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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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EHD - Public
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5.1 AIR QUALITY <br /> 5.1.5.9 Commissioning Impacts Analysis <br /> The commissioning period begins when the CTG and HRSG are prepared for first fire and <br /> ends upon successful completion of initial performance testing. There are several high- <br /> emissions scenarios possible during commissioning. The first is the period prior to SCR <br /> system and oxidation catalyst installation,when the gas turbine combustion system is being <br /> tuned. Under this scenario,NOX emissions would be high because the NO,,emissions control <br /> system would not be functioning and because the gas turbine would not be tuned for <br /> optimum performance. CO emissions would also be high because turbine performance <br /> would not be optimized and the CO emissions control system would not be functioning. The <br /> second high emissions scenario may occur when the gas turbine has been tuned but the SCR <br /> and oxidation catalyst installation is not complete.Since the control system installation <br /> would not be complete,NO,,and CO levels would again be high. Commissioning activities <br /> and expected emissions are shown in more detail in Table 5.0-7,Appendix 5.113. <br /> The existing NCPA Lodi generating unit will be in operation during the commissioning of <br /> the LEC. An assessment of the air quality impacts of this combined operation have been <br /> included in the cumulative impacts analysis,provided in Appendix 5.1G. <br /> Air quality impacts during the commissioning period were determined using the emission <br /> rates in Table 5.113-7. One-hour average NO2 impacts during commissioning were modeled <br /> using AERMOD_OLM and concurrent Stockton ozone data. Modeled impacts are shown in <br /> Table 5.1-30. <br /> TABLE 5.1-30 <br /> Modeled Maximum Impacts During Commissioning of the CTG/HRSG <br /> Maximum Total State Federal <br /> Facility Impact Background Impact Standard Standard <br /> Pollutant Averaging Time (pg/m3) (Ng/m3) (pg/m3) (pg/m3) (pg/m3) <br /> NO2 1-hour 36.4 163.6 200 338 — <br /> CO 1-hour 718.2 5,500 6,218 23,000 40,000 <br /> 8-hour 535.0 3,178 3,713 10,000 10,000 <br /> 5.1.6 Laws, Ordinances, Regulations, and Standards <br /> The EPA has responsibility for enforcing, on a national basis,the requirements of many of <br /> the country's environmental and hazardous waste laws. California is under the jurisdiction <br /> of EPA Region 9,which has its offices in San Francisco. Region 9 is responsible for the local <br /> administration of EPA programs for California,Arizona,Nevada,Hawaii,and certain Pacific <br /> trust territories. EPA's activities relative to the California air pollution control program focus <br /> principally on reviewing California's submittals for the State Implementation Plan (SIP). The <br /> SIP is required by the federal Clean Air Act to demonstrate how all areas of the state will <br /> meet the national ambient air quality standards within the federally specified deadlines <br /> (42 USC§7409, 7411). <br /> The CARB was created in 1968 by the Mulford-Carrell Air Resources Act,through the merger <br /> of two other state agencies. The CARB's primary responsibilities are to develop, adopt, <br /> implement,and enforce the state's motor vehicle pollution control program;to administer <br /> and coordinate the state's air pollution research program;to adopt and update as necessary <br /> 5.1-42 SAC/371322/082410013(LEC_5.1_AIR_QUALITY.DOC) <br />
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