My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
ARCHIVED REPORTS XR0012554
Environmental Health - Public
>
EHD Program Facility Records by Street Name
>
B
>
BENJAMIN HOLT
>
2908
>
3500 - Local Oversight Program
>
PR0544111
>
ARCHIVED REPORTS XR0012554
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
2/7/2019 12:07:41 PM
Creation date
2/7/2019 11:09:29 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012554
RECORD_ID
PR0544111
PE
3528
FACILITY_ID
FA0003625
FACILITY_NAME
ARCO STATION #83560*
STREET_NUMBER
2908
Direction
W
STREET_NAME
BENJAMIN HOLT
STREET_TYPE
DR
City
STOCKTON
Zip
95207
APN
09763032
CURRENT_STATUS
02
SITE_LOCATION
2908 W BENJAMIN HOLT DR
P_LOCATION
01
P_DISTRICT
002
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.
/
446
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
� � � .. - li .3 ..� ' '` gym..-• :: - _' - - Fir <br /> r s" <br /> .ayR -.T�::. 'its :ju �b•.P '� <br /> AW, 42 .` ,, ��4~ iw �r�se'""£,., "'"''�<r' R.4� � �.�;"�'' y '`4",� M1+,� � 1��, g- ,�k ��� M'"k' .�• <br />;rte= <br /> Nlr. Chuck Carmel <br /> July 11, 1991 <br /> Niac 9 <br /> The Slow rate and time-drawdown data were both hand- and computer-analyzed by the <br /> generalized straight-line method of Cooper and Jacob(1946). A simple correction was applied <br /> to the discharge data to account for well storage effects. Analysis of the data is shown on <br /> Figure 6. Data analysis indicates an aquifer transmissiviry (T) of 900 ft''/day. The thickness of <br /> the saturated aquifer(b)that was tested is about 20 ft. Tltereforc,the hydraulic conductivity(1C) <br /> is about 45 feet/day or. <br /> Hydrocarbon Data <br /> Figure 7 shows the estimated extent of benzene, ethylbenzene, toluene, and xylene (BETX) <br /> compounds in the shallow groundwater beneath the site. The numbers refer to the sum,or total, <br /> of benzene, toluene,ethylberrzene and xylenes from the February 1991 groundwater sampling. <br /> Modeling Analysis <br /> A capture zone modeling analysis was performed using RessgM (O'Neill, 1990). RessgM is a <br /> modified version of the popular Ressq model(Javandel et al., 1984). Modifications were made <br /> to make the model user friendly and to provide better graphics support. <br /> Figure 8 shows the capture zone resul-ing from pumping R-13 at a constant discharge rate of 12 <br /> gpm. Model. parameters.included the hydraulic conductivity (45 ft/day), aquifer thickness (20 <br /> ft), hydraulic gradient (0.002) and direction of flow. The model is based on two-dimensional, <br /> steady-state, uniform flow conditions with continuous pumping. <br /> Twelve individual streamlines (groundwater pathlines) appear on Figure S. The bold line on <br /> Figure 8 is the location of the capture zone boundary. Note that the capture zone boundary on <br /> Figure 8 envelops the BETX plume. Therefore, the plume will be captured by pumping the <br /> recovery well (R-13)at a constant discharge rate of approximately 12 gpm. <br /> Figure 9 presents the results for calculations ruade with a flow rate of 10 gpm. Although 10 gpm <br /> is sufficient to capture most of the plume, hydrocarbons hear the capture zone boundary may <br /> migrate downgradient. Currently the recovery well is pumping at an average rate of <br /> approximately 10.8 gprn. <br /> Brawn and Caldwell <br />
The URL can be used to link to this page
Your browser does not support the video tag.