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4800 – General/Other Program
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PR0515018
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Last modified
5/26/2021 3:28:54 PM
Creation date
5/26/2021 1:32:49 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4800 – General/Other Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0515018
PE
2950
FACILITY_ID
FA0012010
FACILITY_NAME
TRADEWAY CHEVROLET/AUTOBODY
STREET_NUMBER
1460
Direction
E
STREET_NAME
YOSEMITE
STREET_TYPE
AVE
City
MANTECA
Zip
95336
CURRENT_STATUS
01
SITE_LOCATION
1460 E YOSEMITE AVE
P_LOCATION
04
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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kn KLEINFELDER <br />3 <br />2. Approximately one week to one month prior to conducting the sampling, the residual <br />j pressures at the air -line of each lysimeter are measured ad the vacuums reset to <br />jmanufactured recommended value (usually 50 centibars). The measurements and applied <br />vacuums are noted on a sampling log form. Kleinfelder has found that resetting the <br />lysimeters vacuums before the sampling yields good sample recovery. <br />3. The residual pressures are measured just prior to collecting the sample. The water line is <br />then opened and nitrogen gas applied to the air line until either fluid or air is discharged <br />(for dry lysimeters). The sample is contained in a 1 liter unpreserved bottle and the <br />volume recovered is estimated. The fluid is then poured into appropriate preserved or <br />unpreserved bottles of the requested analysis. <br />4. After the sample is collected, the lysimeter vacuum is reset to the manufacturer's <br />recommended value. The lysimeter is also tested to evaluate potential leaks that may <br />cause vacuum pressure loss. <br />B-6 Leachate Monitoring <br />1. The leachate riser or wells are first opened and allowed to equilibrate with the <br />atmosphere. <br />2. The leachate elevation is then measured from a set location using a conductivity -based <br />water -level meter. The level is generally measured from a surveyed mark on the north <br />rim of the casing. <br />3. A leachate sample is then collected using a clean, disposable bailer. <br />4. The sample is labeled and immediately stored in an iced cooler pending transport to the <br />analytical laboratory. The sample is logged on a chain -of -custody. <br />B-7 Surface Water MonitorinE <br />1. Prior to collecting surface water samples, the depth of water is estimated at a designated <br />location in the surface water body. <br />2. Surface water samples are collected directly from the stream or surface water using a <br />clean unpreserved plastic bottle, disposable bailer, bailer, coliwasa, DipstikTM, dipper, <br />peristaltic pump, etc., or by directly filling the sample containers. Sampling equipment <br />will either be disposable, dedicated or decontaminated in accordance with the above - <br />defined decontamination protocols. Care is taken not to disturb the stream bottom and <br />introduce sediment in the sample. The fluid is then poured into appropriate preserved or <br />unpreserved bottles for the requested analysis. <br />I <br />20-3978-03.CHEV / ST02R111 Page B-7 <br />Copyright 2002 Kleinfelder, Inc. July 1, 2002 <br />
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