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Final Environmental Impact Statement Rio de los Pinos Vegetation ...

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<strong>Final</strong> <strong>Environmental</strong> <strong>Impact</strong> <strong>Statement</strong> <strong>Rio</strong> <strong>de</strong> <strong>los</strong> <strong>Pinos</strong> <strong>Vegetation</strong> Management Project<br />

would continue. Units that currently have large beetle outbreaks would continue to experience<br />

extensive tree mortality, most likely until the mature spruce component is almost entirely <strong>los</strong>t.<br />

Loss of live basal area due to spruce beetles has already occurred to varying <strong>de</strong>grees within the<br />

analysis watersheds, with some units experencing over 50% mortality. The <strong>los</strong>s of live basal<br />

area could lead to increases in annual water yield and late season stream flows, as well as<br />

changes in peak stream flows. See Section 3.6 Watershed and Aquatic Resources in the EIS for<br />

<strong>de</strong>tailed discussion regarding beetle epi<strong>de</strong>mics and potential effects to watershed hydrology.<br />

The potential effects to stream habitat by the <strong>los</strong>s of live basal area could be mitigated by<br />

increased growth in un<strong>de</strong>rstory vegetation and well established riparian vegetation; as well as<br />

provi<strong>de</strong> a source for woody <strong>de</strong>bris and large woody structure which is important for many<br />

aquatic species including trout and macroinvertebrates. On the other hand, high stand-level<br />

mortality rates can lead to increased runoff and higher flows which can increase streambank<br />

instablity and rates of soil erosion. Increased sediment loading in the streams could lead to <strong>los</strong>s<br />

of spawning and overwintering pool habitat which could be <strong>de</strong>trimental to trout and aquatic<br />

insects which are important as a food source.<br />

The No Action alternative could potentially affect the trout population due to the extensive tree<br />

mortality rates within the analysis area and the possible corresponding increase in erosion and<br />

stream sediment loads.<br />

Alternative 2 – Full Salvage Harvest<br />

In this alternative, approximately 13.1 MMBF would be harvested from 878 acres by salvage<br />

logging <strong>de</strong>ad and dying Engelmann spruce. This would be accomplished with ground-based<br />

(tractor) logging methods. No green, uninfected spruce trees would be harvested and no green or<br />

<strong>de</strong>ad subalpine fir would be harvested. Exceptions to this are those trees that must be removed<br />

from skid trails, landings, or for safety reasons, and scenic patch cuts.<br />

Following removal of the <strong>de</strong>ad or dying spruce, the Forest Service would plant Engelmann<br />

spruce seedlings on those areas where post-sale reforestation surveys indicate that stocking is<br />

below the minimum standard of 150 trees per acre.<br />

This alternative would cause more surface disturbance than Alternative 1 or Alternative 3 due to<br />

the increased size in harvest area and harvest volume; and corresponding increase in ground<br />

disturbance associated with skid trails, roads, and heavy equipment operation. Currently, most<br />

streams and riparian areas within the project area are in good to robust conditions and any fish<br />

habitat concerns within the analysis area tend to be site specific and not an overall threat to the<br />

fish populations throughout the <strong>Rio</strong> <strong>de</strong> Los <strong>Pinos</strong> drainage. All surface disturbances would be<br />

a<strong>de</strong>quately buffered to prevent direct impacts to the water influence zone and riparian areas.<br />

New surface disturbances from skid trails and landings would be limited to acceptable levels<br />

established in the Forest Plan.<br />

Road work is inclu<strong>de</strong>d in this action alternative and some surface disturbances would occur<br />

during pre-haul road maintenance, road reconstruction, road c<strong>los</strong>ure and rehabilitation, and<br />

during construction of a short temporary road. The short-term impacts during these activities<br />

Chapter 3 – Affected Environment & <strong>Environmental</strong> Consequences Page 3-64

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