2016
DOI: 10.1016/j.ijpara.2016.04.008
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Forests of opportunities and mischief: disentangling the interactions between forests, parasites and immune responses

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Cited by 25 publications
(30 citation statements)
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References 54 publications
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“…For instance, forest types change in the Lesser Antilles as a function of altitude, orientation, and whether the forest is primary or secondary (Joseph 2016). This in turn determines the structure of vegetation within patches, which is an important driver of vector-borne parasitism (Abella-Medrano et al 2015, Renner et al 2016, Hernández-Lara et al 2017 and is somewhat independent of the degree of forest fragmentation (Fischer and Lindenmayer 2007). Composition of the habitat matrix among forest patches can also be of great importance, as it could either facilitate or limit vector dispersal and diversity (Pope et al 2005, Mendenhall et al 2013, González-Quevedo et al 2014.…”
Section: Discussionmentioning
confidence: 99%
“…For instance, forest types change in the Lesser Antilles as a function of altitude, orientation, and whether the forest is primary or secondary (Joseph 2016). This in turn determines the structure of vegetation within patches, which is an important driver of vector-borne parasitism (Abella-Medrano et al 2015, Renner et al 2016, Hernández-Lara et al 2017 and is somewhat independent of the degree of forest fragmentation (Fischer and Lindenmayer 2007). Composition of the habitat matrix among forest patches can also be of great importance, as it could either facilitate or limit vector dispersal and diversity (Pope et al 2005, Mendenhall et al 2013, González-Quevedo et al 2014.…”
Section: Discussionmentioning
confidence: 99%
“…The life history and habitat preferences of the avian hosts play an essential role in determining the likelihood of an infection [6,18]. Hence, habitat change alters ecosystem processes and species interactions, leading for example to higher infection rates in more intensively used habitats [19,20].…”
mentioning
confidence: 99%
“…Forest habitat structure and management may therefore affect host-vector-parasite interactions in a predictable way, as a function of both avian and insect abundances. In a previous study, the forest habitat was included explicitly as forest categories (i.e., forest stands dominated by one tree species, such as beech or spruce) and forest structure (i.e., continuous variables assessing the interior structural heterogeneity, such as amount of gaps, canopy heterogeneity and canopy height), but the vectors have not been explicitly included in the models so far [19].…”
mentioning
confidence: 99%
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“…We opened nets 30 min after local sunrise to hit the activity peak of birds and left nets open for five consecutive hours. For improved capture success we placed two playback stations (two per exploratory) close to the mist nets, playing territorial songs of our nine focal species (these are nine species we focus on for other studies: Cyanistes caeruleus, Erithacus rubecula, Fringilla coelebs, Parus major, Periparus ater, Sylvia atricapilla, Troglodytes troglodytes, Turdus merula, Turdus philomelos; [13]). We determined species, sex, and age wherever possible [28].…”
Section: Capturing Of Birdsmentioning
confidence: 99%