My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
FIELD DOCUMENTS
EnvironmentalHealth
>
EHD Program Facility Records by Street Name
>
H
>
HOGAN
>
5154
>
3500 - Local Oversight Program
>
PR0545283
>
FIELD DOCUMENTS
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
2/3/2020 12:27:32 PM
Creation date
2/3/2020 11:38:30 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0545283
PE
3528
FACILITY_ID
FA0004712
FACILITY_NAME
WILLIAM BURKHARDT
STREET_NUMBER
5154
STREET_NAME
HOGAN
STREET_TYPE
LN
City
LODI
Zip
95240
APN
06112001
CURRENT_STATUS
02
SITE_LOCATION
5154 HOGAN LN
P_LOCATION
99
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.
/
94
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
`. ....1 <br /> �. 26 February 1996 <br /> AGE-NC Project No. 95-0152 <br /> Page 4 of 6 <br /> sampling was performed using a metric soil sampler loaded with two clean 2- by 3-inch brass sleeves. <br /> The ends of the lead sleeve were covered with teflon sheets, capped and sealed with tape. The sample <br /> was preserved in a container under ice and transported to a CAL for analysis of TPH-g, BTE&X, and <br /> methyl-tert-butyl-ether(MTBE). Analytical results of stockpile soil sample are included in Table 4. <br /> The laboratory report and chain-of-custody are included in Appendix D. <br /> ` 3.5. EQUIPMENT DECONTAMINATION <br /> All sampling tools and brass sleeves used for sample collection were thoroughly rinsed with clean <br /> ` water after washing with a solution of Alconox. All Geoprobe rods were cleaned prior to <br /> advancement in each soil probe boring. <br /> 3.6. BORING LOGS <br /> During drilling activities, sample duplicates were described on boring logs using the Unified Soil <br /> Classification System (USCS), and monitored for the presence of organic vapors using a photo- <br /> ionization detector(PID: Thermo Environmental 580A, 10.0 eV, calibrated to isobutylene). Boring <br /> logs are summarized in Appendix A. <br /> 4.0. FINDINGS <br /> 4.1. SOIL PROFILE <br /> In each soil probe boring, the general soil profile consisted of dark gray, partially-cemented, fine- <br /> grained silty sand from surface grade to depths of 23 feet bsg. Grey to brown, cemented, clayey silt <br /> was encountered from depths of 23 to 30 feet bsg. Grey to green, partially-cemented, fine- to <br /> medium- grained silty sand was encountered from 30 to 40 feet bsg in each probing. <br /> Organic vapors were detected in all excavation soil samples and soil probing samples from P 1 at <br /> concentrations up to 2,200 parts per million (ppm). No OVs were detected in samples from soil <br /> probes P2, P3 or P4. <br /> 4.2. LABORATORY RESULTS OF EXCAVATION SOIL SAMPLES <br /> TPH-g was detected in excavation soil samples at concentrations ranging from 770 ppm (B5, floor <br /> of excavation)to 3,500 ppm(B 1, west wall of excavation). Toluene, ethyl benzene and xylenes were <br /> detected in each excavation soil sample at concentrations up to 360 ppm (B1, west wall of <br />
The URL can be used to link to this page
Your browser does not support the video tag.