2013
DOI: 10.1016/j.baae.2013.04.001
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Temporal effects of agri-environment schemes on ditch bank plant species

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Cited by 13 publications
(10 citation statements)
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“…Plants depend on various dispersal vectors that impact species' response to landscape habitat composition and connectivity. In drained lowlands, the presence of water in ditch networks offers important corridor potential for hydrochorous species (Ozinga et al, 2004;Vogt et al, 2004;Soomers et al, 2010Soomers et al, , 2013Van Dijk et al, 2013), especially as they provide an effective and long-distance dispersal of plant propagules (Nilsson et al, 2010). However, propagules may also be dispersed by other vectors, such as wind or animals (Ozinga et al, 2004).…”
Section: Introductionmentioning
confidence: 98%
“…Plants depend on various dispersal vectors that impact species' response to landscape habitat composition and connectivity. In drained lowlands, the presence of water in ditch networks offers important corridor potential for hydrochorous species (Ozinga et al, 2004;Vogt et al, 2004;Soomers et al, 2010Soomers et al, , 2013Van Dijk et al, 2013), especially as they provide an effective and long-distance dispersal of plant propagules (Nilsson et al, 2010). However, propagules may also be dispersed by other vectors, such as wind or animals (Ozinga et al, 2004).…”
Section: Introductionmentioning
confidence: 98%
“…Despite being the main instrument of wetland loss, canals represent the only temporal continuity of wetland habitat in many drained landscapes (see Manhoudt et al, 2007 for the Netherlands), and are therefore refuges for organisms with high water demand (Chester & Robson, 2013; Harvolk et al, 2014). This paradoxical situation has led to the recognition that conservation value may be assigned to canals in agricultural landscapes, and therefore canals should be considered in conservation planning and agri-environmental schemes (Blomqvist et al, 2009; van Dijk et al, 2013).…”
Section: Introductionmentioning
confidence: 99%
“…Management requirements for biodiversity in canals may be substantially different from those of natural wetlands, posing new challenges for conservation planners. Conventional management prescriptions of agri-environmental schemes have frequently been reported as ineffective (Blomqvist et al, 2009; van Dijk et al, 2013; Shaw et al, 2015). The main constraints for biodiversity in canals appear to be the high nutrient load, pollution with pesticides and herbicides, and the inappropriate intensity of bed management, including dredging and vegetation cutting (Herzon & Helenius, 2008; Blomqvist et al, 2009).…”
Section: Introductionmentioning
confidence: 99%
“…Four times per year, between early April and the end of July, the area was crossed by foot around the time of sunrise, and all territorial and nesting birds were mapped. After the visits, the total number of Skylark breeding pairs was estimated based on standardised methods (Hustings et al 1989;Van Dijk and Boele 2011).…”
Section: Methodsmentioning
confidence: 99%
“…In arable areas, agri-environment schemes often focus on increasing the area of uncropped land, for example in the form of sown field margins or setaside (Vickery et al 2002;Tscharntke et al 2011). Various species living in agricultural areas depend on the presence of uncropped land, including a range of arthropods (Duelli and Obrist 2003;Tscharntke et al 2005), plants (Hovd and Skogen 2005;Van Dijk et al 2013), and birds (Fuller et al 2004;Henderson et al 2012).…”
Section: Introductionmentioning
confidence: 99%