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COMPLIANCE INFO_1993-2007
Environmental Health - Public
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EHD Program Facility Records by Street Name
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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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\MIGRATIONS\SW\SW_4434_PR0440068_3242 S EL DORADO_1993-2007.tif
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EHD - Public
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Clayton Group Services Page 3 <br />Standard Operating Procedures <br />SOP -7 - Groundwater Sampling <br />is not possible. The final measurement of these parameters is taken as being <br />characteristic of the groundwater. The general appearance of the water during purging <br />(color, turbidity, and odor) should be recorded in the field logbook. <br />Criteria based on purge volume - This is the most commonly used purging <br />method. Although the suggested number of well volumes of groundwater to be <br />removed varies, generally regulatory requirements specify 3 to 5 well volumes of <br />water or until the well goes dry, whichever occurs first. The volume of water <br />purged to dryness from low yielding wells should be reported in the field logbook. <br />Water generally is removed using a bailer (generally stainless-steel, acrylic, or <br />Teflon®) or pump (gas -activated positive displacement pump or submersible <br />pump). <br />• Criteria based on stability of physical properties - Using these criteria, water is <br />removed until the physical properties, generally pH, temperature, Eh, specific <br />conductance, and turbidity (less than 10 or 5 NTUs) stabilize. <br />• Criteria based on hydraulic and chemical characteristics - This method uses <br />aquifer transmissivity as determined by pumping or slug/bail test and field testing <br />of the water characteristics. <br />Although other purging protocols exist, they generally tend to be impractical. <br />In general, purging is conducted near the upper surface of the groundwater, taking into <br />account water drawdown during purging. <br />Prior to sampling, the water level should be allowed to recover to at least 80% of the <br />initial groundwater level. <br />All purge water should be properly contained and containers labeled pending analytical <br />results. If water can and is disposed to the storm drainage system, a NPDES permit is <br />required form the California Regional Water Quality Control Board. <br />6. Groundwater Sampling <br />Commonly the physical properties of the groundwater (pH, temperature, conductivity, <br />turbidity) are measured prior to sample collection by obtaining a sample of groundwater <br />in the same manner as the groundwater samples are collected. <br />Sampling Device - The groundwater sampling device, generally either a pump or bailer, <br />may be the same device as used for purging, with care taken to assure decontamination <br />prior to use or using a device specific to the sampling. Although a wide variety of <br />sampling devices are available, most fit into one of three categories: <br />S:\Ennr`Proj\SOPS ,SOP -7. doe <br />
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