My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
ARCHIVED REPORTS_XR0012740
EnvironmentalHealth
>
EHD Program Facility Records by Street Name
>
K
>
KETTLEMAN
>
501
>
3500 - Local Oversight Program
>
PR0545337
>
ARCHIVED REPORTS_XR0012740
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
2/11/2020 6:44:23 PM
Creation date
2/11/2020 11:53:39 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012740
RECORD_ID
PR0545337
PE
3528
FACILITY_ID
FA0003629
FACILITY_NAME
ARCO STATION #434*
STREET_NUMBER
501
Direction
W
STREET_NAME
KETTLEMAN
STREET_TYPE
LN
City
LODI
Zip
95240
APN
03119028
CURRENT_STATUS
02
SITE_LOCATION
501 W KETTLEMAN LN
P_LOCATION
02
P_DISTRICT
004
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.
/
661
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
r Z- <br /> 03 <br /> em, <br /> Mr. Kyle Christie <br /> December 9, 1988 <br /> .� Page 4 <br /> h <br /> .� To track the dissolved hydrocarbon trends systematically ARCO authorized quarterly <br /> groundwater sampling and analysis for benzene, toluene, and xylene (BTX). Groundwater <br /> samples were collected for analysis on September 29 and 30 and October 3 and 4, 1988. <br /> Monitoring well W-8 was not sampled as dissolved hydrocarbons have never been identified <br /> hydrocarbon occurrence. <br /> in groundwater from 1•:'-8, and it is located some distance from any identified dissolved <br /> Field Methods <br /> Groundwater was purged from each monitoring well prior to sample collection using a bladder <br /> pump and stainless steel bailer. Throughout the purging process, pH and specific conductance <br /> of the discharged water were monitorP.4. These parameters had stabilized (three consecutive <br /> measurements within 10 percent of each other taken 5 minutes apart) before groundwater <br /> samples were collected. Three well volumes of groundwater (one well volume being the <br /> volume of water inside the well casing- g plus 35 percent of the gravel packed annular space) <br /> were evacuated from monitoring wells W-2, W-213, W-3, W-5, W-6, and W-7. The low <br /> groundwater level in September/October 1988 (see Figure 2) made purging difficult in <br /> t` monitoring wells W-1, W-2A, and W-4. Due to slow recharge of <br /> g groundwater into monitoring <br /> wells W-2A and W-4, 0.7 and 1.3 well volumes, respectively, were evacuated from these <br /> wells. Monitoring well W-i contained only muddy water. Therefore, no groundwater sample <br /> !, J was collected from monitoring well W-1. <br /> Each well was sampled with a Teflon bailer equipped with a bottom-eml,tying valve. The <br /> t:3 sample was drained directly from the bottom valve into two 40-milliliter glass bottles with <br /> Teflon-lined septums. The samples were stored on ice from the time of collection through <br /> delivery to Eureka Laboratories Inc., in Sacramento. All purging and sampling equipment was <br /> washed with laboratory-grade detergent and tap water then rinsed with deionized water before <br /> each use. All groundwater produced during purging and sampling was contained in 55-gallon <br /> Fri drums and temporarily stored on site pending results of the laboratory analysts. ARCO <br /> f- contracted with Armour Petroleum, Inc.,of Fairfield,California, to dispose of the contaminated <br /> groundwater. <br /> a <br /> September/October 1988 Field and Analytical Results <br /> €>$ Groundwater levels were measured at approximately 49 feet below ground surface in April <br /> 1987 when the first three monitoring wells were installed. Water level measurements show <br /> that groundwater dropped to approximately 55 feet below ground surface in October 1987 and <br /> E rose to approximateiy 52 feet below ground surface in March I988. Groundwater levels were <br /> measured at approximately 59 feet below ground surface in late September 1988. In late <br /> September 1988, Groundwater flow direction was to the southwest under a hydr4UGc_ <br /> _t _.-. _._of_about.-Il-feet.per-mile 0.2- ------ - -- <br /> - -- P ( percent)- ---- - ---._..- __.—.-.------------ <br /> 1} Dissolved BTX concentrations in groundwater samples collected from April 1987 through <br /> t j September/October 1988 are summarized in. Table 1. September/October 1988 benzen; <br /> concentrations are shown on Figure 1. Complete laboratory reports of the September/October <br /> i a BLOWN AND CALDWILL <br /> 723 S STREET sACRAPAEN -- <br /> TOL CALIFCANLA M141M.glel 441.0127 . <br />
The URL can be used to link to this page
Your browser does not support the video tag.