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

by Rob Fuller

2. Habitat changes in the uplands associated with farming

Two main agricultural processes have been especially significant for birds in the British uplands. Firstly, the widespread improvement of grassland at the hill edge and, secondly, changes in livestock systems, in particular large increases in numbers of sheep.

2.1 Grassland and moorland improvement

Curlew © Derek Belsey
The term 'grassland improvement' embraces a complex of farming activities aimed at raising land productivity; these include drainage, ploughing, fertilising, re-seeding and herbiciding. This has often been a precursor to higher stocking and / or a switch from hay to silage. There is considerable evidence that numbers of ground-nesting birds have declined in moorland-edge habitats (Baines 1988, 1989, 1990, Fuller et al. 2002).
Numbers of breeding curlews and other waders have declined in marginal upland habitats as a result of changes in grassland management.

These include populations of breeding waders - notably Lapwing, Redshank, Snipe and Curlew - and of passerines including Skylark, Twite and Reed Bunting. Loss of damp and rough grassland appears also to be a factor in local declines of Black Grouse and Yellow Wagtail (Ratcliffe 1990). There has been widespread improvement of enclosed land close to open moorland in many upland regions of Britain and these declines in ground-nesting birds are probably associated with these habitat changes. Vickery et al. (2001) describe mechanisms by which changes in lowland grassland management have affected birds and their food resources; these are broadly relevant to upland grasslands. Deterioration of habitat quality through loss of damp feeding areas is probably a key mechanism for breeding waders. Changes in the structure of swards have also been important for many birds. Where improvement has resulted in relatively simple, uniform swards, this can result in increased predation pressure on nests and chicks. Where there has been a switch to silage crops, the vegetation may be too dense for birds to nest and forage efficiently. A general effect of grassland improvement has been reduction of abundance of seeds which is especially important to buntings and finches.
Under some circumstances, grassland and moorland improvement may cause a local increase in some species. Oystercatchers for example, frequently appear to benefit from grassland improvement (Ratcliffe 1990). In the Uists, Outer Hebrides, patches of moorland were fertilised and reseeded in the 1980s. Some of these green 'reseeds' have been colonised by Oystercatcher, Lapwing, Redshank and even Dunlin (Pienkowski et al. 1986). These reseeds may, however, be unusual in having substantial wet areas remaining within them. Where drainage occurs on open moorland, it is likely that high densities of breeding waders would not be sustained. Furthermore, other species of moorland birds that are less obviously birds of wet places, such as Red Grouse and Meadow Pipit, may depend on flushes as sources of insect food for their chicks (Hudson 1988).
Breeding bird territory graph
Numbers of territories of four breeding bird species on two farms in marginal uplands between 1976 and 1988. Solid lines are numbers on Farm 1 (Lancashire) and dotted lines from Farm 2 (West Yorkshire). From Fuller et al. (2002).

Reed Bunting © Tommy Holden   In some areas, especially in areas of Welsh ffridd, and in parts of Scotland, land improvement in the marginal uplands has involved scrub clearance through cutting or burning. Gorse scrub is especially vulnerable.This can cause local habitat loss for many relatively common scrub-nesting birds.
Reed Buntings have fared badly on marginal upland farms in England.

 

2.2. Grazing pressure

Grazing pressure has increased in many upland areas as a result of increases in numbers of sheep or deer. Large increases in numbers of sheep have occurred throughout the main sheep-farming regions of Britain since the mid 1970s with numbers tending to stabilise or slightly decline since around 1990 (Fuller & Gough 1999). The upland regions that have undergone the largest increases in sheep are Wales and northern England. Within Scotland, the greatest increases in sheep have generally been evident in the Southern Uplands but locally there have been large increases in stocking in several parts of Scotland.
Sheep population graph
  The improvement of grassland described above often precedes an increase in sheep numbers so in practice it can be difficult to distinguish the effects of land improvement from those of grazing. Nevertheless, the widespread increase in grazing pressure by sheep over the last 30 years has probably been generally deleterious to bird communities in upland regions (Fuller 1996, Fuller & Gough 1999). In general the species that have benefited either tend to be ones that use very short swards, notably Wheatear, and scavengers or generalists, notably the corvids.
The number of sheep has increased in most areas of Britain in recent decades. Numbers in Wales have increased steadily since 1950, but many other regions have shown increases since the 1970s. Although numbers have tended to decrease since the 1990s sheep still remain far more numerous than in the mid 1970s.

 
Intensified grazing by sheep has affected upland birds through three main mechanisms. Firstly, grazing can alter vegetation types that are preferred by some species. The loss and fragmentation of heather is a principal concern in this respect but alteration of vertical and horizontal vegetation structure is probably also important. Spatial complexity of sward structure in terms of patchiness, height and foliage density appears to be important to several bird species in providing cover for nests and chicks, and feeding sites. Heavy grazing tends to reduce such sward complexity. Secondly, heavy grazing can have complex effects on the food resources used by birds, such as fruit, invertebrates, small mammals and carrion.
Heavy grazing is likely to actually increase availability of soil and dung-associated invertebrates for Starlings, Magpies, Jackdaws and Rooks. Set against this, however, the widespread use of avermectins may act to diminish populations of dung invertebrates. Heavy grazing generally results in a reduction of the small mammals upon which several owls and Kestrels depend.  
Reed Deer © Roger Tidman
 
Increasing numbers of deer have caused added grazing pressure in the uplands.

Carrion is a key resource for Ravens, Crows, several birds of prey and foxes. In many areas the increase in sheep numbers since the 1970s probably led to larger amounts of carrion for scavenging birds. However, there are no simple general relationships between numbers of sheep and carrion because husbandry and stock management practices have to be taken into account as well as sheep density. Thirdly, heavy grazing may affect predation of ground-nesting birds in various ways. By altering the structure and pattern of vegetation, grazing could influence the probability of nests being detected by predators. It may also enhance some of the other food resources used by predators, notably carrion and soil invertebrates. This could lead to increases in numbers of corvids but whether this would necessarily result in an increase in predation pressure on ground-nesting birds is uncertain.

Grazing by deer is not specifically an agricultural issue but it is appropriate to mention it here because the mechanisms by which moorland birds are affected are very similar to those involved with sheep grazing.

Black Grouse © Tommy Holden
  The issue of deer grazing in the uplands is principally a Scottish one and mainly concerns Red Deer, which approximately doubled in numbers between the 1950s and 1990s. One of the main concerns about deer numbers is their effect on woodland habitats, particularly the native pinewoods. Suppression of the field layer appears to be a contributory factor in the decline of Black Grouse and Capercaillie (Baines 1996, Baines & Hudson 1995, Baines et al. 1994). There is also a wider issue of the impact that deer may have on natural regeneration of trees, both within and outside existing woodland.
Heavy grazing of the field layer appears to be a contributory factor in the decline in birds such as the Black Grouse.

 

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