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PR0548753
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Entry Properties
Last modified
3/2/2026 11:33:41 AM
Creation date
3/2/2026 11:15:39 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0548753
PE
2959 - DTSC LEAD AGENCY SITE
FACILITY_ID
FA0027916
FACILITY_NAME
BOBSON CLEANERS, INC.
STREET_NUMBER
600
Direction
N
STREET_NAME
MAIN
STREET_TYPE
ST
City
MANTECA
Zip
95336
APN
22314117
CURRENT_STATUS
Active, billable
QC Status
Approved
Scanner
SJGOV\gmartinez
Supplemental fields
Site Address
600 N MAIN ST MANTECA 95336
Tags
EHD - Public
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Cleanup in Vulnerable Communities'Initiative Final Project Reference:Bobson Cleaners <br /> Discovery and Enforcement Discovery Project Number:60688620-5.1 <br /> Investigation Work Plan <br /> recommended over the use of summa canisters for the collection of indoor air data. However, passive or canister <br /> sampling may be used so long as the sampling protocols are in accordance with the Programmatic QAPP. The DI will <br /> utilize active indoor air sampling using cannisters per the Programmatic QAPP. <br /> Active indoor air samples will be collected in evacuated, individually-certified clean, stainless-steel Summa®canisters <br /> per the DTSC vapor intrusion guidance (2011).The samples will be submitted to Eurofins Air Toxins Laboratory in <br /> Folsom, California, an accredited analytical laboratory,for USEPA Method TO-15 SIM.When collecting indoor air <br /> samples for the evaluation of potential impact of contaminant releases,the following should be considered: <br /> • Indoor air samples should be collected over a 24-hour period for residential structures, over an 8-hour period for <br /> nonresidential structures, and over a typical school day for students.After vapor intrusion is confirmed, <br /> additional sampling events should be conducted to produce representative concentrations of the monitored <br /> compounds over the anticipated daily exposure period for building occupants. <br /> • All floors, including the basement, of a residential structure potentially subject to vapor intrusion should be <br /> sampled for indoor air quality. Based on Site-specific conditions, it may be necessary to sample additional units <br /> of an apartment building. Sampling devices should be located in the breathing zone, approximately 3 to 5 feet <br /> off the ground for adults and at lower sampling heights if the receptors of concern are children as in a daycare <br /> center or school. Samples should be collected in the center of the room, away from doors.At a minimum, it is <br /> recommended that sampling points include the primary living area and likely locations for subsurface vapor <br /> entry(typically the bathroom or kitchen). <br /> • When sampling commercial or industrial buildings,the number and locations of samples should be based on <br /> Site-specific conditions. Samples should be collected from primary work areas and near the points of vapor <br /> entry to help define the potential routes of entry such as sumps, elevator shafts or floor drains. For the initial <br /> indoor air sampling event, the samples should be collected during normal operation of the building's heating and <br /> air conditioning system. <br /> • Extra canisters, pressure gauges, and flow regulators should be taken into the field in case the integrity of some <br /> of the canisters are compromised or if some flow regulators and pressure gauges malfunction. Each sampling <br /> canister should have a dedicated vacuum gauge. Flow regulators should be configured to produce a constant <br /> sampling rate. Sampling canisters, along with all flow regulators and pressure gauges,should be 6-liter <br /> individually certified clean passivated canisters and gauges and analyzed using method TO-15 SIM, reported <br /> down to the laboratory's method detection limit(MDL). <br /> When sampling indoor air, ambient(outdoor)air should be sampled concurrently.The following should be considered <br /> when collecting ambient air samples: <br /> • When deploying samplers outdoors to quantify background conditions,the samplers should be protected <br /> against rainfall and direct sunlight, both of which could bias the sampling results. <br /> • Sampling devices should be located approximately 6 feet off of the ground. <br /> • Ambient sampling should be conducted concurrently with the indoor air sampling. <br /> • Ambient samples should be located away from gasoline stations, automobiles, gasoline powered engines,fuel <br /> and oil storage tanks, chemical storage areas, and dry cleaners. <br /> • Sampling devices should be placed at least 10 feet beyond a tree's drip line. <br /> • Ambient air samples collected on the predominately upwind side of a building should be placed at a distance <br /> equal to twice the height of the building. <br /> • Three ambient samples (plus one duplicate), at a minimum, should be collected during each indoor air sampling <br /> event.The ambient air samples should be placed around the building with respect to up, down, and cross the <br /> prevailing wind direction.This placement will account for changes in the wind direction throughout the day. <br /> • Ambient air samples will be collected in batch cleaned 6-liter stainless-steel Summa canisters. <br /> • Ambient air samples will be analyzed for using method TO-15 reported down to the laboratory's MDL. <br /> Applying these considerations,the following steps will be performed: <br /> Prepared for: Department of Toxic Substances Control AECOM <br /> 15 <br />
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