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SU0004094
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SU0004094
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Last modified
10/27/2020 1:02:10 PM
Creation date
9/6/2019 10:43:21 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
RECORD_ID
SU0004094
FACILITY_NAME
QX-01-0002
STREET_NUMBER
36736
Direction
S
STREET_NAME
KOSTER
STREET_TYPE
RD
City
TRACY
ENTERED_DATE
5/12/2004 12:00:00 AM
SITE_LOCATION
36736 S KOSTER RD
RECEIVED_DATE
1/8/2002 12:00:00 AM
QC Status
Approved
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SJGOV\wng
Supplemental fields
FilePath
\MIGRATIONS\K\KOSTER\36736\QX-01-02_PA-0200065\SU0004094\EIR 2004.PDF
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EHD - Public
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The aggregate from the weigh hopper is dropped into the mixer(pug mill) and dry-mixed for 6 to <br /> 10 seconds. The liquid asphalt is then dropped into a pug mill where it is mixed for an additional <br /> period of time. Total mixing time is usually less than 60 seconds. Then the hot mix is conveyed <br /> to a hot storage silo or is dropped into a truck and hauled to a job site. <br /> Emissions from hot mix plants may be divided into ducted production emissions,pre-production <br /> fugitive dust emissions, and other production-related fugitive emissions. Pre-production fugitive <br /> dust sources include vehicular traffic generating dust on paved and unpaved roads, aggregate <br /> material handling, and other aggregate processing operations. Ducted emissions are usually <br /> collected and transported by an industrial ventilation system having one or more fans, eventually <br /> to be emitted to the atmosphere through some type of stack. The most significant ducted source <br /> of emissions is the rotary drum dryer. The dryer emissions consist of water; PM; product of <br /> combust; and small amounts of organic compounds, including hazardous air pollutants. Other <br /> potential process sources include the hot-side conveying,classifying,and mixing equipment, <br /> which are vented either to the primary dust collector(along with the dryer gas) or to a separate <br /> dust collection system. <br /> Emission controls for PM emissions from the dryer and vent lines include dry mechanical <br /> collectors, scrubbers, and fabric filters, and the use of primary dust collection equipment such as <br /> large diameter cyclones, skimmers,and settling chambers. <br /> Air emissions were determined for the operation of the asphalt batching processing. The air <br /> emission calculations accounted for the proposed production levels(400,000 tons per year), the 1 <br /> number,types, and size of equipment,and the type of material processed and emission controls, if <br /> any. The emission factors were determined using the methodology found in Section 11.1 of <br /> EPA's AP-42. Table AQ-4 presents the emission factors for the asphalt processing operations. _ <br /> Additional emissions include benzene,acetaldehyde,ethyl benzene,PAHs,and various metals. <br /> PM,CO, and VOC emissions also occur during batch mix plant load-out,silo filling, and asphalt r <br /> storage, based on asphalt volatility,mix temperature,predictive emission factor equations found <br /> in AP-42 Section 11.1 (Table 11.1-14), and HAP speciation profiles. <br /> TABLE AQ-4 <br /> EMISSION FACTORS FOR ASPHALT PROCESSING' <br /> Emission Point PM10 CO SO2 NOx VOC <br /> Dryer,hot screen,mixer° 0.4 0.0046 0.025 0.0082 <br /> Uncontrolled 4.5 <br /> Venturi or wet scrubber 0.14 <br /> Fabric Filter 0.042 I <br /> SOURCE:Compilation of Air Pollutant Emission Factors,AP-42,Fifth Edition,Volume 1:Stationary Point and Area <br /> Sources,Section 11.1 Hot Mix Asphalt Plants,December 2000. <br />
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