Ecology. Michael Begon

This guaranteed a near constancy in the number of established, winning plants between 1943 and 1956, accompanied by a variable number of ‘losers’ that not only failed to grow, but usually, in due course, died. Similar patterns can be observed in tree populations. The survival rates, the birth rates and thus the fitnesses of the few established adults are high; those of the many seedlings and saplings are low.

Figure 5.30 Asymmetric competition enhances population size regulation in an anemone. Space pre‐emption in a perennial, Anemone hepatica, in a Swedish forest. Each line represents one individual: straight for unramified ones, branched where the plant has ramified (i.e. produced new plants by vegetative growth), bold where the plant flowered and broken where the plant was not seen that year. Group A were alive and large in 1943, group B alive and small in 1943, group C appeared first in 1944, group D in 1945 and group E thereafter, presumably from seedlings.

      Source: After Tamm (1956).

      5.8.4 Territoriality

      Territoriality refers to active interference between individuals, such that a more or less exclusive area, the territory, is defended against intruders by a recognizable pattern of behaviour. It is one widespread and important example of asymmetric intraspecific competition.

      territoriality is a contest and regulates population size

Individuals of a territorial species that fail to obtain a territory, commonly referred to as ‘floaters’, often make no contribution whatsoever to future generations. Territoriality, therefore, is a ‘contest’. There are winners (those that come to hold a territory) and losers (those that do not), and at any one time there can be only a limited number of winners. The exact number of territories (winners) in a population may vary, depending on resources or environmental conditions. We see this, for example, for the number of tawny owl (Strix aluco) territories in a Finnish population, and especially the number of productive territories, which varies with the abundance of their vole prey (Figure 5.31). Nonetheless, the contest nature of territoriality ensures, like asymmetric competition generally, a comparative constancy in the number of surviving, reproducing individuals. In the past, some felt that these regulatory consequences of territoriality must themselves be the root cause underlying the evolution of territorial behaviour – territoriality being favoured because the population as a whole benefitted from the rationing effects, which guaranteed that the population did not overexploit its resources (e.g. Wynne‐Edwards, 1962). However, there are powerful and fundamental reasons for rejecting this ‘group selectionist’ explanation (essentially, it stretches evolutionary theory beyond reasonable limits): the ultimate cause of territoriality must be sought within the realms of natural selection, in some advantage accruing to the individuals concerned.

Figure 5.31 The number of (successful) territories may increase at higher resource levels. (a) The number of territories occupied by tawny owls, Strix aluco, in a study in Finland tends to increase as the abundance of their vole prey increases, though not significantly, but (b) the proportion of these in which territory holders are successful in breeding increases significantly with prey abundance (P = 0.007).

      Source: After Karell et al. (2009).

      benefits and costs of territoriality

Any benefit that an individual does gain from territoriality, of course, must be set against the costs of defending the territory. In some animals this defence involves fierce combat between competitors, while in others there is a more subtle mutual recognition by competitors of one another’s keep‐out signals (e.g. song or scent). Even when the chances of physical injury are minimal, territorial animals typically expend energy in marking, patrolling and advertising their territories. Hence, for territoriality to be favoured by natural selection, we expect the benefits to exceed these costs. Indeed, we expect territories to be an optimum size – ‘as large as necessary but as small as possible’ (Kittle et al., 2015) – in that as territory size increases, defence costs will also increase but resource access is increasingly likely to exceed the animals’ requirements. This in turn suggests that as habitat quality (and resource ‘concentration’) increases, territory sizes should decrease (they do not need to be as large), which is precisely what we see for the lion territories in Figure 5.32.

Figure 5.32 Territory sizes occupied by male lions (Panthera leo) in Zimbabwe decreased as habitat quality increased. Habitat quality was equated with the estimated concentration of the biomass of a wide range of prey species.

      Source: After Loveridge et al. (2015).

      floater? or territory holder?

On the other hand, explaining territoriality only in terms of a net benefit to the territory owner is rather like history always being written by the victors. A trickier question, which has received less attention, asks to what extent floaters, without a territory, are simply losers or are themselves net beneficiaries of a strategy they have adopted. Three main hypotheses, not mutually exclusive and all receiving some support, have been proposed for what determines whether an individual, as a result of a contest, becomes a floater or a territory holder: (i) territory holders are in some sense ‘stronger’, (ii) they have skills that they have acquired with age, and (iii) they are winners because they have acquired familiarity, as holders of the territory already (Sergio et al., 2009). Variants of these hypotheses also include there being a ‘convention’, respected by the participants, through which the larger animal or the territory holder always wins. There is no doubt that some floaters are simply losers: too small, too young or too lacking in local knowledge, and therefore en route to dying without making any contribution to future generations. However, we see in Figure 5.33, for example, that for black kites, Milvus migrans, in the Doñana National Park in Spain, where floaters are neither smaller, nor in worse condition, and there is no ‘resident always wins’ rule, floaters are predominantly the youngest individuals, and territory holders are all members of the older age classes. Hence, for many of these floaters, it is not so much a case of reproduction‐denied as reproduction‐deferred. It therefore makes evolutionary sense for the young floaters to invest little in territorial contests in their earliest years (and in that sense ‘accept’ their floater status, temporarily) so as to maximise their chances of surviving long enough to win a territory later.

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