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USEPA Region 2 Vapor Intrusion Study. Cayuga Groundwater Contamination Site March 4, 2009. Site Background. 2001 to Present – EPA Field Study Installed 23 Multi-level monitoring wells Seven Rounds of groundwater sampling (>500 groundwater samples)
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USEPA Region 2Vapor Intrusion Study Cayuga Groundwater Contamination Site March 4, 2009
Site Background • 2001 to Present – EPA Field Study • Installed 23 Multi-level monitoring wells • Seven Rounds of groundwater sampling (>500 groundwater samples) • Quarterly water level measurement and geophysics support from USGS • Surface water/sediment samples (Owasco Outlet, Crane Brook, Union Springs)
Site Background (cont’d) • Cayuga County DOH –1999-2008 - Multiple rounds of residential well sampling (>600 samples) • Remedial report and risk evaluations in progress
Ongoing Field Study Efforts • Additional field work under NYSDEC/EPA: • Additional monitoring wells • Additional groundwater sampling • Geophysical survey • Hydraulic testing
Vapor Intrusion Study • EPA field study indicates that chlorinated volatile organic compounds (CVOCs) are present in groundwater • CVOC-contaminated groundwater extends from West Genesee St. to Union Springs • CVOCs in groundwater can form vapors that migrate in the subsurface • Potential exists for vapors to enter buildings • Vapor sampling is being conducted to determine if vapors are present in buildings
Vapor Sampling Locations • Selection of locations based on existing data: • Location of CVOCs in groundwater • Location of CVOCs in surface water • Residential well data • Human health risk evaluation • Geologic/Hydrogeologic factors • Depth to contaminated groundwater (<100 feet) • Degree of bedrock fracturing • Presence of clean groundwater above contaminated zones
Vapor Sampling Locations (cont’d) • Three areas identified that meet initial criteria: • South of West Genesee Street • Pinckney Road/Overbrook Drive Area • Union Springs
South of West Genesee Street • Insert Figure 1
Pinckney/Overbrook Area (east) • Insert Figure 2
Union Springs Area (south) • Insert Figure 3
Residential Vapor Intrusion Sampling Procedures • Presented by: • Gary Newhart – EPA
Ventilation Ventilation Interior space Ambient air Ambient air Vadose Zone Subslab soil gas intruding into interior space Groundwater Contamination Vapor Pathway into Buildings
Key Questions for Vapor Intrusion Impacts • Does groundwater or soil contamination exist? • Yes, in this case, so we move to the next step • Does subsurface gas contamination exist above guidelines? • Answered through collection of subslab soil gas • 3. If subsurface gas does exist above guidelines, is it entering the interior space? • Answered through collection of indoor air samples • 4. If gas contamination exists in the residence, are the concentrations elevated and related to contamination • - Answered by comparing results to health-based guidelines and conducting lifestyle and ambient investigation
Monitoring and Sampling Strategy • Initial Sampling • - Subslab Location + Ambient (outdoor) • 2. Subsequent SUMMA Canister Sampling • - Subslab Location • - Basement Location • - First Floor Location
What is a VI Matrix and how is it developed? • Chemical-specific • Considers potential health effects from long-term exposures for residents including children and adults • Exposure Frequency of 24 hours/day and 350 days/year • Exposure Duration is 30 years • Has comparison values for subslab soil gas and indoor air
Vapor Intrusion Matrix for a Carcinogenic Chemical Step 1. Does the subslab concentration exceed x ug/m3?No = Vapor intrusion investigation is over for this building Yes = Consider indoor air sampling Step 2. Evaluate subslab and indoor air concentrations.
Vapor Intrusion Matrix for a Non-Carcinogenic Chemical Step 1. Does the subslab concentration exceed x ug/m3?No = Vapor intrusion investigation is over for this building Yes = Consider indoor air sampling Step 2. Evaluate subslab and indoor air concentrations.
VI Decisions • VI Profile • Subslab • Indoor/Basement • Indoor/First Floor Living Space • Ambient Concentrations • Confounding Internal Sources • Confounding External Sources
Key Points in VI Decisions • Decision to remediate is not based on one piece of information • Complexity and uncertainty is associated with the fate and transport mechanism of vapors • Multiple lines of evidence are used in the decision making • Rely on “VI Team” to ensure consistency in decisions within EPA Region 2
Contact Information • USEPA Remedial Project Manager - Isabel Rodrigues – (212) 637-4248 • USEPA Community Involvement Coordinator– Mike Basile - (716) 551-4410 • New York State DOH – Krista Anders – (518) 402-7860 • New York State DEC – Kevin Kelley – (315) 426-7421 • Cayuga County DOH – Eileen O’Conner (315) 253-1405