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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 />

This section summarizes a more <strong>de</strong>tailed analysis contained in the wildlife Biological<br />

Assessment (BA) and Biological Evaluation (BE), which is part of this project’s<br />

administrative record.<br />

Past Actions that have affected the Existing Condition<br />

The existing condition in the <strong>Rio</strong> <strong>de</strong> <strong>los</strong> <strong>Pinos</strong> Analysis Area has been impacted by historic<br />

activities, including timber, grazing, and recreation (see sections 3.5, 3.14, and 3.16).<br />

Existing Condition<br />

The current composition of stands within the Analysis Area is primarily spruce/fir. The average<br />

age of the spruce/fir stands varies between 160 to 220 years. The stands may be characterized as<br />

<strong>de</strong>nse, mature to over-mature Engelmann spruce/subalpine fir timber stands, with typical basal<br />

areas between 126 and 205 square feet. Openings created in these stands by past timber harvest<br />

have regenerated to a <strong>de</strong>nse mix of spruce and fir saplings (Section 3.5).<br />

Cattle grazing continues to occur within portions of the analysis area, (primarily in natural parks,<br />

meadows, or openings created by past timber harvest). Within the analysis area, there are 241<br />

acres mapped as suitable rangeland (from the Forest Plan Suitability analysis) for cattle. Of<br />

these 241 acres, 173 acres are mapped as Transitory rangeland and 68 acres are mapped as<br />

Primary rangeland. Access to the project area for livestock is primarily along the existing road<br />

system (Section 3.14).<br />

Dispersed recreation continues to occur in the analysis area and inclu<strong>de</strong>s: driving for pleasure,<br />

sight-seeing, hiking, hunting, fishing, horseback riding, picnicking, firewood gathering, snow<br />

shoeing and cross-country skiing to a system of yurts, use of all-terrain-vehicles (ATVs) on<br />

roads, and snowmobiling (Section 3.16).<br />

Some of the roads in the Analysis Area have been c<strong>los</strong>ed with gates or dirt barriers. Many of<br />

these roads are re-vegetated and in some cases, have blen<strong>de</strong>d into the topography but in most<br />

cases, are still recognizable as travel ways.<br />

Wildlife species that occur or may occur within the <strong>Rio</strong> <strong>de</strong> <strong>los</strong> <strong>Pinos</strong> Analysis Area involve those<br />

species that are most commonly associated with the spruce-fir cover type. Riparian vegetation<br />

also occurs within or adjacent to the analysis area in association with stream and river channels<br />

and small ponds and wetlands. A representative sample of these species groups is as follows:<br />

Reptile and Amphibian Species: Reptile species are relatively scarce in the spruce-fir cover types<br />

of Colorado, with the western terrestrial garter snake being the only common species. This garter<br />

snake has semi-aquatic life history needs and could be expected to respond to habitat changes in<br />

a manner similar to amphibians. The tiger salaman<strong>de</strong>r is likely to be found within the <strong>Rio</strong> <strong>de</strong> <strong>los</strong><br />

<strong>Pinos</strong> analysis area.<br />

Avian Species: There are at least 17 species of birds that are primarily associated with spruce-fir<br />

forests in the Southern Rocky Mountains of Colorado (Beidleman 2000). An additional 11<br />

Chapter 3 – Affected Environment & <strong>Environmental</strong> Consequences Page 3-35

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