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COMPLIANCE INFO_1991-1992
Environmental Health - Public
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4400 - Solid Waste Program
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COMPLIANCE INFO_1991-1992
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Last modified
10/25/2022 9:40:16 AM
Creation date
7/3/2020 10:39:20 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
COMPLIANCE INFO
FileName_PostFix
1991-1992
RECORD_ID
PR0440001
PE
4433
FACILITY_ID
FA0004514
FACILITY_NAME
AUSTIN ROAD/ FORWARD LANDFILL
STREET_NUMBER
9069
Direction
S
STREET_NAME
AUSTIN
STREET_TYPE
RD
City
STOCKTON
Zip
95215
CURRENT_STATUS
02
SITE_LOCATION
9069 S AUSTIN RD
P_LOCATION
01
P_DISTRICT
004
QC Status
Approved
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SJGOV\cfield
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\MIGRATIONS\SW\SW_4433_PR0440001_9069 S AUSTIN_1991-1992.tif
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EHD - Public
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SF,NT BY:Commerce 12- 9-91 3:24AII ;# 6 <br /> 4 <br /> Over the entire lifetime of a power plant project it probably <br /> doesn't exceed about two or three percent of the Total moisture <br /> in the landfill. <br /> Supporting computations are provided in the attached table . <br /> These are for several sites all of which are in California. The <br /> sites are designated according to eneral location. For example, <br /> 'INC V means the first- listed northern California site; SC 3 is <br /> the third- listed southern California site. Column 1 shows total <br /> gas energy recovery (billions of Btus) for the year 1989 through <br /> November 8 (total of 312 days) as the starting point. Assuming <br /> 1009 Btu$ per cubic foot of pure methane and using the typica <br /> plant inlet methane content for each fachi.ty, the inlet flow <br /> rates (millions of standard cubic feet per day) were calculated <br /> as shown in Column 2. The figures inparentheses in Column 2 are <br /> the typical inlet gas Btu contents per cubic foot , by plant. <br /> Column 3 shows the estimated amounts of waste in each landfill in <br /> millions of tons in place. These figures were obtained <br /> extramurally from landfill operators andgovernmental agencies <br /> during power plant project development. The assumed moisture <br /> content (column 4) is based upon Pacific Energy's experience with <br /> various landfills and knowledge of these specific ones. The <br /> percent moisture figures used are almost certainly correct within <br /> a factor of two. <br /> The third and fourth columns directly yield the fifth, which is <br /> millions of tons of water in lace. Water in the saturated as <br /> was computed from an assumed landfill gas temperature of 140F. <br /> At this temperature, the vapor pressure of water is about 150mm <br /> of mercury. At one atmosphere total pressure, this represents <br /> about 20% by volume. Thus Col 6' which is the extraction flow <br /> rate of water vapor in millions of standard cubic feet per day, <br /> is simply 20 percent of Column 2 Column 7 is the same as Column <br /> 6 except for the change of units to the more usual gallons per ' <br /> day. Finally, Columns T and b lead directly to Column 8, which <br /> is the percent of landfill water content removed per year through <br /> the process of gas extraction. The figures in Column 8 are <br /> almost certainly correct to within a factor of about four. <br /> Grouadu ter Cgatamination <br /> To date, there is no scientifically defensible study to show that <br /> returning condensate, or not returning it, has any bearing on <br /> groundwater contamination caused by a landfill. This is the <br /> carie, in part, because of the cellular structure and resulting <br /> horizontal stratification present in most landfills . The lifts <br /> of waste ordinarily constructed in a landfill are separated by <br /> soil laars. The soil layers tend to be limited in terms of <br /> hydraulic permeability, while the trash (especially if relatively <br /> fresh) tends to be fairly easyfor moisture to move through. It <br /> can be expected, therefore, tat as condensate percolates down <br /> into a landfill from a shallow point discharge, <br /> will tend to <br />
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