My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
ARCHIVED REPORTS_2010_20
EnvironmentalHealth
>
EHD Program Facility Records by Street Name
>
A
>
AUSTIN
>
9999
>
4400 - Solid Waste Program
>
PR0440005
>
Archived Reports
>
ARCHIVED REPORTS_2010_20
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
7/17/2020 10:13:35 PM
Creation date
7/3/2020 10:55:28 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2010_20
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_2010_20.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.
/
551
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. Riase the turbidity probe vtith deionized water then place in the standard solutior.L <br />3. Adjust the meter for appropriat6 turbidity.scale then read the turbidity. <br />4. If required use the "calibrate" adjustment on them to correct the instrument to read <br />the correct turbidity. <br />The calibration Process will be recorded on a turbidity calibration 1,09. A Sample Calibration <br />Log is located in Appendix C Copies of calibration logs for each h4vidual instrument are kr�t <br />in a binder at the office. The logs are reviewed periodically top assess whether the instrument is <br />becoming -more difficult to caDrate and therefore needs adjusoent by the manufkctui;er, or if <br />Y ew probes art: reqgired. <br />To redime the potential for introducing contaminants or cross -contaminating samples, samp <br />equipment that is used repeatedly at diffmnt wells (m -line: Mter. matecs) will be Wnished in <br />ftisodium. phosphate solution and tdple rinsed with deloni=d water pdor to -use. in each <br />The monitoring wells am equ4xd with dedicated-sarnpling -systenm vddch-.-wifl not, <br />docontamination. Sterile factory scaled disposable bailers used to collect the samples. <br />cord is replaced between each well. <br />MbZ itoring: Order <br />Groundwater vacrutoring will be conducted such that depth to water.mea=cmeats and sarapfing <br />is <br />Measurement land pedormed in the least wells fust.(based on bistorical results). <br />sampling order will dm move from Les= pp a' wells to the most ir� welLs. This is <br />done to reduce the potentiai ffi2t wensand samples am be cr= contarnfimted. Groundwater <br />manitoringorder begins at MW -20 and then MW -12 -which the &*graund welts, Ue Ma <br />welL%'fisted in order, to be- sampled am MW -15, -10. -1 and -3.. These wtUs rarely contain <br />evidence of chemical The last Wells to be -sampled, listod in ordeinchide JAW -14,43 <br />Impacts <br />Md '-,2- Proposed well 16 will be sainpled in an a�proptiatc order &?=fing on wbat <br />ccusdtu� are detected (if any) in the well upon the first sampling. bitially, MW -16 will -be <br />23-4939*-MIUMORM <br />OwrWw 2M VeWddw tv- <br />M <br />
The URL can be used to link to this page
Your browser does not support the video tag.