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Vertex Environmental Inc. June 15, 2017 Bruce Tunnicliffe Novel Adsorptive Method for Chlorinated Solvent Remediation

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Vertex Environmental Inc.

June 15, 2017

Bruce Tunnicliffe

Novel Adsorptive Methodfor Chlorinated Solvent Remediation

• Adsorptive Material– Activated Carbon– What is it?– How Is It Applied in the Subsurface?

• Case Studies– Dry Cleaner & the Sewer Line– Commercial London Site– Industrial Mississauga Site

• Questions

Outline

• Inexpensive Remediation

• Certainty of Remediation

• Long Term Remediation Solutions

• Sustainable Remediation

What Do Brownfield Developers Want?

Activated Carbon

Starting Materials

• Bituminous Coal• Coconut Shell• Lignite• Peat• Wood• Bone Char

Activated Carbon

5

Activated Carbon

Activated Carbon – Trapping Contamination

7

• Relative adsorption strength increases with molecule complexity– Multi-cyclic > Mono-cyclic > Aliphatic– Double bond > Single Bond– Chlorinated > Non-Chlorinated

Benzene(ppm)

Capacity(mg/g)

10 40

1 1

Ethylbenzene(ppm)

Capacity(mg/g)

10 325

1 53

C6H6 C8H10

• Mechanisms:• Trap the contamination within the GAC matrix

• Treat within the matrix

• BOS-100®

• For Chlorinated Solvents

• GAC & impregnated Iron

• BOS-200®

• For Petroleum Hydrocarbons

• PAC & Nutrients & Blend of Microorganisms

Adsorptive Carbon – Trap and Treat

Delivery

Hose from Pump

Injection TipInjectate

Bentonite Seal

Deepest Point of Injection

Injections using top-down approachSource: AST Environmental

Adsorptive Carbon – Trap and Treat

Case Studies

Case Study #1cVOCs Along Sewer Line

Case Study – Sewer Line

Case Study – Sewer Line

(ug/L)MW-DeepMax Conc

MW-ShallowMax Conc

PCE 4,680 3,410

TCE 4 5

DCE <0.50 <0.50

VC <0.20 <0.20

Total 4,680 3,415

VOC Groundwater Analytical

Case Study – Sewer Line

Dry Cleaner

Sewer Line

Case Study – Sewer Line

Case Study – Sewer LineShallow

Sewer Line

Deep

Sewer Line

Case Study – Sewer Line

• Zero Valent Iron (ZVI) Injection– August 2015, 3 days

– Vertical: 1.8 m to 4.6 m (shale)

– 2,400 kg of ZVI, with guar gum

– 7,000 L of slurry

– 8 injection locations

• Activated Carbon Injection– November 2016, 2 half-days

– Vertical: 1.8 m to 4.6 m (shale)

– 100 kg of BOS100

– 1,500 L of slurry

– 6 injection locations

– Careful delivery over specific vertical intervals

• Before Each Injection– Hydro-vac down to top of Sewer– Camera inside sewer at location of injection

Case Study – Sewer Line

Hydro-vac’ing Top of Sewer

Case Study – Sewer Line

Camera in Sewer

Injection using Geoprobe

Case Study – Sewer Line

Case Study – Sewer Line

Case Study – Sewer Line

Case Study – Sewer Line

Case Study – Sewer Line

Case Study – Sewer Line

Case Study – Sewer Line

(ug/L)Avg Conc

Before WorkAvg ConcAfter ZVI

Avg ConcAfter BOS

PCE 2,370 4.5 1.8

TCE 2 4.6 0.7

DCE <0.50 34 2.2

VC <0.20 23 2.0

Total 2,372 66 6.7

% Reduction - 97.2% 99.7%

VOC Groundwater Analytical – MW-Deep

Case Study – Sewer Line

(ug/L)Avg Conc

Before WorkAvg ConcAfter ZVI

Avg ConcAfter BOS

PCE 2,510 101 <0.20

TCE 3 163 <0.20

DCE <0.50 925 2.3

VC <0.20 115 5.3

Total 2,513 1,304 7.6

% Reduction - 45% 99.7%

VOC Groundwater Analytical – MW-Shallow

Conclusions

• ZVI Injection effective at remediating PCE

– Yet at the shallow MW, daughter products remain

• After BOS Injection:

– Lowest VOC gw concentrations recorded at those MWs

Case Study – Sewer Line

Case Study #2cVOCs Results from London Site

Case Study – London Site

Case Study – London Site

Injection: April 2017

Case Study – London Site

Case Study – London Site

Case Study #3cVOCs Results from Mississauga Site

Case Study – Mississauga Site

AEC-1

AEC-2

Questions?

Thank You for Your Time

Bruce Tunnicliffe

Vertex Environmental Inc.

(519) 249-9184 mobile

[email protected]

www.vertexenvironmental.ca