My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
WORK PLANS_FILE 2
EnvironmentalHealth
>
EHD Program Facility Records by Street Name
>
F
>
F
>
5491
>
3500 - Local Oversight Program
>
PR0545028
>
WORK PLANS_FILE 2
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
12/6/2019 4:58:58 PM
Creation date
12/6/2019 2:58:31 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
WORK PLANS
FileName_PostFix
FILE 2
RECORD_ID
PR0545028
PE
3528
FACILITY_ID
FA0003919
FACILITY_NAME
VAN DE POL ENTERPRISES
STREET_NUMBER
5491
STREET_NAME
F
STREET_TYPE
ST
City
BANTA
Zip
95304
CURRENT_STATUS
02
SITE_LOCATION
5491 F ST
P_LOCATION
99
P_DISTRICT
005
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.
/
63
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
The sampling ports are brass connections,fitted with silicone <br /> septa,and threaded into a tapped hole in the system piping. SOP-14 <br /> Samples are collected by inserting a clean syringe into the SOIL VAPOR SURVEY SAMPLING:INDOOR AIR <br /> septum and the plunger actuated several times. Each SAMPLING WITH SUMA CANISTERS <br /> syringe should be purged of three syringe volumes before <br /> collecting the sample. On the fourth purge,the plunger is Indoor air sampling requires an eight hour air sample <br /> extracted slowly until the syringe is filled with a gas sample, obtained with 6-liter Suma canisters equipped with flow <br /> then the syringe is withdrawn and the needle immediately controllers(calibrated by the laboratory)to a flow rate of 11.5 <br /> plugged with a silicone stopper. The sample should be milliliters per minute(ml/min). Suma canisters are placed in <br /> placed in a non-refrigerated,dry cooler with sufficient each floor of the building at the center of the room being <br /> packing to eliminate breakage during transport. Cooling sampled at a height of approximately three to five feet above <br /> samples will cause condensation of moisture,thereby ground level,to simulate the typical breathing zone. More <br /> distorting laboratory analysis. than one indoor air sample may be required to determine a <br /> Duplicate air samples should be collected as in SOP-10. representative sample of all occupants in the building. <br /> Vapor samples are also subject to the same hold times and Associated with each indoor air quality sample is an ambient <br /> must be stored as stated in SOP-10 air sample that is collected outside the subject building. The <br /> ambient air quality sample consists of one 6-liter Suma <br /> canister with a sample collection time of 8 hours at a flow <br /> SOP-13 rate of 11.5 ml/min. The ambient air Suma canister is placed <br /> SOIL VAPOR SURVEY SAMPLING:"TEDLAR"BAG approximately 5 to 15 feet upwind of the subject building and <br /> SAMPLING TECHNIQUE 5 feet above ground level. Due to most buildings having an <br /> air exchange ratio of 0.5 to 1.0 exchanges per hour, <br /> The sampling equipment consists of a"Tedlar"bag sampling of the ambient air quality will begin at least one <br /> (available in 1,3,5,and 10 liter sizes),an SKC universal hour prior to the indoor air sample. <br /> sample pump,soil vapor probe,and 1/4-inch-diameter <br /> polyethylene tubing(approximately three feet long). With all Suma canister sampling the valve should be opened <br /> and the initial pressure should then be recorded to verify that <br /> A Roto-hammer or slam bar is used to obtain a three foot the Suma canister is under vacuum. The Suma canister is <br /> hole into the ground area,where the soil vapor sample will allowed to collect the soil vapor sample at a predetermined <br /> be collected. Once the hole has been formed the soil vapor duration(usually eight hours). After the sample has been <br /> probe will be inserted into the hole and advanced the collected record the final vacuum reading(approximately five <br /> remaining two feet,five feet total below ground surface pounds per square inch gauge(psig))to ensure that the flow <br /> (bgs),with the use of either a slide hammer,using a tee meter was working properly. Immediately following the <br /> adapter and using physical force. Once the vapor probe has sample collection,complete sampling information is <br /> been inserted into the ground a bentonite seal must be recorded on the label on the air sampling canister(e.g., <br /> formed between ambient air and the sample air. The sample ID,date,time,location,and temperature). The <br /> bentonite must be hydrated and create an air tight seal sample is placed in a non-refrigerated,dry cooler with <br /> around the probe.If required IPA can be placed on the joints sufficient packing to ensure against damage during <br /> of the vapor probe and analyzed for in the sample to ensure transport. Cooling samples will cause condensation of any <br /> that ambient air is not diluting the soil vapor survey samples. moisture within the air sample,thereby distorting laboratory <br /> analysis. <br /> Once the sample apparatus has been set up,new tubing will <br /> be connected to the inlet of the SKC sample pump. The Suma canister samples are subject to hold times of typically <br /> pump operates at a low flow purge rate of approximately 200 30 days and with some compounds a more rigid hold time of <br /> milliliters per minute to prevent air stripping of contaminants 14 days is required. <br /> from the soil. Once three volumes have been evacuated <br /> (minimum 4.2 minutes of sample time)a sample can be <br /> collected. Verification with a PID will determine when the <br /> maximum concentration is obtained and a sample should be <br /> collected. If measurable concentrations are not obtained <br /> with the PID after 7 purge volumes(10 minutes)a sample <br /> should be collected. Once a sample has been determined to <br /> be collected new tubing will be placed on the effluent of the <br /> sample pump running to the Tedlar bag,which should be <br /> filled to 3/4 of volume capacity. Caution should be taken not <br /> to overfill the sampling bag. The sample is placed in a non- <br /> refrigerated dry cooler with sufficient packing to eliminated <br /> damage during transport. Cooling samples will cause <br /> condensation of moisture within the sample,thereby <br /> distorting laboratory analysis. <br /> To minimize the potential for cross-contamination between <br /> air samples new polyethylene tubing will be used for every <br /> sample. <br /> Vapor samples are also subject to the same hold times and <br /> must be stored as stated in SOP-10 <br />
The URL can be used to link to this page
Your browser does not support the video tag.