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      FIG. 7. Changing status of black redstart in Britain showing increase in number of territory holding males during the 1939–45 war with a decline following the final clear-up of war damaged sites after 1950. The solid line gives figures for the whole of Great Britain, while the dotted line is the contribution made by the City of London and Dover combined. (Data from Fitter 1965).

The black redstart was originally a bird of the warm montane regions of the southern Palaearctic, like the rock thrush and crag martin, but spread northwards after the last glaciation. It has adapted itself to a man-made environment, using buildings for nesting sites in lieu of cliff faces, and in parts of Germany it replaces the robin as the familiar follower of man. Its northward spread was still in progress across Germany during the last hundred years, and it only reached Jutland in the second half of the nineteenth century, and Scandinavia in the early 1940s. There is no record of it in Britain before 1819, though it became a regular passage migrant on the south and east coasts during the middle of the nineteenth century. Sporadic nesting attempts followed, in Durham in 1845, Sussex in 1909 and then a slow build-up from 1923 onwards. Three pairs nested at the Palace of Engineering in Wembley, Middlesex from 1926–41 but altogether less than half a dozen pairs were breeding in Britain up to the mid 1930s after which a big increase occurred, detailed in Fig. 7. The ability of the species to establish itself in this way has followed the sudden availability of nesting sites and feeding grounds, in the form of war-time bombed sites, particularly in London and Dover. Rebuilding and the post-war clean-up account for the subsequent decline in numbers.

      There are also examples of bird numbers reduced through direct persecution, especially when the victim is fairly rare. The great crested grebe was certainly widely distributed in suitable places in Britain in the early nineteenth century, but by the middle years of the century a big demand arose for its breast feathers to make ‘grebe furs’ for a fashionable home market, and the slaughter began in 1857. By 1860, the species was reduced to 42 known pairs and was only saved by the sanctuary afforded by private estates, while further help came with the Bird Protection Acts of 1870–1880. Nevertheless, some increase was under way by 1880, before protection could have been very effective, and Harrison and Hollom (1932), who record these early changes, consider that human persecution came at the start of a period of long-term cyclical increase. By 1931, there were around 1,150 breeding pairs (with non-breeders, about 2,650 adults) in England and Wales and about another 80 pairs in Scotland. A sample census by Hollom (1959) showed that about the same number of adult grebes existed in Britain in the 1940s, but that an increase then began. When Prestt and Mills undertook a census in 1965 there were approximately 4,500 adults in Britain. This increase seems to have been favoured by man’s activities in creating numerous new reservoirs and gravel pits, just as the little ringed plover benefited. The 70% increase of the population in about twenty years can be compared with an increase of 84% in sand and gravel production between 1948 and 1957. That an increase followed the creation of new habitats also indicates that saturation had previously been attained and that the bird was regulated in the sense already discussed.

      For a species to extend its range and take advantage of newly developed habitats it would be helpful for it to possess some kind of exploratory behaviour rather than rely on chance movements. It is becoming clear that immediately after breeding, many species, which normally migrate south, first indulge in northerly flights. The large-scale ringing of sand martins has shown that birds breeding at a colony in the south of England may move north to have their second brood, and juveniles marked in southern England have been found again in roosts in the north in the same season. Wood-pigeons also display northerly flights in September and October, before adopting a southerly orientation later in the autumn. Collared doves ringed in Europe as nestlings have moved north to Britain in the same autumn, and numbers of serins have turned up in south-west England in recent autumns. These movements seem adaptive in that young individuals which are surplus to the needs of the area in which they are born will stand more chance of finding new places to settle if they first explore north. The same principle applies to those birds of southeast and east Europe which might be expected to move north-west or west. I suspect that this factor may account for big arrivals of redbreasted flycatchers, woodchat shrikes, barred warblers, melodious and icterine warblers – all predominantly juvenile – into Britain in September 1958 and in subsequent years. Williamson showed that red-breasted flycatchers and icterine warblers arrived in Britain in clear anticyclonic weather with light winds, and as both migrate south-east to Asia, their movement several hundreds of miles off-course is remarkable. The explanation that they drifted in with down winds seems unlikely, and instead I wonder whether the existence of anticyclonic weather facilitated a normal adaptation after breeding in the form of a deliberate dispersal north-west, a process possibly truncated in years of less favourable weather.

      Man has done so much in a passive way to alter the avifauna of Europe that it seems reasonable to take active steps to reintroduce lost species. Any reservations that this would be unnatural, should be tempered by the thought that the environment we have created is in any case artificial. Probably more pleasure than harm has been derived from the reintroduction of the capercaillie. It would seem laudable to follow up a recent suggestion and attempt the reintroduction of the bustard to parts of the East Anglian Breckland, and to encourage black terns to stay and breed. It is quite a different matter to introduce alien species to a new country, especially without sound biological knowledge. In Britain, some of these introductions, red-legged partridge, various pheasants, little owl, Canada and Egyptian goose and Mandarin duck have on balance improved our bird-life, but the same could not be said of the introduction of the house-sparrow and starling to Australia and North America.

      Perhaps a more interesting question to ask here is why the majority of introduced species are unsuccessful. This is part of the much bigger question of what factors determine faunal diversity and enable some habitats to support more species than others. The concept of a niche, which refers to the animal’s place in the biotic environment and its relations to food and predators, should now be widely appreciated. It is a fundamental tenet of ecology that no two species can occupy the same niche in any one habitat, because both cannot be equally well adapted. R. and J. MacArthur (1961) examined numerous habitats at different latitudes for their plant species composition and foliage profile and ‘species diversity’. They found this last to be a more useful measure than the actual number of species because their calculations allowed at a habitat containing 50 of species A and 50 of B to rank a higher diversity than one with 99 of A and 1 of B. (The latter tends to be the farmland situation, the former that of tropical forest.) It turned out that neither the variety of plant species nor the latitude affected the amount of species diversity which instead depended entirely on the variation in foliage height, probably because birds mostly respond to different configurations of vegetation in different layers. This means that habitats of the same structural profile have the same diversity of bird species. In any area, a bird might either feed on all food of a suitable size within a narrowly defined habitat or, alternatively, be selective of food but collect it throughout a wider range of habitats. In other words, birds could partition their food or their habitat. The former has occurred because feeding specialisation brings the greatest advantages and has been favoured by natural selection. Partitioning the habitat would necessitate birds moving from one suitable micro-habitat (say a species of tree) to another, and it would depend on the pattern of the total habitat how much time would be wasted in the process. But adaptation to a comparatively broad habitat structure, for instance, to arboreal or ground feeding, must in turn impose physical limitations which restrict the diversity of feeding adaptations; in practice, bill size and shape is about all that can be much modified to suit the collection of different foods.

      From the viewpoint of zoo-geography, the Palaearctic has existed as an entirety for sufficient time to ensure that most niches are filled by highly efficient species. Furthermore, man and birds have lived side by side since Neolithic times, so that the new habitats created by agriculture and man’s other activities have been occupied by the species best suited to them. The same is not true of Australia and New Zealand, which were cut off from the main centres of evolution at an earlier stage, one result being that primitive marsupial mammals were not replaced by the better adapted placental

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