My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
ARCHIVED REPORTS_XR0003836
Environmental Health - Public
>
EHD Program Facility Records by Street Name
>
W
>
WALNUT GROVE
>
9015
>
3500 - Local Oversight Program
>
PR0545731
>
ARCHIVED REPORTS_XR0003836
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
6/4/2020 12:06:29 PM
Creation date
6/4/2020 12:00:36 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0003836
RECORD_ID
PR0545731
PE
3528
FACILITY_ID
FA0004572
FACILITY_NAME
LOPEZ, ADOR
STREET_NUMBER
9015
Direction
W
STREET_NAME
WALNUT GROVE
STREET_TYPE
RD
City
THORNTON
Zip
95686
APN
00114040
CURRENT_STATUS
02
SITE_LOCATION
9015 W WALNUT GROVE RD 11
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.
/
26
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
Feasibility Study/Corrective Action Plan 7 <br /> The Drake Property 26485 Thornton Road Thornton California November 26 1996 <br /> (MCLS) for drinking water The possibility of a second source (on-or off-site) contributing to <br /> hydrocarbons at the site is a moot point and need not be addressed here because site conditions meet <br /> criteria set forth by the CWQCB-CVR for"low-risk" conditions qualifying the site for"No Further Action" <br /> status (CWQCB-CVR, 1996) <br /> IV) The total pollutant mass remaining in the groundwater is decreasing at predicted rates and neither <br /> creates,nor threatens to create, a risk to human health and safety or future beneficial use(s) of the <br /> aquifer <br /> To verify natural attenuation of hydrocarbon concentrations on site, calculations were performed to <br /> estimate maximum theoretical hydrocarbon concentrations in groundwater (Table 5) Theoretical <br /> values can then be compared to real data obtained from the site <br /> Site specific soil data and or <br /> nd leaching models partitioning coefficients can be used to calculate the <br /> (� maximum theoretical groundwater concentrations for the site The maximum soil Impacts at the site <br /> are from excavation samples at a depth of 9 feet BGS Depth to groundwater at the site varies from 6 <br /> to 11 feet BGS Since the soil with maximum Impacts is periodically saturated with groundwater, the <br />. most conservative estimation of maximum concentrations ,s to use partitioning coefficients and assume <br /> pacted soils are saturated year-round This is done with the following equation <br /> dr <br /> N� <br /> 4 <br /> In which <br /> C.= Maximum Theoretical Groundwater Concentration (milligrams per liter, or mg/L) <br /> C, = Maximum Site Specific Soil Concentration (mg/kg) <br /> K,= Distribution Coefficient(liters per kilogram, or Ukg), a product of Koc (partitioning coefficient) <br /> and foc (fraction organic carbon content) <br /> Calculations for site-specific soil concentrations are shown In Table 5 These calculations indicate that <br /> the maximum toluene, ethylbenzene, and xylenes concentrations that would be expected at the site are <br /> 110 ug/l,420 ugM, and 1830 ug/l, respectively These concentrations have not been detected at the site <br /> in monitoring wells or water from the excavation (Tables 2-3),therefore these calculations are an over- <br /> estimation This is likely because of the following assumptions (which all result in over-eshmatlon) that <br /> are made when conducting these calculations <br /> 41 <br /> 0181 F EA RPT(Mist 15) <br /> FLUOR DANIEL GTI �5_ <br />
The URL can be used to link to this page
Your browser does not support the video tag.