Methane at Bioremediation Sites Todays Talk Why did I write this - - PowerPoint PPT Presentation

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Methane at Bioremediation Sites Todays Talk Why did I write this - - PowerPoint PPT Presentation

Methane at Bioremediation Sites Todays Talk Why did I write this guidance? What has been the result? Answer some frequently asked questions. Why bother? I havent noticed any remediation sites exploding. Groundwater data where


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Methane at Bioremediation Sites

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Today’s Talk

  • Why did I write this guidance?
  • What has been the result?
  • Answer some frequently asked questions.
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Why bother? I haven’t noticed any remediation sites exploding.

  • Groundwater data where methane exceeds its

solubility.

  • Monitoring well methane gas exceeding the

methane lower explosive limit (LEL).

  • Documented soil gas/sub-slab monitoring

points exceeding the methane LEL.

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Ethanol in Indianapolis 30 mg/L Ground water methane!

Date Methane mg/L 02/12/08 22.490 09/16/08 20.139 02/04/09 12.526 09/10/09 23.282 03/02/10 19.503 09/13/10 31.211 03/22/11 19.606

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Please Plan Ahead

  • Be aware you might generate high levels of

methane.

  • Be prepared to address possible methane

issues in your remediation work plans.

  • Consider the increased cost if you have to

mitigate.

  • Make sure it’s technically feasible if necessary

to mitigate.

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Initial Thoughts

  • Goal is to figure out if methane has enough
  • xygen to attenuate before it has ‘space’ to

collect.

  • Precautionary measure for receptors might be

advisable.

  • Ground water is a good place to start since

most reductive dechlorination sites are monitoring methane in ground water.

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Initial Thoughts

  • Soil gas methane in the contaminant source

area exceeding 10% of the LEL or ground water exceeding 10 mg/L indicates the need to monitor methane in the direction of receptors.

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Initial thoughts

  • If bioremediation is induced beneath a structure,

implement subslab methane monitoring and/or mitigation including the installation of a continuous gas monitor in the lower level of the structure if appropriate.

  • Indoor air exceeding 25% of the LEL should result

in building evacuation until mitigation and a comprehensive methane monitoring plan are implemented.

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No NO Yes No Yes Yes No No No Yes Yes Yes

Initiate methane

  • monitoring. Are

concentrations greater than 10% LEL at receptors? Mitigation and Possible Evacuation. Source Area Groundwater > 10,000ug/l or Soil Gas > 10% of LEL? Receptors

  • r

Structures Present? Anaerobic conditions directly beneatha structure? <25% LEL at the Property Border? Done- Monitor Quarterly Done- Monitor Quarterly Done- Monitor Quarterly Mitigation and Possible Evacuation.

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FAQs

Why does the guidance refer to landfill guidance? Landfills are completely different.

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Landfills and remediation sites are the same regarding methane

  • Electromotive potential (anaerobic) amenable to

methanogens.

  • Place for methane to build to 5-10%.
  • Ignition source.
  • No time element. Methane does not have to be

generated for thirty years to be a hazard.

  • Consider nested monitoring wells to gauge

attenuation.

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Landfills and remediation sites are different

Cleaners Landfill

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FAQs

  • Contaminant concentrations aren’t that high

at my site. Do I need to worry about methane?

  • Yes. It’s not the contaminant concentration

that matters. A methanogen’s energy source is not the contaminant, it is what you are injecting.

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FAQs

  • What about Petroleum sites?
  • Concentrations would be applicable. ITRC

guidance on ethanol fuels is listed in the references.

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FAQs

  • What frequency should I monitor?
  • Site-specific determination.

– Monthly

  • Decrease frequency if lines of evidence indicate no

issue.

  • Increase frequency if methane is an issue.
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Soluble Carbon Injections

Ground water mg/L Soil Gas %LEL %CH4 04/27/11 0.840 06/21/11 17 08/10/11 21 09/19/11 512 25.6 09/20/11 302 15.1

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Soluble Carbon Injections

Ground water mg/L Soil Gas %LEL %CH4 10/28/11 264 13.2 11/29/11 0.290 12/15/11 346 17.3

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Enhanced Reductive Dechlorination Injections Injection Depth: 20-32 ft bgs Injection Date: Aug 2007, June 2009, July 2013 Ground water at @20 ft bgs

MMW8S MMW1S 14-24 ft bgs 10-20 ft bgs ug/L ug/L 2/28/2013 12,000 54 5/14/2013 8,600 75 9/24/2013 25,000 24,700 11/13/2013 27,400 427 2/26/2014 22,100 162

ERD Injections

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FAQs

  • What does intrinsically safe mean?
  • Generally the electrical components are

housed so that the spark can’t get out or the casing is reinforced to withstand an explosion.

  • National Electrical Code (NEC) and

Underwriters Laboratory (UL) define and rate.

  • $$$
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FAQs

  • I have methane above the explosive limit. Do I

need to come unglued?

  • Maybe. Look at the complete conceptual
  • model. Is there a place for the methane to

collect before it has attenuated? It’s hard to get the subsurface to explode. Watch for shallow ground water beneath structures.

  • Know your site.
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References

  • Eklund, B.; 2010; Proposed Regulatory Framework for Evaluating the Methane

Hazard due to Vapor Intrusion; presented at the AWMA Vapor Intrusion Conference; September 29-30, 2010, Chicago, IL; available online at: http://events.awma.org/education/vapor-proceed.html

  • ITRC (Interstate Technology Regulatory Council); September 2011;: Biofuels:

Release Prevention, Environmental Behavior, and Remediation

http://www.itrcweb.org/guidancedocuments/biofuels/biofuels-1.pdf .

  • Kean, Judy; Graves, Duane; Lodato, Mike; Enhanced Reductive Dechlorination

and the Relationship Between CIS-1,2-DCE Accumulation and

  • Methanogenesis. Available online at:

http://www.drycleancoalition.org/download/enhanced_reductive_dechlor.pdf

  • USGS. (2006). Methane in West Virginia Ground Water; USGS Fact Sheet 2006-

3011; available online at: http://pubs.usgs.gov/fs/2006/3011/pdf/Factsheet2006_3011.pdf

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Contact Information

Susan Horein Environmental Engineer shorein@idem.IN.gov (317)-234-4155