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Environmental Assessment

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AFFECTED ENVIRONMENT & ENVIRONMENTAL CONSEQUENCES CHAPTER 3<br />

potential impact on shrubs. However, the target species for control with chemicals are not shrubs and<br />

overspray (e.g. windy conditions) would be avoided. The relatively small area to be treated is minor in<br />

comparison to overall amount and distribution of shrub habitats.<br />

Past and planned timber harvest activities may adversely impact shrubs, but generally this impact does<br />

not exceed 25 percent of an area. Planned and future timber harvest will utilize existing skid trails,<br />

landings and roads which will mitigate these effects. PDCs have been incorporated into all planned<br />

treatments to ensure retention of mature/late shrub age/structure classes within treatment units.<br />

Fuels treatments will have the greatest effect on shrub age/structure classes. Proposed treatments for<br />

both action alternatives are targeting the mature/late structure class, however there are units with<br />

inclusions of the mid stage. There is a PDC is in place to mitigate these effects on the mid class. There<br />

is a limited history in the area on past fuels treatment and their effects have been built into the current<br />

condition shrub classes as noted earlier.<br />

In conclusion, the cumulative effect on shrub habitat is not adverse to objectives for big game species<br />

forage availability, nor for associated shrub dependent wildlife. Over 50 percent of the winter range<br />

area will be retained in the mature/late age/structure class. Large blocks of xeric shrublands will not<br />

have any treatments and will continue to provide high value habitats for a variety of wildlife species.<br />

No shrub dependent species will be at risk to federal listing due to cumulative effects on them.<br />

Part 2 of Key Issue #1<br />

(b) Effects of Open Road and Motorized Trails on Habitat Effectiveness<br />

Habitat effectiveness is affected by open road and motorized trail density. The Opine planning area has<br />

a current average open road density of approximately 2.97 miles per square mile and a combined<br />

average road and motorized trail density of approximately 4.96 miles per square mile. The Fox Butte<br />

Cooperative Travel Management Area program (Green Dot system) reduces open road/motorized trail<br />

densities to approximately 2.92 miles per square mile during the deer hunting season. Target road<br />

densities range from 1.0 to 2.5 miles per square mile within designated deer habitat (M7-22, LRMP<br />

page 4-115) and 2.5 miles or less in other land allocations (WL-54 LRMP page 4-58).<br />

Currently 25,976 acres of the planning area are closed to OHV use except on designated roads and trails<br />

(East Fort Rock OHV area). The remaining 28,647 acres are currently open to unrestricted motorized<br />

use including OHV use. Open roads and unrestricted off-road motorized vehicle use fragment wildlife<br />

habitat and disturb wildlife, especially during winter months when animals must use extra energy and<br />

resources to stay alive.<br />

Measurement Standard:<br />

Miles of system roads closed and decommissioned.<br />

Road and motorized trail density.<br />

Acres closed to unrestricted cross country motorized use.<br />

Habitat effectiveness is primarily influenced by open road and motorized trail density. Big game<br />

species generally avoid the areas adjacent to open roads and trails due to the disturbance from the<br />

vehicles and people. This effect reduces the amount of or use of available habitat in these areas. A<br />

number of variables influence the effects of roads and motorized trails. These include but are not<br />

limited to:<br />

the amount and type of traffic;<br />

the road and/or trail location;<br />

vegetation density and pattern; and<br />

topography.<br />

3-32

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