My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
ARCHIVED REPORTS XR0009281
EnvironmentalHealth
>
EHD Program Facility Records by Street Name
>
E
>
EL DORADO
>
2315
>
2900 - Site Mitigation Program
>
PR0544690
>
ARCHIVED REPORTS XR0009281
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
7/24/2019 1:16:34 PM
Creation date
7/24/2019 11:54:08 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0009281
RECORD_ID
PR0544690
PE
3528
FACILITY_ID
FA0005839
FACILITY_NAME
CASTLE AUTOMOTIVE REPAIR INC.
STREET_NUMBER
2315
Direction
N
STREET_NAME
EL DORADO
STREET_TYPE
ST
City
STOCKTON
Zip
95204
APN
12510017
CURRENT_STATUS
02
SITE_LOCATION
2315 N EL DORADO ST
P_LOCATION
01
P_DISTRICT
002
QC Status
Approved
Scanner
SJGOV\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.
/
95
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
LABORATORY NARRATIVE <br /> LT Modified TO-3 <br /> Geological Technics <br /> r., <br /> Workorder#0407517 <br /> �- Three 1 Liter Tedlar Bag samples were received on July 28, 2004. The laboratory performed analysis for <br /> volatile organic compounds in air via modified EPA Method TO-3 using gas chromatography with photo <br /> ionization.and flame ionization detection. The method involves concentrating up to 200 mL of sample. The <br /> �' concentrated aliquot is then dry purged to remove water vapor prior to entering the chromatographic system. <br /> The TPH (Gasoline Range)results are calculated using the response factor of Gasoline and correspond to the <br /> range of hydrocarbons fiom C5 to C10. A molecular weight of 100 is used to convert the TPH (Gasoline <br /> `'' a Ran my result to <br /> Range)pp ug/L. See the data sheets for the reporting limits for each compound <br /> Method modifications taken to run these samples include: <br /> Requirement TO-3 ATL Modifications <br /> Daily Calibration Standard Prior to sample analysis Prior to sample analysis and atter the analytical batch</=20 <br /> Frequency and every 4-6 hrs samples <br /> Initial Calibration Calculation 4-point calibration 5-point calibration using average Response Factor <br /> using a linear <br /> regression model <br /> Initial Calibration Frequency Weekly When daily calibration standard recovery is outside 75- 125 <br /> %,or upon significant changes to procedure or <br /> instrumentation <br /> Moisture Control Nafion system Sorbent system <br /> Minimum Detection Limit(MDL) Calculated using the 40 CFR Pt. 136 App. B <br /> equation DL=A+3.3 S, <br /> where A is intercept of <br /> calibration line and S is <br /> the standard deviation <br /> LN of at least 3 reps of <br /> low level standard <br /> Preparation of Standards Levels achieved Levels achieved through loading various volumes of the gaq <br /> through dilution of gas mixture <br /> mixture <br /> Lo Receiving otes <br /> Sample identifications on the chain of custody were not unique. The time of collection was added to the <br /> identification to assure uniqueness. <br /> L' Analytical Notes <br /> There were no analytical discrepancies. <br /> Definition of Data OuaUj&gFlags <br /> Seven qualifiers may have been used on the data analysis sheets and indicate as follows: <br /> B - Compound present in laboratory blank greater than reporting limit. <br /> J- Estimated value. <br /> E - Exceeds instrument calibration range. <br /> �- S - Saturated peak. <br /> Page 2 of 9 <br /> 4 <br />
The URL can be used to link to this page
Your browser does not support the video tag.