Environmental Assessment
Environmental Assessment
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 />
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