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ENVIRONMENTAL CONSEQUENCES in rocky mountain coniferous ...

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changes <strong>in</strong> the animal comnunities. To discover the primary<br />

causes of the changes <strong>in</strong> the population densities of the dif-<br />

ferent species or of the successional trends of the whole<br />

community, accurate <strong>in</strong>formation would have to be acquired about<br />

the habits and responses of each component species to each<br />

factor at the different stages of their life cycles, together<br />

with detailed long-term microclimatic records not only <strong>in</strong> the<br />

habitat <strong>in</strong> general, but a1 so separately <strong>in</strong> the particular<br />

microhabitat of each species.<br />

Direct Effects of Treatment<br />

Consider<strong>in</strong>g harvest<strong>in</strong>g and residue management procedures, prescribed burn<strong>in</strong>g is<br />

probably the only treatment tbat directly affects forest floor macrofauna. Some<br />

studies have concluded that the heat of the burn<strong>in</strong>g-over is very destructive to a1 1<br />

grou s, and that the bulk of some populations may be destroyed (Huhta and others<br />

1957y . Other <strong>in</strong>vestigators report that with the exception of mesofaunal species and<br />

spiders, population reductions do not seem to be directly caused by heat of fire<br />

(Ahlgren 1974)-. The direct effect of prescribed burn<strong>in</strong>g is not only <strong>in</strong> kill<strong>in</strong>g the<br />

organisms, but <strong>in</strong> the partial or complete destruction of the 1 i t ter and humus, as<br />

we1 1 as the above-ground portions of low-grow<strong>in</strong>g surface vegetation. In such cases,<br />

only scanty material may be left on the surface of the m<strong>in</strong>eral soil (Huhta and<br />

others 19671.<br />

Indirect Effects of Treatment<br />

In add? tion to direct effects, harvest<strong>in</strong>g and residue manipulation practices<br />

have two general <strong>in</strong>direct effects: a change <strong>in</strong> the forest environment and micro-<br />

climate and changes <strong>in</strong> successional development of vegetation.<br />

Changes <strong>in</strong> the microclimate will depend on the condition of the stand prior to<br />

treatment. The removal of all or part of a dense <strong>coniferous</strong> stand where the forest<br />

floor is heavily shaded will have more strik<strong>in</strong>g effects than the manipulation of a<br />

more open-grown stand where more light reaches the forest floor and where understory<br />

vegetation may be more abundant,<br />

Partial or complete removal of trees and residues alters the forest environment,<br />

hence <strong>in</strong>directly <strong>in</strong>fluenc<strong>in</strong>g the forest soil fauna, by chang<strong>in</strong>g temperature, moisture,<br />

llght <strong>in</strong>tensity, w<strong>in</strong>d, and humidity regimens. Of the harvest<strong>in</strong>g methods, clearcutt<strong>in</strong>g<br />

no doubt has the greatest impact. However, all treatments disrupt both diurnal and<br />

seasonal fluctuations <strong>in</strong> these physical factors.<br />

Some animal groups, unable to tolerate the new microcl imate, are at a disadvan-<br />

tage and disappear. Other groups not only survive the environmental change but may<br />

even <strong>in</strong>crease as a result of treatment. Some <strong>in</strong>vestigators have reported that the<br />

factor decid<strong>in</strong>g the succession of fauna <strong>in</strong> clearcut areas is whether the fell<strong>in</strong>g<br />

residues are left on the site or removed (Huhta and others 1969). Some animals,<br />

dependent on litter for food have been known to disappear <strong>in</strong> a burned-over area after<br />

the unburned 1 itter had decomposed.

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