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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 />

Existing Conditions<br />

The following table <strong>de</strong>scribes existing soil conditions and current soil impacts.<br />

Table 3.7-2 Existing soil conditions and current soil impacts.<br />

Harvest Units Sum of Soil<br />

<strong>Impact</strong>s by<br />

percent of<br />

activity area*<br />

Nature of <strong>Impact</strong>s<br />

1 2-4% Some past harvest, compaction<br />

2,3,4 2-4% Some compaction evi<strong>de</strong>nt in trails<br />

5 3-5% Compaction due to light past<br />

harvests<br />

* Percent of soil impacts on an aerial extent basis within an activity area. An activity area is <strong>de</strong>fined as: An area of land impacted<br />

by a management activity or activities. It can range from a few acres to an entire watershed <strong>de</strong>pending on the type of monitoring<br />

being conducted. It is commonly a timber sale cutting unit.<br />

During on-site visits, skid trail spacings were measured in the proposed harvest units. The skid<br />

trail spacing provi<strong>de</strong>s an initial estimate of potentially impacted area. Soil samples using a tile<br />

spa<strong>de</strong> were then observed in the field for compaction to <strong>de</strong>fine the percent of skid trails having<br />

compaction. Platy structure, <strong>de</strong>nse layers and wheel ruts indicate compaction. Estimates of soil<br />

impacts outsi<strong>de</strong> of skid trails are also estimated including landings, ero<strong>de</strong>d areas, severely burned<br />

soils and displacement.<br />

The Region 2 Supplement allows for a wi<strong>de</strong> range of soil monitoring tools as <strong>de</strong>scribed below:<br />

“2.42 - SOIL SAMPLING TECHNIQUES. Sampling techniques range from extensive visual<br />

observations to intensive sampling techniques using statistically sound methodologies. The<br />

intensity of sampling must be <strong>de</strong>termined on a case by case basis <strong>de</strong>pending on the values and<br />

risks at stake.”<br />

The sampling techniques conducted on these harvest units is well within the R2 Supplement<br />

requirements.<br />

All of the stands proposed for harvest are currently meeting soil quality standards. This means<br />

that, based on on-site investigations, soil impacts are estimated to be well below the 15 percent<br />

soil standard. Most stands have had only light logging in the past. Compaction is the primary soil<br />

impact.<br />

Direct, Indirect, and Cumulative Effects<br />

All standards and gui<strong>de</strong>lines from the Forest Plan would be implemented and are incorporated<br />

into action alternatives as <strong>de</strong>sign criteria. Design criteria are non-discretionary actions that must<br />

be implemented as part of the action alternatives. One of the key soils standards states the<br />

following:<br />

Forest Plan Standard (III-10, Soil Productivity Std #1): “Manage land treatments to limit the<br />

sum of severely burned and <strong>de</strong>trimentally compacted, ero<strong>de</strong>d, and displaced land to no more than<br />

Chapter 3 – Affected Environment & <strong>Environmental</strong> Consequences Page 3-31

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