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4.7 Geology,Soils,and Seismicity <br /> r <br /> materials to construct the slopes would be laid down, watered, and compacted in 6-inch lifts with <br /> heavy equipment. The reclamation slopes would be sculpted as one continuous feature extending <br /> from the bottom of the pit up approximately 100 vertical feet at a 26 degree slope.The slopes <br /> would be hydroseeded to protect the exposed slopes after construction and to promote maximum <br /> vegetation growth. According to its Reclamation Plan (November 2003), "the applicant would <br /> prepare a Revegetation Plan based upon mitigations agreed upon during the permitting process to <br /> _ address soil amendments,erosion control, seed mix, planting, irrigation, and test plots."The <br /> revegetation practices developed by the applicant must be consistent with performance standards <br /> for regrading, backfilling,revegetation, and drainage, as set forth in California Code of <br /> Division 2, Chapter, Subchapter 1, Sections 3704 to 3706. Although it is possible that soil <br /> erosion of the 2:1(H:V) slopes could occur immediately following hydroseeding,the potential for <br /> that erosion to cause damage is minimal because while the compacted surface would promote <br /> runoff, the compacted clay materials would hinder the removal of soil particles and the eventual <br /> formation of rills and gullies. <br /> ., The proposed 100-vertical-foot,2:1 (H:V)reclamation slopes constructed without terracing could <br /> he subject to erosion hazards and soil collapse more readily than a 100-foot slope with a 50-foot <br /> terraced midslope because of the greater length of uninterrupted slope. The potential for surface <br /> water to erode soil is partly dependant on the velocity and erosive energy of surface runoff.This <br /> is greater for longer lengths of slopes not interrupted by a midslope terrace. However, the <br /> compacted clay material and vegetation proposed for the reclamation slopes are relatively <br /> resistant to erosion; the revegetated slopes would reduce the velocity of the surface water flows <br /> that could initiate rill erosion, gully erosion, and debris flows. <br /> The applicant has not proposed terracing for 100-foot-high, 2:1 (H:V)final reclamation slopes, <br /> and as discussed above,this is not consistent with Chapter 9-1415-3(k)(1) (Terracing)of the San <br /> Joaquin County Development Title,Ordinance for Quarry Excavations (see Regulatory <br /> W Background section). It is unknown at this time whether the applicant could apply to San Joaquin <br /> County for a variance to construct the proposed slopes. If the applicant does apply for a variance <br /> ` to the slope ordinance, it would likely be required to demonstrate that the slope would remain <br /> stable to avoid erosion in the proposed configuration. Information reviewed for this EIR indicates <br /> that the applicant has based its proposal for non-terraced slopes on the success of 2:1 (H:V) <br /> slopes at other RMC Pacific Vernalis Quarry mining sites, including Huck Quarry in San Joaquin <br /> County. Implementing the erosion control plan as proposed by the applicant in its Reclamation <br /> Plan, which includes revegetation,drainage,and monitoring practices consistent with the <br /> provisions required by the California Code of Regulations(CCR Title 14) and the Counties of <br /> San Joaquin and Stanislaus, would reduce the potential for long-term,damaging erosion and <br /> would ensure that impacts related to post-mining erosion would remain less than significant. <br /> r <br /> Mitigation: No mitigation is required. <br /> RMC Pacific Vernalis Quarry Mining and Reclamation Project 4.7-21 ESA 1203015 <br /> Draft Environmental Impact Report May 2006 <br /> r <br />