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2900 - Site Mitigation Program
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PR0528038
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
9/26/2019 9:54:09 AM
Creation date
9/26/2019 8:57:07 AM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0528038
PE
2950
FACILITY_ID
FA0018998
FACILITY_NAME
NCPA LODI ENERGY CENTER
STREET_NUMBER
12751
Direction
N
STREET_NAME
THORNTON
STREET_TYPE
RD
City
LODI
Zip
95242
APN
05513016
CURRENT_STATUS
01
SITE_LOCATION
12751 N THORNTON RD
P_LOCATION
02
P_DISTRICT
004
QC Status
Approved
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5.11:SOILS <br /> During construction of the project, dust erosion control measures would be implemented to <br /> minimize the wind-blown loss of soil from the site.Water of a quality equal to or better than <br /> existing surface runoff would be sprayed on the soil in construction areas to control dust <br /> prior to completion of permanent control measures. <br /> Sediment barriers slow runoff and trap sediment. Sediment barriers include straw bales, <br /> sand bags, straw wattles, and silt fences. They are generally placed below disturbed areas, at <br /> the base of exposed slopes, and along streets and property lines below the disturbed area. <br /> Sediment barriers are often placed around sensitive areas to prevent contamination by <br /> sediment-laden water near areas such as wetlands,creeks, or storm drains. <br /> The site will be constructed on relatively level ground;therefore,it is not considered <br /> necessary to place barriers around the entire site perimeter. However,some barriers would <br /> be placed in locations (such as the southern boundary) where offsite drainage could occur to <br /> prevent sediment from impacting the canal or from leaving the other areas of the site. If <br /> used, sediment barriers would be properly installed (staked and keyed),then removed or <br /> used as mulch after construction. Runoff detention basins, drainage diversions,and other <br /> large-scale sediment traps are not considered necessary due to the small site size,level <br /> topography, and surrounding paved areas. Any soil stockpiles, including sediment barriers <br /> around the base of the stockpiles,would be stabilized and covered. <br /> Mitigation measures, such as watering exposed surfaces, are used to reduce PM10 emissions <br /> during construction activities. The PM10 reduction efficiencies are taken from the SCAQMD <br /> CEQA Handbook (1993) and were used to estimate the effectiveness of the mitigation <br /> measures. Table 5.11-4 summarizes the mitigation measures and PMlo reduction efficiencies. <br /> Additional fugitive dust mitigation measures are discussed in Section 5.1,Air Quality. <br /> TABLE 5.11-4 <br /> Mitigation Measures for Fugitive Dust Emissions <br /> PM10 Emission Reduction <br /> Mitigation Measure Efficiency(%) <br /> Water active sites at least twice daily 34-68 <br /> Enclose, cover,water twice daily,or apply non-toxic soil binders,according to 30-74 <br /> manufacturer's specifications,to exposed piles(i.e., gravel, sand,dirt)with <br /> 5 percent or greater silt content <br /> Source: SCAQMD CEQA Handbook, Table 11-4 (1993) <br /> 5.11.4.2 Permanent Erosion Control Measures <br /> Permanent erosion control measures on the site will include graveling,paving, and drainage <br /> systems, as well as revegetating to stabilize land surfaces. <br /> 5.11.5 Laws, Ordinances, Regulations, and Standards <br /> Federal, state,county, and local LORS applicable to soils are discussed below and <br /> summarized in Table 5.11-5. <br /> SACI371322I082330009(LEC_5.11_SOILS.DOC) 5.11-13 <br />
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