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2900 - Site Mitigation Program
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PR0516259
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Last modified
11/19/2024 4:01:48 PM
Creation date
4/1/2020 3:39:00 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0516259
PE
2960
FACILITY_ID
FA0012534
FACILITY_NAME
BARREL TEN QUARTER CIRCLE LAND CO
STREET_NUMBER
21801
Direction
E
STREET_NAME
STATE ROUTE 120
City
ESCALON
Zip
95320
APN
20525002
CURRENT_STATUS
01
SITE_LOCATION
21801 E HWY 120
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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Kennedy/Jenks Consultants <br /> (3) At the beginning of purging and periodically thereafter, record the following information <br /> and water quality parameters/observations on the groundwater purge and sample form: <br /> As guidance, field parameters may be measured after one purge volume is removed <br /> and every % purge volume thereafter. <br /> - Date and time <br /> - Purge volume and/or flow rate <br /> - Water depth <br /> - Temperature <br /> - pH <br /> - Specific conductance <br /> - Dissolved oxygen <br /> - Oxidation-reduction potential (ORP) <br /> - Other observations as appropriate (turbidity, color, presence of odors, sheen, etc.). <br /> (4) Continue purging until water quality parameters have stabilized (refer to "Stabilization <br /> Criteria for Adequacy of Monitoring Well Purging" below) and/or a minimum of three <br /> wetted-casing volumes of water have been removed from the well. If a well purges dry, <br /> let it recover to 80 percent of original water column, then sample. If the well takes a very <br /> long time to recover(i.e., longer than 2 hours), try to sample the well at the end of day <br /> or first thing the next day. <br /> (5) Collect the sample in pre-cleaned sample containers suitable for the laboratory <br /> analyses to be performed. <br /> (6) If sampling using a bailer, use a bottom-emptying device or other technique to avoid <br /> sample agitation. If the collected water is very turbid, or a bottom-emptying bailer is not <br /> used, properly transfer the water from the bailer into the appropriate sample containers. <br /> Be careful to avoid agitating the sample. When sampling for VOCs, turn the bottle <br /> upside down after filling the container to identify possible headspace. If bubbles are <br /> present, top off the sample container or resample. <br /> b. Low-flow purging and sampling. <br /> (1) Place the pump intake at a depth equal to the approximate middle or just slightly above <br /> the middle of the well screen interval or water column or otherwise as dictated by well- <br /> specific soil stratigraphy and project-specific requirements. For example, it may be <br /> appropriate that the pump intake be set opposite to any preferential flow pathways (i.e., <br /> zones of higher permeability). <br /> (2) Place an electronic water-level indicator probe in the well, approximately 0.5 to 3 inches <br /> below the piezometric surface. If available, a transducer of sufficient accuracy can also <br /> be used to measure depth to water when purging. <br /> (3) Connect the pump discharge tube to a flow-through cell housing a water quality <br /> parameter probe. <br /> (4) Activate the pump for purging at a flow rate ranging from approximately 0.1 to 0.5 liters <br /> per minute (L/min) or other flow rate as dictated by project-specific and/or site-specific <br /> requirements. (Note: Some regulatory agencies may require specific flow rates). <br /> Determine the flow rate by timing the rate at which the flow-through cell is filled. <br /> Monitoring Well Installation Work Plan, D-4 <br /> Barrel Ten Quarter Circle Land Company, Escalon, California <br /> \\SFO\Groups\I S-Group\Admi n1J ob\03\0301 18.27_BTOC LC\09-Reports\M W-Install-WPI n1Appendix\APP_D.doc <br />
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