Rapid Sub-Slab Soil Gas Sampling for Finding Sources and ... · Figure from DiGiulio et al., 2006,...

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Rapid Sub-Slab Soil Gas Sampling for Finding Sources and Assessing Vapor Intrusion Martin (Mort) Schmidt, CPG-08432 Ohio Brownfield Conference, May 24, 2012

Transcript of Rapid Sub-Slab Soil Gas Sampling for Finding Sources and ... · Figure from DiGiulio et al., 2006,...

Page 1: Rapid Sub-Slab Soil Gas Sampling for Finding Sources and ... · Figure from DiGiulio et al., 2006, Raymark Investigation, EPA/600/R -05/147 Tubing Connections LIMITATIONS Seal is

Rapid Sub-Slab Soil Gas Sampling for Finding Sources and

Assessing Vapor Intrusion

Martin (Mort) Schmidt, CPG-08432

Ohio Brownfield Conference, May 24, 2012

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Manufacturing Facility in Ohio w/ Tetrachloroethene (PCE) Contamination in Groundwater

New Area of Interest

PCE Decline

Persistent PCE Original Areas of Interest

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Geologic Cross Section

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Chlorinated Solvent Contamination

• Tetrachloroethene (PCE) above MCL of 5 ug/L

• Breakdown products, TCE & DCE in groundwater.

• Source of contamination assumed to be former PCE degreasers or ASTs.

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Former PCE Use & Storage

Degreasers

ASTs

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Former PCE Use & Storage

Degreasers

ASTs

Earlier Overfill

Up Gradient of Well

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Unexpected Groundwater Contamination

PCE 97 ug/L TCE 8.6 ug/L

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Source Investigation

• Earlier sampling inconclusive

• Recent sampling revealed unknown

source location

• Needed to locate all possible sources

Proposed to locate source with grid of subslab soil gas

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Typical Vapor Intrusion CSM

Figure Modified After ITRC, 2007

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Conventional Subslab Sample Point

Figure from DiGiulio et al., 2006, Raymark Investigation, EPA/600/R-05/147

Tubing Connections LIMITATIONS

Seal is Prone to Leak When Connecting Tubing Difficult Working Space Cement Set Up Time Extended Open Time

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Vapor PinTM

Barbed Connection

Threaded Shoulder

Silicone Seal

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Drilling Through Slab

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Installing Point

Flush Mount

Stick-Up

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Purging and Sampling

Equilibration Monitor O2 & VOCs While Purging Withdraw Soil Gas Inject Into Evacuated Glass Vials

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Example Purge Data

0

5

10

15

20

25

4:32 PM 4:33 PM 4:34 PM 4:35 PM

Con

cent

ratio

n

Time

O2 (%)

VOCs (ppm)

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Soil Sampling vs Soil-Gas Prospecting

• Less Obtrusive than Soil Sampling

• Real-Time Data Reduces Delays and Cost

• Soil Gas Detects Nearby Sources

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Field Soil-Gas (PID) Results

Don’t Blame the Usual Suspects!

Black: 100-100,000 ppb, Calibrated for Isobutylene (57-57,000 ppb, when corrected for PCE) Gray: ND

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Lab Soil-Gas Results Blue: PCE Red: TCE Yellow: cis-1,2-DCE Green : 111-TCA Gray: ND Max Total 58,000 ppb

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Lab GC to Field PID Correlation

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Lab Soil Results Blue: PCE Red: TCE Yellow: cis-1,2-DCE Green : 111-TCA Gray: ND Max Total 241,000 ug/kg

• Soil Data Used for Remediation • Contamination ~15 ft deep • Avoided Sampling North Half of Bldg

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Groundwater Data Blue: PCE Red: TCE Yellow: cis-1,2-DCE Gray: ND Max Total 272 ug/L

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Building Configuration 1924 SOIL Blue: PCE Red: TCE Yellow: cis-1,2-DCE Green : 111-TCA Gray: ND Max Total 241,000 ug/kg

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Building Configuration 1938 SOIL Blue: PCE Red: TCE Yellow: cis-1,2-DCE Green : 111-TCA Gray: ND Max Total 241,000 ug/kg

Manufacturing Started in 1933

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Building Configuration 1950 SOIL Blue: PCE Red: TCE Yellow: cis-1,2-DCE Green : 111-TCA Gray: ND Max Total 241,000 ug/kg

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Building Configuration 1952 SOIL Blue: PCE Red: TCE Yellow: cis-1,2-DCE Green : 111-TCA Gray: ND Max Total 241,000 ug/kg

Contamination Probably Between 1933 and 1952

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Building Configuration 2012 SOIL Blue: PCE Red: TCE Yellow: cis-1,2-DCE Green : 111-TCA Gray: ND Max Total 241,000 ug/kg

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Benefits

• Low Costs Enable Dense Sampling Grid • Low Risk of Missing Sources • No Interruption to Plant Operations • Reduced Time Before Remediation • Faster, More Quantitative than Passive Sorbents • Sample Points Reusable • Applicable to Vapor Intrusion – Draft SOP by MI DEQ

• (Vapor PinsTM are Commercially Available)

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Pick Two!

Good

Fast

Cheap Cheap

MOST STUFF VAPOR INTRUSION

Are You Kidding?

Are You Kidding?

We Obsess on Good at the Expense of Complete

Complete

Good

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Comparison of Results from Vapor PinsTM & SwagelokTM Fittings, Michigan DEQ

Data Collected with Michigan DEQ. Includes Multiple Dates, Labs, Container Types, & Analytes. Excludes VI-12.

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Comparison of Results from Vapor PinsTM to Permanent Implants, H&P Labs, California

Samples Collected Over 2 Days (Acetone removed)

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Innovative Soil-Gas Sampling

QUESTIONS?

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O2 Concentrations Don’t Suggest Leakage

Gray: Sample Point Black: Least O2 Depletion

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Manufacturing Facility in Northern Ohio

Work Plan Showed 14 Suspected Source Areas. Existing Soil Data Didn’t Match Groundwater Plumes

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248 Soil-Gas Samples 40 feet Grid at 5 feet Below Grade

Soil Gas via GeoprobeTM & Vials

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Once Again, Not the Usual Suspects

CI = 5,000 ppb Total HVOCs

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Problems with Conventional Subslab Points

• “Compression fittings should be avoided for all connections except at the Summa canister…” Soil Gas Sampling Protocol, Missouri Risk-Based Corrective Action Technical Guidance, 2006.

• “Some leakage may occur despite the investigator’s best efforts to seal the gap between the sampling probe and the slab hole…” Guidance for Evaluating Soil VI in WA State, Investigation and Remedial Action, Draft, October 2009.

• “7.3.1 If the probe assembly breaks loose from the anchoring compound while removing or installing the hex socket plug…” Vapor Intrusion Guidance, Ohio EPA, May, 2010.

• “Only two probes were sampled using EPA Method TO-15 because one probe P[B], became loose during sampling…” DiGiulio et al., 2006, EPA Raymark Investigation.

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Background VOCs

Figure from USEPA 2011, Background Indoor Air Concentrations, EPA /530/R-10/001