My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
CORRESPONDENCE_2016-2017
Environmental Health - Public
>
EHD Program Facility Records by Street Name
>
W
>
WAVERLY
>
6484
>
4400 - Solid Waste Program
>
PR0440004
>
CORRESPONDENCE_2016-2017
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
4/17/2025 10:07:34 AM
Creation date
1/7/2022 10:13:31 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
CORRESPONDENCE
FileName_PostFix
2016-2017
RECORD_ID
PR0440004
PE
4433 - LANDFILL DISPOSAL SITE
FACILITY_ID
FA0004517
FACILITY_NAME
FOOTHILL LANDFILL
STREET_NUMBER
6484
Direction
N
STREET_NAME
WAVERLY
STREET_TYPE
RD
City
LINDEN
Zip
95236
APN
09344002
CURRENT_STATUS
Active, billable
SITE_LOCATION
6484 N WAVERLY RD
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
Scanner
SJGOV\cfield
Supplemental fields
Site Address
6484 N WAVERLY RD LINDEN 95236
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.
/
367
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
connects the control panel to the sensor. Cable markings are stamped at 1-foot <br /> increments. The water level is measured by lowering the sensor into the monitoring well. <br /> A low-current circuit is completed when the sensor contacts the water, which serves as an <br /> electrolyte. The current is amplified and fed into an indicator light and audible buzzer, <br /> signaling when water has been contacted. A sensitivity control compensates for highly <br /> saline or conductive water. The electric sounder is decontaminated by rinsing with <br /> deionized water after each use. <br /> Depth to water is recorded to the nearest 0.01 foot in the field logbook. The groundwater <br /> elevation at each monitoring well is calculated by subtracting the measured depth to <br /> water from the surveyed elevation of the top of the well casing. The total depth of the <br /> well is then measured in the monitoring wells scheduled for sampling by lowering the <br /> sensor to the bottom of the well. The total depth of the well, used to calculate purge <br /> volumes and to determine whether the well screen is partially obstructed by silt, is <br /> recorded to the nearest 0.1 foot in the field logbook. <br /> Sample Collection <br /> Sample collection procedures include equipment cleaning, water level and total well <br /> depth measurements, well purging and sampling, surface water sampling, leachate <br /> sampling, and lysimeter sampling. <br /> Equipment Cleaning <br /> All sample containers are provided by the laboratory and prepared with preservatives as <br /> needed. <br /> During field sampling, equipment surfaces that are placed in the well or contact <br /> groundwater are decontaminated using a steam cleaner and deionized water before the <br /> next well is purged or sampled. <br /> Water Level and Total Well Depth Measurements <br /> Immediately before a monitoring well is purged, the water level and total well depth are <br /> measured using an electric sounder as described in the previous section "Groundwater <br /> Elevation Survey." The electric sounder is decontaminated by rinsing with deionized <br /> water after each use. <br /> Well Purging <br /> Before sampling occurs, standing water in the casing and gravel pack are purged from the <br /> monitoring well using a dedicated submersible pump. In most monitoring wells, the <br /> amount of water purged before sampling is equal to or greater than three casing volumes. <br /> Foothill WQPS Rev Ldoc <br /> A-2 <br />
The URL can be used to link to this page
Your browser does not support the video tag.