Abstract
Host–parasitoid dynamics are intrinsically unstable unless the risk of parasitism is sufficiently heterogeneous among hosts. Spatial aggregation of parasitoids can contribute to this heterogeneity, stabilising host–parasitoid population dynamics and thereby reducing pest outbreaks. We examined the spatial distribution of mango gall fly (Procontarinia matteiana, Kiefer and Cecconi), a non-native pest of South African mango orchards, which is controlled by a single parasitoid (Chrysonotomyia pulcherrima, Kerrich). We assessed whether spatial aggregation of parasitoids is associated with proximity to natural vegetation and/or to host density-dependent and host density-independent factors at three spatial scales. We found evidence for higher parasitism rates near natural vegetation at the field scale, and inverse host-density dependent and density-independent parasitoid aggregation at both the leaf scale and field scale. Therefore, we conclude that natural vegetation plays a role in promoting stabilising aggregation of parasitoids, possibly through provision of non-host resources (nectar, pollen), in this system.
Highlights
IntroductionNatural vegetation has been associated with improved pest control (Thies and Tscharntke 1999; Thies et al 2011)
In agricultural landscapes, natural vegetation has been associated with improved pest control (Thies and Tscharntke 1999; Thies et al 2011)
The role of natural vegetation in causing aggregation of parasitoids was the main host density-independent (HDI) factor investigated in this study
Summary
Natural vegetation has been associated with improved pest control (Thies and Tscharntke 1999; Thies et al 2011). A less explored idea is the role of natural vegetation in promoting aggregation of parasitoids (but see Thomson and Hoffmann 2013) and stabilising host–parasitoid population dynamics by providing a host ‘‘refuge’’ deeper within the crop (Holt and Hassell 1993). Specialist parasitoids have been shown to exert important long-term suppression of their host species, so the role of parasitoids in biocontrol is important (Snyder and Ives 2001, 2003). The dynamics of simple host–parasitoid interactions are inherently unstable and prone to diverging oscillations, resulting in extinction of one or both species, and cycles of high host abundance (Hassell 2000). A stable pest population maintained at a low level by a specialist parasitoid may be more desirable for successful biocontrol. Integrated pest management programs that tolerate a level of pest infestation below the economic threshold could help maintain environmental quality and reduce unnecessary management activities and costs (Cameron et al 2001; El-Wakeil 2010)
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