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Draft Environmental Impact Report - California Off Highway Vehicle ...

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3.5 Biological Resources<br />

The annual grassland and vernal pool habitat in the excavated basin of the SVRA is unlikely to<br />

support special‐status plant species because of the degraded nature of this area. The remnant<br />

natural vernal pool grassland on the terrace along Larkin Road provides potential habitat for<br />

special‐status vernal pool plants (i.e., Ahart’s dwarf rush, Ahart’s paronychia, Butte County golden<br />

clover, Butte County meadowfoam, Greene’s tuctoria, and slender Orcutt grass). It is possible that<br />

seeds of special‐status vernal pool plants from nearby source populations could drift onto the<br />

project site naturally (by wind or wildlife deposition) during the life of the General Plan, and these<br />

seeds could colonize vernal pools at Clay Pit SVRA. However, because of the continual disturbance<br />

by OHVs, it is unlikely that these species would establish self‐sustaining populations. Suitable<br />

habitat for Sanford’s arrowhead (CNPS List 1B.2) is present in the cattail vegetation community in<br />

wetlands and drainages at the SVRA. However, this species has not been observed during special‐<br />

status plant surveys conducted at Clay Pit SVRA, and the closest known occurrence of Sanford’s<br />

arrowhead is approximately 2 miles southwest of the SVRA (CNDDB 2011).<br />

Implementation of Plants Goal 1 and associated guidelines in the General Plan would ensure that<br />

future development and improvements within Clay Pit SVRA would not result in significant<br />

adverse impacts on special‐status plants. In particular, these measures stipulate that special‐<br />

status plant surveys would be conducted in areas proposed for facility development prior to<br />

construction. If any special‐status plant species were found, they would be mapped and avoided to<br />

the extent feasible. If avoidance were not possible, mitigation measures would be developed in<br />

coordination with DFG and/or USFWS, as appropriate, for any direct or indirect impacts that could<br />

occur as a result of actions envisioned in the General Plan. Mitigation measures could include<br />

preserving or enhancing populations on‐site, transplanting plants, and/or restoring or creating<br />

suitable habitat off‐site in sufficient quantities to achieve no net loss of occupied habitat or<br />

individuals.<br />

The potential for loss or disturbance of special‐status plants would be less than significant<br />

because (1) no known special‐status plants are on the project site; (2) it is unlikely that special‐<br />

status plants would establish self‐sustaining populations on the project site; and, (3) the General<br />

Plan includes guidelines that would protect special‐status plant species if they were found in areas<br />

that would be disturbed during site development envisioned in the General Plan.<br />

Mitigation Measures: No mitigation is required.<br />

IMPACT<br />

3.5-2<br />

Potential Loss of or Substantial Disturbance to a Sensitive Vegetation Community<br />

The vernal pools on the project site, both along the terrace and in the basin, are classified as vernal<br />

pools, which are designated by DFG as a “sensitive vegetation community,” as described in Section<br />

2.3.2, “Biotic Resources,” of the General Plan. Other undisturbed, nearly pristine northern hardpan<br />

vernal pool habitat exists near Clay Pit SVRA and in the region. Although this type of vernal pool<br />

Clay Pit State Vehicular Recreation Area<br />

<strong>Draft</strong> EIR 3.5-9 February2012

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