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Environmental Assessment

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AFFECTED ENVIRONMENT & ENVIRONMENTAL CONSEQUENCES CHAPTER 3<br />

Winter Range<br />

Habitat Unit or<br />

LRMP allocation<br />

(forested acres)<br />

Thermal Cover Quality Categories 31 (acreages)<br />

Optimal Acceptable Marginal<br />

3-10<br />

Nonthermal<br />

Sub-Area Totals: acres 32<br />

/percentage of forested<br />

acreage<br />

Pine Mountain- gross<br />

area (5077 ac.)<br />

421 523 1746 10754 944 / 19%<br />

Potholes (5580 ac.) 5 105 1151 8428 110 / 2%<br />

TePee Draw (7734 ac.) 19 334 1318 9249 353 /5 %<br />

Totals:<br />

26550 forested project<br />

acres 25768 acres<br />

WRHUs<br />

21814acres winter range<br />

485 1932 8231 43979<br />

2,417 / 9% forested project<br />

acres<br />

2,169 ac. / 8% WRHUs<br />

1,338 ac./ 6% winter range<br />

The analysis shows that approximately nine (9) percent of the forested acres within the planning area<br />

rates as thermal cover. The general forest land allocation (MA-8) has the highest percentage, 32<br />

percent, but there is no thermal cover requirement for that allocation. It is not utilized by wintering<br />

mule deer because it is also outside of biological winter range.<br />

The acreage within WRHUs is predominately the deer winter range allocation (MA-7). Thermal cover<br />

averages approximately eight (8) percent, but is highly variable between WRHUs, ranging from a low<br />

of two (2) percent in the Tepee Draw WRHU (dominated by black-bark ponderosa pine stands) to a<br />

high of 20 percent in the Lavacicle WRHU (multi-storied lodgepole pine).<br />

When only winter range acres (MA-7) are considered, the percentage of thermal cover declines to<br />

approximately six (6) percent of the forested acres across the project.<br />

Existing Condition Shrub Habitat - Shrubs, primarily bitterbrush, Purshia tridentata (PUTR),<br />

provide critical mule deer winter forage. With approximately 89 percent of the planning area in<br />

designated winter range, the quality, quantity, and distribution of bitterbrush is an important<br />

consideration. They also provide nesting and foraging habitat for shrub-associated species such as the<br />

yellow pine chipmunk and golden-mantle ground squirrel and neotropical migrant birds such as<br />

Brewer’s sparrow, sagebrush sparrow, and green-tailed towhee. Many of these species, particularly the<br />

seed-caching rodents like the the yellow pine chipmunk, serve an important ecological role in the<br />

regeneration of shrub species.<br />

The planning area contains six (6) ponderosa pine plant associations, nine (9) lodgepole pine<br />

associations, and six (6) xeric shrub associations. Three plant associations: ponderosa pine /<br />

bitterbrush-sagebrush (Artemisia spp.) / fescue (22 percent); big sagebrush-bitterbrush / bunchgrass (22<br />

percent); and ponderosa pine / bitterbrush / fescue (19 percent) dominate over 60 percent of the<br />

planning area acreage. In total, approximately 33 percent of the area is in open, xeric shrublands and 67<br />

percent is in forested habitat types.<br />

Table 3-6 summarizes the current conditions of shrub habitats within the planning area.

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