water & wastewater treatment-2ocw.snu.ac.kr/sites/default/files/note/16_water... · 2019. 9. 6. ·...

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Changha Lee School of Chemical and Biological Engineering Seoul National University http://artlab.re.kr 고도산화환원 환경공학 연구실 Advanced Redox Technology (ART) Lab Water & Wastewater Treatment - 2 - Chemical Oxidation (from MWH's Water Treatment Principles and Design by Crittenden et al.)

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  • Changha Lee

    School of Chemical and Biological Engineering

    Seoul National University

    http://artlab.re.kr

    고도산화환원환경공학연구실

    Advanced Redox Technology (ART) Lab

    Water & Wastewater Treatment-2- Chemical Oxidation

    (from MWH's Water Treatment Principles and Design by Crittenden et al.)

  • Definition of Reduction and Oxidation

    Definition of reduction & oxidation reactions (i.e., redox reactions)

    - Oxidation: loss of e− or H, gain of O, increase of oxidation number

    - Reduction: gain of e− or H, loss of O, decrease of oxidation number

    e.g., C + H2 → CH4

    C + O2 → CO2

    Fe0 → Fe2+ + 2e−

    e.g., O2 + H2 → H2O2

    O2 + 2e− + 2H+ → H2O2

    e.g., O2 + 2H2 → 2H2O

    O2 + 4e− + 4H+ → 2H2O

  • Oxidation number

  • Half

    Reactions

    2e−

    Reductant Oxidant

    Oxidant and Reductant

  • Oxidation Processes for Water Treatment

    1. Chlorine

    2. Ozone

    3. Chlorine dioxide

    4. Permanganate

    5. Hydrogen peroxide

    6. Organic contaminants

  • TASTE AND ODOR CONTROL

    - In surface water: originated from algal bloome.g., Geosmin, 2-Methylisoborneol (2-MIB)

    - Threshold odor concentration: 4 ng/L for geosmin, 9 ng/L for 2-MIB

    - In groundwater: sulfides (hydrogen sulfide and organic sulfides)Production of polysulfides (oxidation byproducts, usually S8, generates turbidity) is a problem when H2S > 1 ppm

  • COLOR REMOVAL

    OXIDATION AS A COAGULATION AID

    IRON AND MANGANESE REMOVAL

    OXIDATION OF SELECTED TRACE ORGANIC CONSTITUENTS

    2D Graph 3

    DEA

    Eili

    min

    ation (

    %)

    0

    20

    40

    60

    80

    100

    120

    Col 1 vs Col 2 - Col 2

    Col 1 vs Col 3 - Col 3

    Col 1 vs Col 4 - Col 4

    Col 1 vs Col 5 - Col 5

    Iopromide

    Diazepam

    Atrazine

    DIA

    Ibuprofen

    Clofibric acid

    Cyanazine

    Atenolol

    Bezafibrate

    Caffeine

    Propanolol

    Naproxen

    Trimethoprim

    Carbamazepine

    17-Estradiol Diclofenac

    17-ethinylestradiolSulfamethoxazole

    Predicted oxidation of grouped organic pollutants in 1 ppm of ozone dose

  • Fundamentals of Oxidation and Reduction

    Definitions of oxidation and reduction

    Half Reactions

    Balancing Redox Reactions

  • Define final products (make an unbalanced equation with them)

    Balance atoms and charge (Use H+, OH− or H2O if necessary)

  • Standard Redox Potential

  • “Reduction (redox) potential” is not for a compound, but for a reaction

    (or a redox couple)!

    The reduction potential of A3+ is ??? VSHE X

    e.g.,

    Because A3+ may go through different redox reactions with

    different reduction potentials.

    A3+ + e− → A2+

    A3+ + 3e− → A0

    The reduction potential of A3+ + e− → A2+ is ??? VSHE O

    The reduction potential of A3+/A2+ is ??? VSHE O

    Eo[A3+/A2+] = ??? VSHE O

    Expression of Redox Potential

  • Standard Redox Potentials for Several Oxidants

    Source: Lee et al., 2019 (Membr. Wat. Treat.)

  • We can tell if a certain redox reaction is thermodynamically favored or not

    by reduction (redox) potentials of its half reactions!

    Ni0 + Fe2+ → Ni2+ + Fe0 (favored or unfavored) ?

    e.g.,

    Fe2+ + 2e− → Fe0 Eo = −0.44 VSHE

    Ni2+ + 2e− → Ni0 Eo = −0.20 VSHE

    Fe2+ + 2e− → Fe0 Eo = −0.44 VSHE

    H+ + 2e− → H2 Eo = 0 VSHE

    Redox Potential and Thermodynamics

    Fe0 + 2H+ → Fe2+ + H2 (favored or unfavored) ?

  • Redox Potential and Thermodynamics

    Ni0 + Fe2+ → Ni2+ + Fe0 (favored or unfavored) ?

    e.g.,

    Fe2+ + 2e− → Fe0 Eo(1) = −0.44 VSHE

    Ni2+ + 2e− → Ni0 Eo(2) = −0.20 VSHE

    Fe0 + 2H+ → Fe2+ + H2 (favored or unfavored) ?

    Fe2+ + 2e− → Fe0 Eo(2) = −0.44 VSHE

    H+ + 2e− → H2 Eo(1) = 0 VSHE

    Ni0 → Ni2+ + 2e− Eo(2) = +0.20 VSHE

    E◦Rxn = Eo(1) + Eo(2) = −0.24

    Fe0 → Fe2+ + 2e− Eo(2) = +0.44 VSHE

    E◦Rxn = Eo(1) + Eo(2) = +0.44

    E◦Rxn > 0 Thermodynamically favored

    E◦Rxn < 0 Thermodynamically unfavored

    G◦ = −nFE◦

  • Redox Potential and Thermodynamics

  • Redox Potentials of Combined Reactions

    Eo(3) = 2Eo(1) + Eo(2) / (2 + 1) = (2x0.4 + 0.2)/3 = 0.33 VSHE

    A3+ + 2e− → A+ Eo(1) = +0.4 VSHE

    A+ + e− → A0 Eo(2) = +0.2 VSHE

    e.g.,

    A3+ + 3e− → A0 Eo(3) = ?

  • pH-Dependence of Redox Potential

    m

    ??? + ne- + mH+ → ???

    m

    m

    Ered (at specific pH) − Eredo (pH =0)

    Gr = Gro + RT lnQr

    −nFEred = − nFEredo + RT lnQr

    Ered − Eredo = − RT/nF lnQr

    Ered − Eredo = − 2.303RT/nF log(1/[H+]m)

  • OXYGEN

    HYDROGEN

    2H+ + 2e− H2(g) Eo = 0 V

    (at pH 0)

    (at pH 14)

  • *pe = −log[e−] = F/(2.3RT)Eh

  • CHLORINE SPECIES

    (1)

  • (2)

    (3)

  • pKa = 7.5

  • (4)

  • (1)

    (2) (3)

    (4)

    *pe = −log[e−] = F/(2.3RT)Eh

  • Kinetics of Redox Reactions

  • Homework

    What would the Eh-pH diagram for chlorine species look like

    when the total chlorine concentration changes?

    Think about it !

  • Common Chemical Oxidants for Water Treatment Applications

    Oxidation rate

  • Redox potential

    Applications

    - Oxidation of iron, manganese,and sulfides

  • Redox potential

    Applications

    - Oxidation of iron, manganese, sulfides, taste and odor compounds (but not applicable to Geosmin & 2-MIB), ammonia

    - Oxidation byproducts (chlorinated organic compounds) are problematic

  • Redox potential

    Decomposition

    Applications

    - Oxidation of iron, manganese, sulfides, taste and odor compounds (little applicable to Geosmin & 2-MIB), and some of organic compounds

    ClO2 + e− → ClO2

    − Eored = 0.95~1 V

  • Redox potential

    Applications

    - Oxidation of iron, sulfides

    - A Reagent for advanced oxidation technology (a precursor of OH radical)e.g., UV/H2O2, O3/H2O2, Fe(II)/H2O2

  • Redox potential

    Applications

    - Oxidation of iron, manganese, sulfides, taste and odor compounds, micropollutamnts, removal of color, control of DBP precursors (oxidation of NOM)

    - A Reagent for advanced oxidation technology (a precursor of OH radical)e.g., UV/O3, O3/H2O2, Fe(II)/O3

  • pH

    5 6 7 8 9

    log

    (k

    O3, a

    pp (M

    -1 s

    -1))

    -1

    0

    1

    2

    3

    4

    5

    6

    7

    8

    9

    10

    log

    (

    (s))

    -5

    -4

    -3

    -2

    -1

    0

    1

    2

    3

    4

    5D M F A

    D M A

    T M A

    D M A B

    D M E A

    D M D C

    D M A ID M A P

    pH

    5 6 7 8 9

    log

    (k

    ClO

    2, a

    pp (M

    -1 s

    -1))

    -3

    -2

    -1

    0

    1

    2

    3

    4

    5

    6

    7

    8

    9

    log

    (

    (s))

    -4

    -3

    -2

    -1

    0

    1

    2

    3

    4

    5

    6

    7

    D M F A

    D M A

    T M A

    D M A B

    D M E A

    D M D C

    D M A I

    D M A P

    O3 ClO2

    pH

    5 6 7 8 9

    log

    (k O

    H (M

    -1 s

    -1))

    7

    8

    9

    10

    11

    log

    (

    (s))

    1

    2

    3

    4

    D M F A

    D M A

    T M A

    D M A B

    D M E A.

    D M D C

    D M A I

    D M A P

    •OH

    Second-order rate constants for reactions of NDMA precursors with oxidants

    Source: Lee et al., 2007 (Environ. Sci. Technol.)

  • Redox potential

    Applications

    - Oxidation of iron, manganese, taste and odor compounds

    - Pink color: needs dosage control

    MnO4−

    MnO4−