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ARCHIVED REPORTS LEC APPLICATION FOR CERTIFICATION
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2900 - Site Mitigation Program
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PR0516806
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ARCHIVED REPORTS LEC APPLICATION FOR CERTIFICATION
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Last modified
9/26/2019 8:41:30 AM
Creation date
9/25/2019 4:52:39 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
LEC APPLICATION FOR CERTIFICATION
RECORD_ID
PR0516806
PE
2965
FACILITY_ID
FA0012817
FACILITY_NAME
WHITE SLOUGH WATER POLLUTION CONTRO
STREET_NUMBER
12751
Direction
N
STREET_NAME
THORNTON
STREET_TYPE
RD
City
LODI
Zip
95241
APN
05513016
CURRENT_STATUS
01
SITE_LOCATION
12751 N THORNTON RD
P_LOCATION
02
P_DISTRICT
004
QC Status
Approved
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APPENDIX 5.1G <br /> Cumulative Impacts Analysis for the LEC <br /> Cumulative air quality impacts from the LEC and other reasonably foreseeable projects <br /> will be both regional and localized in nature. Regional air quality impacts are possible for <br /> pollutants such as ozone,which is formed through a photochemical process that can take <br /> hours to occur. Carbon monoxide,NOx,and SOx impacts are generally localized in the <br /> area in which they are emitted. PM10 can create a local air quality problem in the vicinity <br /> of its emission source,but can also be a regional issue when it is formed in the <br /> atmosphere from VOC,SOx, and NOx. <br /> The cumulative impacts analysis considers the potential for both regional and localized <br /> impacts due to emissions from proposed operation of LEC. Regional impacts are <br /> evaluated by comparing maximum daily and annual emissions from LEC with emissions <br /> of ozone and PM10 precursors in both San Joaquin County and the entire San Joaquin <br /> Valley. Localized impacts are evaluated by looking at other local sources of pollutants <br /> that are not included in the background air quality data to determine whether these <br /> sources in combination with LEC would be expected to cause significant cumulative air <br /> quality impacts. <br /> Regional Impacts <br /> Regional impacts are evaluated by assessing LEC's contribution to regional emissions. <br /> Although the relative importance of VOC and NOx emissions in ozone formation differs <br /> from region to region and from day to day,state law requires reductions in emissions of <br /> both precursors to reduce overall ozone levels. The change in the sum of emissions of <br /> these pollutants,equally weighted,provides a rough estimate of the impact of LEC on <br /> regional ozone levels.12 Similarly, a comparison of the emissions of PM10 precursor <br /> emissions from LEC with regional PM10 precursor emissions provides an estimate of the <br /> impact of LEC on regional PM10 levels. <br /> Under SJVAPCD regulations,LEC will be required to provide offsets for increases in <br /> NOx,VOC,SO2,and PM10 emissions from the project above certain regulatory thresholds. <br /> Regulatory offset requirements are calculated based on quarterly emissions,but the <br /> regional inventories are expressed in tons per day of emissions. Comparisons are shown <br /> on both a daily and annual basis. <br /> Tables 5.1G-1 and 5.1G-2 summarize these comparisons. LEC emissions are compared <br /> with regional emissions in 2012,as that is the year the project is expected to begin <br /> operation.San Joaquin County and SJVAPCD emissions projections for 2012 were <br /> estimated by averaging the projected emissions inventories for 2010 and 2015 obtained <br /> from the Air Resources Board's web-based emission inventory projection software, <br /> available at www.arb.ca.gov/applemsinvlemssumcat2007.php. <br /> 12 LEC is proposing to use direct, and not interpollutant,offsets for ozone precursors,so all NOx emissions <br /> from the project will be offset using NOx ERCs while all VOC emissions will be offset using VOC ERCs. <br />
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