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1 Samuel M. Scheiner and Michael R. Willig, eds. 1. A General ...

1 Samuel M. Scheiner and Michael R. Willig, eds. 1. A General ...

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trend were based on the ratio between body volume <strong>and</strong> surface area. The square-versus-cube<br />

relationship makes the area of a solid proportional to the two-third power of its mass, so<br />

metabolic rate should also be proportional to mass. But a thorough study by Kleiber (1932)<br />

found that, for mammals <strong>and</strong> birds, metabolic rate was mass to the power of 0.73 (approximately<br />

three-quarters) <strong>and</strong> not 0.67 (two-thirds as postulated based on surface to volume ratios). Other<br />

research supported this new three-quarter-power law, although consensus is still elusive (Grant<br />

2007). It was, however, much harder to find a theoretical reason why metabolic rate should be<br />

proportional to mass raised to power of 3/4. Furthermore, it was not clear why quarter-power<br />

scaling laws should be so prevalent in biology. Nevertheless, the generalization <strong>and</strong> the<br />

difficulties with the putative causes of it led West et al. (1997) to develop a new explanation of<br />

why metabolic rate should equal the three-quarter power of body mass.<br />

Indeed, the generalization that larger organisms have lower metabolism is such a noisy<br />

one that some question its relevance. What is important is that an early strong empirical<br />

generalization inspired development of sophisticated theoretical explanations. A considerable<br />

value of these explanations to ecology arises not from whether they are correct or accepted but<br />

rather whether they have been formulated <strong>and</strong> tested. The very process of doing so identifies<br />

further problems, questions, <strong>and</strong> directs new empirical <strong>and</strong> theoretical pursuits; which advances<br />

underst<strong>and</strong>ing.<br />

Another theory formulated in response to an empirical generalization is the neutral theory<br />

of species diversity (Hubbell 1997). Most communities, irrespective of the scale of data<br />

collection, harshness of the environment, or productivity, show a general qualitative regularity of<br />

species abundances: few species are abundant while many more are rare, with species of<br />

intermediate abundance filling the range in between according to one of several abundance<br />

partitioning models. Numerous theoretical efforts have been made in the past to account for this<br />

general pattern (e.g., May 1975, Ugl<strong>and</strong> <strong>and</strong> Gray 1982, Tokeshi 1993). The most familiar of<br />

those is the broken stick model of MacArthur’s (1957). None have gained full acceptance.<br />

Hubbell’s proposition is a culmination of these efforts <strong>and</strong> a stimulus for further tests.<br />

Admittedly, sometimes a good generalization does not lead to the development of a theory (but<br />

see Fox et al., Chapter 14, on gradients regarding a possible solution). Holdridge’s schematic,<br />

illustrating vegetation types as a function of evapotranspiration <strong>and</strong> annual precipitation (Figure<br />

2.3), represents a useful generalization that does not need or inspire a complex theory. In case of<br />

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