My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
ARCHIVED REPORTS_1988_2
Environmental Health - Public
>
EHD Program Facility Records by Street Name
>
C
>
CORRAL HOLLOW
>
31130
>
4400 - Solid Waste Program
>
PR0440003
>
Archived Reports
>
ARCHIVED REPORTS_1988_2
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
7/17/2020 3:52:44 PM
Creation date
7/3/2020 11:04:07 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
1988_2
RECORD_ID
PR0440003
PE
4434
FACILITY_ID
FA0003698
FACILITY_NAME
CORRAL HOLLOW LANDFILL
STREET_NUMBER
31130
STREET_NAME
CORRAL HOLLOW
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
25303010
CURRENT_STATUS
01
SITE_LOCATION
31130 CORRAL HOLLOW RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
Scanner
SJGOV\rtan
Supplemental fields
FilePath
\MIGRATIONS\SW\SW_4434_PR0440003_31130 CORRAL HOLLOW_1988_2.tif
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.
/
278
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
Central Coast Analytical Services (Central Coast) of San Luis Obispo, <br /> California performed the analyses. As stated in Section 1 .0, the <br /> laboratory analyzed for VOCs using GC/MS instead of using a gas chro- <br /> matograph with electron capture and photoionization detectors as <br /> described in the Guidelines. Due to the elevated VOC concentrations <br /> in the gas samples, the laboratory had to use smaller sample volumes, <br /> thereby increasing their standard laboratory detection limits. As a <br /> result, the laboratory detection limits for ethylene dibromide and <br /> chloroform are above their respective regulatory detection limits. <br /> Analytical procedures are presented in Appendix D. <br /> 2.4.2 Integrated Surface Walk <br /> On May 25, 1988, the integrated surface sampler was used to collect a <br /> surface air sample of approximately 8 liters. The site was dry and no <br /> rain had fallen for 72 hours. The sampling probe was held approxi- <br /> mately 2 to 3 inches above the disposal site surface, and the collec- <br /> tion flow rate was set to approximately 333 cubic centimeters per <br /> minute. The actual flow rate was also recorded. A technician walked <br /> the grid continuously for 25 minutes through a course of approximately <br /> 2,600 linear feet. <br /> An anemometer and wind vane with a continuous recorder were installed <br /> at the landfill site to record wind speed and direction data. Both <br /> wind speed and direction were recorded continuously during the inte- <br /> grated surface sampling period. After the integrated surface walk <br /> area had been sampled, the wind speed data were reviewed. The wind <br /> data were evaluated and the sample was considered valid according to <br /> the criteria in the Guidelines since the average wind speed did not <br /> exceed 5 mph and instantaneous wind speed did not exceed 10 mph. <br /> Table 1 presents the integrated surface walk wind data. <br /> Immediately after collection, the bag sample was analyzed in the field <br /> with an organic vapor analyzer (OVA) for total organics measured as <br /> methane. Within 72 hours after collection, the bag sample was ana- <br /> PJ9 9390304.00D 2-3 Rev. 0 09/20/88 <br />
The URL can be used to link to this page
Your browser does not support the video tag.