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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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  • © 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

  • 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

  • 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

    .3

    PFAS Sources, Regulation and Treatment Challenges

  • 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

  • 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

    .5

  • Bench Test Methodologyand Results

    Isotherm Testing

    Column Testing

    Regeneration

    Synthetic Media surfaces as potential solution

  • 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

    7

    Media Selection

    Ion Exchange

    Polymeric

    Carbonaceous

  • Isotherm Results

    .8

  • 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 .

  • 10

    Bench Test Setup

    Add a coloured

    transparent

    segment and

    caption if

    required.

    .

    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.

  • 11

    Adsorption and Regeneration of Leading Resins from Column Testing

    -

    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

  • 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

    12

    Final Outcome of Bench Test

    Add a coloured

    transparent

    segment and

    caption if

    required.

    Sorbix A3F

    A strong base anion exchange resin

  • Pilot Test Setup and Methodology

    Influent Characterization

    Process Design

    Results

  • Site 8 Layout

    14

  • 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

    15

    • Concentrations approximately 15 times higher than bench test

  • © Amec Foster Wheeler 2016.16

    Pilot Test Process Flow Diagram

  • © Amec Foster Wheeler 2016.17

    Pilot Test General Arrangement

    Process

    pumps

    Cartridge filters

    for solids removal

    GAC (front)

    and resin

    (rear) vessels

  • © Amec Foster Wheeler 2016.18

    Ion Exchange Vessels

  • © 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

  • PFOA breakthrough at 5-min EBCT

  • © 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

  • PFOS breakthrough at 5-min EBCT

  • © Amec Foster Wheeler 2016.

    Precursor

  • © Amec Foster Wheeler 2016.

    Precursor

  • © Amec Foster Wheeler 2016.

    3 Carbons

  • © Amec Foster Wheeler 2016.

    4 Carbons

  • © Amec Foster Wheeler 2016.

    6 Carbons

  • © Amec Foster Wheeler 2016.

    6 Carbons

  • © Amec Foster Wheeler 2016.

    7 Carbons

  • © Amec Foster Wheeler 2016.

    7 Carbons

  • © Amec Foster Wheeler 2016.

    9 Carbons

  • © Amec Foster Wheeler 2016.32

    Volume Treated Before Breakthrough:All Observed PFAS

  • © 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

  • Why is Ion Exchange so effective?

    34

    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

  • Path Forward - 2 full-scale designs

    Aims

    600

    gpm

  • Path Forward - 2 full-scale designs

    Site 8

    200

    gpm

  • Full Scale Application

    37

    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

  • 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

  • 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

  • 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?