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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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EHD - Public
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5.1 AIR QUALITY <br /> 5.1.1.3.9 Airborne Lead <br /> The majority of lead in the air results from the combustion of fuels that contain lead. Until <br /> 30 years ago,motor gasolines contained relatively large amounts of lead compounds used as <br /> octane-rating improvers,with the result that ambient lead levels were relatively high. <br /> Beginning with the 1975 model year,however,manufacturers began to equip new <br /> automobiles with exhaust catalysts,which are poisoned by the exhaust products of leaded <br /> gasoline. Thus,unleaded gasoline became the required fuel for an increasing fraction of new <br /> vehicles, and the phase out of leaded gasoline began. As a result, ambient lead levels <br /> decreased dramatically, and for several years California air basins,including the San Joaquin <br /> Valley Air Basin,have been in attainment of state and federal airborne lead standards for air <br /> quality planning purposes. Table 5.1-10 lists the state air quality standard for airborne lead <br /> and the levels recorded in the Stockton-Hazelton station between 1998 and 2003.Table 5.1-10 <br /> indicates that airborne lead levels have been well below the ambient air quality standard of <br /> 1.5 µg/m3 for the period 1998 through 2003. <br /> TABLE 5.1-10 <br /> Airborne Lead at Stockton-Hazelton, Stockton, 1998-2003(µg/m3) <br /> 1998 1999 2000 2001 2002 2003 <br /> Highest Daily Average 0.02 0.02 0.03 0.02 0.02 0.02 <br /> Number of Day Exceeding <br /> Federal Standard (1.5 Ng/m3) 0 0 0 0 0 0 <br /> Source: AIRData, EPA <br /> 5.1.2 Project Description <br /> 5.1.2.1 Current Facility <br /> The equipment at the existing NCPA STIG plant consists of one 49 MW GE LM-5000 natural <br /> gas-fired, steam-injected (STIG) combustion gas turbine and one 240 HP Cummins diesel fire <br /> pump engine. There is also a small cooling tower at the facility,which is exempt from <br /> permitting under the SJVAPCD rules because its circulation rate is less than 10,000 gallons <br /> per minute (Rule 2020,Section 6.2). The only change to be made to the existing facility is the <br /> relocation of the exempt cooling tower. <br /> 5.1.2.2 Proposed Facility <br /> The proposed combined-cycle unit will consist of a General Electric PG7241FA combustion <br /> turbine, a heat recovery steam generator with duct firing, and a 95 MW (nominal) <br /> condensing steam turbine,for a total nominal plant output of 255 MW. The CTG will use <br /> "Rapid Response" technology. The Rapid Response package,which includes a modified <br /> HRSG design and an auxiliary boiler,is designed to allow earlier startup of the steam turbine <br /> by decoupling the gas turbine from the HRSG,thereby reducing startup emissions. The <br /> project will also include a cooling tower. <br /> The combustion turbine, duct burners and auxiliary boiler will be fueled exclusively with <br /> natural gas. The combustion turbine will be equipped with an inlet air evaporative cooling <br /> system to maintain turbine output across the full range of ambient temperatures. Based on <br /> operation at an ambient temperature of 61.2°F,with evaporative cooling of the CTG inlet air <br /> to 55.8°F and without duct firing,the facility will have a heat rate of approximately <br /> 5.1-20 SAC/371322/082410013(LEC_5.1_AIR_QUALITY.DOC) <br />
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