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SU0004098
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2600 - Land Use Program
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SU0004098
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Entry Properties
Last modified
5/7/2020 11:30:31 AM
Creation date
9/6/2019 10:43:12 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
RECORD_ID
SU0004098
PE
2605
FACILITY_NAME
PA-0300550
STREET_NUMBER
35775
Direction
S
STREET_NAME
KOSTER
STREET_TYPE
RD
City
TRACY
ENTERED_DATE
5/12/2004 12:00:00 AM
SITE_LOCATION
35775 S KOSTER RD
RECEIVED_DATE
3/10/2004 12:00:00 AM
QC Status
Approved
Scanner
SJGOV\rtan
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FilePath
\MIGRATIONS\K\KOSTER\35775\PA-0300550\SU0004098\APPL.PDF \MIGRATIONS\K\KOSTER\35775\PA-0300550\SU0004098\CDD OK.PDF \MIGRATIONS\K\KOSTER\35775\PA-0300550\SU0004098\EH COND.PDF \MIGRATIONS\K\KOSTER\35775\PA-0300550\SU0004098\CORRESPOND.PDF
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EHD - Public
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Appendix J <br /> Air Quality Technical Information <br /> Carbon Monoxide Modeling <br /> Dispersion Modeling <br /> Predicting the ambient air quality impacts of pollutant emissions requires an <br /> assessment of the transport,dispersion,chemical transformation, and removal <br /> processes that affect pollutant emissions after their release from a source. <br /> Gaussian dispersion models are frequently used for such analyses. The term <br /> "Gaussian dispersion"refers to a general type of mathematical equation used to <br /> describe the horizontal and vertical distribution of pollutants downwind from an <br /> emission source. <br /> i Gaussian dispersion models treat pollutant emissions as being carried downwind <br /> in a defined plume, subject to horizontal and vertical mixing with the <br /> surrounding atmosphere. The plume spreads horizontally and vertically with a <br /> reduction in pollutant concentrations as it travels downwind. Mixing with the <br /> surrounding atmosphere is greatest at the edge of the plume, resulting in lower <br /> pollutant concentrations outward(horizontally and vertically) from the center of <br /> y, the plume. This decrease in concentration outward from the center of the plume <br /> is treated as following a Gaussian("normal') statistical distribution. Horizontal <br /> and vertical mixing generally occur at different rates. Because turbulent motions <br /> in the atmosphere occur on a variety of spatial and time scales,vertical and <br /> horizontal mixing also vary with distance downwind from the emission source. <br /> The CALINE4 Model <br /> The ambient air quality effects of traffic emissions were evaluated using the <br /> CALINE4 dispersion model (Benson 1989). CALINE4 is a Gaussian dispersion <br /> model specifically designed to evaluate air quality impacts of roadway projects. <br /> r. <br /> Each roadway link analyzed in the model is treated as a sequence of short <br /> segments. Each segment of a roadway link is treated as a separate emission <br /> source producing a plume of pollutants which disperses downwind. Pollutant <br /> concentrations at any specific location are calculated using the total contribution <br /> y <br /> y� DeSilva Gates Quarry Project <br /> Draft Environmental Impact Report J_1 <br /> AS85105M <br />
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