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ARCHIVED REPORTS_2007
Environmental Health - Public
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EHD Program Facility Records by Street Name
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C
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CORRAL HOLLOW
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31130
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4400 - Solid Waste Program
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PR0440003
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ARCHIVED REPORTS_2007
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Last modified
9/14/2020 4:12:02 AM
Creation date
7/3/2020 11:04:44 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2007
RECORD_ID
PR0440003
PE
4434
FACILITY_ID
FA0003698
FACILITY_NAME
CORRAL HOLLOW LANDFILL
STREET_NUMBER
31130
STREET_NAME
CORRAL HOLLOW
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
25303010
CURRENT_STATUS
01
SITE_LOCATION
31130 CORRAL HOLLOW RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
Scanner
SJGOV\rtan
Supplemental fields
FilePath
\MIGRATIONS\SW\SW_4434_PR0440003_31130 CORRAL HOLLOW_2007.tif
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EHD - Public
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sampling for volatile organics. These bottles are filled completely to prevent air from remaining in the <br /> bottle. A positive meniscus forms when the bottle is completely full. A convex Teflon septum is <br /> placed over the positive meniscus to eliminate air. After the bottle is capped,it is inverted and tapped <br /> to verify that it contains no air bubbles. <br /> Dissolved Metals <br /> To determine dissolved concentrations of metals, appropriate field filtration techniques are used. <br /> When using a Teflon bailer, the sample is filtered by emptying the contents of the bailer into a <br /> pressure transfer vessel. A disposable 0.45-micron acrylic copolymer filter is threaded onto the <br /> transfer vessel at the discharge point and the vessel is sealed. Pressure is applied to the vessel <br /> with a hand pump and the filtrate is directed into the appropriate containers. Each filter is used <br /> once and discarded. <br /> When using a bladder pump to collect samples for dissolved constituents, the sample is filtered by <br /> attaching a disposable 0.45-micron acrylic copolymer falter directly to the pump effluent line with <br /> a pressure fitting. As the pump cycles, the effluent is pressured through the filter and directed into <br /> the appropriate containers. Each filter is used once and discarded. <br /> Spring (or Surface Water) Sampling <br /> If sufficient flow is observed, spring(or surface water) samples are collected with a dipper consistent <br /> with the procedures listed in Section 9 of "Test Methods for Evaluating Solid Waste: <br /> Physical/Chemical Methods," SW-846, 3rd edition, November 1986. If low-flow conditions are <br /> encountered,a stainless steel scoop is used to collect samples. The flat bottom of the scoop is pressed <br /> against the bank and the water will flow with little disturbance into the scoop. Samples collected with <br /> a dipper or scoop are transferred into the appropriate sample containers. Spring (or surface water) <br /> samples are filtered as required. <br /> Leachate Sampling <br /> If leachate sampling and analysis is required, samples are collected after purging approximately <br /> one casing volume using a Teflon bailer. Leachate samples are filtered as required and transferred <br /> into the appropriate containers. <br /> Lysimeter Sampling <br /> If lysimeter sampling and analysis is required, a vacuum is applied to the lysimeter only if an <br /> electrical conductivity monitor indicates that the soil-moisture content and soil suction are adequate <br /> for attempting to collect a sample. Vacuum and pressure is alternately applied to lysimeter over a <br /> 72-hour period to achieve the sample volume required for analysis. If sufficient sample volume is not <br /> Groundwater Monitoring A-4 Department of Public Works/Solid Waste <br /> County of San Joaquin <br />
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