My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
ARCHIVED REPORTS_XR0005951
Environmental Health - Public
>
EHD Program Facility Records by Street Name
>
F
>
FRONTAGE
>
1022
>
2900 - Site Mitigation Program
>
PR0534875
>
ARCHIVED REPORTS_XR0005951
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
4/7/2020 2:19:47 PM
Creation date
4/7/2020 1:49:04 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0005951
RECORD_ID
PR0534875
PE
2960
FACILITY_ID
FA0020170
FACILITY_NAME
AAA TRUCK WASH/JIMCO TRUCK PLAZA
STREET_NUMBER
1022
Direction
E
STREET_NAME
FRONTAGE
STREET_TYPE
RD
City
RIPON
Zip
95366
APN
26102004
CURRENT_STATUS
01
SITE_LOCATION
1022 E FRONTAGE RD
P_LOCATION
05
P_DISTRICT
005
QC Status
Approved
Scanner
SJGOV\sballwahn
Tags
EHD - Public
There are no annotations on this page.
Document management portal powered by Laserfiche WebLink 9 © 1998-2015
Laserfiche.
All rights reserved.
/
114
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
.13 December 1999 ; <br /> AGE-NC Project No. 980433 . .. <br /> Page 9of13 <br /> MW1-30 were 1,800 Mg/kg, 830 Mg/kg and 340 Mg/kg, respectively, as quantified by EPA " <br /> Method 8260. <br /> • TBA was detected in four soil samples analyzed. Soil near the former UST area at.a depth . <br /> of 10 feet bsg contained the greatest concentration of TBA at 15,000 Mgpkg. The <br /> concentration of TBA decreased with depth (20'),in soil boring B 1 to a concentration of 120 <br /> gg/kg and to concentration of 28 Mg/kg at 30 feet bsg in soil boring B L. <br />' TBA was detected in soil at a depth of 25 feet bsg at the northwest corner of the former UST <br /> area. Yet TBA was not detected in soil collected from boring B2 at 30 feet bsg; in soil boring <br /> B5 at 25 feet bsg or in soil boring B6 at 25 feet bsg. ; <br /> Laboratory results.of soil samples analyzed for petroleum hydrocarbons are summarized in Tables 2 <br /> and.3. The laboratory reports (MAI Laboratory ID' 12447 to 12472 and 1.7920 to 17931), quality <br /> assurance and quality control (QA/QC) reports and chains-of-custody are included in Appendices <br /> D and E. <br /> 4.3. PHYSICOCHEMICAL AND MICRO-BIOENUMERATION <br /> Soil Analy sis <br /> ' Analytical results of soil samples submitted for physicochemical analysis and microbiological <br /> enumeration indicate that there were no measurable petroleum bio-degrading microbe activity at the <br /> site. The lack of biodegrading bacteria may be due to the presence of biotoxic.compounds in the. ; <br /> subsurface at the site, such as metals, caustic materials(salts)or pesticides. Adequate concentrations <br /> of necessary nutrients for microbe growth and minimal sustenance were present in the soil at the site, <br /> however.the pH of the soils analyzed were above the optimal ranges for microbial growth. The <br /> microbiological laboratory report (A. Keith Kaufman report dated 18 June.1.999) and chain-of- <br /> custody form are included in Appendix F.- <br /> Ground <br /> .-Ground Water Analysis <br /> A water sample from well MW-1 was analyzed for bio-enumeration and physicochemical <br /> characterization by A. Keith Kaufman, M.S. <br /> The water sample was found'to have concentrations of inorganic components sufficient to support <br /> a microfauna for bioremediation. Nitrogen, potassium and phosphates was at sufficient levels to <br /> support a microfauna for bioremediation for undetermined time period. The water sample had <br /> ' significant microbiological populations as biodegraders as compared to the general concentration <br /> Advanced GcoEnvironmental,Inc. <br />
The URL can be used to link to this page
Your browser does not support the video tag.