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Factors affecting the survival of
Birds of Conservation Concern

by David Leech

 

5.2.2 Agricultural intensification

 
Agricultural intensification during the post-war period has greatly reduced the amount of food available to foraging birds, especially granivorous species, on farmland habitats (O'Connor and Shrubb, 1986; Donald, 1998; Robinson and Sutherland, 2002).
 
  • Increased use of herbicides and insecticides has led to a decrease in the abundance of weeds growing on arable land and therefore to a decrease in both the availability of seeds to foraging birds (Figure 5.1) and the abundance of invertebrate prey.
 
Seed density graph

Graph showing long-term trend in seed density in arable soils.

 
  • Destruction of hedgerows and field margins has reduced the area available for colonisation by seed-producing weed species and invertebrates.
  • As the efficiency of harvesting has increased, the amount of grain spillage has decreased ten-fold.
  • Planting of winter cereal crops has also increased, reducing the amount of fallow land and particularly the area of seed-rich stubble on which birds are able to forage during the winter. Stubble has been identified as the preferred winter foraging habitat for a variety of farmland bird species including corn buntings (Donald and Evans, 1994) and reed buntings (Wilson et al., 1997b).
At present, little direct evidence exists to link variation in the survival rates of declining farmland birds with specific changes in agricultural practices (see Section 4). This is partly due to the fact that data concerning such changes (eg variation in seed abundance) are not available at a sufficient temporal and spatial resoluation to permit reliable analyses of relationships with long-term variation in survival rates. However, the results of several studies suggest that certain land management practices may affect population sizes of some species.
 
  • The results of studies by Siriwardena et al. (1998, 1999) suggest that declines in the population sizes of a variety of farmland bird species are due to decreasing survival rates, which in turn may be related to changes in their food supply.
  • Several farmland bird species have been observed to forage preferentially on seed-rich fields (Donald and Evans, 1994; Wilson et al., 1997; Donald and Vickery, 2000). A reduction in seed density may result in reduced intake or increased foraging times, potentially leading to a decrease in survival rates, particularly during adverse weather conditions (Robinson, 2001).
  • Donald (1997) observed that the area of spring cereals sown annually in the UK between 1968 and 1993, and therefore the area covered by stubble during the winter, was positively correlated with the abundance of corn buntings at a national scale (Figure 5.2). However, this study provides only weak evidence for a link between seed availability and corn bunting survival as many other factors with the potential to influence the size of the population may also have displayed variation over this period, eg field sizes, pesticide use, hedge removal.
cereals and corn bunting graph

Graph showing the positive relationship between area of spring sown cereals and corn bunting abundance.

 
Corn Bunting © Tommy Holden

A reduction in seed availability has been proposed as the principle factor responsible for the decline of the corn bunting population.

  • Evans (1997) reported an increase in the number of cirl bunting pairs from 120 to 350 over a 4-year period in response to the increased provision of field margins and winter stubbles.
  • Examining the population recovery, Peach et al. (2001) found that cirl bunting abundance had increased by 83% in areas where field margins and stubble had been provided, compared to a population increase of just 2% in 'unimproved' areas.
Further investigation is needed to determine whether increased food availability over the winter period affects population size by decreasing mortality rates or by increasing brood productivity in these species.
 

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