water & wastewater treatment-2ocw.snu.ac.kr/sites/default/files/note/16_water... · 2019. 9. 6. ·...
TRANSCRIPT
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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.)
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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
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→
Oxidation number
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Half
Reactions
2e−
Reductant Oxidant
Oxidant and Reductant
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Oxidation Processes for Water Treatment
1. Chlorine
2. Ozone
3. Chlorine dioxide
4. Permanganate
5. Hydrogen peroxide
6. Organic contaminants
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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
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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
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Fundamentals of Oxidation and Reduction
Definitions of oxidation and reduction
Half Reactions
Balancing Redox Reactions
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Define final products (make an unbalanced equation with them)
Balance atoms and charge (Use H+, OH− or H2O if necessary)
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Standard Redox Potential
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“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
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Standard Redox Potentials for Several Oxidants
Source: Lee et al., 2019 (Membr. Wat. Treat.)
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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) ?
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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◦
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Redox Potential and Thermodynamics
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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) = ?
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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)
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OXYGEN
HYDROGEN
2H+ + 2e− H2(g) Eo = 0 V
(at pH 0)
(at pH 14)
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*pe = −log[e−] = F/(2.3RT)Eh
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CHLORINE SPECIES
(1)
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(2)
(3)
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pKa = 7.5
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(4)
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(1)
(2) (3)
(4)
*pe = −log[e−] = F/(2.3RT)Eh
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Kinetics of Redox Reactions
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Homework
What would the Eh-pH diagram for chlorine species look like
when the total chlorine concentration changes?
Think about it !
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Common Chemical Oxidants for Water Treatment Applications
Oxidation rate
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Redox potential
Applications
- Oxidation of iron, manganese,and sulfides
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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
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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
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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
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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
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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.)
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Redox potential
Applications
- Oxidation of iron, manganese, taste and odor compounds
- Pink color: needs dosage control
MnO4−
MnO4−