My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
ARCHIVED REPORTS XR0010889
EnvironmentalHealth
>
EHD Program Facility Records by Street Name
>
E
>
ELKHORN
>
1050
>
2900 - Site Mitigation Program
>
PR0505234
>
ARCHIVED REPORTS XR0010889
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
8/1/2019 3:25:51 PM
Creation date
8/1/2019 2:23:45 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0010889
RECORD_ID
PR0505234
PE
2951
FACILITY_ID
FA0001103
FACILITY_NAME
Elkhorn Golf Club
STREET_NUMBER
1050
STREET_NAME
ELKHORN
STREET_TYPE
DR
City
STOCKTON
Zip
95209
CURRENT_STATUS
02
SITE_LOCATION
1050 ELKHORN DR
P_LOCATION
99
P_DISTRICT
003
QC Status
Approved
Scanner
SJGOV\wng
Tags
EHD - Public
There are no annotations on this page.
Document management portal powered by Laserfiche WebLink 9 © 1998-2015
Laserfiche.
All rights reserved.
/
77
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
1,frJ <br /> 27 June 1996 <br /> AGE-NC Project No. 95-0118 <br /> _r Page 13 of 23 <br /> thermal destruction. All are feasible methods of remediating sandy soil contaminated with gasoline. <br /> Off-site disposal generally involves the transportation of the impacted soil to a licensed <br /> treatment/disposal facility. <br /> —_� 7.2.1. EXCAVATION <br /> All of the mentioned methods of ex-situ treatment require excavation of the impacted soil, which is <br /> generally the fastest and most effective method for soil remediation. Impacted soil in the vadose and <br /> smear zones extend to a depth in excess of 35 feet bsg. Therefore, soil would have to excavated to <br /> depths greater than 35 feet bsg. Once excavated;the impacted soil is generally stockpiled onsite for <br /> treatment or transportation for disposal. If soil is treated on-site and hydrocarbon concentrations can <br /> be reduced to non-detectable(ND) levels,the soil can be used to backfill the excavation; if the soil <br /> is disposed off-site, backfill must be imported for the excavation. <br /> 7.2.2. FEASIBILITY OF EXCAVATION <br /> Excavation of impacted soil, followed by ex-situ treatment and/or disposal is a very effective method <br /> -- of remediation; non-detect (ND) can usually be achieved by excavation since, theoretically, all <br /> =_ contaminated soil is removed. However, excavation is usually too costly if the volume of impacted <br /> soil is too great or if the impacted soil is present at depths requiring special equipment or extensive <br /> -:� shoring. Both special excavation equipment and shoring would be required at the Elkhorn Country <br /> Club site. <br /> Excavation at the Elkhorn site is not a very feasible considering the depth of impacted soil, space <br /> limitations, current site usage and the cost for disposal and backfill. . <br /> 7.2.3. ESTIMATED COSTS FOR EXCAVATION <br /> At the subject site, impacted soil could not be excavated with standard excavating equipment. If <br /> F disruption of site operations and space Iimitations force off-site disposal,the cost for excavation of <br /> impacted soil could exceed $150 per cubic yard. Soil at the site would have to be excavated to depths <br /> of approximately 40.feet bsg. Based upon the removal of at least 1,200 cubic yards (25 vertical feet <br /> Of soil with a radius of approximately 20 feet) of hydrocarbon-impacted soil,the costs would range <br /> from $120,000 to $250,000. <br /> ,J - - <br /> .r-3 <br />
The URL can be used to link to this page
Your browser does not support the video tag.