My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
SU0004149
EnvironmentalHealth
>
EHD Program Facility Records by Street Name
>
K
>
KOSTER
>
36869
>
2600 - Land Use Program
>
QX-96-0001
>
SU0004149
Metadata
Thumbnails
Annotations
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
Scanner
SJGOV\wng
Supplemental fields
FilePath
\MIGRATIONS\K\KOSTER\36869\QX-96-01_EIR 96-3\SU0004149\PUB REC REL APPL.PDF
Tags
EHD - Public
Jump to thumbnail
< previous set
next set >
There are no annotations on this page.
Document management portal powered by Laserfiche WebLink 9 © 1998-2015
Laserfiche.
All rights reserved.
/
782
PDF
Print
Pages to print
Enter page numbers and/or page ranges separated by commas. For example, 1,3,5-12.
After downloading, print the document using a PDF reader (e.g. Adobe Reader).
View images
View plain text
K L E I N F F L D E R <br /> A, .t <br /> 3. Water level measurements are made using a conductivity-based water-level meter. <br /> Depth-to-water is generally measured from a surveyed mark on the north rim of the PVC <br /> well casing. <br /> The water level measurements are converted to elevations using the surveyed casing elevations. <br /> B-4.2 Groundwater Sampling <br /> 1 Groundwater samples are collected from the monitoring wells at the site. The sampling protocol <br /> for each well is as follows: <br /> i <br /> 1. Down-well equipment (pumps, bailers, etc.) is decontaminated by steam cleaning, or by <br /> scrubbing in a trisodium-phosphate or non-phosphate detergent wash followed by a <br /> distilled water rinse, prior to use in each well. Bailer cord is replaced prior to use in each <br /> well. <br /> 2. The depth to groundwater is measured using a conductivity-based water-level meter. <br /> 3. The volume of water in gallons standing in the well is calculated by subtracting the depth <br /> to groundwater measurement from the depth of the well and multiplying by the <br /> appropriate conversion factor(0.16 for 2-inch wells, and 0.65 for 4-inch wells). <br /> + 4. Three to five well volumes of water are purged from each well using a submersible pump, <br /> bladder pump, or Teflon bailer. <br /> 5. Physical parameters (pH, electrical conductivity, and temperature) are monitored for <br /> stability while purging. The physical parameter measurements are recorded on purge- <br /> and-sample logs, along with the time and volume of water purged at each measurement. <br /> 6_ Samples are collected with a disposable bailer or bladder pump into appropriately <br /> prepared bottles provided by the analytical laboratory. <br /> 7. Samples for metals analysis are usually filtered in the field at the time of collection. <br /> 8. Samples are immediately labeled and placed in an iced sample container. At the end of <br /> the day, the samples are delivered to the analytical laboratory under chain-of-custody <br /> k <br /> control. <br /> B-5 Vadose Zone Monitoring <br /> { <br /> 1. Prior to conducting lysimeter sampling, the pressure-vacuum equipment is checked and <br /> cleaned. A Soil-Moisture hand pump with a pressure-vacuum gage is used to measure <br /> residual and implied pressure-vacuum. Nitrogen gas is used to purge the lysimeter <br /> system for sampling. An air pump is available as a back up. <br /> 2. Approximately one week to one month prior to conducting the sampling, the residual <br /> pressures at the air-line of each lysimeter are measured ad the vacuums reset to <br /> 20-2245-36.EOi/201IR279 Page B-6 <br /> Copyright 2001,Kleinfelder,Inc March 14,2001 <br /> Y <br /> i <br />
The URL can be used to link to this page
Your browser does not support the video tag.