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SU0004149
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SU0004149
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Entry Properties
Last modified
10/27/2020 1:00:10 PM
Creation date
9/6/2019 10:44:51 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
RECORD_ID
SU0004149
FACILITY_NAME
QX-96-0001
STREET_NUMBER
36869
Direction
S
STREET_NAME
KOSTER
STREET_TYPE
RD
City
TRACY
ENTERED_DATE
5/12/2004 12:00:00 AM
SITE_LOCATION
36869 S KOSTER RD
RECEIVED_DATE
9/22/1996 12:00:00 AM
QC Status
Approved
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FilePath
\MIGRATIONS\K\KOSTER\36869\QX-96-01_EIR 96-3\SU0004149\PUB REC REL APPL.PDF
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EHD - Public
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i <br /> AIR QUALITY STANDARDS <br /> Ambient air quality is described in terms of compliance with state and national standards. <br /> Ambient air quality standards are the levels of air pollutant concentration considered safe <br /> to protect the public health and welfare. They are designed to protect people most <br /> sensitive to respiratory distress, such as asthmatics, the elderly, very young children, 'i <br /> people already weakened by other disease or illness, and persons engaged in strenuous <br /> 'I <br /> work or exercise. National Ambient Air Quality Standards (NAAQS) were established by <br /> the EPA in 1971 for six air pollution constituents. States have the option to add other <br /> pollutants, to require more stringent compliance, or to include different exposure periods. �� <br /> California Ambient Air Quality Standards (CAAQS) and NAAQS are listed in Table 4.5-1. !I <br /> Air Quality Monitoring <br /> Figure 4.5-1 depicts the air quality monitoring station locations in the Basin. Ambient air <br /> quality data for the project area was obtained from monitoring stations operated by the <br /> SJVUAPCD, which are closest to the project site. Table 4.5-2 presents a summary of the <br /> air quality data obtained from the Stockton (Hazelton) monitoring station, which offers I <br /> gaseous and articulate monitoring; and the Trac monitoring station which offers gaseous <br /> P g Y 9 9 j� <br /> pollutant monitoring. As indicated, some exceedances of state standards for 03 and PM,o <br /> occurred between the years 1991 and 1995. Based on data obtained from the Stockton it <br /> (Hazelton) monitoring station, the state 03 standard was exceeded an average of eight <br /> days per year; the federal 03 standard was exceeded twice; and the state and federal CO <br /> 8-hour standards were each exceeded once during this period. In addition, the state PM,o r <br /> standard was exceeded in approximately 24% of the samples taken at the Stockton ,9 <br /> (Hazelton) monitoring station over the five-year period. The federal standard was not <br /> t .I <br /> exceeded during this time. Data obtained from the Tracy monitoring station is considered <br /> "...valid but incomplete in that an insufficient number of data points were collected to meet <br /> I^{ EPA and/or CARB criteria for representativeness" (CARB, 1995). <br /> Meteorological Influences on Air Quality <br /> i <br /> Regional flow-patterns-have an,effect on air quality patterns by directing pollutants <br /> downwind of sources. Localized meteorological conditions, such as light winds and it <br /> shallow vertical mixing; and topographical features, such as surrounding mountain ranges, <br /> create areas of high pollutant concentrations by hindering dispersal. An inversion layer is <br /> produced when a layer of warm air traps cooler air close to the ground. Such temperature <br /> F' inversions hamper dispersion by creating a ceiling that traps air pollutants near the ground <br /> (SJVUAPCD, 1992). <br /> Draft Environmental Impact Report 4-63 ER-96-3 !i <br />
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