My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
ARCHIVED REPORTS_2011 REVISED FEASABILITY STUDY
Environmental Health - Public
>
EHD Program Facility Records by Street Name
>
I
>
INDUSTRIAL
>
230
>
2900 - Site Mitigation Program
>
PR0009051
>
ARCHIVED REPORTS_2011 REVISED FEASABILITY STUDY
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
2/5/2020 2:26:35 PM
Creation date
2/5/2020 10:37:50 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2011 REVISED FEASABILITY STUDY
RECORD_ID
PR0009051
PE
2960
FACILITY_ID
FA0000649
FACILITY_NAME
FORMER NESTLE USA INC FACILITY
STREET_NUMBER
230
STREET_NAME
INDUSTRIAL
STREET_TYPE
DR
City
RIPON
Zip
95366
APN
25938001
CURRENT_STATUS
01
SITE_LOCATION
230 INDUSTRIAL DR
P_LOCATION
05
P_DISTRICT
005
QC Status
Approved
Scanner
SJGOV\sballwahn
Tags
EHD - Public
Jump to thumbnail
< previous set
next set >
There are no annotations on this page.
Document management portal powered by Laserfiche WebLink 9 © 1998-2015
Laserfiche.
All rights reserved.
/
276
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
Registry, General Reporting Protocol, Version 3, April 2008, annual CO2 emissions would <br /> amount to approximately 9,900 tons per year. <br /> 4.0 CONCLUSIONS <br /> It is concluded that neither aerobic cometabolism-based biosparging nor air-based biosparging <br /> is feasible for treating dissolved phase contamination near the City of Ripon WWTP Lagoons <br /> based on the analysis of effectiveness, implementability and cost of implementing a full-scale <br /> biosparging biobarrier described herein. <br /> The effectiveness analysis concluded that: <br /> • Air or oxygen injection alone would not effectively treat TCE. <br /> • TCE is not amenable to aerobic biodegradation and would not be treated by injecting <br /> air or pure oxygen into the subsurface with co-metabolites. <br /> • Aerobic cometabolism has been shown to treat the target CDCs in laboratory and <br /> research applications but would involve injecting hazardous, explosive gases into the <br /> subsurface under high pressure. <br /> • Aerobic cometabolism has not been widely used or further demonstrated and therefore <br /> it's effectiveness is highly uncertain <br /> • Achieving adequate distribution of air channels in heterogeneous, layer geology would <br /> be extremely challenging. Biosparging would likely not be effective based on delivery <br /> considerations. <br /> The implementability analysis concluded that: <br /> • The length of the barrier and likely duration of treatment would require long term <br /> access to a number of properties along the Stanislaus River. There are significant <br /> implementation challenges associated with property access. <br /> • The final full-scale system would be an almost mile long fenced compound adjacent to <br /> the Stanislaus River. There are significant implementation challenges associated with <br /> public acceptance of an almost mile long fenced remediation compound adjacent to <br /> the Stanislaus River. <br /> The estimated cost and energy requirements analysis concluded that: <br /> • The total cost for a biosparging barrier is estimated to be approximately $86.5 million. <br /> This is not cost effective compared to other measures such as water replacement, <br /> institutional controls and intrinsic remediation (these other measures would likely still <br /> be required in addition to biosparging given its dubious effectiveness). <br /> AMEC Geomatrix, Inc. <br /> \\oad-fs1\doc_safe\9000s\9837.006\4000 REGULATORYTS Assessment_Apx B_012711\Attachment B.1\Attach B1.doc Bl-10 <br />
The URL can be used to link to this page
Your browser does not support the video tag.