Vapor Intrusion Assessment...

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Delivering sustainable solutions in a more competitive world

Vapor Intrusion Vapor Intrusion Assessment ToolsAssessment Tools

Derek W. TomlinsonDerek W. Tomlinson, M.A.Sc., P.Eng., M.A.Sc., P.Eng.Environmental Resources ManagementEnvironmental Resources Management

Exton, Pennsylvania, USAExton, Pennsylvania, USA28 October 200828 October 2008

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Overview

• What is Vapor Intrusion?• Guidance Documents• Investigative Tools• Management Options• Questions

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Photo: Dave Webb, Ill. DPH

Vapor Intrusion is Real(sometimes visible)

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Vapor Intrusion Definition

Vapor Intrusion (VI), the migration of a compound of concern (COC) vapor from a subsurface soil or groundwater source into the indoor air environment of an existing or planned structure. (ASTM 2008)

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Vapor Intrusion

IndoorAir

Vadose Zone Soil

Gas

Soil and Groundwater

Contamination

Commercial/Industrial Worker

Working over Plume Without BasementResident Living over Plume

Basement or Crawl Space

(USEPA 2002, ITRC 2007)

Migration of volatile chemicals from the subsurface into overlying buildings

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Regulatory Vapor Intrusion Guidance

USEPA 2002Draft Guidance for Evaluating the Vapor Intrusion to Indoor Air Pathway from Groundwater and Soilshttp://epa.gov/osw/hazard/correctiveaction/eis/vapor.htm

ITRC 2007 Vapor Intrusion Pathway: A Practical Guidehttp://www.itrcweb.org/teampublic_Vapor.asp

ASTM 2008Standard Practice for Assessment of Vapor Intrusion into Structures on Property Involved in Real Estate Transactions (ASTM E2600)http://www.astm.org/Standards/E2600.htm

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General Regulatory Process

• Federal and many State Guidance use multiple lines of evidence approach

• Typically three Tiers evaluating• Groundwater (Soil)

• Soil Gas

• Indoor Air

• Spatial relationship of indoor air contamination to subsurface contamination

• Modeling can also be used to assess

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Typical Screening Distances

Petroleum VOCs = 10 m (30 feet)

Other VOCs = 30 m (100 feet)

LNAPL = 30 m (100 feet) Petroleum VOCs = 10 m (30 feet)

Other VOCs = 30 m (100 feet)

-30m

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Multiple Lines of EvidenceApproach

1. Groundwater2. Soil gas3. Sub-slab soil gas4. Indoor air

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PetroChlorinated VOCs Freshwater Lens

Depth

Groundwater

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Groundwater Assessment Tools

• Direct-push tools• Membrane Interface Probe (MIP)

• Waterloo Profiler

• Passive diffusion bag samplers• Low-flow purging and sampling• Volume-averaged purge and sample

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Groundwater – Membrane Interface Probe (MIPs)

(Photo courtesy Geoprobe)

(image courtesy Geoprobe)

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SLIDE 13(Images courtesy R. Joseph Fiacco, Jr, ERM)

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Groundwater –Waterloo Profiler™

(Photo courtesy Geoprobe)

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SLIDE 15(Images courtesy R. Joseph Fiacco, Jr, ERM)

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(Image courtesy R. Joseph Fiacco, Jr, ERM)

Example Profiling Data

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Groundwater – Passive Diffusion Bag Samplers

• Use in monitoring wells

• Limited to VOCs• Diffusion of VOCs

through membrane• 2 week

implacement

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Groundwater – Traditional Methods

• Low-Flow Purging and Sampling• Samples collected at a low flow 100 to 250 mL/min

• Parameters (DO, ORP, Eh, pH) monitored until stable and sample collected

• Able to target shallow water

• Volume-averaged Purge and Sampling• Not recommended for new data related to vapor

intrusion as concentration averaged

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In Well Transport

• Wells that are screened over a large distance may sample deeper water

• Key for VI assessment is shallow water

Silty Sand

Sand

Clay

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LNAPL - Laser Induced Florescence (LIF)

(courtesy Dakota Technologies)

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Soil Gas Assessment Methods

• Active sampling• Direct push temporary and permanent points

• Permanent wells

• Passive sampling• Passive diffusion samplers (e.g., Gore Sorbers)

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Soil Gas Sample Locations

Building Exterior> 3 m (10 ft) from slab

Sub-SlabSamples collected

beneath the slab

Near Slab< 3 m (10 ft) from slab

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Soil Gas Sample Locations

• Soil gas profile may be affected by building

• More significant for biodegradable compounds

(Johnson & Abreu, 2006)

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Soil Gas Sampling Wells

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Temporary Rod Used for Sampling

(Photo courtesy B. Hartman, H&P Mobile Geochemistry)

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Temporary Soil Vapor Implants

(Photo courtesy B. Hartman, H&P Mobile Geochemistry)

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Installing Sub-slab soil point

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Permanent Temporary

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Typical fittings – Permanent Point

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Soil Gas Point Tightness Testing• Add helium (He) to shroud• Sample directly with helium

detector from the soil gas point

• Collect Tedlar and screen air within Tedlar

• Laboratory screening

• <5% He in extracted air point passes test

• Fails re-seal and re-test

He

He

HeHe He

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Purging Permanent Subslab Soil Gas Point

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Subslab Sample Collection- Permanent Point

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Sub-Slab Sample CollectionSubslab Sample Collection – Temporary Point

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Near Slab Sample Collection– Permanent Point

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Soil Gas – Passive• GORE-TEX® Membrane

• Chemically inert, waterproof, vapor permeable

• Designed for vapor diffusion• Hydrophobic, engineered sorbents

• VOCs, SVOCs, PAHs

Sampler insertion

Hammer drill

Slam barHammer drill Module insertion

(photos & image courtesy J. HodnyW. L. Gore & Associates, Inc.)

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Passive SamplerExample Results- TCE

(Image courtesy Dr. J. Hodny, W. L. Gore & Associates, Inc.)

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Indoor Air Assessment Methods

• Active sampling• Summa Canisters

• Sorbent Tubes

• Passive sampling• Passive diffusion samplers (e.g., Gore Sorbers)

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Indoor Air Sampling - Summa Canisters

• Summa Canister used for indoor air sampling

• 30 day hold times• 6 L stainless steel canister with flow

controller, moisture trap, and pressure gauge

• Regulated to collect either:• 8 hr sample – Commercial

• 24 hr sample – Residential

• Analyzed via either TO-14a or TO-15

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Sample Volumes

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Indoor AirSampling

• Typically, co-located with sub-slab location

• Sample breathing zone

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Indoor Air Sampling – Sorbent Tubes

• Based on VOC or SVOC, tubes are different and flow rates/sample rate/ times vary

• Must be shipped at 4°C• Limited hold times• Analyzed via TO-17

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Passive Air Sampling

• AirCrawlspace airIndoor air

(photos & image courtesy J. HodnyW. L. Gore & Associates, Inc.)

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Assessing Lines of EvidenceAssemble as many lines as necessary

Chemistry of Air Samples:Breakdown productsIn-building sourcesOutdoor air qualityFresh vs weathered petroBasement vs upper floors

ModelingJohnson & EttingerSite-specific inputs

Totality of Evidence For VI

Totality of Evidence Against VI

Conceptual Site Model

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Management Options

1. Remediation2. Institutional Controls3. Mitigation

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Mitigation Methods

• Passive Systems• Vapor Barriers• Passive Venting

• Active Systems• Sub-Slab Depressurization• Sub-Membrane Depressurization• Sub-Slab Pressurization• Building Pressurization• Indoor Air Treatment

(ITRC, 2007)

(Courtesy Liquid Boot)

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Questions?

Derek W. Tomlinson, M.A.Sc., P.Eng.derek.tomlinson@erm.com

Environmental Resources Managementwww.erm.com

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