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Weather and storms
The exposed position of many CFT biotopes places them at risk from
severe weather conditions. However, two factors will mitigate against damage. One is the
depth of most biotopes, usually 20 m or greater, and the rapid rate at which wave induced
exposure attenuates with depth is described in section II.D. The other is the generally
robust nature of exposed CFT species, which are adapted to withstanding severe water
movement. In coral reef biotopes there are records of storm damage to substantial depths -
to 27 m in Hawaii (Walsh, 1983), to 30 m in Jamaica (Huston, 1985), and to over 35 m in
French Polynesia (Harmelin-Vivien & Laboute, 1986). However there are no confirmed
reports of similar effects in British CFT biotopes, though the systematic recording to
detect such damage is probably lacking. In the Gulf of Maine rock wall communities were
monitored by Sebens (1985a) through a series of violent storms, but no damage was
observed. In fact a modest amount of storm damage would not necessarily have adverse
effects. By creating patches of free space it can limit dominance by a few species and
maintain high levels of biodiversity - the intermediate disturbance
hypothesis.
There are two biotopes more likely to suffer storm damage. Scour-prone
biotopes on unstable substrata are clearly at risk, from scouring action, and from
covering by mobile sediments. However these generally have an impoverished community of
scour-tolerant species, so storm effects may be difficult to detect. CFT communities in
relatively shallow waters, normally on vertical or steeply sloping surfaces, would also be
sensitive to storm damage. These shallow biotopes are relatively scarce, and their
accessibility gives them added value and requirement for management consideration. Only
intensive monitoring programmes will determine the extent to which storm damage actually
occurs.
Indirect effects of weather can arise from the effects of heavy rains
and floods, which can be mediated by climatic cycles such as the N.A.O. These can affect
rate of nutrient transport to the sea, water stratification, and the initiation of
plankton blooms. These effects are more likely to impact shallow and semi-enclosed
biotopes.
Next Section
References
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