The impact of grassy field margins on macro-invertebrate abundance in adjacent arable fields
Research highlights
▶ Presence of grassy margins in arable fields increases macro-invertebrate abundance. ▶ Abundance of carabids and earthworms increases, abundance of gastropods decreases. ▶ Effects were mainly noticeable on the edge, but may also occur further in the field.
Introduction
About 38% of the total land area of the world was used for agricultural purposes in 2004 (Clay, 2004), an area potentially valuable for an array of species (e.g. Chamberlain et al., 2000, Robinson and Sutherland, 2002). However, especially after the Second World War, farm management rapidly changed and intensified resulting in a reduction in diversity of landscapes (Robinson and Sutherland, 2002, Foley et al., 2005). Consequently, changes in agricultural management have frequently been mentioned as one of the major causes for the loss of species diversity and abundance (e.g. Krebs et al., 1999, Donald et al., 2001, Robinson and Sutherland, 2002, Foley et al., 2005).
Agri-environment schemes were introduced into the agricultural policy of the USA, Australia and in the European Union, during the last few decades, partly with the aim of protecting biodiversity and also in an attempt to reverse some of the negative impacts of agricultural intensification on wildlife and the environment (Australian Government, 2009, European Commission, 2009, USDA, 2009). Many existing agri-environment schemes have provision for grassy, or uncultivated, field margins (e.g. Benton, 2007, Butler et al., 2007). Many studies focus on the effect of different arable field margin management strategies on invertebrates (e.g. Morris and Webb, 1987, Kromp and Steinberger, 1992, Baines et al., 1998, Asteraki et al., 2004, Woodcock et al., 2005, Woodcock et al., 2007). However few studies investigated the impact of the presence of a grassy field margin in itself in comparison with its absence (Yu et al., 2006). More studies investigate whether a possible positive effect of grassy field margins on invertebrate abundance extends to surrounding arable fields (Kromp and Steinberger, 1992, Kádár et al., 2004, Saska et al., 2007, Smith et al., 2008, Werling and Gratton, 2008, Twardowski and Pastuszko, 2008), but many of these studies focus on a specific group of invertebrates.
Marshall et al. (2006) investigated the impact of agri-environment field margins and found positive impacts on diversity or abundance for flora, bees and orthoptera, but not for birds, spiders and carabids. However, it has also been found that undisturbed boundaries such as hedges and beetle banks, may act as winter reservoirs for some species of carabids in arable landscapes (Sotherton, 1984, Sotherton, 1985, Morris and Webb, 1987). Dennis and Fry (1992) found that the predatory arthropod species diversity is higher near grassy field boundaries. Whether the abundance of earthworms and gastropods may be enhanced in arable fields by the presence of an unmanaged boundary is currently not well studied and might be important with respect to the conservation of invertebrates and their predators, and to pest management. Complementary to the available literature, this paper investigates if the presence of grassy field margins affects the abundance of macro-invertebrates (earthworms, gastropods and carabids) in the field margin, and in adjacent arable fields.
Section snippets
Materials and methods
A total of 32 arable fields were sampled for invertebrate abundance in May–July 2009. All fields were surrounded by an established hedgerow of at least 2 m wide. Half of these fields were surrounded by a grassy field margin of 4–6 m wide and managed through an agri-environment scheme (Entry Level Stewardship [Natural England, 2008]). The remaining 16 fields did not have a grassy field margin; they were either harvested up to the hedgerow or a fringe (<1 m) of scrub and or nettles was still
Earthworms
The mean number of earthworms in the soil was significantly higher on fields with than on fields without a grassy margin (Wilcoxon signed-rank test: Z = −5.874, p < 0.001) at 0 and 20 m from the edge (Wilcoxon signed-rank test 0 m: Z = −5.855, p < 0.001, 20 m: F = −2.458, p = 0.014), but not at 10 m from the edge (Wilcoxon signed-rank test: Z = −0.235, p = 0.814). The mean biomass of earthworms was also significantly higher on fields with than on fields without a grassy margin (Wilcoxon signed-rank test: Z = −3.701,
Discussion
In our study carabids were more abundant on arable fields that had grassy margins along the edges. Although this appeared to be especially so away from the edge of the field; we did not find any significant differences at both 10 and 20 m from the edge, likely due to the high standard error of the mean. However, it must be noted that pitfall trap catches not only depend on the density of populations, but on other factors such as activity and body size of the species as well (Lang, 2000). Indeed,
Acknowledgements
We wish to thank the farmers who were so kind in permitting fieldwork on their land. We were also grateful for the help of fieldwork assistants Michael Bennett and Pieter Berends. The entire project was funded jointly by the People's Trust of Endangered Species, the British Hedgehog Preservation Society and by a legacy of Dilys Breece, to whom we are greatly indebted. We would also like to thank two anonymous referees for their useful comments.
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