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
amec�9 <br /> be treated. An area 120 acres in size and 15 feet in saturated thickness, with an average <br /> porosity of 0.3, has a pore volume of 540 acre-feet, or approximately 176 million gallons. <br /> Because this area is so large, a full-scale bioaugmentation program would likely involve a bio- <br /> curtain configuration intended to curtail the movement of VOC-affected groundwater rather <br /> than treatment of the entire pore volume. Although the bio-curtain is expected to be more cost- <br /> effective than an area-wide bioaugmentation program, major limitations to effectiveness and <br /> cost are identified later in this document. <br /> The proposed bio-curtain alignment is shown in Figures B.2-1. The water table is <br /> approximately 25 feet below ground surface in the WWTP area. For cost estimating purposes, <br /> the bio-curtain length is assumed to be 4,500 feet and the target treatment interval is assumed <br /> to be from approximately 120 to 135 feet bgs to the base of the C1-zone of Intermediate <br /> Aquifer. The total thickness of the treatment area is assumed to be 15 feet. The assumed <br /> treatment area for this feasibility analysis is based on groundwater samples from the existing <br /> monitoring well network which are too far apart to base a final design. Full scale <br /> implementation of this bio-curtain would require a significant amount of additional subsurface <br /> characterization along the proposed alignment to ensure adequate distribution of microbes <br /> across zones of groundwater with high VOC concentrations. <br /> 3.2 EFFECTIVENESS <br /> Bioaugmentation could be effective if microbes could be distributed evenly across the entire <br /> bio-curtain alignment at the target concentration. However, effective delivery may not be <br /> achieved because of filtration and attachment of injected bacteria to aquifer sediments, as <br /> discussed in earlier sections of this technical assessment. Attachment and filtration of injected <br /> bacteria would likely cause clogging of pore-spaces near the injection location resulting in <br /> additional delivery limitations. Although partial treatment could result from this scenario, it is <br /> possible that VOC-affected groundwater could pass through large sections of the intended bio- <br /> curtain alignment without treatment because of the uneven distribution of microbes, where <br /> decreased permeability would coincide with areas of higher microbial concentration. <br /> Therefore, AMEC concludes that the effectiveness of a full-scale bio-curtain is highly <br /> uncertain. <br /> 3.3 IMPLEMENTABILITY <br /> Of the above potential side-effects associated with bioaugmentation described in Section 2.2, <br /> the two most undesirables are the increase in total dissolved solids (TDS; from increased <br /> dissolved metals, alkalinity and organic carbon) and the increased mobility of arsenic in the <br /> aquifer system. These are undesirable because both TDS and arsenic concentrations have <br /> already exceeded groundwater quality objectives in the past and continue to be major <br /> groundwater quality concerns for stakeholders in the Ripon area. The addition of organic <br /> substrates during bioaugmentation could exacerbate these existing groundwater quality <br /> AMEC Geomatrix, Inc. <br /> \\oad-fs1\doc_safe\9000s\9837.006\4000 REGULATORYTFS Assessment_Apx B_01 2711\Attachment B.2\Attach B-2.doc 132-8 <br />
The URL can be used to link to this page
Your browser does not support the video tag.