Home > Research > Information for Conservationists > Habitat changes in lowland landscapes > Section 2

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

by Rob Fuller

2. Habitat loss, habitat deterioration and habitat fragmentation

A distinction needs to be made between impacts that result in the loss or destruction of habitat, and impacts that leave the habitat apparently intact, but in some way reduced in quality. The destruction of habitat can be clear-cut, for example the destruction of a wood and its conversion to agriculture or the building of a housing estate on a heath. There have been virtually no studies of what happens to individual birds displaced by such extreme habitat loss but presumably many die, especially when alternative habitat is scarce. Habitat loss should be regarded as the most powerful threat to the persistence of populations at all scales.

Marsh Tit © Mike WestonDeterioration of habitat quality is more insidious. The potential mechanisms are various, for example a reduction in food supplies, an increase in vulnerability to predators or the gradual loss of some preferred habitat structure. Over a period of time the breeding output or the survival of a population living in a patch of deteriorating habitat may be reduced to a point where the population is no longer self-sustaining. Under such circumstances, the continued occupancy of the patch will depend on immigration and the patch will have become a 'population sink'. Many of the recent effects of agricultural intensification are essentially ones of habitat deterioration. There is evidence that many birds show considerable site fidelity under conditions of moderate change in habitat. However, there will be a threshold beyond which habitat deterioration becomes so severe that the patch will be abandoned. This may mean that there is a time lag between the onset of habitat change and a numerical response in the population. This appears to have been the case with farmland birds in Britain, which only started to decline several years after the onset of intensification of agriculture (Chamberlain et al. 2000). If habitat deterioration proceeds unchecked, then a point will be reached at which the process has effectively become one of habitat loss.

Habitat fragmentation has become widely regarded as a critical issue in conservation science (Hansson et al. 1995, Wiens 1995, Villard 2002). Habitat fragmentation is concerned with spatial processes, such as negative edge effects (e.g. predation pressure) and dispersal problems that become increasingly severe as habitat is divided into smaller units. Several studies have indicated that fragmentation effects are likely to become relevant once the total amount of habitat has dropped below a certain critical threshold. When patches become small they are more vulnerable to processes that will lead to habitat deterioration. In practice it has proved extremely difficult to separate effects of habitat loss from those of habitat fragmentation. This is partly because habitat fragmentation can, by definition, only occur when the extent of habitat is reduced.

Two points are worth bearing in mind with respect to the effects of habitat fragmentation on birds in lowland Britain. Firstly, many habitats in lowland Britain have been fragmented into relatively small patches for many hundreds of years so that species have had a long period to adapt. Secondly, compared with most taxa, birds have relatively strong dispersal ability and, with a few exceptions, do not have great difficulty moving between habitat patches. In summary, habitat fragmentation is increasingly thought of as a secondary issue to that of habitat loss. This is not to say that fragmentation of blocks of extant habitat, for example by roads, is a trivial issue but the main thrust of conservation effort should be on maintaining or restoring large areas of good quality habitat.

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