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SU0004149
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2600 - Land Use Program
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SU0004149
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Entry Properties
Last modified
10/27/2020 1:00:10 PM
Creation date
9/6/2019 10:44:51 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
RECORD_ID
SU0004149
FACILITY_NAME
QX-96-0001
STREET_NUMBER
36869
Direction
S
STREET_NAME
KOSTER
STREET_TYPE
RD
City
TRACY
ENTERED_DATE
5/12/2004 12:00:00 AM
SITE_LOCATION
36869 S KOSTER RD
RECEIVED_DATE
9/22/1996 12:00:00 AM
QC Status
Approved
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FilePath
\MIGRATIONS\K\KOSTER\36869\QX-96-01_EIR 96-3\SU0004149\PUB REC REL APPL.PDF
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EHD - Public
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i <br /> --- k" KLEINFELDER <br /> manufactured 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 /> I 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 lysirneter 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 stared 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 Monitoring <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 /> p y g <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 /> r unpreserved bottles for the requested analysis. <br /> 3. The sample is labeled and immediately stored in an iced cooler pending transport to the <br /> E analytical laboratory. The sample is logged on a chain-of-custody. <br /> I. <br /> 20-2245-36.E01 1201 I R279 Page B-7 <br /> Copyright 2001,Kleinfelder, Inc. March 14,2001 <br /> i <br />
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