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Danny Reible, University of Texas

Danny Reible, University of Texas · 2021. 3. 3. · 720 µg/kg PCB (10 ng/L) 360 µg/kg PCB (intertidal areas) 1300 µg/kg cPAH (intertidal areas) (6.5 ng/L) ENR w/AC amendment 1300

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  • Danny Reible, University of Texas

  • Projected performance in various enhanced naturalrecovery scenarios No action alternative Unamended enhanced natural recovery AC amended enhanced natural recovery Mixed layer Thin amendment layer (e.g. reactive core mat or surface layer)

    Partitioning Assumptions Sediment shows reduced availability according to typically

    observed behavior Sorption to AC from literature Typical bioturbation depths and rates Sensitivity to groundwater upwelling

  • Reproduced from Ghosh et al., 2003.

    7 "" ..

    6 r" -

    5 ,...

    - ~ ~ "' ~ I

    - -r"

    ,..

    -2

    1

    0 ' •

  • 91.00

    S.OO

    'tl ~

    ~ ~ 7.00

    8 .J I;G

    .9 6.00

    4.00

    3.00

    3.00 3.5{)

    !Figure 2 - tog K0w versus ~observed 1\,c All Sediment Site IOata

    D

    D

    X

    X

    D

    ~

    4.00 4.50 5.00 16.00

    Log K.,.

    0 JoJil:er ;;11d Smed~. 1000

    X 1-t;w;tbome 'eli: ; 1., !006

    X JoJI r ;;J~d l oelm; ru, 2.001

    o Klh ; lil et ; I.., lOOti

    l e~- ., 2006

    0 Oe>11 et ; t , 2006

    - Obioerved Koc = Kow

    - Obioerved Koc = 10 x low

    65 0

    PAHs

  • Wyckoff- Eagle Harbor

    r2

  • Figure 4 - Log K0 w vs, Obs~erved log Kac

    9.0 ~--------------------------------------------------------------------------------~

    8.5

    a_o

    7.5 :g

    :lll!

    J 1:1 ., 7.0 a D 'W

    ~

    ~ 0

    6.5

    D Obsel!'l.'eii Ko~~: Dat a from Anp, 2.009

    6.0 IJ - OI¥se l!1.'e,d Ko~~: = Kow

    -Obse~rJeii Ko~~: = 5 x Kow

    5.5 ~Best Fit Line for Observed li>ata

    - 95% Confidence lnteii'Val for Be-st Fit Line

    5.0 ~------------~------------~----------~------------~------------~------------~

    s 5.5 6 6.5 7 7.5

    Log !KII'il!

    Log ~ va1 ues f rom Haw ker, 1988

    PCBs

  • Grey/Green (1300 µg/kg) ~2 % TOC

  • ENR w/o amendment (areas not subject to scour) 720 µg/kg PCB (10 ng/L) 360 µg/kg PCB (intertidal areas) 1300 µg/kg cPAH (intertidal areas) (6.5 ng/L)

    ENR w/AC amendment 1300 µg/kg PCB (19 ng/L) 3000 µg/kg cPAH (15 ng/L)

    cPAH (BaP)- Log Kow=6, Koc=10 Kow PCB (52)- LogKow=5.84, Koc=5 Kow 2%TOC

    http:LogKow=5.84

  • ~0 cm/yr

    ~1 cm/yr

    ~5 cm tug mixing Assumed Bioturbation 10 cm

  • Virgin AC Fouled AC PCB O-Cl LogKf 1/n Log Kf 1/n Di Cl Kow (ng/kg)(L/ng)^1/n (ng/kg)(L/ng)^1/n 4 4.65 2 8.75 0.57 7.235 0.885 12 5.22 0 8.37 0.73 7.635 0.82 Tri b 18 5.24 2 8.23 0.7 7.4 0.8 Tetra Cl 54 5.21 4 7.88 0.86 6.89 0.94 53 5.62 3 7.53 1.08 6.87 0.995 52 5.84 2 7.82 1.03 7.02 0.99 72 6.26 1 8.39 0.83 7.62 0.79 77 6.36 0 8.9 0.82 7.96 0.765 Penta Cl 126 6.89 0 8.95 0.94 8.21 0.805

    Estimated from data from Average 1/n 0.93 0.88 McDonough et al 2008

  • LogKF_AC

    Log KF_DOM

    Power (LogKF_AC)

    Power (Log KF_DOM)

    y = 0.0011x0.86 R² = 0.742

    y = 7E-05x0.9222 R² = 0.8902

    1

    10

    100

    1000

    1 10 100

    Kf (L

    /mg)

    Kow

    x 100000

    Estimated from data from McDonough et al 2008

    Fresh AC

    Fouled AC

    Fouled AC Fresh AC

  • 720 µg/kg PCB (PCB52) – 10 ng/L AC – Log Kf ~7 (fouled), n~1 0 & 1 cm/yr deposition , 10 cm bioturbation layer Upwelling of 0 and 365 cm/yr Scenarios No Action ENR (w/o AC) 10 cm sand layer (0.1% organic carbon)

    ENR (w/AC) 0.4 lb/ft2 (~2% AC) mixed over 10 cm layer 0.4 lb/ft2 in 1 cm thin layer (e.g. RCM or unmixed layer) and 10 cm sand

    layer In-Situ Treatment w/AC 0.4 lb/ft2 mixed over 10 cm bioturbation layer Theoretical reduction in availability – 78%

  • D. I 4

    EQ

    n e [ J

  • .ODB -

    0. I)

    ll 0

    D. 01.

    a oo ~~~--~~~~~~~~~~~~~~ 0 2Q ~(I E:Q

    TI e [ l

  • De .D n

    T T ! !

    DAl-02$ ! --D . ~ 2 - -

    D.'IJOL5 - ·-

    D.il-DlO - -

    O.G C - -

    D ~f: OIJ ~~~-----·~~~~·-~~~·-~~---~.• ~~~~ 0 2Q ...,(1 EJJ 1

    TI e [ l

  • er1 De th = §.0

    "1 ' I

    7.0e-D ~ -

    -

    S..Oe-D 1- -

    4.~ 1- ·-

    3.0e-D ~ ·-

    Oe:- 1- ·-

    De-04 t- ·-

    c o-= llC . i i I i 0 2Q .qo 6Q aJ 1

    n e [ '1]

  • Hypothetical site for comparison

    10 cm AC mixed layer 2% carbon

    10 cm bioturbation layer

    2 kg/m2 activated carbon

  • Hypothetical site for comparison

    1 cm AC RCM layer 10 cm bioturbation

    layer 2 kg/m2 activated

    carbon

  • Slow natural attenuation of hydrophobics Minimal protectiveness of sand cap if upwelling significant and

    source maintained AC mixed into surficial sediments Substantial reduction in availability and mobility even with AC fouling

    (~78% reduction) AC mixed into cap layer Strongest reduction in exposure and flux with ENR cap incorporating

    AC More complicated placement and depth reduction

    Primary uncertainties Contaminant bioavailability in existing sediment Significance of groundwater upwelling

    Contaminant partitioning and bioavailabilityOutlineSlide Number 3Slide Number 4Slide Number 5Slide Number 6PCB�DistributionsSome Proposed Limits for ENR/AC enhanced ENRSlide Number 9Sorption onto fresh and fouled (NOM and Biofilm AC)PCB Sorption – Correlation with Kow (Tetra PCBs & higher)Evaluation conditionsNo Action10 cm sand capAC mixed into upper 10 cm AC mixed in 10 cm capped layerActivated Carbon Cap �Activated Carbon Cap �Conclusions

    barcode: *552496*barcodetext: SDMS Doc ID 552496