My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
ARCHIVED REPORTS_XR0006239
EnvironmentalHealth
>
EHD Program Facility Records by Street Name
>
P
>
PERSHING
>
4444
>
2900 - Site Mitigation Program
>
PR0540885
>
ARCHIVED REPORTS_XR0006239
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
4/10/2020 5:06:30 PM
Creation date
4/10/2020 3:03:25 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0006239
RECORD_ID
PR0540885
PE
2960
FACILITY_ID
FA0023381
FACILITY_NAME
FORMER EXXON SERVICE STATION NO 73942
STREET_NUMBER
4444
Direction
N
STREET_NAME
PERSHING
STREET_TYPE
AVE
City
STOCKTON
Zip
95207
APN
11022017
CURRENT_STATUS
01
SITE_LOCATION
4444 N PERSHING AVE
P_LOCATION
01
QC Status
Approved
Scanner
SJGOV\sballwahn
Tags
EHD - Public
There are no annotations on this page.
Document management portal powered by Laserfiche WebLink 9 © 1998-2015
Laserfiche.
All rights reserved.
/
198
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
water table was dry and fractured from the long period of drought, but after continuous infection <br /> is started, a decrease in soil permeability is expected from the swelling of the clay particles in the <br /> soil underlying the site, which consist mostly of silt and clay with lenses of more-sandy sedi- <br /> ments Fractures will decrease or disappear when the soil becomes saturated In addition, <br />' hydrocompaction might occur during water infection, which will further decrease the permeabili- <br /> ty of the underlying soil. At least 10-15 gpm of groundwater is expected to be extracted at the <br /> site, and even more if any additional extraction wells must be installed offsite to capture the <br />' plume To secure sufficient capacity of the injection wells, more than one was necessary Exist- <br /> ing monitoring wells MW4 and MW7 were connected to the injection system (Figure 4) To <br /> spread injected water more evenly and provide an efficient barrier separating the site from an <br />' upgradient plume, one more injection well (IW I) midway between MW4 and MW7 was in- <br /> stalled (see Figure 4). To monitor the groundwater level outside of the injection wells, two <br />' piezometers (P1, P2, Figure 4) were installed <br /> Assuming that each well is injecting about 5 gpm of water, the rise in groundwater level upgradi- <br /> ent near the middle injection well was estimated using the same equations as for the system of <br /> three pumping wells in line (Muskat 1937) Although these equations are used to estimate <br /> drawdown in the pumping wells, they are also used to estimate the mound or a rate of injection <br />' with good approximation (Driscoll 1986) <br /> Mound in the middle well (IW1) can be derived from the equation <br /> SPH - sd = PQ log(R/[rd2l 033))/1 36k <br />' for outer wells (MW4, MW7) <br /> so(2H - so) = (3Q log(R/12rd2]0 33))/i 36k <br />' where <br />' Q = single well pumping rate 26.5 m3/day <br /> sc = mound in the central well (m) <br /> s = mound in the outer well (m) <br /> 0 = hydraulic conductivity, 3 04 m/day <br />' H = aquifer thickness, 6 1 m <br /> d = distance between wells, 12 m <br /> R = radius of influence (assumed 48 m as a distance to a downgradient stagnation <br />' point for pumping wells RW1-RW3) <br /> r = well diameter, 0 15 m <br />' Mound in well IW 1 is estimated to be about 2 43 m (8 feet) and in wells MW4 and MW7, 2 18 <br /> m (7.15 feet) This would create a hydraulic barrier sufficient to isolate former Exxon <br /> RS 7-3942 and prevent an upgradient plume from moving toward the site The height of this <br /> bamer can be monitored using the proposed piezometers (P1 and P2) (Figure 4) <br />' �9 10 <br />
The URL can be used to link to this page
Your browser does not support the video tag.