My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
SITE HISTORY
EnvironmentalHealth
>
EHD Program Facility Records by Street Name
>
B
>
BUSINESS LOOP 205
>
5157
>
3500 - Local Oversight Program
>
PR0544135
>
SITE HISTORY
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
2/12/2019 10:21:39 AM
Creation date
2/12/2019 10:02:15 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
SITE HISTORY
RECORD_ID
PR0544135
PE
3528
FACILITY_ID
FA0005488
FACILITY_NAME
STRONG, RUTH
STREET_NUMBER
5157
Direction
W
STREET_NAME
BUSINESS LOOP 205
City
TRACY
Zip
95376
CURRENT_STATUS
02
SITE_LOCATION
5157 W BUSINESS LOOP 205
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
Scanner
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.
/
100
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
29 April 2005., .\ <br /> . . . AGE-NC-Project No..98-044.0 <br /> ` ' •Page•17 of-18- . . •• .. . - �. .._ : . <br /> Oxygen depletion in the subsurface is a characteristic'of biodegradation:Tli&bore of a contaminant <br /> 'plume is typically under anaerobic conditions wind only the margins,are aerobic. Therefore, even <br /> ,though anaerobic biodegradation is much slower than aerobic.biodegradation, anaei'ebic processes ...' <br /> e, 'May dominate;the degradation of contaminants:Ground,watei movement will'•gene' 11:'assist inthe ` <br /> ,. <br /> transport of nutrients in'the saturated zone. . <br /> _ ,The objective of the MNA is to collect-ground water samples through techniques which generally <br /> minimize undesired exposure to atmospheric conditions when and where allowable;and to monitor <br /> for parameters which signal'the natural attenuation ' f dissolved-hydrocarbons. Generally the <br /> geochemical parameters-selected:for monitoring are based on the.use of terminal electroh;acceptors <br /> as-microorganisms consume hydrocarbons. The sampling for NINA analysis would be.conducted , <br /> _ during.the'monitoring events to reduce overall-costs, to established a trend of the.geochemical <br /> parameters'and demonstrate the presents of terminal electron acceptors.metabolized by-products. <br /> Natural attenuation is normally used where .low. concentrations of hydrocarbons are present, <br /> following completion of another form of remediation or in an area where no domestic or irrigation <br /> _ wells are threatened. <br /> Costs for natural attenuation are generally.lower than most active remediation options; however, <br /> costs can be highly variable depending on the duration and type of monitoring required.' <br /> Fate and Transport modeling may be used to demonstrate the.potential for hydrocarbons to impact, <br /> nearby ground water receptors. Quarterly.grourid,water monitoring may also be.used,to demonstrate, <br /> a stable and declining ground;water-plume. ' <br /> 8.0. .RECQMMENDATIQNS , <br /> The, following recommendations for.remediation- are based upon data collected during the <br /> inve's#igatiori"of the property and predicted responses frons the site conceptual'model. <br /> .8.1. REMEDIATION 0E-HYDROCARB6N-1MPACTED SOIL <br /> ;Nadose;zarie soil impacted?by TFH-d, TPH-g; and BTEX extends vertically to the saturated zone <br /> under.the former UST and.surrourfding areas to an approximate depth of 17 feet bsg. Excavation. <br /> would require' the removal of a moderate volume of overburden soil in'the former'UST' and <br /> surrounding areas.Figure 9 illustrates the approxiinate area-of proposed excavation. Because'there- <br /> appears.to be a low-feasibility for bioremediation and monitored natural attenuation,AGE concludes <br /> -Advanced Geo$nvfrOimmentih Inc. <br />
The URL can be used to link to this page
Your browser does not support the video tag.