My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
ARCHIVED REPORTS_XR0004843
EnvironmentalHealth
>
EHD Program Facility Records by Street Name
>
L
>
LOUISE
>
2901
>
3500 - Local Oversight Program
>
PR0545440
>
ARCHIVED REPORTS_XR0004843
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
3/9/2020 5:55:33 PM
Creation date
3/9/2020 2:32:26 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0004843
RECORD_ID
PR0545440
PE
3528
FACILITY_ID
FA0003845
FACILITY_NAME
MUSD-DISTRICT OFFICE
STREET_NUMBER
2901
Direction
E
STREET_NAME
LOUISE
STREET_TYPE
AVE
City
MANTECA
Zip
95336
APN
19811004
CURRENT_STATUS
02
SITE_LOCATION
2901 E LOUISE AVE
P_LOCATION
99
P_DISTRICT
003
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.
/
61
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
16 <br /> On July 12, 1993, an area 20 feet by 35 feet at the south end of the excavation was deepened to a <br /> depth of approximately 23 feet Confirmation soil and grab groundwater samples were collected <br /> on July 12, 1993 at the locations shown on Figure 4 Samples were placed on ice, transported <br /> under chain-of-custody documentation to Sparger Technology and analyzed for TPHg and <br /> BTEX The samples contained TPHg and BTEX above method detection limits Analytical data <br /> are summarized in Table 3 According to the results of confirmation soil samples (WIf, August <br /> 1993) residual hydrocarbon contaminated soil is mainly confined to the north end of the <br /> excavation The excavation was subsequently backfilled and paved with asphalt <br /> 4.2.1 Stockpiled Soil <br /> The soil generated duringthe tank removals and the overexcavation activities was stockpiled to the <br /> north of the site The soil was stored on visquene plastic until samples could be collected to determine <br /> its disposition On December 4, 1994, soil samples were collected from the locations shown on Figure <br /> 5 The samples were placed on ice and transported under chain-of-custody documentation to Argon <br /> Laboratories in Ceres, California The samples were composited in the laboratory at 4 to 1 and <br /> analyzed for TPH& TPHd, and BTEX The samples contained no detectable concentrations of TPH& <br /> TPHd, or BTEX Analytical results are summarized to Table 4 The soil stockpile is estimated to be <br /> approximately 1,600 cubic yards <br /> On April 4, 1996, Smith Environmental personnel collected 18 soil samples from the stockpiled sod <br /> Samples were placed on ice and transported under chain-of-custody to Argon Laboratories The <br /> samples were composited in the lab at 2 to 1 ratio and analyzed for TPHg, TPHd, and BTEX The <br /> samples contained no detectable concentrations of TPH& TPHd, or BTEX Analytical results are <br /> summarized in Table 4 and laboratory reports are contained in Appendix C <br /> 4.3 Assessment of Soil Contamination <br /> On October 10 and 11, 1994, RESNA personnel supervised advancement of five soil borings <br /> (SB2, SB3, MW 1, MW2, MW3) at the site to depths ranging from approximately 15 to 30 feet <br /> below grade Three of the borings, NMI, MW2, and NM, were completed as groundwater <br /> monitoring wells The boring locations are shown on Figure 2 <br /> ' Drilling was conducted by Spectrum Exploration, Inc (C57# 512289) utilizing a hollow stem <br /> auger drill ng A field geologist continuously fogged all drill cuttings and cored soil samples <br /> Descriptions of soil types encountered and sample collection intervals are included on the <br /> bonng/well logs in Appendix D Cored soil samples were collected at five foot intervals using a <br /> 2-inch diameter split-spoon sampler containing three brass tubes A photo ionization detection <br /> ' meter (PID) was used as a field screening device for the detection of petroleum hydrocarbon <br /> vapors in drill cuttings and cored samples Soil samples collected at approximately 10 5 and 16 <br /> feet below grade were selected for laboratory analysis Soil samples were placed on ice and <br /> transported under chain-of-custody to Argon Labs for analysis The samples were analyzed for <br /> TPHg, TPHd, and BTEX The analytical results for soil are summarized in Table 5 <br /> w 1943371cbs=doe 3 <br /> • <br /> SMTH <br /> 1 <br />
The URL can be used to link to this page
Your browser does not support the video tag.