Edge effects on flower-visiting insects in grapefruit plantations bordering premontane subtropical forest.

By N. Chacoff, M. Aizen. 2005

223 citations recorded by the source corpus.

Subfields: Ecology, Evolution, Behavior and Systematics, Insect Science, Plant Science

View Paper: https://www.semanticscholar.org/paper/62deef59e97aebcf518112ce4f732669cf00be88

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In Ecology, Evolution, Behavior and Systematics

In Insect Science

In Plant Science

Citations in the corpus

Stability of pollination services decreases with isolation from natural areas despite honey bee visits. (2011, background): “…canephora Apis spp., Trigona spp., Halictidae, solitary bees No, no 0 Tropical rain forest 0–1415 Indonesia, Sulawesi 15, 3–4 trees No data Grapefruit Chacoff & Aizen 2006; Chacoff et al. 2008 Citrus paradisi A. mellifera, stingless bees (Meliponini) No, yes 95 Subtropical, premontane forest…”
The Swiss agri-environment scheme enhances pollinator diversity and plant reproductive success in nearby intensively managed farmland (2007, background): “Social bees were found to decline along isolation gradients from bee habitats for up to several hundred metres (Steffan-Dewenter & Tscharntke 1999; Kremen, Williams & Thorp 2002; Klein, Steffan-Dewenter & Tscharntke 2003a; Chacoff & Aizen 2006 ).”
Pollinator diversity increases fruit production in Mexican coffee plantations: The importance of rustic management systems (2009, background): “, 2008), where bee abundance and/or species richness decreases with increasing isolation from natural habitat patches (Aizen and Feinsinger, 1994; Kremen et al., 2002; Klein et al., 2003a,b; Ricketts, 2004; Chacoff and Aizen, 2006).”
Wild bee pollinators provide the majority of crop visitation across land‐use gradients in New Jersey and Pennsylvania, USA (2007, background): “104 wild bee visits to grapefruit in Argentina ( Chacoff & Aizen 2006 ); 615 wild bee visits to coffee in Costa Rica (Ricketts 2004); and 3349 wild bee visits to watermelon in California (Kremen, Williams & Thorp 2002; Kremen et al. 2004).”
Protecting an ecosystem service: approaches to understanding and mitigating threats to wild insect pollinators (2016, background): “natural habitats has to some extent been demonstrated (Chacoff and Aizen, 2006; Kleijn and 1044 Sutherland, 2003; Klein et al., 2003; Kremen et al., 2004; Morandin and Winston, 2006).”
How well do we understand landscape effects on pollinators and pollination services (2012, background): “…crops are directly affected by changes in landscape structure, resulting in productivity loss that endangers both biodiversity and the stability of food production in the world (Steffan-Dewenter et al. 2005; Tscharntke et al. 2005; Chacoff & Aizen 2006, Carvalheiro et al. 2010; Isaacs & Kirk 2010).”
Stingless bees in applied pollination: practice and perspectives (2006, background): “increases abundance and diversity of flowervisiting insects, and that these crops have a higher yield than crops growing away from natural vegetation (Wille and Orozco, 1983; Venturieri et al., 1993; Heard and Exley, 1994; Kremen et al., 2002; Klein et al., 2003a, b; Ricketts, 2004; Ricketts et al.,”
Managing ecosystem services in broadacre landscapes: what are the appropriate spatial scales? (2008, background): “This has been demonstrated for honeybee visits to macadamia flowers in Australian orchards near rainforests (Blanche et al. 2006) as well as for honeybee and other pollinator visits to grapefruit flowers near remnants of subtropical Argentinean forest (Chacoff and Aizen 2006).”