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2900 - Site Mitigation Program
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PR0537963
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Last modified
7/7/2020 10:39:16 AM
Creation date
7/7/2020 10:38:37 AM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0537963
PE
2950
FACILITY_ID
FA0021913
FACILITY_NAME
WRIGHT'S PETROLEUM INC
STREET_NUMBER
1512
STREET_NAME
WEISS
STREET_TYPE
WAY
City
ESCALON
Zip
95320
APN
22708001
CURRENT_STATUS
01
SITE_LOCATION
1512 WEISS WAY
P_LOCATION
06
P_DISTRICT
004
QC Status
Approved
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• • <br /> GROUND ZERO ANALYSIS,INC. Quality ControUQuality Assurance Plan <br /> be utilized for purgeable and semivolatile hydrocarbons analyses are shown on Table 2. <br /> 9.0 GROUNDWATER MONITORING PROTOCOL <br /> Monitoring of depth to water and free phase LNAPL (light non-aqueous phase liquids) thickness <br /> within wells will be conducted using an interface probe or conductivity meter. For consistency, all <br /> measurements will be taken from the north side of the wellhead at the survey mark. To assess <br /> potential infiltration of fine grained sediments,total well depth will also be sounded. <br /> Thickness of LNAPL on the groundwater surface is calculated by subtracting the depth to product <br /> from the depth to water. In addition, water elevations are adjusted for the presence of fuel with the <br /> following calculation: <br /> (LNAPL Thickness)(specific gravity)+(Water Elevation)=Corrected Water Elevation <br /> Newly installed wells will be allowed to stabilize for 24 hours after development prior to free phase <br /> thickness determination. <br /> An acrylic Surface Sampler will be used for visual inspection of the groundwater in order to note <br /> sheen (difficult to detect with the Interface Probe), odors, microbial action and sediments. The <br /> sampler is calibrated in inches and centimeters for visual inspection of product thickness. <br /> To reduce the potential for cross contamination between wells, the monitoring will take place in <br /> order from the least to most contaminated, if known. Well containing free product will be <br /> monitored last. Between each well monitoring the equipment will be decontaminated. <br /> Water level data collected from the wells will be used to develop a groundwater contour map for <br /> the project site. Groundwater flow will be estimated to be perpendicular to equipotential lines <br /> drawn on the map. <br /> 10.0 WELL DEVELOPMENT PROTOCOL <br /> Groundwater monitoring wells will be surged and developed prior to sampling activities. <br /> Approximately 10 times the volume of water in the casing will be withdrawn if possible. <br /> If the aquifer is slow to recharge, development will continue until recharge is too slow to practically <br /> continue. The volume of water produced versus time will be recorded. All purged groundwater <br /> will be stored on-site in 55 gallon waste drums unless permission is granted by the appropriate <br /> regulatory agency to discharge the water to the ground surface or sanitary sewer. Drummed water <br /> will be labeled with the source of the water to help ensure appropriate disposal based on <br /> contamination levels. <br /> G:\Data\GROUNDZE\QAQC\QAQC.doc <br /> 5 <br />
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