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CO0020059
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2500 – Emergency Response Program
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CO0020059
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Last modified
5/14/2019 10:35:10 AM
Creation date
2/22/2019 8:47:41 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2500 – Emergency Response Program
RECORD_ID
CO0020059
PE
2546
STREET_NUMBER
23577
STREET_NAME
MOUNTAIN HOUSE
STREET_TYPE
PKWY
City
TRACY
Zip
95391
ENTERED_DATE
12/5/2003 12:00:00 AM
SITE_LOCATION
23577 MOUNTAIN HOUSE PARKWAY
RECEIVED_DATE
12/4/2003 12:00:00 AM
QC Status
Approved
Scanner
ADMIN
Supplemental fields
FilePath
\MIGRATIONS4\M\MOUNTAIN HOUSE\23577\CO0020059.PDF
Tags
EHD - Public
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1H KLEINFELDER <br /> • The wells are secured in an aboveground or underground locking stovepipe. The <br /> well heads may be enclosed in a water tight cement utility box set flush to the <br /> ground surface when located in a traffic area. <br /> B-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 hydrocarbon <br /> layer or sheen. If no product layer or sheen is observed on the water, the well is developed by <br /> surging, pumping or bailing. Surging along the screened interval of the well is performed to <br /> draw the sediment from the formation into the filter pack and the well, and to set the sand pack. <br /> Development continues until the discharge runs relatively clear of fines. Approximately 5 to 10 <br /> well volumes are generally removed from each monitoring well. Discharge water is stored in 55- <br /> gallon drums and left on site for later discharge or disposal by the client, depending on laboratory <br /> results. The drums are labeled with the date, well number, and a contact person and phone <br /> number. <br /> B-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 /> B-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 depth <br /> to static groundwater is measured from a set location at the top of the PVC casing (usually the <br /> north rim). The depth of water is then subtracted from the elevation of the top of the well casing <br /> to provide a groundwater elevation for each monitoring well location. <br /> B4 GROUNDWATER MONITORING <br /> B-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 /> 1. 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 /> 44843.T04/ST04RI 121r Page B-5 <br /> Copyright 2004,Kleinfelder,Inc. September 2,2004 <br />
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