Michael Begon - Ecology

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Ecology: краткое содержание, описание и аннотация

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A definitive guide to the depth and breadth of the ecological sciences, revised and updated The revised and updated fifth edition of
– now in full colour – offers students and practitioners a review of the ecological sciences. 
The previous editions of this book earned the authors the prestigious ‘Exceptional Life-time Achievement Award’ of the British Ecological Society – the aim for the fifth edition is not only to maintain standards but indeed to enhance its coverage of Ecology.
In the first edition, 34 years ago, it seemed acceptable for ecologists to hold a comfortable, objective, not to say aloof position, from which the ecological communities around us were simply material for which we sought a scientific understanding. Now, we must accept the immediacy of the many environmental problems that threaten us and the responsibility of ecologists to play their full part in addressing these problems. This fifth edition addresses this challenge, with several chapters devoted entirely to applied topics, and examples of how ecological principles have been applied to problems facing us highlighted throughout the remaining nineteen chapters. 
Nonetheless, the authors remain wedded to the belief that environmental action can only ever be as sound as the ecological principles on which it is based. Hence, while trying harder than ever to help improve preparedness for addressing the environmental problems of the years ahead, the book remains, in its essence, an exposition of the
of ecology. This new edition incorporates the results from more than a thousand recent studies into a fully up-to-date text. 
Written for students of ecology, researchers and practitioners, the fifth edition of
is anessential reference to all aspects of ecology and addresses environmental problems of the future.

Ecology — читать онлайн ознакомительный отрывок

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(5.27) картинка 226

where a is a constant. Similarly, we expect mean plant weight, P , to be related to D by:

(5.28) where b is also a constant Putting Equations 526 528together we obtain - фото 227

where b is also a constant. Putting Equations 5.26– 5.28together, we obtain:

(5.29) This is structurally equivalent to the 32 power relationship in Equation - фото 228

This is structurally equivalent to the −3/2 power relationship in Equation 5.23, with the intercept constant, c , given by b(L/a) 3/2.

It is apparent, therefore, why thinning lines might generally be expected to have slopes of approximately −3/2. Moreover, if the relationships in Equations 5.27and 5.28were roughly the same for all plant species, and if all plants supported roughly the same leaf area per unit area of ground ( L ), then the constant c would be approximately the same for all species. On the other hand, suppose that L is not quite the same for all species, or that the powers in Equations 5.27and 5.28are not exactly 2 or 3, or that the constants in these equations ( a and b ) either vary between species or are not actually constants at all. Thinning lines will then have slopes that depart from −3/2, and slopes and intercepts that vary from species to species. It is easy to see why, according to the areal argument, there is a broad similarity in the behaviour of different species, but also why, on closer examination, there are likely to be variations between species and no such thing as a single, ‘ideal’ thinning line.

complications of the areal argument

Furthermore, contrary to the simple areal argument, the yield–density relationship in a growing cohort need not depend only on the numbers that die and the way the survivors grow. We have seen (see Section 5.8) that competition is frequently highly asymmetric. If those that die in a cohort are predominantly the very smallest individuals, then density ( individuals per unit area) will decline more rapidly as the cohort grows than it would otherwise do. It seems possible, too, to use departures from the assumptions built into Equations 5.26– 5.29to explain at least some of the variations from a ‘general’ −3/2 rule. We see this in a study by Osawa and Allen (1993), who estimated a number of the parameters in these equations from data on the growth of individual plants from two species: mountain beech ( Nothofagus solandri ) and red pine ( Pinus densiflora ). They estimated, for instance, that the exponents in Equations 5.27and 5.28were not 2 and 3, but 2.08 and 2.19 for mountain beech, and 1.63 and 2.41 for red pine. These suggest thinning slopes of −1.05 in the first case and −1.48 in the second, which compare quite remarkably well with the slopes that they observed: −1.06 and −1.48 ( Figure 5.38). The similarities between the estimates and observations for the intercept constants were equally impressive. These results show, therefore, that thinning lines with slopes other than −3/2 can occur, but can be explicable in terms of the detailed biology of the species concerned. They also show that even when slopes of −3/2 do occur, they may do so, as with red pine, for the ‘wrong’ reason (−2.41/1.63 rather than −3/2).

Figure 538 The species boundary line for populations of red pine Pinus - фото 229

Figure 5.38 The species boundary line for populations of red pine, Pinus densiflora , from northern Japan (slope = −1.48).

Source : After Osawa & Allen (1993).

self‐thinning in sessile animals

Animals must also ‘self‐thin’, insofar as growing individuals within a cohort increasingly compete with one another and reduce their own density. And in the case of some sessile, aquatic animals, we can think of them, like plants, as being reliant on a resource falling from above (typically food particles in the water) and therefore needing to pack ‘volumes’ beneath an approximately constant area. It is striking, therefore, that in studies on rocky‐shore invertebrates, mussels have been found to follow a thinning line with a slope of −1.4, barnacles a line with a slope of −1.6 (Hughes & Griffiths, 1988), and gregarious tunicates a slope of −1.5 (Guiñez & Castilla, 2001). There is, however, nothing linking all animals quite like the shared need for light interception that links all plants.

5.9.5 A resource‐allocation basis for thinning boundaries

This need to include all types of organisms in considerations of self‐thinning is reflected in studies seeking alternative explanations for the underlying trend itself. Most notably, Enquist et al . (1998) made use of the much more general model of West et al . (1997) that we discussed in Chapter 3, which considered the most effective architectural designs of organisms. We saw there that the rate of resource use per individual, u , or more simply their metabolic rate, should be related to mean organism body mass, M , according to the equation:

(5.30) Ecology - изображение 230

where a is a constant and the value ¾ is the ‘allometric exponent’.

−4/3 or −3/2?

They then argued that we can expect organisms to have evolved to make full use of the resources available, and so if S is the rate of resource supply per unit area and N maxthe maximum density of organisms possible at this supply rate, then:

(5.31) Ecology - изображение 231

or, from Equation 5.30:

(5.32) Ecology - изображение 232

But if the organisms have arrived at an equilibrium with the rate of resource supply, then S should itself be constant. Hence:

(5.33) Ecology - изображение 233

where c is another constant. In short, the expected slope of a population boundary on this argument is −4/3 rather than −3/2. Similarly, the figure in biomass–density relationships ( equations 5.24and 5.25) would be −1/3 rather than −1/2.

Enquist and colleagues themselves considered the available data to be more supportive of their prediction of a slope of −4/3 than the more conventional −3/2, though this had not been the conclusion drawn from previous data surveys. Indeed, as we saw in Chapter 3, the idea of ¾ being a consistent or universal allometric exponent, and a slope of −4/3 therefore being expected, has itself been called increasingly into question (e.g. Glazier, 2005). Nonetheless, Begon et al . (1986) had found a mean value of −1.29 (close to a value of −4/3) for self‐thinning in experimental cohorts of grasshoppers, and Elliott (1993) a value of −1.35 for a population of sea trout, Salmo trutta , in the English Lake District. On the other hand, studies on house crickets, Acheta domesticus , have shown that the allometric exponent in in their case is not ¾ but 0.9 (Jonsson, 2017), and the estimated slope of their self‐thinning line −1.11 (the exact reciprocal of the allometric exponent; Figure 5.39a).

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