2017
DOI: 10.1098/rsos.160535
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Parasite vulnerability to climate change: an evidence-based functional trait approach

Abstract: Despite the number of virulent pathogens that are projected to benefit from global change and to spread in the next century, we suggest that a combination of coextinction risk and climate sensitivity could make parasites at least as extinction prone as any other trophic group. However, the existing interdisciplinary toolbox for identifying species threatened by climate change is inadequate or inappropriate when considering parasites as conservation targets. A functional trait approach can be used to connect pa… Show more

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Cited by 100 publications
(77 citation statements)
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References 102 publications
(139 reference statements)
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“…The size of the LNHM data allows for the creation of global helminth parasite richness maps at the country level. Understanding species global distributions is a pressing need given land use change and an accelerating rate of species extinctions (Carlson et al, ; Cizauskas et al, ; Pimm et al, ). Further, understanding hotspots of parasite richness and diversity is a first step toward understanding spatial variation in transmission risk and parasite spillover (Poulin, Guilhaumon, Randhawa, Luque, & Mouillot, ; Poulin, Krasnov, Mouillot, & Thieltges, ).…”
Section: Helminth Macroecological Patternsmentioning
confidence: 99%
“…The size of the LNHM data allows for the creation of global helminth parasite richness maps at the country level. Understanding species global distributions is a pressing need given land use change and an accelerating rate of species extinctions (Carlson et al, ; Cizauskas et al, ; Pimm et al, ). Further, understanding hotspots of parasite richness and diversity is a first step toward understanding spatial variation in transmission risk and parasite spillover (Poulin, Guilhaumon, Randhawa, Luque, & Mouillot, ; Poulin, Krasnov, Mouillot, & Thieltges, ).…”
Section: Helminth Macroecological Patternsmentioning
confidence: 99%
“…Despite this expectation, different parasitic taxa across multiple host taxa show varying LDG patterns (see below). Given the changes in projected distributional range and species abundance (Altizer et al 2013), extinctions (Cizauskas et al 2017), secondary extinctions and coextinctions (Colwell et al 2012a) predicted with global climate and anthropogenic changes, the need to document parasite diversity is pressing and critical to increasing our knowledge of the biodiversity, biogeographical patterns and ecology of parasitic organisms before this biodiversity is lost. With around 40% of known biodiversity estimates representing parasitic species and an estimated 75 000-300 000+ species of helminths (parasitic nematodes, trematodes, cestodes and acanthocephalans) alone (Dobson et al 2008), the need to document the biodiversity of parasitic organisms is certainly no less than that of free-living species.…”
Section: Introductionmentioning
confidence: 99%
“…Integrating phylogenetics with community ecology could help in understanding patterns of host phylogenetic clustering and overdispersion across spatiotemporal scales. This holds great potential for the development of new tools to predict parasite host breadths (H P and H O in our proposed framework), a key component of understanding disease transmission dynamics at the landscape level [56,77]. Additionally, ecophylogenetics may provide insights on potential spillover events that could result in disease emergence, a highly relevant topic under global change and increased international movement of species leading to shifts in host communities and translocation of parasites to new areas and hosts [79,80].…”
Section: From Disease Distributions To Risk Mappingmentioning
confidence: 99%
“…Selection of ecologically relevant predictor variables is necessary to generate reliable modeling outputs and should be supported by the biology of the species and the spatiotemporal scale at hand [26,55]. Variables directly affecting a species' physiology are preferred since their relationships with its geographic distribution are assumed to be stable across spatiotemporal scales [26,56]. Indirect variables may be employed as proxies for direct variables, although these should be avoided if they are correlated with factors driving the demography, dispersal, or distribution of biotic interactors [26].…”
Section: Environmental Predictorsmentioning
confidence: 99%