My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
SITE HISTORY
Environmental Health - Public
>
EHD Program Facility Records by Street Name
>
F
>
FREMONT
>
2804
>
3500 - Local Oversight Program
>
PR0545172
>
SITE HISTORY
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
1/13/2020 10:57:22 AM
Creation date
1/13/2020 10:42:43 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
SITE HISTORY
RECORD_ID
PR0545172
PE
3528
FACILITY_ID
FA0009349
FACILITY_NAME
DIESEL PERFORMANCE INC
STREET_NUMBER
2804
Direction
E
STREET_NAME
FREMONT
STREET_TYPE
ST
City
STOCKTON
Zip
95205
APN
14343001
CURRENT_STATUS
02
SITE_LOCATION
2804 E FREMONT ST
P_LOCATION
99
P_DISTRICT
001
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.
/
160
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
F �P- Passive Bioremediation Assays -%, <br /> Passive bioremediation is generally based on the microbiological degradation of contaminants <br /> under reduced (anaerobic) conditions. Passive bioremedial considerations require detailed site <br /> characterizations encompassing historical data review and process modeling, typically generated <br /> .. from geologic, hydraulic, biological, geochemical, analytical (contaminant) and distribution data <br /> } (presumably reflects decreasing concentrations over time). The general premise behind passive <br /> modeling is to correlate various parameter measurements (i.e., contaminant, biological, and al- <br /> ternate electron acceptor/donors, etc.) obtained from the impacted interior of the plume with <br /> measurements from the unimpacted exterior area of the plume. Based on observed increases or <br /> decreases in levels of these parameters, comparative interpretations can be made as to 1) <br /> whether and to what degree microbial degradation of the contaminant is occurring; 2) the <br /> existence of background parameter concentrations; and 3) the potential to continuously replen- <br /> ish the "nutrients" utilized via biodegradation processes. Once the efficacy of passive biore- <br /> mediation is scientifically established, a Long Term Monitoring Plan (LTM) is implemented to <br /> ensure that what is expected is actually occurring. Site characterizations performed to assess the <br /> potential for passive bioremediation are often incomplete, and, at the minimum, typically require <br /> one hydrogeological cycle (four quarters) of monitoring data to evaluate site conditions. <br /> In addition to possessing the capabilities to perform complete required biotechnical site assess- <br /> ment and modeling, BioLogic offers the following specific tests routinely performed for both <br /> initial site assessment or long term monitoring. <br /> Routine Testing for Passive Bioremediation <br /> 0 General and Selective Enumerations 8 Total Organic Carbon (TOCK <br /> 0 Physicochemistry (inclusive of nitrate) 0 Alkalinity <br /> 0 Sulfate 0 Iron II(Fe 2-1) <br /> -- Ll Chloride 0 Manganese <br /> In addition to conducting biotechnical laboratory analyses, BioLogic recommends that field <br /> personnel conduct on-site analyses consisting of temperature, dissolved oxygen (DO), Redox <br /> potential, and conductivity measurements when collecting samples (please inquire with Bio- <br /> Logic for procedures and appropriate sampling techniques). Environmental evaluations should <br /> consist of contaminant concentration analysis and perhaps, more importantly, analyses of <br /> methane, ethane and ethene levels with additional considerations (and precautions) given to the <br /> accumulation of ammonium and hydrogen sulfide both of which are metabolic byproducts of <br /> anaerobic processes which could threaten environmental health and safety and preclude the use <br /> of a passive bioremediation approach. <br /> Environmental practitioners should be careful not to confuse passive intrinsic bioremediation <br /> with "Natural Attenuation" (NA) or "Risk Based Corrective Action" (RBCA). While pas- <br /> sive/intrinsic bioremediation is perhaps quite often the most important and integral component of <br /> NA & RBCA approaches, the investigation, implementation and effectiveness of these method- <br /> ologies also take into consideration parameters such as dilution, sorption, and migratory activity <br /> (fate & transport) of potential sensitive receptors. As such, caution must be taken in making <br /> biological interpretations in consideration of these factors. <br /> 8 <br />
The URL can be used to link to this page
Your browser does not support the video tag.