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Environmental Assessment

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AFFECTED ENVIRONMENT & ENVIRONMENTAL CONSEQUENCES CHAPTER 3<br />

Based on the dead wood analysis, there is habitat for this species across the planning area and landscape.<br />

There are no identified short-term direct or indirect effects on this species or its habitat under Alternative<br />

1. Uncharacteristic wildfire events and bark beetle epidemics are likely to reduce or eliminate habitat for<br />

this species in both the short and long-term. Long-term, the retention of dense stands with the resulting<br />

slow diameter growth may delay the development of larger snags that provide nesting habitat for this<br />

species.<br />

No trees 21 inches dbh or greater or any existing snags (except those for safety reasons) would be<br />

removed under either Alternative 2 or 3. Alternative 2 proposes to treat approximately 2,059 acres of<br />

ponderosa pine habitat including 35 percent of the acres in structural stage 6 and 33 percent in structural<br />

stage 7. The number of acres increases to approximately 2,560 acres with 44 percent of structural stage 6<br />

and 37 percent of structural stage 7. In lodgepole pine habitat, Alternative 2 would treat approximately<br />

709 acres or 13 percent of the acreage in structural stages 4-7; alternative 3 would treat approximately<br />

804 acres or 15 percent of structural stages 4-7.<br />

With the exception of vegetation and fuel reduction treatments proposed or implemented in adjacent<br />

planning areas, none of the current, on-going, or reasonable and foreseeable actions would have any<br />

cumulative or cumulatively significant effects on this species or its habitat. None of these actions would<br />

remove habitat.<br />

Management actions would not remove existing habitat, i.e. snags. Current and future treatments would<br />

utilize thinning from below and would be expected to result in the development of larger diameter trees<br />

(and ultimately snags) faster than no treatment alternatives. As a result, habitat would be developed and<br />

be more widespread across the landscape. Populations would be expected to remain stable.<br />

Alternative 1 would also result in the development of additional habitat although at a slower rate than the<br />

action alternatives assuming there is no large scale bark beetle epidemic and/or uncharacteristic wildfire<br />

event. It would create a gap in the landscape with different qualities, quantities, and distributions of<br />

habitat than would likely result in treated areas. The risk of loss of existing and potential habitat would<br />

remain high; uncharacteristic fire and/or bark beetle epidemics could result in a short-term flush and a<br />

long-term deficit in habitat.<br />

In the short-term, both alternatives would remove potential nest trees (16 to 21 inches dbh). Both<br />

alternatives would also reduce canopy closure levels below the average (39 percent) for this species. As<br />

noted in the previous discussion for the black-backed and white-headed woodpeckers, it is unlikely that<br />

future management activities would maintain the high canopy closure levels indicated for this species<br />

given the risk of bark beetle attack and subsequent loss of that component of the habitat. It is also<br />

unlikely that most of the sites in the planning area are not capable of sustaining those levels without<br />

accepting the high risk of bark beetle attack and/or uncharacteristic wildfire events.<br />

Long-term, both alternatives are more likely to result in developing better habitat more quickly than<br />

Alternative 1 due to the residual trees responding to the thinning. Both would also produce more and<br />

larger diameter trees more quickly.<br />

Hairy woodpeckers utilize both lodgepole pine and ponderosa pine habitats in a variety of seral stages.<br />

Moderate sized snags are required for nesting. There are significant amounts of hairy woodpecker habitat<br />

in the project area and adjacent lands presently. Snags are variable with localized concentrations.<br />

Because neither the alternatives nor any ongoing or reasonably foreseeable project proposes to cut snags,<br />

cumulative effects (i.e. additive removal of snags) will be rare, incidental, and not useful or relevant to<br />

making an informed decision between the alternatives. The Opine project will treat approximately 2059<br />

(35 percent of SS6 and 33 percent of SS7) acres of ponderosa pine habitat in stages 6 and 7 by Alternative<br />

3-150

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