My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
ARCHIVED REPORTS XR0000668
EnvironmentalHealth
>
EHD Program Facility Records by Street Name
>
C
>
CAPITOL
>
6421
>
2900 - Site Mitigation Program
>
PR0522496
>
ARCHIVED REPORTS XR0000668
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
2/15/2019 9:19:56 PM
Creation date
2/15/2019 3:19:27 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0000668
RECORD_ID
PR0522496
PE
2957
FACILITY_ID
FA0015317
FACILITY_NAME
FLAG CITY CHEVRON
STREET_NUMBER
6421
STREET_NAME
CAPITOL
STREET_TYPE
AVE
City
LODI
Zip
95245
APN
05532024
CURRENT_STATUS
02
SITE_LOCATION
6421 CAPITOL AVE
P_LOCATION
99
P_DISTRICT
004
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.
/
41
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
� Y1) <br /> 12 March 2003 <br /> AGE-NC Project No 96-0236 <br /> Page 2 of 5 <br /> 2 1 GRAB GROUND WATER SAMPLE COLLECTION <br /> Grab ground water samples were collected from P-36, P-37 and P-38 utilizing hydro-punch <br /> technology A Geoprobe water sampling assembly was advanced to selected depths utilizing hollow <br /> steel rods The hollow steel rods were then retracted upward approximately four f eet, thereby <br /> exposing a PVC screen to ground water A bailer fitting was then placed on the end of-'/8-inch <br /> diameter polyethylene tubing, inserted through the rod assembly into the exposed screen, through <br /> which water was manually pumped Sufficient sample was collected from each hydro-punch to fill <br /> three 40-m1 EPA-approved VOA vials containing 0 5 ml 18% hydrochloric acid as a preservative <br /> and a one 1-liter amber bottle without sample preservative Ground water sample containers were <br /> labeled with probe boring designation, date, time, and samplers initials <br /> Each preserved sample was logged on a chain-of-custody form, placed m a chilled container and <br /> transported to Castle Analytical Laboratory (CAL)and McCampbell Analytical Inc (MAI), both <br /> DHS-certified laboratories, selected samples were analyzed for <br /> • EPA Method 5030/8015M for total petroleum hydrocarbons quantified as gasoline and diesel <br /> (TPH-g and TPH-d, respectively), <br /> o EPA Method 8020 for volatile aromatic compounds (benzene, toluene, ethyl benzene and <br /> xylene BTEX) with methyl-tertiary butyl ether(MTBE), and <br /> • EPA Method 8260 modified for methanol, ethanol, MTBE, tertiary butanol (TBA), <br /> di-isopropyl ether (DIPE), ethyl tent butyl ether (ETBE), tert amyl methyl ether (TAME), <br /> 1,2-dichloroethane (1,2-DCA) and ethylene dibromide (EDB) <br /> Due to a laboratory oversight, grab water samples collected from P-37 were not analyzed for EPA <br /> Method 8260 constituents <br /> 2 2 EQUIPMENT DECONTAMINATION <br /> Pnor to sample collection,Geoprobe groundwater sampling equipment were thoroughly rinsed with <br /> clean water after washing with a solution of Alconox Geoprobe rods were thoroughly cleaned prior <br /> to soil probe boring advancement <br /> Advanced GeoEnvironmental,Inc <br />
The URL can be used to link to this page
Your browser does not support the video tag.