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Final Environmental Impact Statement

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Vestal <strong>Final</strong> <strong>Environmental</strong> <strong>Impact</strong> <strong>Statement</strong> Chapter 3<br />

Meadow Jumping<br />

Mouse<br />

(Zapus hudsonius<br />

campestris)<br />

Summary of Effects to SOLC<br />

decreased potential in the long term. Would reduce MPB and wildfire risk.<br />

Cumulative Effects<br />

Activities such as vegetation management, fuels management, livestock grazing,<br />

recreational activities and other management activities have and are expected to<br />

continue within the project area. These activities would likely occur on private<br />

lands as well. Private lands would likely continue to be developed, some of which<br />

may include roads. All may affect flying squirrels through direct mortality,<br />

modification of behavior, habitat alteration, spread of exotics, or disturbance.<br />

Additionally, private lands would continue to be thinned to reduce the threat of<br />

MPB. Northern flying squirrels have relatively small ranges, generally less than 42<br />

acres (Cotton & Parker 2000), and are non-migratory. Privately-owned lands within<br />

and adjacent to the project boundary may also provide suitable northern flying<br />

squirrel habitat, but resource management and conservation by private citizens and<br />

companies depend on a number of factors (e.g., desired goals, market prices,<br />

development potential). Private lands managed for timber harvest may tend toward<br />

fewer acres in the late-successional stage forest and fewer snags. Potential northern<br />

flying squirrel habitat is assumed to occur on private lands across the project area;<br />

however, the extent and persistence of such habitat is uncertain.<br />

Summary<br />

Both alternatives affect habitat for the flying squirrel. However, the proposed action<br />

treats stands to mostly SS4A, and more acreage of SS 4B, 4C, and 5 would remain<br />

within the project area, providing little more habitat for this species. More future<br />

replacement snags would also be expected to remain on the landscape.<br />

The proposed action would meet Forest Plan standards and guidelines. Therefore,<br />

the alternatives would contribute toward meeting Forest Objective 221. This<br />

species is likely to persist on the Forest.<br />

Alternative 1<br />

No Action<br />

No treatments in riparian areas<br />

would occur. Livestock grazing<br />

would continue and riparian grasses<br />

may continue to receive high<br />

seasonal use. Expected MPB<br />

activity would increase hardwoods<br />

and meadows by killing more pine.<br />

This may increase quality habitat<br />

for this mouse species.<br />

Direct and Indirect Effects<br />

Alternative 2<br />

Proposed Action<br />

Possible direct effects from proposed<br />

activities.<br />

Treatments would enhance meadow and<br />

riparian hardwood habitat.<br />

Cumulative Effects<br />

Activities such as vegetation management, fire suppression, livestock grazing,<br />

recreational activities and natural events such as drought and flooding have caused<br />

impacts to riparian areas within the project area. Fire suppression has resulted in an<br />

increase of pine trees which may lead to a change in water tables. Other<br />

management activities have and will continue in and adjacent to the project area.<br />

These activities would likely occur on private lands as well. Private lands would<br />

likely continue to be developed, some of which may include roads. All may affect<br />

jumping mice through direct mortality, modification of behavior, habitat alteration,<br />

spread of exotics, or disturbance.<br />

Private lands occur frequently within riparian areas. These private lands provide<br />

suitable habitat, but conditions may have been altered by private land management<br />

activities such as livestock grazing or draining to convert to drier site conditions for<br />

subsequent haying.<br />

93

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