My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
ARCHIVED REPORTS_XR0011925
Environmental Health - Public
>
EHD Program Facility Records by Street Name
>
N
>
NEWTON
>
3931
>
2900 - Site Mitigation Program
>
PR0540573
>
ARCHIVED REPORTS_XR0011925
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
4/9/2020 2:37:59 PM
Creation date
4/9/2020 2:26:01 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0011925
RECORD_ID
PR0540573
PE
2960
FACILITY_ID
FA0023207
FACILITY_NAME
GILLIES TRUCKING INC
STREET_NUMBER
3931
STREET_NAME
NEWTON
STREET_TYPE
RD
City
STOCKTON
Zip
95205
APN
13207017
CURRENT_STATUS
01
SITE_LOCATION
3931 NEWTON RD
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.
/
54
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
i <br /> A groundwater elevation map for each aquifer was constructed from the data in Table 1 to illustrate <br /> • the groundwater flow direction Figure 3 shows the elevation in the 1st Riverbank aquifer The <br /> elevation of the piezometric surface in this aquifer increases to the northwest from —34 98 feet in <br /> GT-21 to —34 79 feet in GT-20, and from —34 96 feet in GT-6 to —34 65 feet in GT-13A The <br /> contours depict a trough-shaped piezometric surface, implying that groundwater is funneled from <br /> the southwest as well as from the northwest toward the axis of the trough, wluch trends toward the <br /> F east-southeast This implies a primary flow direction toward the east-southeast, which is illustrated <br /> i by the arrow in Figure 3 The hydraulic gradient averages about 0 0045 ft/ft, which is identical to <br /> t <br /> the gradient that was measured in March <br /> In the two wells that are screened in both the I"and 2„d Riverbank aquifers, the piezometric surface <br /> is approximately 0 2-0 5 feet shallower in the 2"d Riverbank than in the 1st Riverbank The elevation <br /> difference in GT-17 was 0 23 feet in March and 0 20 feet in July, and in GT-16 it was 0 51 feet in <br /> March and 0 32 feet in July (Table 1) When the piezometric surface in the 2nd Riverbank is <br /> contoured, it also has a southeast-trending trough, but there are other undulations in this surface as <br /> well Because of these undulations, the elevation is shallower in some areas but deeper in other <br /> areas than is the piezometric surface in the 1st Riverbank(e g GT-14) (Figure 4) This also suggests <br /> a more variable groundwater flow direction to the north near GT-12, east near GT-15, and <br /> southeast near GT-14 <br /> In the First Quarter 2005 Report we observed that static water levels in the 3rd Riverbank aquifer <br /> were higher by a few inches than those in the 2nd Riverbank aquifer In the second quarter, the <br /> • opposite was true, the elevation of the piezometnc surface in most wells that are screened in both <br /> aquifers was slightly lower in the 3rd Riverbank than in the 2nd Riverbank Again, the differences <br /> between wells were not uniform, so the shape of the piezometric surface in the 3rd Riverbank is <br /> different from the surface in the 2nd Riverbank but is quite similar to that in the I" Riverbank <br /> (Figure 5) Although northward groundwater flow may be occurring near GT-14, it appeals that the <br /> predominant flow direction in the 3rd Riverbank was to the southeast Thus, there is general <br /> agreement on all three maps that the main flow direction was to the southeast <br /> 3.2 Analytical Results <br /> Twenty-one groundwater samples were collected for analysis, one more than in March The <br /> damaged casing in GT-9 has been repaired, making it possible to collect a sample from this well <br /> this quarter The results are given in Table 3, and the laboratory report is ni Appendix D <br /> Diesel fuel was detected in 16 of the 21 samples, and there was very little variation in the <br /> concentrations The maximum concentration was 847 µg/l in GT-16A and the minimum was 59 5 <br /> pg/1 in GT-12B Three others were also near the 50 ppb detection limit, and the rest ranged from <br /> 100 to 350 ppb Except for the sample from GT-16A, these concentrations are all within the range <br /> that was reported in the first quarter(57 to 370 ppb) <br /> The laboratory data are contoured for each aquifer in Figures 6-8 The three maps are in good <br /> agreement, they depict an elongate plume of slightly contaminated groundwater that trends mostly <br /> north-south through the site and decreases in areal extent with depth The highest concentrations of <br /> i 3 <br />
The URL can be used to link to this page
Your browser does not support the video tag.