On a finer scale than ecotypes, it
may also be possible to detect levels
of variation within populations. Such
variation is known as polymorphism.
Specifically, genetic polymorphism is ‘the occurrence together
in the same habitat of two or more discontinuous forms of a species
in such proportions that the rarest of them cannot merely be
maintained by recurrent mutation or immigration’ (Ford, 1940).
Not all such variation represents a match between organism and
environment. Indeed, some of it may represent a mismatch, if,
for example, conditions in a habitat change so that one form is
being replaced by another. Such polymorphisms are called transient.
As all communities are always changing, much polymorphism
that we observe in nature may be transient, representing
the extent to which the genetic response of populations to
environmental change will always be out of step with the
environment and unable to anticipate changing circumstances.
Many polymorphisms, however, are
actively maintained in a population by
natural selection, and there are a number
of ways in which this may occur.
1 Heterozygotes may be of superior fitness, but because of the
mechanics of Mendelian genetics they continually generate less
fit homozygotes within the population. Such ‘heterosis’ is
seen in human sickle-cell anaemia where malaria is prevalent.
The malaria parasite attacks red blood cells. The sickle-cell mutation
gives rise to red cells that are physiologically imperfect
and misshapen. However, sickle-cell heterozygotes are fittest
because they suffer only slightly from anemia and are little
affected by malaria; but they continually generate homozygotes
that are either dangerously anemic (two sickle-cell genes) or
susceptible to malaria (no sickle-cell genes). None the less, the
superior fitness of the heterozygote maintains both types of
gene in the population (that is, a polymorphism).
2 There may be gradients of selective forces favoring one form
(morph) at one end of the gradient, and another form at the
other. This can produce polymorphic populations at intermediate
positions in the gradient – this, too, is illustrated
below in the peppered moth study.
3 There may be frequency-dependent selection in which each of
the morphs of a species is fittest when it is rarest (Clarke &
Partridge, 1988). This is believed to be the case when rare color
forms of prey are fit because they go unrecognized and are
therefore ignored by their predators.
4 Selective forces may operate in different directions within different
patches in the population. A striking example of this is provided
by a reciprocal transplant study of white clover (Trifolium
repens) in a field in North Wales (UK). To determine whether
the characteristics of individuals matched local features of
their environment, Turkington and Harper (1979) removed
plants from marked positions in the field and multiplied them
into clones in the common environment of a greenhouse. They
then transplanted samples from each clone into the place in
the sward of vegetation from which it had originally been taken
(as a control), and also to the places from where all the
others had been taken (a transplant). The plants were allowed
to grow for a year before they were removed, dried and
weighed. The mean weight of clover plants transplanted back
into their home sites was 0.89 g but at away sites it was only
0.52 g, a statistically highly significant difference. This provides
strong, direct evidence that clover clones in the pasture had
evolved to become specialized such that they performed best
in their local environment. But all this was going on within a
single population, which was therefore polymorphic.
In fact, the distinction between
local ecotypes and polymorphic populations
is not always a clear one. This
is illustrated by another study in North
Wales, where there was a gradation in
habitats at the margin between maritime cliffs and grazed
pasture, and a common species, creeping bent grass (Agrostis
stolonifera), was present in many of the habitats.
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