My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
REMOVAL_1995
Environmental Health - Public
>
EHD Program Facility Records by Street Name
>
C
>
CHRISMAN
>
35200
>
2300 - Underground Storage Tank Program
>
PR0505718
>
REMOVAL_1995
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
4/1/2020 11:52:50 AM
Creation date
11/2/2018 5:26:28 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2300 - Underground Storage Tank Program
File Section
REMOVAL
FileName_PostFix
1995
RECORD_ID
PR0505718
PE
2381
FACILITY_ID
FA0003299
FACILITY_NAME
Tracy Golf And Country Club
STREET_NUMBER
35200
Direction
S
STREET_NAME
CHRISMAN
STREET_TYPE
Rd
City
Tracy
Zip
95377
APN
25327019
CURRENT_STATUS
02
SITE_LOCATION
35200 S Chrisman Rd
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
Scanner
SJGOV\rtan
Supplemental fields
FilePath
\MIGRATIONS\C\CHRISMAN\35200\PR0505718\REMOVAL 1995.PDF
Tags
EHD - Public
There are no annotations on this page.
Document management portal powered by Laserfiche WebLink 9 © 1998-2015
Laserfiche.
All rights reserved.
/
93
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
_ 04 December 1995 <br /> AGE-NC Project No. 95-0183 <br /> Page 2 of 4 <br /> 3.0 PROCEDURES <br /> 3.1. SCOPE OF WORK <br /> _ Since no permit was secured for the tank removal, the PHS-EHD required a subsurface investigation <br /> at the eleventh tee area to evaluate whether or not the excavated soil was impacted by hydrocarbon. <br /> The scope of work was to comply with the requirement of the PHS-EHD. <br /> 3.2. DRILLING AND SAMPLING <br /> On 9 October 1995, eight soil borings (B 1 through 138) were advanced to depths of approximately <br /> 13 feet bsg at the site. Each boring was drilled using a truck-mounted drill rig equipped with 8-inch <br /> diameter hollow stem augers. Boring locations are illustrated on Figure 2. Cuttings and rinseate <br /> generated during drilling activities were containerized in properly labeled D.O.T. model 17H 55- <br /> gallon drums, and stored on-site in an area inaccessible to the general public. <br /> Each boring was sampled continuously beginning at a depth of 5 feet bsg utilizing a five-foot sampling <br /> core assembly. Upon sample retrieval, the core was removed from the assembly, and inspected by <br /> representatives of AGE and the PHS-EHD. After inspection of each five-foot sample core, the PHS- <br /> EHD directed an AGE representative to collect soil samples at selected intervals. <br /> Soil samples were preserved in brass sleeves by covering both ends of the sleeve with Teflon tape, <br /> capped and sealed with tape. Each sample was labeled with the following: boring location, depth, <br /> time, and sampler's initials. The samples were immediately stored under ice in a chilled container and <br /> transported to McCampbell Analytical, Inc. (MAI), a California State-certified laboratory . Each <br /> sample was analyzed for total petroleum hydrocarbons quantified as gasoline (TPH-g), volatile <br /> aromatics (benzene, toluene, ethyl benzene and xylene: BTE&X) and total lead in accordance with <br /> EPA methods 5030, 602, and 6010, respectively. <br /> 3.3. 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 hollow stem augers were steam-cleaned prior to <br /> advancement in each borehole. <br /> 3.4. LOGGING <br /> Soil was continuously monitored for the presence of organic vapors using a photo-ionization detector <br />
The URL can be used to link to this page
Your browser does not support the video tag.