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DOE/EIS-0332; McNary-John Day Transmission Line Project Draft ...

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BPA <strong>McNary</strong>-<strong>John</strong> <strong>Day</strong> <strong>Transmission</strong> <strong>Project</strong><br />

<strong>Draft</strong> <strong>EIS</strong><br />

February 2002<br />

Vegetation<br />

Fire damage in lithosol vegetation communities could result in expansion of nonvegetated,<br />

bare rock areas. The shallow soils over bedrock in these communities are<br />

stabilized by vegetation. Loss of the vegetation could lead to the loss of soils in some<br />

areas.<br />

Fire in the cottonweed plantation would result in losses of trees. Replacement of mature,<br />

harvestable trees would take 7 to 10 years. Fire loss of trees in hedgerows and isolated<br />

patches elsewhere on the alignment would take longer to replace. Tree species identified<br />

on the right-of-way would take approximately 25 years to regenerate to mature<br />

individuals.<br />

Impact acreage from access road operation would be highest in the grazed shrub-steppe<br />

cover type. Ten acres of this cover type would be converted to roadbed. Many of the<br />

existing two-track roadbeds in this cover type, and throughout the route, are dominated<br />

by low cheatgrass. As such they have a close affinity to the surrounding degraded shrubsteppe,<br />

even while converted to access roads. Impact acreage within higher quality<br />

vegetation communities (such as shrub-dominated shrub-steppe) are lower, but would<br />

result in the creation of new edge communities and a permanent avenue of invasion for<br />

nonnative and/or disturbance-favored species.<br />

Tower Operation and Maintenance<br />

The proposed line would require the placement of 360 steel lattice towers. Each tower<br />

would take up approximately 0.05 acre. Of the towers to be placed, approximately 144<br />

would be placed in grazed shrub-steppe vegetative cover, 118 would be placed in<br />

agricultural cover, 75 would be in grasslands, 26 would be in scabland/lithosol<br />

communities, and 11 would be in shrub-dominated shrub-steppe cover. No towers would<br />

be placed in riparian communities. Acreages permanently impacted by tower placement<br />

are presented in Table 3-12.<br />

Tower operation is regarded as a permanent impact to vegetation communities, because it<br />

requires the removal and displacement of existing vegetation and results in the<br />

compaction of soils. However, the grassland and grazed shrub-steppe communities<br />

would likely return to and recover at least some of the area beneath the towers within 1 to<br />

5 years of construction. Shrub-dominated shrub-steppe and scabland/lithosol<br />

communities may also return to portions of the areas under towers, but over a longer time<br />

period, and with more intensive management. Based on conditions observed at existing<br />

towers, it is likely that a combination of native and nonnative species would establish<br />

around the towers. Nonnatives commonly observed around towers include cheatgrass,<br />

medusa-head wild rye, and bulbous bluegrass. Native species seen around existing<br />

towers include bluebunch wheatgrass, big sagebrush, and gray rabbitbrush. Agricultural<br />

cover types would not return to the areas under new towers.<br />

3-47

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