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ENVIRONMENTAL CONSEQUENCES in rocky mountain coniferous ...

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I<br />

I<br />

Habitat Manipulation<br />

Small mammals have evolved with the communities that they <strong>in</strong>habit (Bendell 1974).<br />

Mutual compatibility is a result of this evolution. Disruptions such as fire or<br />

logg<strong>in</strong>g may cause serious imbalances (Tevis 1956b): some animal populations may be<br />

elim<strong>in</strong>ated, new species may <strong>in</strong>vade, some species will greatly <strong>in</strong>crease <strong>in</strong> numbers.<br />

Fires or logg<strong>in</strong>g may <strong>in</strong>itiate an early successional stage as a disclimax. This<br />

may be perpetuated by recurrent fire, unusual ly high rodent populations, heavy graz<strong>in</strong>g<br />

by large mammals, or edaphic factors. Special consideration, <strong>in</strong>clud<strong>in</strong>g a1 ternative<br />

harvest<strong>in</strong>g methods, should be given to situations with this potential.<br />

To reduce impacts on forest regeneration, small mammal control is best imple-<br />

mented by not creat<strong>in</strong>g suitable habitat for potentially destructive specie^.^<br />

Consideration should be given to the k<strong>in</strong>d of habitat created by different treatments<br />

and the proximity of logg<strong>in</strong>g to potentially coloniz<strong>in</strong>g populations. For example,<br />

pocket gophers <strong>in</strong>vade and multiply <strong>in</strong> clearcuts where they damage and destroy tree<br />

seedl<strong>in</strong>gs. Retention of 500-foot wide buffer strips <strong>in</strong> lodgepole p<strong>in</strong>e forests has<br />

been suggested to a1 leviate this situation. Another a1 ternative for discourag<strong>in</strong>g<br />

pocket gopher populations, is partial cutt<strong>in</strong>g to ma<strong>in</strong>ta<strong>in</strong> partial shade and m<strong>in</strong>imal<br />

soil disturbance (Barnes 1974).<br />

Golden-mantl ed ground squirrel s are considered a threat to reforestation because<br />

of their seed-eat<strong>in</strong>g habits. Historically, <strong>in</strong> northwestern California, these<br />

squirrels occurred only <strong>in</strong> open granite outcropp<strong>in</strong>gs and avoided the virg<strong>in</strong> Douglasfir<br />

(~seudotsu~a -baxifoZia) and white fir (~bies concolor) forests. After the<br />

<strong>in</strong>itiation of harvest programs, golden-mantled ground squirrels spread from these<br />

isolated areas through virg<strong>in</strong> forest <strong>in</strong>to clearcuts 2-1/2 miles distant (Tevis 1956a).<br />

In areas where a1 1 vegetation has been removed by clearcutt<strong>in</strong>g and burn<strong>in</strong>g, as<br />

much as 100 percent of on-site conifer seeds have been consumed by wildlife<br />

(Tevis 1956~). Halvorson (In Press), Tevis (1956c), and Sullivan (1979) have sug-<br />

gested that leav<strong>in</strong>g some patches of unburned vegetation would provide alternate food<br />

sources and might reduce seed depredation. Unburned patches allow more species of<br />

small mammals to survive the fire, but there is also a wider variety of food rema<strong>in</strong><strong>in</strong>g<br />

to buffer the effect of seed consumption.<br />

The effectiveness of aerial seed<strong>in</strong>g <strong>in</strong> northern Montana was improved by delay<strong>in</strong>g<br />

seed<strong>in</strong>g until snow was on the ground. This made the seed unavailable to rodents<br />

until spr<strong>in</strong>g when small mammal populations are at a seasonal low. Seed was also<br />

unavailable to birds because it penetrated <strong>in</strong>to the snow. Germ<strong>in</strong>ation occurred <strong>in</strong> the<br />

spr<strong>in</strong>g after snow me1 t, thereby reduc<strong>in</strong>g the time the seed was exposed to<br />

depredation.<br />

If wildlife habitat is a major consideration <strong>in</strong> forest management, priority<br />

should be given to the creation of a vegetative mosaic of species composition and<br />

vegetative structure. Benefits of a vegetative mosaic <strong>in</strong>clude:<br />

a) Variety of food and<br />

b) Edge effects.<br />

2Personal Communication; W i<br />

Office, Missoula, Mont.<br />

9 Personal Communication: G.<br />

cover.<br />

11 iam Beaufai t, USDA Forest Service, Regiona<br />

Wilson.

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