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Environmental Health - Public
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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
Fields
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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5.9 PUBLIC HEALTH <br /> concentration of each TAC with acute health effects is divided by the specific TAC's acute <br /> REL to obtain a health hazard quotient for health effects caused by relatively high, <br /> short-term exposure to air toxics. An additional conservative procedure in this health risk <br /> assessment is that the health hazard quotients for all TACs having potential acute impacts <br /> were summed regardless of target organ. This method leads to an upper bound assessment. <br /> RELs used in the hazard index calculations were those published in the CARB/OEHHA <br /> listings dated May 2008. <br /> 5.9.4.2 Construction Impacts <br /> Construction of LEC is expected to take approximately 24 months. No significant public <br /> health effects are expected during construction. Strict construction practices that incorporate <br /> safety and compliance with applicable LORS will be followed. In addition,mitigation <br /> measures to reduce air emissions from construction impacts will be implemented as <br /> described in Section 5.1. <br /> Temporary air emissions from construction are presented in detail in Appendix 5.1E, <br /> followed by a criteria pollutant air dispersion analysis that demonstrates ambient air quality <br /> standards will not be exceeded by construction of the project. The dominant emission with <br /> potential health risk is Diesel particulate matter (DPM) from combustion of Diesel fuel in <br /> construction equipment (e.g.,cranes, dozers, excavators, graders,front-end loaders, <br /> backhoes).DPM emissions from construction are summarized in Table 5.9-3. <br /> TABLE 5.9-3 <br /> Maximum Construction DPM Emissions <br /> Emitting Activity Pounds per Day Tons per Year <br /> Construction Equipment 4.5 0.4 <br /> The detailed HRA calculations in Appendix 5.1D demonstrate that the potential cancer risk <br /> of DPM emissions during project construction will exceed the significance threshold of 10 in <br /> one million,based on adjusting the 70-year lifetime risk for a period of 9 years in accordance <br /> with OEHHA (2003) guidance. The resulting maximum cancer risk would be approximately <br /> 24 in one million. The area in which the 10 in one million risk level barely extends beyond <br /> the construction and laydown/parking areas and does not include any residences or <br /> sensitive receptors (see Figure 5.9-3). <br /> Ambient air modeling for PM1o, CO,SO2,and NO2 was performed as described in <br /> Section 5.1.5.3 and Appendix 5.1D. Construction-related emissions are temporary and <br /> localized,resulting in no long-term significant impacts to the public. <br /> Small quantities of hazardous waste may be generated during the life of the project. <br /> Hazardous waste management plans will be in place so the potential for public exposure is <br /> minimal. Refer to Section 5.14,Waste Management,for more information. No acutely <br /> hazardous materials will be used or stored on-site during construction (see Section 5.5, <br /> Hazardous Materials Handling). To assure worker safety during construction, safe work <br /> practices will be followed (see Section 5.16,Worker Health and Safety). <br /> SACI371322I082340007(LEC_5.9_PUBLIC_HEALTH.DOC) 5.9-11 <br />
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