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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
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SJGOV\rtan
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\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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San Joaquin County Community Diesel Engine Emission Control Technologies <br /> Development Department _ <br /> full day or shift and are regenerated at the end of the day or shift with the vehicle <br /> or equipment shut off. A number of the smaller filters are removed and <br /> regenerated externally at a"regeneration station." <br /> Because they have control over their regeneration and are not dependent on the <br /> heat carried in the exhaust, active DPFs have a much broader range of application <br /> and a much lower probability of getting plugged than passive DPFs. One result _ <br /> of this is that emission control groups for active systems are most likely larger <br /> than those for passive filters,depending on the particular system. <br /> While actively regenerated traps do not generally increase NO2 emissions as <br /> passive DPFs may(unless they include catalysis), special attention needs to be <br /> given to active traps during regeneration. Spikes in emissions have been — <br /> observed to occur during regeneration,prompting European researchers involved <br /> with the VERT project to require emission measurements over the regeneration <br /> period(Mayer 2001). ARB's verification procedure incorporates the same <br /> requirement. <br /> Ash <br /> Filter technology has been identified by ARB staff as potentially generating a <br /> new waste stream. As discussed earlier, DPFs are designed to trap diesel PM to <br /> achieve a net decrease in PM emissions. The carbonaceous component of the <br /> PM captured by the filter,which is by far the majority,is burned off when the — <br /> filter regenerates. Any inorganic components are left behind as ash in the filter <br /> and accumulate over time. This ash must be cleaned from the filter periodically <br /> and properly disposed of _ <br /> Ash Production and Composition _ <br /> Ash that accumulates within a DPF is comprised of inorganic substances carred <br /> along in an engine's exhaust stream. The primary source of ash is the <br /> combustion of lubrication oil in the engine. The nature of the inorganic additives <br /> present in the oil,therefore, determines the composition of the majority of the ash <br /> in a DPF. Other sources of ash include material arising from engine wear(small — <br /> compared to oil ash)and any inorganic fuel additives that may be used. Not <br /> considering fuel additives,the rate of ash accumulation within a DPF is primarily <br /> a function of the rate at which an engine bums oil. <br /> Ash collected from a diesel engine using typical lubrication oil and no fuel <br /> additives is primarily composed of oxides of the following elements: calcium, <br /> zinc,phosphorus, silicon, sulfur, and iron. Zinc is the component of primary <br /> concern,because it can be considered a hazardous waste depending on its <br /> concentration. In Section 66261.24,Title 22, of the California Code of <br /> Regulations, identifies two threshold limits for zinc: 250 mg/l for the Soluble — <br /> Threshold Limit Concentration and 5,000 mg/kg for the Total Threshold Limit <br /> DeSilva Gates Quarry Project <br /> Draft Environmental Impact Report L.t <br /> As 05105.05 <br />
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