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ENVIRONMENTAL CONSEQUENCES in rocky mountain coniferous ...

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Spiders and fire.--Several studies of the effects of fire on spiders have been<br />

made <strong>in</strong> this country; however, the most exhaustive research on spider-fire <strong>in</strong>terac-<br />

tions has been done <strong>in</strong> F<strong>in</strong>land.<br />

In the northern Rockies where a wildfire had been allowed to burn, Clayton<br />

(1975) found spiders to be more numerous <strong>in</strong> areas that had been burned than <strong>in</strong><br />

control areas, With<strong>in</strong> the burned areas, spiders were def<strong>in</strong>itely more numerous and<br />

more species were represented <strong>in</strong> a riparian woodland than on a south slope ponderosa<br />

p<strong>in</strong>e savanna. El sewhere <strong>in</strong> these proceed<strong>in</strong>gs, Fell <strong>in</strong> (1 98Ob) reports the results<br />

of a recent study of the effect of prescribed burn<strong>in</strong>g and harvest<strong>in</strong>g practices on<br />

spiders and other forest floor macrofauna <strong>in</strong> western Montana,<br />

Reichert and Reeder (1972) studied the immediate and long-term effect of<br />

burn<strong>in</strong>g on spiders <strong>in</strong> Wiscons<strong>in</strong> prairies, They found that species active on the<br />

surface at the time of burn<strong>in</strong>g were elim<strong>in</strong>ated, while those occupy<strong>in</strong>g subsurface<br />

burrows, or sacs under rocks or cl umps of dense vegetation escaped thermal damage.<br />

The greatest decrease <strong>in</strong> numbers was noticed two weeks after the burn, followed by<br />

a slow <strong>in</strong>crease. Even after 45 days, however, the numbers <strong>in</strong> the burn were not<br />

equal to those <strong>in</strong> the controls.<br />

Reichert and Reeder (1972) recognize that some spider species may be <strong>in</strong>directly<br />

affected by a burn through changes <strong>in</strong> the plant cgver and that "seasonal activity<br />

patterns 1 argely determ<strong>in</strong>e the different response of spider populations to the<br />

immediate effects of burn<strong>in</strong>g. " They concl uded that the abundance and species<br />

composition of spiders are both relatively stable, and that species <strong>in</strong>habit<strong>in</strong>g the<br />

prairie have adapted to the effects of periodic burn<strong>in</strong>g.<br />

In other studies, Pearse (1943) considered sptders, along with roaches and<br />

ants, to be well adapted for existence <strong>in</strong> a burned area; but Rice (1932), Buff<strong>in</strong>gton<br />

(1967), and Heyward and Tissot (1 936) thought spiders to be one of the groups least<br />

well adapted to burn<strong>in</strong>g. Algren (1974) cites several authors <strong>in</strong> report<strong>in</strong>g that<br />

spiders, primari ly surface dwellers, are drastic81 ly reduced by fire <strong>in</strong> most areas,<br />

with population decreases of from 9 to 31 percent. In one study, Hurst (1970)<br />

reported an <strong>in</strong>crease, primarily ground and wolf spiders, fol low<strong>in</strong>g fire.<br />

Huhta (1965, 1971 ) has <strong>in</strong>tensively studied ecology of spiders <strong>in</strong> the 1 itter and soil of F<strong>in</strong>nish forests, mostly <strong>in</strong> relation to silvicultural practices and<br />

prescribed burn<strong>in</strong>g. He found that after clearcutt<strong>in</strong>g, the abundance of ty ical<br />

species decreased, and species foreign to the orig<strong>in</strong>al fauna spread <strong>in</strong>to t ll e cutover<br />

areas; though the species were varied, the total numbers of <strong>in</strong>dividuals were about<br />

60 percent less than <strong>in</strong> the uncut area (Huhta and others 1967). Follow<strong>in</strong>g burn<strong>in</strong>g,<br />

which almost totally destroyed most of the origtnal populations (Huhta and others<br />

1967), the number of <strong>in</strong>dividuals rema<strong>in</strong>ed cont<strong>in</strong>uously low and the composition of<br />

the fauna was unstable; most species were markedly less frequent after burn<strong>in</strong>g and<br />

occurred only sporadically <strong>in</strong> the burned soil (Huhta, 19651.. Between years 7 and<br />

13, follow<strong>in</strong>g cutt<strong>in</strong>g and burn<strong>in</strong>g, the composition of the spider comnunity reverted<br />

towards the orig<strong>in</strong>al forest situation. In a more recent study, Huhta (19.76) confirmed<br />

his earl ier observations that the density of spiders decreased considerably<br />

after clearcutt<strong>in</strong>g, but <strong>in</strong> two of his clearcut areas, he was not able to show signs<br />

of spider recovery.<br />

El sewhere <strong>in</strong> Europe, Brabetz (1 978) studied the effects of control 1 ed burn<strong>in</strong>g<br />

i.n some uncultivated grasslands. In March and April of 1975 and 1976, two parcels<br />

of land (20 x 56 meters) were burned, and two parcels set aside as a control. In<br />

the spr<strong>in</strong>g and summer after the first burn<strong>in</strong>g, significantly more spiders were<br />

trapped <strong>in</strong> the burned area; however, after the second burn<strong>in</strong>g, spiders were more<br />

numerous <strong>in</strong> unburned areas.

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