My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
ARCHIVED REPORTS_DR OM AGREEMENT 2017 JANUARY
EnvironmentalHealth
>
EHD Program Facility Records by Street Name
>
G
>
GREAT VALLEY
>
0
>
2900 - Site Mitigation Program
>
PR0542222
>
ARCHIVED REPORTS_DR OM AGREEMENT 2017 JANUARY
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
2/5/2020 4:05:32 PM
Creation date
1/27/2020 2:25:13 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
DR OM AGREEMENT 2017 JANUARY
RECORD_ID
PR0542222
PE
2959
FACILITY_ID
FA0024253
FACILITY_NAME
MOUNTAIN HOUSE DEVELOPERS-SHEA HOMES
STREET_NUMBER
0
STREET_NAME
GREAT VALLEY
STREET_TYPE
PKWY
City
MOUNTAIN HOUSE
Zip
95391
CURRENT_STATUS
02
SITE_LOCATION
GREAT VALLEY PKWY
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.
/
148
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
Quality Assurance Project Plan for Removal Action <br /> APN 209-450-03,Mountain House,CA <br /> Page 8 <br /> 5.2.1 Laboratory Reagent Blanks <br /> A laboratory reagent blank is deionized water and it is extracted by the laboratory and analyzed as a <br /> sample. Analysis of the reagent blank indicates potential sources of contamination from laboratory <br /> procedures (e.g., contaminated reagents, improperly cleaned laboratory equipment, or persistent <br /> contamination due to presence of certain compounds in the ambient laboratory air). A reagent blank will <br /> be analyzed at least once each day for each method utilized by the laboratory for that day. <br /> 5.2.2 Field Equipment Blanks <br /> A field equipment blank is a sample that is prepared in the field by pouring distilled water into or through <br /> cleaned sampling equipment. The water is then collected and analyzed as a sample. Field equipment <br /> blanks are labeled such that they are not discernable as a blank to the laboratories. The field equipment <br /> blank gives an indication of degree of contamination from field procedures (e.g., improperly cleaned <br /> sampling equipment, cross-contamination). Field equipment blanks will be collected at a minimum <br /> frequency of at least one per ten, or 10 percent of primary field samples when non-dedicated equipment is <br /> utilized. The field equipment blanks will be analyzed using the same analyses requested for the associated <br /> primary samples. <br /> 5.2.3 Matrix Spike Samples <br /> Matrix spikes are performed by the analytical laboratory to evaluate the efficiency of the sample <br /> extraction and analysis procedures, and are necessary because matrix interference (that is, interference <br /> from the sample matrix,water or soil)may have a widely varying impact on the accuracy and precision of <br /> the extraction analysis. The matrix spike is prepared by the addition of known quantities of target <br /> compounds or acceptable surrogates to a sample. The sample is extracted and analyzed. The results of the <br /> analysis are compared with the known additions and a matrix spike recovery is calculated giving an <br /> evaluation of the accuracy of the extraction and analysis procedures. Matrix spike recoveries are reviewed <br /> to check that they are within acceptable range. However, the acceptable ranges vary widely with both <br /> sample matrix and analytical method. Matrix spikes and matrix spike duplicates will be analyzed by the <br /> laboratory at a frequency of at least one per twenty, or 5 percent of the primary field samples. Typically, <br /> matrix spikes are performed in duplicate, in order to evaluate the precision of the procedures as well as <br /> the accuracy. Precision objectives (represented by agreement between matrix spike and matrix spike <br /> duplicate recoveries) and accuracy objectives (represented by matrix spike recovery results) are based on <br /> statistically generated limits established annually by the analytical laboratory. It is important to note that <br /> these objectives are to be viewed as goals, not as criteria. If matrix bias is suspected, the associated data <br /> will be qualified and the direction of the bias indicated in the data validation report. <br /> 5.2.4 Field Duplicate Samples <br /> Field duplicate samples will be collected and analyzed to evaluate sampling and analytical precision. <br /> Field duplicates are collected and analyzed in the same manner as the primary samples. Agreement <br /> between duplicate sample results will indicate good sampling and analytical precision. Specific locations <br /> will be designated for collection of field duplicates prior to the start of field activities. Field duplicates <br /> will be collected at a frequency of 10 percent of the primary samples collected. The duplicate samples <br /> will be analyzed for all laboratory analyses requested for their primary sample counterparts. <br /> 5.2.5 Performance Evaluation Samples <br /> Double-blind performance evaluation (PE) samples may be submitted to the analytical laboratory during <br /> any Site investigation. These samples are used to assess the accuracy of analytical procedures employed <br /> CONDOR <br />
The URL can be used to link to this page
Your browser does not support the video tag.