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OCTOBER 26-28, 2020 Colloidal Activated Carbon used to Reduce PFAS and Chlorinated Solvent Concentrations Ryan E. Moore, CHMM REGENESIS, Sr. Technical Manager/PFAS Program Manager

Colloidal Activated Carbon used to Reduce PFAS and ......MW-29c (21’-26’) Existing monitoring well New monitoring well Direct-push injection location Direct-push searcher core

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OCTOBER 26-28, 2020

Colloidal Activated Carbon used to Reduce PFAS and Chlorinated Solvent Concentrations

Ryan E. Moore, CHMM

REGENESIS, Sr. Technical Manager/PFAS Program Manager

OCTOBER 26-28, 2020

• Multiple PFAS point sources

• Comingled with PCE plume

• Identified at the property boundary and migrating off-site

• Many potential downgradient receptors

• Limited budget for field testing of remedial technologies

• Question:

Can CAC be used to mitigate the risk of PFAS to the sensitive receptors?

Problem Statement

OCTOBER 26-28, 2020

Grayling Army Airfield

Grayling, MI

OCTOBER 26-28, 2020

Site Description

• Founded 1913

• 147,000 acres

• Largest National Guard training center in the country

• Training facility for military, emergency responders, and private-sector from all over the world

• Home to the Grayling Army Airfield

Grayling Army Airfield (GAAF)

• 900-acre

• Built during World War II

Site Location:Camp Grayling Joint Maneuver Training Center

OCTOBER 26-28, 2020

Former Bulk Fuel Storage Area

GAAF

N

Aquifer:• Sand & Gravel with some clay

layers• ~250’/yr gw seepage velocity• Treatment Interval 15-27’bgs

Contaminant levels:• 10 µg/L PCE• 130 ng/L Total PFAS ( PFOS,

PFHxS)

Sensitive Receptors:• Residential areas• Surface water bodies• Property Boundary

OCTOBER 26-28, 2020

Former Bulk Fuel Storage Area

*1994 Photo

OCTOBER 26-28, 2020

Remediation History

Diesel fuel release, GW extraction, GAC, and

reinjection/infiltration for diesel fuel replaced by

1984

1988

GW extraction /ex situ bio-film treatment system to

improve diesel fuel remediation, not effective on newly discovered volatiles,

replaced by

GW extraction, GAC treatment for PCE

1992

1999

Air Sparge/ Soil Vapor Extraction system installed to address identified PCE source

areas

AS/SVE system expanded and operated continually until

2002

2001

2004

Recovery well network and GAC system expanded

GAC replaced by air stripper, which is still active

2006

2016

PFAS first discovered in monitoring wells; Precise dates

and locations are not known, but suspected from AFFF

VAP conducted at boundary fence identified PFAS at

property boundary

2017

2018

CAC Field Test Initiated in the Former Bulk Fuels

Storage Area

OCTOBER 26-28, 2020

Colloidal Activated Carbon

• Size: 1 – 2 µm• 2-3 OOM smaller than GAC (500-1,000 µm)

• Size of a red blood cell

• Suspended in water/polymer

• Distributes widely at low pressure

• Huge surface area that allows for extremely fast sorption

• Converts polluted aquifer into purifying filter

OCTOBER 26-28, 2020

Why Colloidal Activated Carbon?

• Limited destructive options

• Low Cost• No O&M costs or generated waste• Reapplication only after years/decades

• Localized containment/concentration of PFAS• Pair with future destructive technologies?

• In Situ Sequestration • Preventing contaminant migration • Removes exposure → removes the immediate

risk

OCTOBER 26-28, 2020

Treatment of Flux Zones and Control of Back Diffusion

OCTOBER 26-28, 2020

CAC: Modes of Action

• Mode of Action with PFAS:• Dynamic adsorption

• Not a permanent immobilization

• Effect: Increases the retardation of a PFAS plume• Groundwater retardation factor of 1

• Natural retardation factors for PFAS: 3-20

• Retardation factors achievable with CAC: 10,000• Containment for decades

• PlumeForce Modeling™

• Third Party Modeling (scientific articles available)

OCTOBER 26-28, 2020

Longevity-Third Party Review

• University of Waterloo, Waterloo, Ontario, Canada

• University of Toronto, Toronto, Ontario, Canada

• Porewater Solutions, Ottawa, Ontario Canada

• In Situ Remediation Services Ltd., St. George, Ontario, Canada

Longevity-Conclusions:• Increased by CAC concentration injected

• Length of treatment area

OCTOBER 26-28, 2020

Simple Plume Cut-Off Barrier

OCTOBER 26-28, 2020

Modeling in the Design Process

Considerations• Soil Type/Porosity

• Groundwater Seepage Velocity/Mass Flux

• Vertical Variations

• Barrier Thickness

• Carbon Demand

• Time

PlumeForce™• Long-Term Prediction Model

• Competitive Sorption and Degradation (if applicable)

• Compound Specific Isotherms

• VOCs, PFAS, etc.

OCTOBER 26-28, 2020

Modeling in the Design Process

Inputs• GW 219 feet/year

• Infinite Source

• PFOS 110 ng/L

• PFOA 8 ng/L

• PFHxA -HpA – HxS 112 ng/L

• Other PFAS 9 ng/L

• PCE 10 ug/L

• No degradation of any PFAS compound or CVOC’s

• Time (>75yrs)

Groundwater Flow

CAC

OCTOBER 26-28, 2020

Field Test Layout

2

1

3

4 5

6

7

8

9

GW Flow

5.8’

MW-29a (15’-20’) MW-29b (21’-26’)

MW-29e (15’-20’)MW-29d (21’-26’)

MW-29 (15’-20’)

MW-29c (21’-26’)

Existing monitoring well

New monitoring well

Direct-push injection location

10’

10’

6’

42’

OCTOBER 26-28, 2020

Field Test Layout

OCTOBER 26-28, 2020

Field Test Layout

2

1

3

4 5

6

7

8

9

GW Flow

sb9-4

sb1-2.5

5.8’

sb7-2.5

sb8-2.5

sb9-2.5

sb2-2.5

sb5-2.5

MW-29a (15’-20’) MW-29b (21’-26’)

MW-29e (15’-20’)MW-29d (21’-26’)

MW-29 (15’-20’)

MW-29c (21’-26’)

Existing monitoring well

New monitoring well

Direct-push injection location

Direct-push searcher core

10’

10’

6’

42’

OCTOBER 26-28, 2020

CAC-Distribution Confirmation

30 feet bgs

15 feet bgs

27 feet bgs

0 feet bgs

OCTOBER 26-28, 2020

Soil Vial Shake Test

CAC-Distribution Confirmation

OCTOBER 26-28, 2020

CAC-Distribution Confirmation

30 feet bgs

15 feet bgs

27 feet bgs

0 feet bgs

OCTOBER 26-28, 2020

Soil Vial Shake Test

CAC-Distribution Confirmation

OCTOBER 26-28, 2020

Field Test KitSample MW-29c

CAC-Distribution Confirmation

OCTOBER 26-28, 2020

Field Test Layout

2

1

3

4 5

6

7

8

9

GW Flow

sb9-4

sb1-2.5

5.8’

sb7-2.5

sb8-2.5

sb9-2.5

sb2-2.5

sb5-2.5

MW-29a (15’-20’) MW-29b (21’-26’)

MW-29e (15’-20’)MW-29d (21’-26’)

MW-29 (15’-20’)

MW-29c (21’-26’)

Existing monitoring well

New monitoring well

Direct-push injection location

Direct-push searcher core

CAC present in searcher core

10’

10’

6’

42’

OCTOBER 26-28, 2020

CAC-Distribution Confirmation

OCTOBER 26-28, 2020

OCTOBER 26-28, 2020

OCTOBER 26-28, 2020

2

1

3

4 5

6

7

8

9

sb9-4

sb1-2.5

5.8’

sb7-2.5

sb8-2.5

sb9-2.5

sb2-2.5

sb5-2.5

MW-29a (15’-20’) MW-29b (21’-26’)

MW-29e (15’-20’)MW-29d (21’-26’)

MW-29 (15’-20’)

MW-29c (21’-26’)

Existing monitoring well

New monitoring well

Direct-push injection location

Direct-push searcher core

CAC present in searcher core

10’

10’

6’

42’

Wells for water-level monitoring

to evaluate true flow-paths

New nested downgradient monitors

MW-29M

(15’-20’)

MW-29K

(15’-20’)

MW-29N

(15’-20’)

26’

45’

MW-29f (21’-26’)MW-29G (15’-20’)

MW-29h (21’-26’)

MW-29j (15’-20’)

GW Flow

OCTOBER 26-28, 2020

OCTOBER 26-28, 2020

OCTOBER 26-28, 2020

OCTOBER 26-28, 2020

Summary

• Very Successful Test• Verified distribution of CAC

• Sustained reductions of PFAS and PCE over time

• Anticipated to last for decades

• Low cost alternative for possible remediation

• ANSWER: Yes, CAC can be used to eliminated risk to potential multiple receptors!

OCTOBER 26-28, 2020

PFAS Research Articles

• In-Situ treatment of PFAS-impacted groundwater using colloidal activated carbon

• http://www2.regenesis.com/pfas-wiley-article

• Evaluating the longevity of a PFAS in situ colloidal activated carbon remedy

• http://www2.regenesis.com/grant-carey-wiley-remediation-journal

OCTOBER 26-28, 2020

Thank you

Patricia Byrnes LymanInvestigation/Remediation ManagerEnvironmental Section, JFHQMichigan Army National [email protected]

OCTOBER 26-28, 2020

Thank you!QUESTIONS?

• Ryan Moore, CHMM

• Sr. Technical Manager/PFAS Program Manager

[email protected]