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Habitat changes in British lowland landscapes and their
implications for bird populations

by Rob Fuller

3. Agriculture

Impacts of agriculture on birds have been of two broad types. The first is the loss of habitat, especially hedgerows and semi-natural habitats, and the second concerns the intensification of systems of growing crops and grass.

The destruction of semi-natural habitat was particularly widespread in the immediate post-war decades. Large areas of ancient woodland were destroyed and wet meadows have more or less completely disappeared in many river valleys as a result of drainage. More locally there were also losses of heathland, though agricultural reclamation of heaths dates back at least to the Enclosure Acts. Destruction of hedgerows in many regions took place on a very large scale during the period 1950 to 1980, probably reaching its peak in the 1960s. The effects of this habitat loss on bird populations have not been adequately quantified but we do know that populations of breeding waders have collapsed in many river valleys as the wet meadows have disappeared. Hedgerow loss and woodland destruction would have had very large effects on bird populations at a local scale. In those parts of the country where hedge removal was most severe, such as parts of East Anglia, there must have been large reductions in the regional populations of specialist hedgerow birds such as Lesser Whitethroat, Whitethroat, Yellowhammer and Linnet.

Tree Sparrow © Tommy HoldenThe intensification of agriculture since the Second World War and its effects on birds and other wildlife have been well documented (Stoate 1995, 1996, Aebischer et al. 2000, Vickery et al. 2001, Robinson & Sutherland 2002). It is now widely accepted that changes in farming practices are the root cause of the large declines that have occurred in populations of most specialist farmland birds (see Baillie et al. 2002, information on declines). In most cases, these declines started in the mid 1970s, which co-incided with the main period of intensification (Chamberlain et al. 2000). A range of processes has been involved. These are summarized in Boxes 1 and 2. The drive to increase efficiency and yields has been so effective that the changes outlined in the boxes have been ubiquitous. The net result has been a general reduction in food resources and habitat quality for most farmland birds at all seasons. Recent years have seen major efforts to restore habitats and foods for birds through various agri-environment initiatives, though farmland bird populations generally remain at a low ebb compared with the situation 50 years ago. See section 4.6 for information on farm woodlands.

Population trend graphs

Box 1: Major changes in arable farming since 1950 and their relevance to farmland bird populations in lowland Britain (based on Fuller 2000)

    Increasing mechanization
    The use of machinery allows farming activities such as cultivation, chemical application, harvesting and hedgerow management to be undertaken extremely rapidly on a large scale. The capacity for changing the face of the countryside is greater than ever. Use of combines and more efficient harvesting have resulted in less food for seed-eating birds. Ground-nesting birds may be at greater risk of losing nests and chicks.

    Fertilizer and pesticide usage
    Nitrogen inputs increased greatly on tilled land during the 1970s and 1980s and there was increasing reliance on inorganic compounds but less use of farmyard manure (FYM). This has resulted in faster growing crops, which are less suitable for ground-nesting birds such as Skylarks and Lapwings. The increasing reliance on synthetic fertilizers has reduced Poppie field © Su Goughthe need for mixed farming with fertility-building leys and livestock to produce FYM. Mixed farming offers a wider range of food resources, feeding sites and nesting sites for farmland birds than pure arable or grassland. Since the 1950s farming has become dependent on a large number of herbicides, insecticides, molluscicides and rodenticides. Many of these chemicals act in some way to reduce potential foods of farmland birds including seeds and invertebrates. Furthermore, the development of herbicides that could control grass weeds was a major factor enabling the switch from spring to autumn sowing (see below). The use of pesticides to control disease has also contributed to the demise of traditional rotations and, hence, of mixed farming.

    Reduction of spring sowing
    Since approximately 1970 there has been a decline in spring sowing of cereals. The general move towards late summer and autumn sowing has resulted in far less overwinter stubble with an associated reduction in winter-feeding opportunities for seed-eating birds, notably buntings, sparrows, finches and Skylarks. Cereal crops now grow throughout much of the winter period and consequently by the spring are often too tall and dense for ground-nesting birds.

    Simplification of rotations and reduction in mixed farming
    There has been a trend of specialization in farming with arable dominating in the east of lowland Britain and grassland in the west. Within arable systems, grass leys have become scarce and rotations are much simplified with cereals often being grown for several successive years. The implication for birds is that the countryside has become more uniform in terms of the foods and nest sites that it offers. Skylarks and Lapwings are examples of breeding species that benefit from a diversity of field types.

Rape field © Susan Waghorn

    New crops and the introduction of set-aside
    Two major features of positive significance to birds are the increasing prominence of oilseed rape in the countryside and the large-scale introduction of set-aside during the 1990s. Rape fields have proved attractive to several nesting birds and to Linnets, which feed on the seeds. Rotational set-aside has acted to some extent as a substitute for the loss of traditional stubbles as it has provided food resources for many seed-eating birds in winter as well as being used heavily by nesting Skylarks and many feeding birds during the summer (Henderson & Evans 2000).

Box 2: Major changes in grassland farming since 1950 and their relevance to farmland bird populations in lowland Britain (based on Fuller 2000)

    Increasing mechanization
    This has made it possible to apply fertilizer on a large scale and to readily implement under-drainage (see below). However, an immediate impact has been the destruction of nests and young of ground-nesting birds of which the Corncrake has proved to be one of the most vulnerable.

    Drainage and improvement of rough grassland
    This has been ongoing since the 1930s. A major consequence has been widespread loss of habitat for breeding waders notably Redshank, Snipe and Lapwing.

    Photo - river valley © Andy WilsonFertilizer usage
    There were escalating inputs of inorganic fertilizer and slurry on grass throughout the 1970s and 1980s. Grass yields accordingly rose dramatically and floristic diversity decreased. The general consequences have been reduction of many invertebrate groups, fewer seeding broadleaved plants and much denser vegetation. All these factors generally acted to reduce the quality of grassland as both a nesting and foraging habitat for many species, especially for insectivorous birds in summer and for seed-eating birds at all times of year. However, birds such as Starlings and crows that depend on soil invertebrates, have not been affected deleteriously as intensive grass management may have actually increased the availability of food for these species, especially in winter.

    Reduction of hay and increase in silage
    Since the 1960s silage has become the dominant system for mown grass. Silage making is highly mechanized, usually with multiple cuts, and involves heavy fertilizer inputs (see above for consequences).

    Changing livestock patterns
    Between the mid 1970s and 1990s numbers of sheep increased in most regions of Britain while numbers of dairy cattle decreased over the same period. Intensive sheep grazing produces relatively short, uniform swards that are poor nesting habitats for most ground-nesting birds. For a review of the implications for birds see Fuller and Gough (1999).

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