My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
FIELD DOCUMENTS
EnvironmentalHealth
>
EHD Program Facility Records by Street Name
>
A
>
ACACIA
>
501
>
2900 - Site Mitigation Program
>
PR0508319
>
FIELD DOCUMENTS
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
2/1/2019 5:15:32 PM
Creation date
2/1/2019 4:25:06 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0508319
PE
2950
FACILITY_ID
FA0008031
FACILITY_NAME
FORTIFIBER
STREET_NUMBER
501
Direction
E
STREET_NAME
ACACIA
STREET_TYPE
ST
City
STOCKTON
Zip
95202
CURRENT_STATUS
01
SITE_LOCATION
501 E ACACIA ST
P_LOCATION
01
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.
/
110
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
' CGeo' icalTechnics Inc. • • Page 3 <br /> Fonzia <br /> SGWI Report <br /> Project No.: 774.2 <br /> April 1, 1999 <br /> ' providing sediment description using the USCS and field observations, were maintained by <br /> Ray Kablanow, a registered geologist. The boring logs are included in Appendix C. <br /> 1.2 Groundwater Sample Collection <br /> Upon reaching the capillary fringe a hydropunch type sampling tool was advanced into the <br /> groundwater and a groundwater sample was collected from each borehole. The samples were <br /> collected by use of a watera type sampling tube and gently transferred into 1-liter amber <br /> glass bottles. The bottles were capped, inverted, tapped, and checked for headspace bubbles. <br /> The bottles were then labeled and placed in a cooler at 4° Celsius for transport to the <br /> laboratory following Chain of Custody protocol. <br /> Clean surgical gloves are worn at all times in handling of the sample and sampling <br /> ' equipment. The bailer was washed in an Alconox solution and rinsed with clean water <br /> between used. <br /> 1.3 Laboratory Analyses <br /> ' Soil <br /> Two to four soil samples from each borehole were submitted to Sherwood Laboratories of <br /> ' Hilmar (State Certified Laboratory #1400). They were analyzed for the following: <br /> • Total extractable petroleum hydrocarbons as diesel, kerosene, motor and dielectric oils <br /> (TEPH-D, MO, DEO) by EPA method 3540/8015 (m). The detection limits for these <br /> compounds are listed below. <br /> etection imrts: I EPH-D, T , <br /> of mg Kg <br /> ' Water <br /> One groundwater sample from each borehole was submitted to Sherwood Laboratories of <br /> ' Hilmar (State Certified Laboratory #1400). They were analyzed for: <br /> • Total extractable petroleum hydrocarbons as diesel, kerosene, motor and dielectric oils <br /> (TEPH-D, MO, DEO) by EPA method 3510/8015 (m). The detection limits for these <br /> ' compounds are listed below. <br /> DetectionLim-its: TEPH-D, MO, DEO <br /> water µg <br /> 2.0 SITE GEOLOGY <br /> ' The soils beneath the site consisted of very dark brown, slightly plastic silty clay down to the <br /> capillary fringe, 6.5 to 7 feet bgs. The soil then became lighter brown very plastic clay down <br /> ' to approximately 11 feet bgs. In several of the boreholes, sandy clay was encountered from <br /> 11 to 12 feet bgs. <br /> Groundwater was encountered in the boreholes from between 6 and 8 feet bgs. <br /> The boring logs that summarize information and observations made in the field are included <br /> in Appendix C. <br />
The URL can be used to link to this page
Your browser does not support the video tag.