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SU0004094
Environmental Health - Public
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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
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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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\MIGRATIONS\K\KOSTER\36736\QX-01-02_PA-0200065\SU0004094\EIR 2004.PDF
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EHD - Public
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We further note that the Draft EIR's calculations assume that 75 percent of the <br /> fugitive dust will be controlled, presumably using watering. The Draft EIR does not <br /> explain how this control efficiency would be achieved. Generally, watering of B-33 <br /> unpaved roads achieves no more than 50 percent control. The Draft EIR should be cont. <br /> r- revised to explain and support the basis for the assumed 75 percent control <br /> efficiency and should further require that this level of control be achieved by listing <br /> it as mitigation. <br /> r <br /> IV.D.2 Wind Erosion <br /> The Draft EIR states that the emission factor for wind erosion is 5.25 pounds <br /> of PM10 per square meter of stockpile area (uncontrolled) and 1.31 pounds per <br /> �. square meter of stockpile area (controlled) ("Ib/m2"). The Draft EIR also states that <br /> these emissions are based on a continuously exposed stockpile area of 50 square <br /> meters. (Draft EIR, Appx. D, p. 10.)There are several problems here. <br /> First, we were unable to reproduce the stated emission factors. Second, no <br /> support is provided for the velocities used to the make the wind erosion calculations B-34 <br /> and they appear low. Third, a 50 square meter stockpile area seems extraordinarily <br /> small for a quarry that will produce in excess of 4.0 million tons per year of material. <br /> v. Fourth, the Excel spreadsheets in Exhibit 1 calculated wind erosion emissions <br /> assuming that these emission factors are actually in units of grams per square meter <br /> and the stockpile has an area of 2500 square meters or 50 meters squared. Fifth, the <br /> calculations assume 75 percent control with no discussion of how it will be achieved <br /> or any requirement that it actually be achieved. This is an extraordinarily high <br /> control efficiency for wind erosion of storage piles if achieved using watering, the <br /> only fugitive dust control measure mentioned in the Draft EIR. (See, e.g., Draft EIR, <br /> p. 3-15 and AP42, Sec. 13.2.4.4.) We were unable, given the time constraints, to <br /> untangle these various messes and determine what the wind erosion emissions <br /> should be. <br /> ` IV.D.3 Handling and Storage <br /> The Draft EIR states that the emission factor for handling and storage <br /> L activities is 0.0052 pounds of PM10 per ton of material processed (uncontrolled) and <br /> 0.00131b/ton (controlled). Draft EIR, Appx. D, p. 9. There are several problems here. B-35 <br /> 6. First, we were unable to reproduce the stated emission factors. Our <br /> calculations indicate that the emission factors should be 0.00811b/ton uncontrolled <br /> Land 0.00201b/ton controlled. Second, no support is provided for the mean wind <br /> speed (7.4 mph) and material moisture content(0.7%) used to make the calculations. <br /> L 25 <br /> L <br />
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