My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
WORK PLANS
EnvironmentalHealth
>
EHD Program Facility Records by Street Name
>
F
>
FRESNO
>
1405
>
2900 - Site Mitigation Program
>
PR0505137
>
WORK PLANS
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
1/15/2020 2:25:10 PM
Creation date
1/15/2020 1:23:17 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0505137
PE
2960
FACILITY_ID
FA0006565
FACILITY_NAME
STOCKTON SOIL TREATMENT FAC
STREET_NUMBER
1405
Direction
S
STREET_NAME
FRESNO
STREET_TYPE
AVE
City
STOCKTON
Zip
95206
CURRENT_STATUS
01
SITE_LOCATION
1405 S FRESNO AVE
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
Scanner
SJGOV\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.
/
46
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
APR 20 '94 03:52PM OGDEN PROJECTS ENVIRONMENTAL DPT P.9'1© <br /> rim of the PVC well casing, but may vary depending on previous reference points. <br /> 4. The water level measurements will be converted to relative groundwater elevations <br /> with respect to mean sea level or a local benchmark by subtracting them from the <br /> surveyed casing elevations. The resulting groundwater elevations will be contoured <br /> to assess the direction of the groundwater gradient at the time of sampling. The <br /> information can then be used to assess which wells represent upgradient and which <br /> wells represent downgradient groundwater conditions. <br /> Groundwater Sam lin <br /> Groundwater samples are collected from the monitoring wells at the site. The sampling <br /> protocol for each well is as follows: <br /> 1. Down-well equipment (pumps, bailers, etc.) will be decontaminated by steam <br /> cleaning,or by scrubbing in a trisodium-phosphate wash followed by a distilled water <br /> rinse, prior to use in each well. Bailer cord will be replaced prior to use in each <br /> well_ <br /> 2. The depth to water will be measured using a conductivity-based water level meter. <br /> 3. The volume of water standing in the well will be calculated by subtracting the depth- <br /> to-water measurement from the depth of the well and multiplying the appropriate <br /> conversion factor (3.1.4 * radius'). <br /> 4. Three or more well volumes of water are purged from each well using a submersible <br /> pump, bladder pump or Teflon bailer, until physical parameters are reasonably <br /> stable. <br /> j. Physical parameters(pH,electrical conductivity and temperature)are monitored for <br /> stability during purging. The physical parameter measurements are recorded on <br /> purge-and sample logs, along with the time and volume of water purged at each <br /> 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. For all lead, TRPH, and TPH-diesel samples, in-line field filtration will be used to <br /> prevent the entrainment of air into the sample. Any samples to be analyzed for <br /> volatile constituents such as BTEX and TPH-gasoline, however, will not be in-line <br /> filtered. <br /> 8_ Samples will immediately be placed and sealed in labelled glass bottles, and stored <br /> on ice until delivery to the analytical laboratory. A custody seal will be placed on <br /> 4 <br />
The URL can be used to link to this page
Your browser does not support the video tag.