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CORRESPONDENCE_1991-2001
EnvironmentalHealth
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4400 - Solid Waste Program
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PR0515734
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CORRESPONDENCE_1991-2001
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Last modified
8/27/2025 11:32:48 AM
Creation date
9/25/2020 3:47:55 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
CORRESPONDENCE
FileName_PostFix
1991-2001
RECORD_ID
PR0515734
PE
4430 - SOLID WASTE CIA SITE
FACILITY_ID
FA0012312
FACILITY_NAME
CITY OF TRACY LANDFILL
STREET_NUMBER
0
STREET_NAME
CORRAL HOLLOW
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
25303015
CURRENT_STATUS
Active, billable
SITE_LOCATION
CORRAL HOLLOW RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Pending
Scanner
SJGOV\cfield
Supplemental fields
Site Address
CORRAL HOLLOW RD TRACY 95376
Tags
EHD - Public
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--- - ------ — --_-- KLEINFELDER <br />A-3.2 Monitoring Well Development <br />The wells are developed to reduce the effects of drilling on the formation and to increase the <br />effective hydraulic radius of the wells. <br />Monitoring wells are generally developed 24 to 48 hours after installation to allow the grout to <br />set. Each well is first sampled with a clear disposable bailer to visually inspect for a <br />hydrocarbon layer or sheen. If no product layer or sheen is observed on the water, the well is <br />developed by surging, pumping or bailing. Surging along the screened interval of the well is <br />performed to draw the sediment from the formation into the filter pack and the well, and to set <br />the sand pack. Development continues until the discharge runs relatively clear of fines. <br />Approximately 5 to 10 well volumes are generally removed from each monitoring well. <br />Discharge water is stored in 55 -gallon drums and left on site for later discharge or disposal by <br />the client, depending on laboratory results. The drums are labeled with the date, well number, <br />and a contact person and phone number. <br />A-3.3 Equipment Decontamination <br />To reduce the potential for cross -contamination between wells, developing equipment is washed <br />in a trisodium phosphate or non -phosphate detergent solution and rinsed in distilled water or <br />steam cleaned prior to use in the next monitoring well. <br />A-3.4 Well Survey <br />The locations of soil borings and monitoring wells, and the elevation of the top of the PVC <br />casings are usually surveyed and tied into permanent markers, if readily available. Survey <br />accuracy is 0.1 foot for the "x" and "y" coordinates and .01 foot for the "z" coordinate. The <br />depth to static groundwater is measured from a set location at the top of the PVC casing (usually <br />the north rim). The depth of water is then subtracted from the elevation of the top of the well <br />casing to provide a groundwater elevation for each monitoring well location. <br />A-4.1 Water Level Measurements <br />Water level measurements are made in the wells prior to purging and sampling the wells. <br />Measurement protocol is as follows: <br />Prior to obtaining water level measurements, the monitoring wells would be opened and <br />allowed to equilibrate for a period of approximately %2 hour. <br />2. The water level probe is decontaminated in a trisodium phosphate or non -phosphate <br />detergent wash, followed by a distilled water rinse, prior to use in each well. <br />20-1108-33.001/2011R1188 Page A-5 <br />2001, Kleinfelder, Inc. October 17, 2001 <br />
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