My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
WORK PLANS
EnvironmentalHealth
>
EHD Program Facility Records by Street Name
>
B
>
BATES
>
7770
>
2900 - Site Mitigation Program
>
PR0523602
>
WORK PLANS
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
2/6/2019 9:12:16 AM
Creation date
2/6/2019 9:10:56 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0523602
PE
2965
FACILITY_ID
FA0015931
FACILITY_NAME
LINNE ESTATES LLC
STREET_NUMBER
7770
Direction
W
STREET_NAME
BATES
STREET_TYPE
RD
City
TRACY
Zip
95324
APN
24809009
CURRENT_STATUS
01
SITE_LOCATION
7770 W BATES RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
Scanner
WNg
Tags
EHD - Public
There are no annotations on this page.
Document management portal powered by Laserfiche WebLink 9 © 1998-2015
Laserfiche.
All rights reserved.
/
27
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'q KLEINFELDER <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 /> control. <br /> A-5 VADOSE ZONE MONITORING <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 /> 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 /> 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 /> 34091.E01/ST05R040/JZ:ly Page A-6 <br /> ©2005,Kleinfelder,Inc. January 13,2005 <br />
The URL can be used to link to this page
Your browser does not support the video tag.