My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
ARCHIVED REPORTS_2006_1
EnvironmentalHealth
>
EHD Program Facility Records by Street Name
>
A
>
AUSTIN
>
9999
>
4400 - Solid Waste Program
>
PR0440005
>
Archived Reports
>
ARCHIVED REPORTS_2006_1
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
7/17/2020 3:53:23 PM
Creation date
7/3/2020 10:50:58 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2006_1
RECORD_ID
PR0440005
PE
4433
FACILITY_ID
FA0004516
FACILITY_NAME
FORWARD DISPOSAL SITE
STREET_NUMBER
9999
STREET_NAME
AUSTIN
STREET_TYPE
RD
City
MANTECA
Zip
95336
APN
20106001-3, 5
CURRENT_STATUS
01
SITE_LOCATION
9999 AUSTIN RD
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
Scanner
SJGOV\rtan
Supplemental fields
FilePath
\MIGRATIONS\SW\SW_4433_PR0440005_9999 AUSTIN_2006_1.tif
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.
/
641
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
2. -Rinse the turbidity probe with Monized water'then place in the standard solution, <br /> 3. Adjust the meter for appropriate turbidity.scale then read the turbidity. <br /> 4. If required use the "calibrate' adjustment'on the meter to correct the instrument to read <br /> the correct turbidity. . <br /> The CaRbration.procass will be recorded on a turbidity calibration log. A Sample Calibration <br /> Log is located in Appendix C. Copies of calibration logs for each individual fiLstrument arc kept <br /> in a binder at the office. The logs are reviewed periodically top assess whether the instrument is <br /> becoming more difficult to calibrate and therefore needs adjustment by the manu£actuxer, or if <br /> new probes are required. <br /> .Equipment Decontamination <br /> To reduce the potential for introducing contaminants or-cross-contaminating samples,sampling <br /> equipment that is used repeatedly at different wells (i 4ine filter, meters) will be washed in a <br /> trisodium•pltosplYate solution and triple rinsed with dcioni=d water }mor to-use•in each-we1L. <br /> Tine monitoringwells are with dedicated-sampling <br /> Pled ' s which---will not require <br /> decontamination. Sterile factory scaled disposable bailers are used to collect the samples_ Bailer <br /> cord is replaced between each well- <br /> Monitoring Order <br /> . s <br /> Groundwater monitoring will be conducted such that depth to waxer moments and sampling <br /> is performed in the least contaminated wells frst(based on historical results). Measurement and <br /> sampling order will then move from lesser impacted wells to the most impacted wells. This is <br /> done to reduce the potential tint wells and samples can be cross contaminated. Gmundwat r <br /> twr&oring order begins at MW-20 and then 1"42 which are the back wells. The next <br /> wells, listed in order, to liesampled .arc MW-15, -10, -1 and -3.. These wells rarely contain <br /> evidence of chemical irupacts. The last wells to be'sampled, listed in order, include MW-14,.-13 <br /> and '-2. - Proposed well 16 will be sainpled in an ippropniate order depending on what <br /> constituents are detected Cif any) in the well upon the first sampling. Initially, MW-16 will-be <br /> the last.well sampled. <br /> It49384940IN23 IOR325 A-5 July 14,2000 <br /> cartstu 2M xktader,tom. <br />
The URL can be used to link to this page
Your browser does not support the video tag.