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ARCHIVED REPORTS XR0011270
Environmental Health - Public
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EHD Program Facility Records by Street Name
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FREMONT
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2050
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3500 - Local Oversight Program
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PR0543791
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ARCHIVED REPORTS XR0011270
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Last modified
10/1/2018 5:12:12 AM
Creation date
9/28/2018 4:53:26 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS XR0011270
FileName_PostFix
XR0011270
RECORD_ID
PR0543791
PE
3526
FACILITY_ID
FA0003592
FACILITY_NAME
Aries Tek, LLC
STREET_NUMBER
2050
Direction
E
STREET_NAME
FREMONT
STREET_TYPE
St
City
Stockton
Zip
95205
CURRENT_STATUS
02
SITE_LOCATION
2050 E Fremont St
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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Well Purging <br /> The wells were purged prior to sampling Before sampling occurred, a polyvinyl chloride <br /> (PVC) bailer, centrifugal pump, low-flow submersible pump, or Teflon bailer was used to <br /> purge standing water in the casing and gravel pack from the monitoring well In most <br /> monitoring wells, the amount of water purged before sampling was greater than or equal <br /> to three casing volumes Some monitoring wells were expected to be evacuated to <br /> dryness after removing fewer than three casing volumes These low-yield monitoring <br /> wells were allowed to recharge for up to 24 hours Samples were obtained as soon as the <br /> monitoring wells recharged to a level sufficient for sample collection If insufficient <br /> water recharged after 24 hours, the monitoring well was recorded as dry for the sampling <br /> event <br /> Groundwater purged from the monitoring wells was contained in 55 gallon DOT drums <br /> and removed from the site by Reno Drain Oil <br /> Field measurements of pH, specific conductance, and temperature were recorded in a <br /> waterproof field logbook Figure A-2 shows an example of the water sample field data <br /> sheet on which field data are recorded Field data sheets were reviewed for completeness <br /> by the sampling coordinator after the sampling event was completed <br /> The pH, specific conductance, and temperature meter were calibrated each day before <br /> • field activities were begun The calibration was checked once each day to verify meter <br /> performance Field meter calibrations were recorded on the water sample field data sheet <br /> Well Sampling <br /> A Teflon bailer was the only equipment acceptable for well sampling Because samples <br /> for volatile organic analysis were being collected, the flow of groundwater from the bailer <br /> was regulated to minimize turbulence and aeration Glass bottles of at least 40-milliliters <br /> volume and fitted with Teflon-lined septa were used in sampling for volatile organics <br /> These bottles were filled completely to prevent air from remaining in the bottle A <br /> positive meniscus formed when the bottle was completely full A convex Teflon septum <br /> was placed over the positive meniscus to eliminate air After the bottle was capped, it was <br /> inverted and tapped to verify that it contained no air bubbles The sample containers for <br /> other parameters were filled, filtered as required, and capped <br /> Sample Preservation and Handling <br /> The following section specifies sample containers, preservation methods, and sample <br /> handling procedures <br /> I <br /> SAC1E WACHEIREPORTSWACP102 DOC-98Vsg 2 C-3 mon <br /> Rev 0,5/21/99 <br />
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