My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
WORK PLANS
Environmental Health - Public
>
EHD Program Facility Records by Street Name
>
T
>
TULLY
>
17725
>
2900 - Site Mitigation Program
>
PR0526486
>
WORK PLANS
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
5/28/2020 4:22:25 PM
Creation date
5/11/2020 11:39:37 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0526486
PE
2965
FACILITY_ID
FA0017927
FACILITY_NAME
LOCKEFORD COMMUNITY SVCS DIST
STREET_NUMBER
17725
Direction
N
STREET_NAME
TULLY
STREET_TYPE
RD
City
LOCKEFORD
Zip
95237
APN
05303039
CURRENT_STATUS
01
SITE_LOCATION
17725 N TULLY RD
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
Scanner
LSauers
Tags
EHD - Public
There are no annotations on this page.
Document management portal powered by Laserfiche WebLink 9 © 1998-2015
Laserfiche.
All rights reserved.
/
94
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
Section 1 Introduction and Background <br /> respectively. Additional soil descriptive,physical, and chemical properties are provided as <br /> Appendix A of this report, for further reference. <br /> 1.2.2 SHALLOW GROUNDWATER OCCURRENCE <br /> Groundwater elevation data were obtained froin both the existing WWTF groundwater <br /> monitoring program (MW-1 through MW-3)and from the California Department of Water <br /> Resources (DWR). This information was subsequently imported into a geographic information <br /> system(GIS) in order to graphically evaluate groundwater elevations and flow direction within <br /> the project area. Figure 1 illustrates groundwater elevation contours for the fourth quarter of <br /> 2005 and represents the typical reported groundwater flow direction in the vicinity of the <br /> treaiinent ponds,which has historically been towards the southwest. Figures 2 and 3 represent <br /> groundwater elevation obtained from the DWR for periods extending from January through June <br /> and July through December 2005, respectively. These figures indicate that regional groundwater <br /> flow direction is predominantly towards the south and south southeast, approximately 45 to 90 <br /> degrees to that of historic groundwater contours in the vicinity of the treatment ponds. It should <br /> be noted however,that the spacing of existing monitoring wells MW-1, MW-2, and MW-3 are <br /> such that accurate interpretation of groundwater flow direction may not be possible. <br /> Additionally,the well completion details for the DWR monitoring program is not known and <br /> therefore reported groundwater elevations may not be representative of first recoverable <br /> groundwater in the area. <br /> Variations in the depth to first recoverable gr urndwater was similarly assessed using the existing <br /> WWTF groundwater monitoring network and a DWR well,which was reportedly located within <br /> 1100 feet of the disposal fields(Figure 5). Based on these sources of information the depth to <br /> groundwater at the wastewater treatment pon s and disposal fields is expected to occur between <br /> approximately 100 to 130 feet bgs and similar to that reported by ENGEO for monitoring wells <br /> constructed just to the east of the WWTF and at a proposed disposal area expansion site. <br /> Additionally,these monitoring data(WWTF ells) indicate that the depth to groundwater can <br /> vary seasonally and up to approximately 5 feet. As such,these seasonal variations in <br /> groundwater elevations should be accounted for when designing the new monitoring wells. <br /> March 2006 Lockeford CSD <br /> 1.2 Groundwater Monitoring Well Installation Workplan <br />
The URL can be used to link to this page
Your browser does not support the video tag.