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Draft EIS/EIR for the San Luis Reservoir SRA Resource ...

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5. Environmental Analysis<br />

density in <strong>the</strong> sou<strong>the</strong>rn part of <strong>San</strong> <strong>Luis</strong> <strong>Reservoir</strong> (from 50–110 acres per<br />

boat with <strong>the</strong> o<strong>the</strong>r alternatives to 20–50 acres per boat with Alternative 4)<br />

and <strong>the</strong> eastern part of O’Neill Forebay (from 20–50 acres per boat with<br />

<strong>the</strong> o<strong>the</strong>r alternatives to 10–20 acres per boat with Alternative 4). 9 These<br />

changes in boat density would be partly offset by <strong>the</strong> three-year phaseout<br />

of noncon<strong>for</strong>mant two-stroke engines; however, short-term, minor adverse<br />

effects could remain.<br />

Dust Emissions Caused by Motorized Vehicles, Construction, or Recreation<br />

Dust and particulate matter in <strong>the</strong> Plan Area are potentially generated from three<br />

sources: automobile traffic and OHV use on dirt roads and unpaved areas;<br />

nonmotorized recreational trail use, including hiking, horseback riding, and<br />

mountain biking; and grading disturbance from facilities construction. The dust<br />

generated by motor vehicles—including OHVs—driving on dirt roads and<br />

unpaved areas would result in localized minor adverse air quality impacts. O<strong>the</strong>r<br />

recreational trail use such as hiking and horseback riding is not likely to result in<br />

air quality impacts because is not usually fast or intensive enough to create<br />

substantial dust clouds. O<strong>the</strong>r effects of trail erosion are discussed in Section<br />

5.4.1.2 (under Trail and Road Use, Maintenance, and Construction). Site<br />

maintenance and facilities construction that includes ground-disturbing activities<br />

could raise dust and cause minor adverse impacts to air quality.<br />

These effects would vary by alternative as follows:<br />

• Alternative 1, No Action/No Project, would not expand or construct<br />

facilities, roads, or trails, but use of unpaved roads and trails, along with<br />

standard maintenance activities such as trail grading, would continue.<br />

These activities could have minor, short-term adverse effects to air quality,<br />

but to a lesser degree than <strong>the</strong> action alternatives.<br />

• Alternative 2 proposes some additional features and facilities that could<br />

accommodate or support additional visitors and increase motorized vehicle<br />

travel in unpaved areas (see “Emissions from Motorized Vehicles and<br />

Vessels,” above). These changes could result in minor adverse effects to<br />

air quality that are greater than Alternative 1 but less than Alternatives 3<br />

and 4. Implementation of a trails management plan that incorporates<br />

BMPs to reduce dust could have a beneficial impact on dust emissions that<br />

would not be realized under Alternative 1. With implementation of<br />

measures such as those described in Section 5.4.2.4, any residual impacts<br />

would be minor.<br />

• Alternative 3 would allow <strong>for</strong> a greater number of features and facilities<br />

that could accommodate or support additional visitors and increase<br />

motorized vehicle travel in unpaved areas (see “Emissions from Motorized<br />

Vehicles and Vessels,” above), compared with Alternative 2. This<br />

alternative would also allow <strong>for</strong> new trails linking Basalt Use Area with<br />

9 Acres per boat <strong>for</strong> each WROS zone are described in Sections 4.3.1 through 4.3.3.<br />

<strong>San</strong> <strong>Luis</strong> <strong>Reservoir</strong> <strong>SRA</strong> 5-21<br />

<strong>Draft</strong> RMP/GP and <strong>Draft</strong> <strong>EIS</strong>/<strong>EIR</strong>

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