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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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5.1 AIR QUALITY <br /> • Protection of Class I areas <br /> • Growth,visibility, soils,and vegetation impacts <br /> Although the existing power plant is not a major stationary source,the proposed project <br /> itself will result in emissions exceeding the applicable PSD thresholds for NO2 and C017 <br /> emitted from this source category18 listed in the federal PSD regulations (40 CFR 52.21). <br /> Therefore, the proposed project is subject to PSD review. As the SJVAPCD does not have <br /> delegation for the PSD program,a separate PSD application is being filed with the EPA. <br /> Air Quality Monitoring <br /> At its discretion,EPA Region 9 may require pre-construction and/or post-construction <br /> ambient air quality monitoring for PSD sources if representative monitoring data are not <br /> already available. Pre-construction monitoring data must be gathered over a one-year period <br /> to characterize local ambient air quality. Post-construction air quality monitoring data must <br /> be collected as deemed necessary by EPA Region 9 to characterize the impacts of proposed <br /> project emissions on ambient air quality. <br /> Best Available Control Technology <br /> BACT must be applied to any new or modified major source to minimize the emissions <br /> increase of those pollutants exceeding the PSD emission thresholds. EPA defines BACT as an <br /> emissions limitation based on the maximum degree of reduction for each subject pollutant, <br /> considering energy,environmental,and economic impacts,that is achievable through the <br /> application of available methods, systems, and techniques. BACT must be as stringent as any <br /> emission limit required by an applicable NSPS or NESHAP. BACT is defined below in the <br /> discussion of the SJVAPCD NSR regulatory requirements. <br /> Air Quality Impact Analysis <br /> An air quality dispersion analysis must be conducted to evaluate impacts of significant <br /> emission increases from new or modified facilities on ambient air quality. PSD source <br /> emissions must not cause an exceedance of any ambient air quality standard,and the <br /> increase in ambient air concentrations must not exceed the allowable increments shown in <br /> Table 5.1-31. <br /> TABLE 5.1-31 <br /> PSD Class II Increments <br /> Pollutant Averaging Period Allowable Increment(µg/m3) <br /> NO2 Annual 25a <br /> PM10 Annual 17a <br /> 24-Hour 30b <br /> SO2 Annual 20a <br /> 24-Hour 91b <br /> 3-Hour 512b <br /> 17 While EPA made a"determination of attainment'of the federal PM10 standard for the San Joaquin Valley Air Basin on <br /> October 30,2006,the EPA has not yet"redesignated"the basin as attainment for PM10(see 73 FR 22307;April 25,2008). <br /> Therefore,PSD requirements are not applicable for PM10. <br /> 18 Fossil fuel-fired steam-electric plant with heat input greater than 250 MMBtu/hour. <br /> SAC/371322/082410013(LEC_5.1_AIR_QUALITY.DOC) 5.145 <br />
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