Andrew M. Wilson

Numbers and distribution of Northern Lapwings Vanellus vanellus breeding in England and Wales in 1998

This paper presents the results of the BTO/RSPB survey of breeding Northern Lapwings Vanellus vanellus in England and Wales carried out in 1998. Numbers of breeding Lapwings and land-use types were recorded by volunteers in 1312 randomly selected tetrads using identical methods to those adopted in a previous survey in 1987. The results suggest a population of 62 923 breeding pairs (95% confidence intervals 55 268 to 74 499), representing a 49% decline in 11 years. The declines were greatest in southwest England and Wales, resulting in a marked contraction in range. Both arable and pastoral farmland was found to be important for Lapwings, highlighting their vulnerability to changes in a range of agricultural systems. Recent major changes in land management practices, including the switch from spring to autumn sowing and the conversion of rough to intensively managed, improved grassland is likely to have reduced both the area and the suitability of these habitats for Lapwings. Grassland within arable areas is known to provide important chick rearing habitat, and spring tillage with adjacent grassland was significantly more likely to hold Lapwings than spring tillage that did not abut grass fields. The prevalence of grass and spring tillage fields in close proximity has declined in recent years with the loss of traditional mixed farming and the polarization of pastoral systems in the west of Britain and arable in the east. The implications of these results for the conservation of Lapwings are discussed and it is recommended that, in the light of the scale of the decline recorded, Lapwings should be afforded much higher conservation priority in Britain than they are at present. The range contraction has resulted in high numbers being concentrated on reserves, highlighting the importance of sensitive management of these areas for this species. However, wider countryside measures should also be considered, such as specific options within agri-environment schemes, designed to enhance farmland habitats for Lapwings.

Changes in the numbers of breeding waders on lowland wet grasslands in England and Wales between 1982 and 2002

Capsule Lapwing, Snipe, Curlew and Redshank decreased significantly between 1982 and 2002, while over the same period Oystercatcher increased. Aims To provide current status and population trends for waders breeding on lowland wet grassland in England and Wales. Methods Waders were counted and mapped on three visits to 1051 lowland wet grassland sites, between April and June 2002. Data were compared with those gathered using identical methods in a survey in 1982 and related to land use characteristics and conservation designation. Results Between 1982 and 2002 there were significant declines of 38% for Lapwing Vanellus vanellus, 61% for Snipe Gallinago gallinago, 40% for Curlew Numenius arquata and 29% for Redshank Tringa totanus. Oystercatcher Haematopus ostralegus increased significantly by 47% in the same period. Populations of all species were highly aggregated with most of the birds found on a small number of key sites. Site designation was found to be an important predictor of breeding wader distribution, density and density change. Conclusions The marked population declines of four grassland wader species over the last 20 years are of considerable concern. Careful management of nature reserves and other key sites is essential to halt these declines, while wider scale and more carefully targeted agri-environment schemes may hold the key to reversing declines in the longer term. The efficacy of site designation and current agri-environment schemes for conserving breeding waders on wet grasslands needs to be reviewed.

Population estimates, trends and habitat associations of breeding Lapwing Vanellus vanellus, Curlew Numenius arquata and Snipe Gallinago gallinago in Northern Ireland in 1999

Capsule Declines in the breeding populations of Snipe, Lapwing and Curlew were recorded between April and June 1999 and compared with previous estimates in 1987. Aims To compare populations of non-coastal breeding waders between 1987 and 1999. Methods In 106 2 km × 2 km square tetrads, observers recorded the number of breeding pairs of waders and habitat details on 1:10 000 scale maps. Results A significant decline of c. 60% for Lapwing and Curlew, and a non-significant decline of 30% for Snipe was recorded over 12 years. Concentrations of these species were found in County Tyrone, but Counties Antrim, Down and Armagh supported few breeding pairs of any species. Very few pairs of any species were recorded on improved grassland despite its widespread availability. Conclusion A successful conservation strategy for these species must address the wider countryside and not just key sites. Intensive pastoral farming in upland and lowland areas and activities such as drainage and peat extraction will further reduce the suitability of open habitats for these wader species.

Distribution and abundance of birds and their habitats within the lowland farmland of Britain in winter

Capsule Farmland bird species occurred at low densities and were highly aggregated in a small proportion of available pastures, stubble fields and farmyards. Aim To document the current distribution and abundance of farmland birds and their habitats within the lowland farmland of Britain in winter. Methods Over three winters volunteer observers visited a stratified random sample of 1090 1-km squares within which they counted a suite of 30 farmland bird species and mapped agricultural habitats. Results For individual species, less than 10% of habitat patches were occupied and densities in occupied patches were low. Several differences were apparent in patterns of relative abundance compared to the 1980s. In particular marked declines of Tree Sparrow and Corn Bunting were apparent. The national distribution of cereal stubbles was localized. A large proportion of most species was found in grassland. Positive associations at the patch scale were apparent for improved grassland by invertebrate feeders and cereal and maize stubbles and farmyards, mostly by granivores. Conclusion Many farmland passerines are highly aggregated, even within particularly favoured field types. These results are consistent with winter food resources being highly localized and the need to create more food-rich patches if declines are to be reversed.

Decline in Yellow Wagtail Motacilla flava flavissima breeding on lowland wet grassland in England and Wales between 1982 and 2002

Capsule Numbers had fallen by 65% in 20 years.