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ENVIRONMENTAL CONSEQUENCES in rocky mountain coniferous ...

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forests are cavity nesters. They are especially sensitive to timber harvest<strong>in</strong>g<br />

practices because of their need for nest<strong>in</strong>g and roost<strong>in</strong>g cavities with<strong>in</strong> snags or<br />

live trees with heartrot. This group of birds is largely <strong>in</strong>sectivorous. Thus<br />

harvest<strong>in</strong>g and residue utilization practices that affect <strong>in</strong>sect populations also<br />

<strong>in</strong>fluence cavi ty-nest<strong>in</strong>g bird populations. The birds affect <strong>in</strong>sect numbers through<br />

predation and may ma<strong>in</strong>ta<strong>in</strong> endemic population levels of some forest <strong>in</strong>sects, or at<br />

1 east 1 engthen <strong>in</strong>terval s between epidemics (Beebe 1974). But consideration of cavity<br />

nesters, or any other 1 ife form, should not be conf<strong>in</strong>ed to possible economic benefits<br />

of the speci.es or group (Ehrenfeld 1974). Ecological , scientific, and esthetic values<br />

also are essential factors, though not easily quantified. The fact that cavity nest-<br />

ers are a natural part of forest ecosystems is by itself sufficient reason for forest<br />

managers to give them careful consideration. Perpetuation of cavity nesters with<strong>in</strong><br />

a forest subjected to harvest<strong>in</strong>g is possible only with careful plann<strong>in</strong>g based on<br />

know1 edge of the environmental consequences of the proposed manipulation.<br />

Conner and Crawford (1 974) studied woodpecker forag<strong>in</strong>g <strong>in</strong> Appalachian cl earcuts.<br />

Conner et a1 . (1975) evaluated the <strong>in</strong>fluence of cutt<strong>in</strong>g on woodpecker nest<strong>in</strong>g habitat<br />

<strong>in</strong> Virg<strong>in</strong>ia. Other studies have dealt with the impact of cutt<strong>in</strong>g on both open and<br />

cavi ty-nest<strong>in</strong>g birds: Ha ar (1 960) <strong>in</strong> Cal ifornia; Franzreb (1978) <strong>in</strong> Arizona;<br />

Titter<strong>in</strong>gton et a1. (19793 <strong>in</strong> Ma<strong>in</strong>e; Kessler (1979) <strong>in</strong> Alaska.<br />

The study described <strong>in</strong> this report was designed to provide some of the basic<br />

<strong>in</strong>formation needed by managers concerned with the welfare of cavity nesters <strong>in</strong><br />

western larch/Douglas-fir1 forests. Study objectives were: 1) to evaluate the <strong>in</strong>-<br />

fluence of alternate timber harvest<strong>in</strong>g and residue utilization practices on the nest-<br />

<strong>in</strong>g and feed<strong>in</strong>g activities of cavity-nest<strong>in</strong>g birds; 2) to quantify variables descrip-<br />

tive of the timber, character of dead material, the area, and of harvest<strong>in</strong>g prescrip-<br />

tion and residue utilization that significantly <strong>in</strong>fluence cont<strong>in</strong>ued use by cavity<br />

nesters; 3) to provide recommendations for modify<strong>in</strong>g harvest<strong>in</strong>g and utilization prac-<br />

tices to m<strong>in</strong>imize adverse impacts on these species.<br />

In this study students and I have concentrated on "primary" cavity nesters, the<br />

woodpeckers (fig. I), all of which are capable of excavat<strong>in</strong>g their own nest<strong>in</strong>g cavi-<br />

ties with<strong>in</strong> trees. Most secondary cavity-nesters (e.g., bluebirds, small owls<br />

(fig. 2), some swallows and ducks) must rely on the woodpeckers or on natural decay<br />

processes for production of nest and roost cavities.<br />

'scientific names are listed <strong>in</strong> the Appendix.

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