Environmental Assessment
Environmental Assessment
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.