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SU0015801
EnvironmentalHealth
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PATTERSON PASS
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2600 - Land Use Program
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PA-2200137
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SU0015801
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Last modified
3/27/2024 1:55:05 PM
Creation date
8/31/2023 1:18:11 PM
Metadata
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Template:
EHD - Public
ProgramCode
2600 - Land Use Program
RECORD_ID
SU0015801
PE
2675
FACILITY_NAME
PA-2200137
STREET_NUMBER
20042
Direction
W
STREET_NAME
PATTERSON PASS
STREET_TYPE
RD
City
TRACY
Zip
95377-
APN
20910019, 99B-7885-002, 99B-7590-1-3
ENTERED_DATE
8/29/2023 12:00:00 AM
SITE_LOCATION
20042 W PATTERSON PASS RD
RECEIVED_DATE
11/14/2023 12:00:00 AM
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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Air Quality and Greenhouse Gas Technical Report Griffith Energy Storage Project <br /> Document: Health Risk Assessments for Land Use Projects(CAPCOA 2009)for determining when and <br /> how to conduct risk assessments. Both documents include recommendations for buffer distances for <br /> siting sensitive receptors near various types of common sources. The project type and buffer distance are <br /> as follows: <br /> 00 Freeways and high traffic roads—Sensitive receptors should be sited at least 500 feet from <br /> freeways or urban roads with 100,000 vehicles per day or rural roads with 50,000 vehicles per <br /> day. <br /> 00 Distribution centers—Sensitive receptors should be sited at least 1,000 feet from distribution <br /> centers accommodating more than 100 trucks per day or more than 40 trucks per day with <br /> operating transport refrigeration units. <br /> 00 Railyards—Sensitive receptors should be sited at least 1,000 feet from a major service and <br /> maintenance rail yard. Sensitive receptors sited within one mile of a major service and <br /> maintenance railyard should consider mitigation and/or restrictions. <br /> 00 Ports—Avoid siting of new sensitive land uses immediately downwind of ports in the most heavily <br /> impacted zones. <br /> 00 Refineries—Avoid siting new sensitive land uses immediately downwind of petroleum refineries. <br /> oo Chrome Platers—Avoid siting new sensitive land uses within 1,000 feet of a chrome plater. <br /> 00 Dry Cleaners using Perch loroethylene—Avoid siting new sensitive land uses within 300 feet of <br /> any dry-cleaning operation. For operations with two or more machines, provide 500 feet. For <br /> operations with three or more machines, consult with the local air district. Do not site new <br /> sensitive land uses in the same building with perch loroethylene dry cleaning operations. <br /> oo A Gasoline Dispensing Facility—Avoid siting new sensitive land uses within 300 feet of a large <br /> gas station (defined as a facility with a throughput of 3.6 million gallons per year or greater). A <br /> 50-foot separation is recommended for typical gas dispensing facilities. <br /> The Project is an industrial project but does not fit into any of the project categories above. The reference <br /> distances from the CARB Air Quality and Land Use Handbook are not being used to analyze how existing <br /> conditions might impact future users or residents, but can be used as guidance to demonstrate that <br /> nearby residences are at an appropriate buffer distance to the project. As previously noted, the closest <br /> residence on land not owned by the Project's current property owner is located approximately 1,000 feet <br /> from the Project boundary. Tracy is located approximately 7 miles from the site. <br /> SJVAPCD also provides significance thresholds for TACs: <br /> Exposes sensitive receptors to substantial pollutant concentrations, including those resulting in: <br /> oo A cancer risk greater than or equal to 20 in a million, and/or <br /> oc A Hazard Index (non-cancerous)greater than or equal to 1. <br /> A HRA was not conducted for the Project. A qualitative discussion of Diesel Particulate Matter(DPM) risk <br /> is provided in Section 2.5.4. <br /> 2.5 IMPACT ANALYSIS <br /> The Project is expected to have emissions less than 100 lbs/day for all pollutants during on-site <br /> construction. Therefore, Project construction emissions will not cause or contribute to a violation of an <br /> ambient air quality standard by exceeding any CAAQS or NAAQS. Since operational activities would be <br /> minimal and are also well below the modeling threshold, ambient air quality modeling was not performed <br /> for operational emissions. <br /> OTETRA TECH 23 July 2023 <br />
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