sustainable removal of poly- and perfluorinated alkyl ......2016/11/09 · presentation outline 1....
TRANSCRIPT
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© Amec Foster Wheeler 2016.
Sustainable Removal of Poly- and Perfluorinated Alkyl Substances (PFAS) from Groundwater Using Synthetic Media
Nathan Hagelin, Amec Foster Wheeler; Steve Woodard, ECT
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Presentation Outline
1. The team: Amec Foster Wheeler and ECT
2. PFAS sources, regulations and treatment challenge
3. An effective PFAS treatment technology: Synthetic Ion Exchange
Media
1. Bench testing results
2. Pilot testing results
3. Full-scale design
4. Ongoing Research
2
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Sources of PFAS include firefighting
foam, TeflonTM, ScotchgardTM, Gore-
Tex®, etc.
USEPA has issued a combined
drinking water Health Advisory Level
(HA) for:
Perfluorooctane sulfonate
(PFOS) = 70 ppt
Perfluorooctanoic acid
(PFOA) = 70 ppt
The carbon-fluorine bond is one of
the strongest in nature
Granular activated carbon (GAC) is
accepted technology, but has
limitations
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PFAS Sources, Regulation and Treatment Challenges
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Challenge: Remediation –State of the Practice
Contaminants of Emerging Concern – few proven
technologies
Recalcitrant compounds – tough bonds to break
Lack of enforceable standards – wait and see approach
Emergency response mode – must use proven technology
to address completed exposure pathways
Most sites have not progressed beyond SI/RI
Few opportunities to date for field-scale trails – coming
soon
Proven technologies have limitations and are expensive
© Amec Foster Wheeler 2016.4
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An Urgent Opportunity for Technology
Widespread groundwater contamination emerging nationwide at
military installations, airports, refineries and industrialized communities
Widespread use of AFFF resulting in persistent groundwater plumes
Emergency response at municipal and private drinking water supplies
Fisheries shut down at some sites
Widespread and troubling media coverage
Proven technologies (primarily GAC) have shortcomings
Innovation needed
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Bench Test Methodologyand Results
Isotherm Testing
Column Testing
Regeneration
Synthetic Media surfaces as potential solution
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Synthetic media (resins)
removes various contaminants
from liquids, vapor or
atmospheric streams
Isotherm testing to identify
potentially effective media
Potential for indefinite reuse via
regeneration
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Media Selection
Ion Exchange
Polymeric
Carbonaceous
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Isotherm Results
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Bench Test PFAS Influent Concentrations
PFAS Compound Average Influent Concentration (µg/L)
PFOA 0.291
PFOS 3.33
Other PFAS 3.11
Total PFAS 6.73
9 .
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10
Bench Test Setup
Add a coloured
transparent
segment and
caption if
required.
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Control
Resin A
Resin B
Resin C
Feed
pump
Ground
-water
drum
Isotherm testing
narrowed down the
field to 3 top performing
synthetic media (ion-
exchange resins).
Column tests evaluated
the ability of the resins
to remove PFCs from
the groundwater.
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11
Adsorption and Regeneration of Leading Resins from Column Testing
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50,000
100,000
150,000
200,000
250,000
300,000
350,000
400,000
450,000
PF
AS
Mass (
ng
)
Resin A Resin B Resin C
PFAS MassDelivered
PFAS MassRemoved
PFAS MassRecovered
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Adsorption of PFCs to resin
below detection limits
No breakthrough observed
>99% regeneration of
media with solvent/brine
solution
Success of bench test led
to a pilot test for evaluation
at the Site
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Final Outcome of Bench Test
Add a coloured
transparent
segment and
caption if
required.
Sorbix A3F
A strong base anion exchange resin
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Pilot Test Setup and Methodology
Influent Characterization
Process Design
Results
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Site 8 Layout
14
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Pilot Test PFAS Influent Concentrations
PFAS Compound Average Influent Concentration (µg/L)
PFOA 11.5
PFOS 27.4
Other PFAS 55.6
Total PFAS 94.5
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• Concentrations approximately 15 times higher than bench test
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© Amec Foster Wheeler 2016.16
Pilot Test Process Flow Diagram
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© Amec Foster Wheeler 2016.17
Pilot Test General Arrangement
Process
pumps
Cartridge filters
for solids removal
GAC (front)
and resin
(rear) vessels
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© Amec Foster Wheeler 2016.18
Ion Exchange Vessels
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© Amec Foster Wheeler 2016.19
PFOA Breakthrough Results
0.001
0.01
0.1
1
10
100
0 10,000 20,000 30,000 40,000 50,000
PFO
A (
ug
/L)
Bed Volumes
Influent
Lead GAC
Lead Resin
Lag GAC
Lag Resin
EPA PFOA+PFOSHA
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PFOA breakthrough at 5-min EBCT
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© Amec Foster Wheeler 2016.21
PFOS Breakthrough Results
0.001
0.01
0.1
1
10
100
0 10,000 20,000 30,000 40,000 50,000
PFO
S (u
g/L
)
Bed Volumes
Influent
Lead GAC
Lead Resin
Lag GAC
Lag Resin
EPA PFOA+PFOSHA
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PFOS breakthrough at 5-min EBCT
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© Amec Foster Wheeler 2016.
Precursor
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© Amec Foster Wheeler 2016.
Precursor
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© Amec Foster Wheeler 2016.
3 Carbons
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© Amec Foster Wheeler 2016.
4 Carbons
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© Amec Foster Wheeler 2016.
6 Carbons
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6 Carbons
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7 Carbons
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© Amec Foster Wheeler 2016.
7 Carbons
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9 Carbons
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© Amec Foster Wheeler 2016.32
Volume Treated Before Breakthrough:All Observed PFAS
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© Amec Foster Wheeler 2016.33
Successful Regen at Pilot Scale
0.0
1.0
2.0
3.0
4.0
5.0
6.0
- 1,000 2,000 3,000 4,000 5,000 6,000 7,000 8,000
Tota
l PFA
S C
on
cen
trat
ion
(p
pb
)
Volume Treated (Bed Volumes)
Total PFAS Concentration from Lead IX Media Bed
Virgin Media
Post Regen
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Why is Ion Exchange so effective?
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Regeneration tells the story – ion exchange and adsorption combined
• Ion exchange resin is a strong adsorbent with ion exchange functionality
• The resin has high affinity for PFOA (carboxylate head) and PFOS (sulfonate head). Over time, PFOA and PFOS replace other anions on the resin
• Regeneration with solvent-brine solution
o High concentration salt dislodges the anionic heads of PFAS molecules from the resin
o High concentration solvent desorbs the PFAS molecules from the resin
IX Resin takes advantage of the unique properties of PFAS to both exchange ions and adsorb
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Path Forward - 2 full-scale designs
Aims
600
gpm
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Path Forward - 2 full-scale designs
Site 8
200
gpm
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Full Scale Application
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Lifecycle cost evaluation performed for full-scale 200 gpm system at Pease
AFB (Site 8)
Capital cost for Resin system is +/- 15% higher than GAC Media cost
Regeneration system
O&M cost is +/- 50% lower than GAC Resin has higher capacity
No media replacement
Even without regeneration (resin exchange program), lifecycle cost of resin
system is lower, depending upon PFAS mix
Two full-scale systems in detailed design Site 8: 200 gpm; AFFF source area
AIMS Site: 600 gpm; up-gradient of Haven drinking water well
Both systems scheduled to start up next Fall
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Ongoing R&D
© Amec Foster Wheeler 2016.38
►Iron sequestration at Pease using pilot scale vessels
►Multiple regenerations for resin longevity testing
►Distillation optimization for spent regenerant solution
► Reduce in solvent use
► Reduce distillation time
►Alternative regeneration solutions
► Ammonium chloride
► Ammonium hydroxide
► Ethanol
► Various salt combination
►Alternative media testing – Sorbix A3F compared to
► Other commercial IX media
► Carbonaceous GAC
► Coconut GAC
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Market Opportunities for IX
© Amec Foster Wheeler 2016.39
►Drinking water applications – UCMR3 data
► Municipal supply
► Point of use
►Pre-treatment or polish on GAC systems, and vice versa
►Single use / exchange or regeneration systems
►On-site regeneration
►Centralized regeneration
►Concentrated brine
disposal
►In-Situ Applications
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Nathan HagelinAmec Foster [email protected](207) 232-6968
Steve [email protected](207) 210-1551
Thank you to our co-authors:Brandon Newman, Amec Foster WheelerMike Nickelsen, ECT2
Questions?