Population-level effects of pesticides and other toxicants on arthropods.

By J. Stark, J. Banks. Annual Review of Entomology, 2003

762 citations recorded by the source corpus.

Subfields: Health, Toxicology and Mutagenesis, Insect Science, Pollution

View Paper: https://www.semanticscholar.org/paper/f0030ab6174282a23ae803c6a1f41e983386ce7a

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Citations in the corpus

Sublethal effects of imidacloprid and pymetrozine on population growth parameters of cabbage aphid, Brevicoryne brassicae on rapeseed, Brassica napus L. (2007, methodology): “As a population endpoint, r m has been successfully utilized to determine the effect of several different xenobiotic compounds, such as pesticide, metal and radiation on aquatic invertebrates (Stark & Bank, 2003).”
Sublethal effects of fenpyroximate on life table parameters of the predatory mite Phytoseius plumifer (2010, background): “However, several studies showed that sublethal effects of pesticides can impact life span, fertility, sex ratio, feeding, behavior, and oviposition of phytoseiid mites (Dempster 1968; Strong and Brown 1987; Stark and Rangus 1994; Blu ¨mel et al. 2000; Stark and Banks 2003; Nadimi et al. 2009).”
The impacts of metals and metalloids on insect behavior (2010, background): “Stark & Banks (2003) reviewed the available literature on toxicant effects on insects and determined that 95% of the reports used the lethal concentration, LC50 (50% of insects die), or simple mortality as a toxicological endpoint.”
Side effects of selected insecticides on the Tuta absoluta (Lepidoptera: Gelechiidae) predators Macrolophus pygmaeus and Nesidiocoris tenuis (Hemiptera: Miridae) (2011, background): “These sublethal effects may have significant consequences for different life history parameters and interfere with the efficiency of natural enemies (Stark and Banks 2003; Desneux et al. 2007).”
Pesticide-Induced Stress in Arthropod Pests for Optimized Integrated Pest Management Programs. (2016, background): “Therefore, population growth rate is generally recognized as a more suitable ecotoxicological endpoint (48, 49, 122, 123).”
Insecticide‐induced hormesis in an insecticide‐resistant strain of the maize weevil, Sitophilus zeamais (2010, background): “In addition, fitness parameters and their implications have been understudied, despite their importance for a comprehensive understanding of the effects of pesticides in pest populations (Forbes and Calow 1999; Stark and Banks 2003; Guedes et al. 2009).”
The role of resources and risks in regulating wild bee populations. (2011, background): “Stark JD, Banks JE.”
Mitigating the effects of insecticides on arthropod biological control at field and landscape scales (2014, background): “Stark and collaborators (Stark et al., 1995; Stark and Banks, 2003) argued, however, that relying on mortality does not provide an accurate assessment of the potential impacts of insecticides.”
Effects of neonicotinoids and fipronil on non-target invertebrates (2014, positive): “…models that account for differential demographics and population growth rates within communities have been shown to provide more accurate assessments of potential pesticide impacts on populations and communities than conventional lethal concentration estimates can provide (Stark and Banks 2003).”
Pesticide selectivity for the insect egg parasitoid Telenomus remus (2010, methodology): “Pesticide impact on non-target insects includes lethal and sub-lethal effects (Desneux et al. 2007; Stark and Banks 2003).”
Indirect Effects of Pesticides on Natural Enemies (2012, background): “Any indirect effects, which are sometimes referred to as sub-lethal, latent, or cumulative adverse effects may be associated with interfering with the physiology and behavior of natural enemies by inhibiting longevity, fecundity, reproduction (based on the number of progeny produced or eggs laid by ”