My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
ARCHIVED REPORTS XR0012747
Environmental Health - Public
>
EHD Program Facility Records by Street Name
>
K
>
KETTLEMAN
>
2448
>
3500 - Local Oversight Program
>
PR0544300
>
ARCHIVED REPORTS XR0012747
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
4/2/2019 4:20:35 PM
Creation date
4/2/2019 3:38:29 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012747
RECORD_ID
PR0544300
PE
3528
FACILITY_ID
FA0003855
FACILITY_NAME
TESORO (SHELL) 68153
STREET_NUMBER
2448
Direction
W
STREET_NAME
KETTLEMAN
STREET_TYPE
LN
City
LODI
Zip
95240
APN
05814001
CURRENT_STATUS
02
SITE_LOCATION
2448 W KETTLEMAN LN
P_LOCATION
02
P_DISTRICT
004
QC Status
Approved
Scanner
WNg
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.
/
362
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
a <br /> average transmissivity for the tested area of 6,000 gpf/day. The <br /> me <br /> cone of depression produced during the 18 hours pumping period <br /> r <br /> Affected most of the site. <br /> Slug tests of zone 3 were run in wells MW-22, and MW-31. The <br /> E ' i <br /> calculated transmissivity values were 871 gpf/day and 3198 t <br /> gpf/day, respectively. The slug test results are considered to <br /> # e <br /> be semi-quantitative. Details of slug test methods and <br /> r � <br /> calculations are given in Appendix B. ; <br /> R-� <br /> w The observed transmissivity of zone 3 appears to vary across the <br /> site in a similar Way to which sediment grain size and sorting <br /> { vary. Average grain size, sediment sorting, and zone 3 <br /> � ! <br /> � . transmissivit appear to increase to the southeast. <br /> Iid�rater Oyzo1�+t, <br /> Groundwater quality is d_j <br /> rectly affected by the rate and are.i <br /> extent by which leaked <br /> gasoline from the underground storage tank <br /> Pit percolate down through the vadose zones. Hydrocarbon t <br /> contamination in the vadose zone at this site is primarily <br /> limited to the contact between zones 1 and 2 near the tank pit <br /> and a small soil column extending down to the <br /> water table. <br /> Lateral migration of petroleum hydrocarbons apparently occurred <br /> ti,f <br /> along the contact between zone 1 and zone 2. However,. based on ; <br /> Y <br /> J coil cora analy$es, Table 3, the current degree of petroleum <br /> t " <br /> hydrocarbon in the vadose zone does not appear to <br /> Y p� significant. <br /> Th® contamination eventually roaches the. water table where. eome <br /> -;a of the gasoline dissolves in <br /> groundwater. Seasonal water table <br /> �� 13 r . <br />
The URL can be used to link to this page
Your browser does not support the video tag.