nimr; and Persian, Panthera pardus tulliana, leopards, and overlapped predictions with protected areas (PAs) coverage. We show that leopard subspecies differ in their environmental associations and vulnerability to future changes. The African and Arabian leopards are predicted to lose ~25% and ~14% of their currently suitable range, respectively, while the Persian leopard is predicted to experience ~12% range gains. We found that most areas predicted to be suitable were not protected, with only 4%–16% of the subspecies' ranges falling inside PAs, and that these proportions will decrease in the future. The highly variable responses we found between leopard subspecies highlight the importance of considering intraspecific variation when modelling vulnerability to climate and land‐use changes. The predicted decrease in proportion of suitable ranges falling inside PAs threatens global capacity to effectively conserve leopards because survival rates are substantially lower outside PAs due to persecution. Hence, it is important to work with local communities to address negative human‐wildlife interactions and to restore habitats to retain landscape connectivity where PA coverage is low. On the other hand, the predicted increase in range suitability across southern Europe presents opportunities for expansion outside of their contemporary range, capitalising on European rewilding schemes.
“…For example, the Eurasian lynx has been reintroduced across Europe (Linnell et al., 2009 ) to Poland (Skorupski et al., 2022 ) and Slovenia, from where they were extirpated in the early 20th century (Kos et al., 2012 ). There is also discussion about reintroducing lynx to its former range in Scotland (Bavin et al., 2023 ; Ovenden et al., 2019 ). However, carnivore translocations can face challenges, primarily due to reported anthropogenically caused mortality (Stepkovitch et al., 2022 ), stressing the importance of considering implications for farmers, hunters and the forestry sector (Drouilly & O'Riain, 2021 ).…”
Predicting the effects of global environmental changes on species distribution is a top conservation priority, particularly for large carnivores, that contribute to regulating and maintaining ecosystems. As the most widespread and adaptable large felid, ranging across Africa and Asia, leopards are crucial to many ecosystems as both keystone and umbrella species, yet they are threatened across their ranges. We used intraspecific species distribution models (SDMs) to predict changes in range suitability for leopards under future climate and land‐use change and identify conservation gaps and opportunities. We generated intraspecific SDMs for the three western leopard subspecies, the African, Panthera pardus pardus; Arabian, Panthera pardus nimr; and Persian, Panthera pardus tulliana, leopards, and overlapped predictions with protected areas (PAs) coverage. We show that leopard subspecies differ in their environmental associations and vulnerability to future changes. The African and Arabian leopards are predicted to lose ~25% and ~14% of their currently suitable range, respectively, while the Persian leopard is predicted to experience ~12% range gains. We found that most areas predicted to be suitable were not protected, with only 4%–16% of the subspecies' ranges falling inside PAs, and that these proportions will decrease in the future. The highly variable responses we found between leopard subspecies highlight the importance of considering intraspecific variation when modelling vulnerability to climate and land‐use changes. The predicted decrease in proportion of suitable ranges falling inside PAs threatens global capacity to effectively conserve leopards because survival rates are substantially lower outside PAs due to persecution. Hence, it is important to work with local communities to address negative human‐wildlife interactions and to restore habitats to retain landscape connectivity where PA coverage is low. On the other hand, the predicted increase in range suitability across southern Europe presents opportunities for expansion outside of their contemporary range, capitalising on European rewilding schemes.
“…We highlight the importance of having qualitative questions to gather perceptions and attitudes [30]. Having mixed qualitative and quantitative questionnaires, however, often entails smaller sampling efforts than having just multiple-choice online surveys [38][39][40][41]. Other important information to consider at the regional level would be the different types of farmers that would have a different perception of the topic [42].…”
Apex predators were extirpated from the UK hundreds of years ago. Practitioners have recently advocated for reintroductions of predators in the UK given their role as keystone species. For a reintroduction to take place, a survey of public desirability needs to be conducted. We aimed to understand the perspectives of people across the United Kingdom on the reintroduction of Eurasian lynxes, gray wolves, and brown bears. We collected data via mixed-methods questionnaires from 78 key stakeholders, such as farmers, the general public, nature conservationists, and those in environmental sectors, with these areas being seen as the most affected by these reintroductions. It was organizations that front these stakeholder groups which mainly distributed the survey as well as social media groups. We ran a path analysis, which highlighted that there was a negative correlation between respondents viewing the species as a danger toward livestock and humans, and the respondent seeing it as being good to have that species in their region. Overall, participants who stated that rewilding their region was a priority also stated that it would be good to have Eurasian lynx in their region. That said, 70% of farmers strongly disagreed with the reintroduction of Eurasian lynx. These findings showed that much of the United Kingdom would welcome the reintroduction of Eurasian lynx, but both farmers and the public would fear the loss of livestock that may come along with these species. Support can be gained through education and knowledge, which is a necessary step needed especially targeting farmers before any reintroduction plans can be made.
“…Opinions about whether to reintroduce a given species can vary, with different levels of support or opposition held among individuals with different interests (Auster et al, 2020;Bavin et al, 2023;IUCN/ SSC, 2013;Niemiec, Berl, et al, 2020). Naming individual animals can be an effective and popular pro-reintroduction action that engages publics and facilitates an understanding of the natural characteristics of reintroduced species where a flagship individual approach is taken (Jarić et al, 2023).…”
Section: Con Clus I On: Think It Throug Hmentioning
1. Individual animals are often given names by humans. For example, names are attributed to domestic animals to acknowledge their closeness to people, some research studies use names to identify differences between individuals in a study group, or zoos often use names to tell stories that attract public or media attention.2. Publicly naming individual animals can provide opportunities in conservation, but there are also risks. In this perspective we exemplify such opportunities and risks
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