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WORK PLANS_CASE 2
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0508370
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WORK PLANS_CASE 2
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Last modified
11/19/2024 1:52:24 PM
Creation date
4/1/2020 1:52:14 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
FileName_PostFix
CASE 2
RECORD_ID
PR0508370
PE
2950
FACILITY_ID
FA0008045
FACILITY_NAME
PACIFIC AUTO CENTER
STREET_NUMBER
25355
Direction
N
STREET_NAME
STATE ROUTE 99
City
ACAMPO
Zip
95220
CURRENT_STATUS
01
SITE_LOCATION
25355 N HWY 99
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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f , <br /> 12 February 1999 <br /> AGE-NC Project No. 98-0540 <br /> Page 7 of 8 <br /> 4.4.1. Static Water Level Measurements <br /> Before sampling and during quarterly groundwater monitoring, static water level will be measured <br /> using an electric water level indicator. Water level data will be recorded to the nearest 0.01 foot <br /> from a reference point marked of the top of the PVC well casing. Before and after each use, the <br /> measurement device will be rinsed with water. <br /> 4.4.2. Well Evacuation <br /> Subsequent to measurement of depth to water and prior to sampling, the well will be purged using <br /> a two-stage submersible pump to ensure that the sample is representative of the formation, rather <br /> than water standing in the well casing. The well will be purged until: 1) a minimum of three casing <br /> volumes is removed from the well; and 2) the field-measured ground water parameters have <br /> stabilized. However, if a well is purged dry prior to evacuating three casing volumes, a ground water <br /> sample will be collected following 80 percent recovery of ground water within the well or within 8- <br /> hours of well evacuation. <br /> 4.43. Sample Withdrawal <br /> Water samples will be collected from the monitoring well using a disposable polyethylene bailer. <br /> These bailers are disposed of after one use and require no decontaminating, therefore minimizing <br /> cross contamination due to sampling devices. Samples will be drawn and collected in such a manner <br /> that agitation and exposure of the groundwater to the atmosphere is minimal. Sample containers will <br /> be filled using the appropriate disposable sampling attachment which allows controlled flow out of <br /> the bottom of the bailer by lifting up on the check valve. <br /> 4.4.4. Sample Handling <br /> Ground water samples will be collected into laboratory supplied containers. Ground water samples <br /> for BTEX, TPH-g and fuel oxygenate analyses will be collected into 40-m1 VOA vials containing <br /> 0.5-m1 of hydrochloric acid as preservative. Following collection the samples will be placed on ice <br /> and kept in a cooler until delivered to the laboratory for analysis. Chain-of-custody protocols will <br /> be used to document sample custody transfer from the field to the analytical laboratory. A chain-of- <br /> custody form will accompany the samples. <br /> Before sampling and during quarterly groundwater monitoring, static water level will be measured <br /> using an electric water level indicator. Water level data will be recorded to the nearest 0.01 foot <br /> Advanced GeoEnvironmental,Inc. <br />
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