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COMPLIANCE INFO_1993-2007
Environmental Health - Public
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4400 - Solid Waste Program
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PR0440068
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COMPLIANCE INFO_1993-2007
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Last modified
7/20/2021 2:45:06 PM
Creation date
7/3/2020 11:10:13 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
COMPLIANCE INFO
FileName_PostFix
1993-2007
RECORD_ID
PR0440068
PE
4434
FACILITY_ID
FA0001871
FACILITY_NAME
CALIFORNIA CLAY LANDFILL
STREET_NUMBER
3242
Direction
S
STREET_NAME
EL DORADO
STREET_TYPE
ST
City
STOCKTON
Zip
95206
APN
17702029
CURRENT_STATUS
02
SITE_LOCATION
3242 S EL DORADO ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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SJGOV\sfrench
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FilePath
\MIGRATIONS\SW\SW_4434_PR0440068_3242 S EL DORADO_1993-2007.tif
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EHD - Public
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0 0 <br />Clayton Group Services Page 4 <br />Standard Operating Procedures <br />SOP -7 - Groundwater Sampling <br />Grab Mechanisms including bailers and syringe devices that are either reusable or <br />disposable. Bailers are used most commonly and generally are 2 -inch or 4 -inch <br />diameter. Clayton maintains a supply of reusable Teflon®, PVC, stainless-steel, <br />and acrylic bailers and disposable PVC and Teflon® bailers. If a bailer is used, <br />the rope used to raise and lower the bailer should be made of cotton Teflon® and <br />discarded after each sampling. <br />• Suction pumps including centrifugal and peristaltic pumps. These have the <br />disadvantage that they are limited to groundwater at depths of 25 feet or less and <br />may cause the loss of volatiles from the applied suction. <br />• Positive -displacement pumps including gas -drive, gas -operated bladder, electric <br />submersible, and gas -driven piston pumps. Gas -drive pumps may cause gas - <br />stripping of volatile components and for most applications are not recommended. <br />Clayton maintains a 4 -inch submersible pump and a 2 -inch ISCOW Bladder <br />Pump. <br />The attached forms for data collections should be filled in and made a part of the <br />permanent file. <br />All equipment should be decontaminated between sampling episodes in which the same <br />equipment is used and following final use. <br />7. Filtration - <br />In general, filtration in the field is not done on water samples destined for volatile organic <br />analyses since volatiles may be lost during the filtration process. However, filtration in <br />the field may be appropriate for. water samples where suspended particles may interfere <br />with the analyses such as for dissolved metals and PCBs. The USEPA, in its RCRA <br />Technical Enforcement Guidance Document (1986), recommends that water samples to <br />be collected for metals analyses be collected in two portions, one unfiltered for "total <br />metals" and one filtered through a 0.45 um membrane filter for analyses for "dissolved <br />metals". Field filtration devices fall into three categories: vacuum filtration; pressure <br />filtration; and, in-line filtration generally using glass microfibre or cellulose membrane <br />with a typical pore size of 0.45 um. <br />8. Sample Preservation - <br />The use of chemical preservation, if any, added to the water sample in the field depends <br />on the analyses to be conducted. Generally, the analytical laboratory will provide sample <br />containers with chemical preservatives that have been added to the containers in the <br />laboratory prior to delivery to the field. The analytical laboratory should be consulted <br />S:AEmir\ProiASOPS\SOP-7.doc <br />
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