My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
ARCHIVED REPORTS_XR0004121
EnvironmentalHealth
>
EHD Program Facility Records by Street Name
>
K
>
KETTLEMAN
>
1301
>
3500 - Local Oversight Program
>
PR0545342
>
ARCHIVED REPORTS_XR0004121
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
2/12/2020 3:18:50 PM
Creation date
2/12/2020 9:01:12 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0004121
RECORD_ID
PR0545342
PE
3528
FACILITY_ID
FA0000392
FACILITY_NAME
FLAMES LIQUOR
STREET_NUMBER
1301
Direction
W
STREET_NAME
KETTLEMAN
STREET_TYPE
LN
City
LODI
Zip
95242
APN
03104030
CURRENT_STATUS
02
SITE_LOCATION
1301 W KETTLEMAN LN
P_LOCATION
02
P_DISTRICT
004
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.
/
22
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
' 20 December 2001 <br /> • AGE-NC Project No 99-0624 <br />' Page 2 of 4 <br />' 22 COLLECTION AND ANALYSIS OF GROUND WATER SAMPLES <br /> Water samples were collected from each monitoring well using new disposable bailers after allowing <br />' the wells to achieve a minimum 80%recovery of the pre-purge water volume The samples were <br /> transferred into laboratory-supplied 40-m1 EPA-approved VOA vials containing 0 5 ml 18% <br /> hydrochloric acid as a sample preservative The sample vials were then labeled with the monitoring <br />' well designation,date,time of sampling and the sampler's Initials The samples were transported in <br /> a chilled container under chain of custody to McCampbell Analytical, Inc (MAI), a California <br />' Department of Health Services(DHS)-certified analytical laboratory for analysis The samples were <br /> analyzed for <br />' • Total petroleum hydrocarbons quantified as gasoline (TPH-g) in accordance with EPA <br /> Method 5030/8015 Modified, <br /> • Benzene, toluene, ethylbenzene, and total xylenes (BTEX) and methyl tertiary butyl ether <br /> (MTBE) in accordance with EPA Method 8020, and <br /> • Fuel oxygenates - tertiary butanol (TBA), di-isopropyl ether (RIPE), ethyl tert-butyl ether <br /> (ETBE), tert-amyl methyl ether (TAME), and MTBE in accordance with EPA Method <br /> 8260M <br /> r <br /> 3.0. FINDINGS <br /> The ground water elevation in each well was determined by subtracting the measured depths-to- <br /> water from the surveyed casing elevations and are presented in Table 1 Groundwater flow direction <br /> was determined by contouring the ground water elevations on a scaled site plan (Figure 2) <br /> Hydrocarbon-impact and MTBE-impact to ground water were assessed from laboratory analysis of <br /> the ground water samples <br /> 3 1 GROUND WATER ELEVATION AND GRADIENT <br /> Depths to ground water ranged from 54 33 feet to 55 40 feet below the tops of the well casings <br /> Ground water elevations at the site ranged from 15 90 feet (MW-4) to 16 14 feet (MW-2) below <br /> Imean sea level The top of the saturated zone occurred witlnn the screened intervals of all the <br /> morutonng wells <br /> IThe ground water flow direction was determined by contouring the ground water elevation data The <br /> • ground water underlying the site was inferred to have an average gradient of 0 003 ft/ft, the flow <br /> Advanced GeuEnvironmental,Inc <br />
The URL can be used to link to this page
Your browser does not support the video tag.