TWO-PHASE METAL REMOVAL USING GRANULAR ACTIVATED CARBON AND 5 METHYLBENZOTRIAZOLE
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Transcript of TWO-PHASE METAL REMOVAL USING GRANULAR ACTIVATED CARBON AND 5 METHYLBENZOTRIAZOLE
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TWO-PHASE METAL REMOVAL USING GRANULAR ACTIVATED CARBON AND
5 METHYLBENZOTRIAZOLE
7 August 2002
Cheryl Horn, Muna Abu-Dalo, Mark Hernandez
Presented by: Cheryl Horn
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Presentation Outline
Problem Statement and Goal Background Research approach / experimental design Results Interpretation of results Conclusion and acknowledgements
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Problem Statement 1300 miles of streams in Colorado affected by
acid mine drainage (AMD) AMD is generally characterized by high metal
loadings and low pH Removal of metals can be accomplished by
precipitation– Costly– Large sludge volumes produced– No metals recovery
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Project Goal Methylated benzotriazoles derivatives may be
useful in the removal of metals from solution Adsorption characteristics have not been heavily
researched Better understanding of the adsorption and metal-
complexing behaviors of 5-Methylbenzotriazole (5MeBT) are necessary
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Background5MeBT
Commonly used in aircraft deicing fluids and corrosion inhibitors– Has been shown to be biodegradable under aerobic
conditions– Strong sorption characteristics (hydrophobic)
Preliminary research indicates adsorption onto granular activated carbon (GAC) may be accurately predicted using a standard Freundlich isotherm
N
N
HN
H3C
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BackgroundFreundlich Isotherm Adsorption modeled by the equation:
q = KFc1/n
In linear form:
log q = log KF + 1/n log c
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Research ApproachAdsorption of 5MeBT onto GAC
Experiment pH Temperature,C Carbon 1 1 5 Calgon 2 1 15 Calgon 3 1 25 Calgon 4 3 5 Calgon 5 3 15 Calgon 6 3 25 Calgon 7 3 15 Norit 8 5 15 Calgon
Experiments conducted at varying temperature, pH, concentrations, and GAC type:
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Research ApproachAdsorption of 5MeBT onto GAC Experiments were conducted in triplicate at
concentrations in the range of 100-2000 ppm 5MeBT– Each experiment included 15-50 ml
microcosms and one 50 ml control– Microcosms were prepared using Briton-
Robinson buffer to maintain acidic conditions Samples were collected and analyzed over
three days
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Research ApproachSample Analysis
Analyses were accomplished using high performance liquid chromatography (HPLC)– fitted with a UV detector ( = 254 nm)
• Aromatic compounds absorb UV light
N
N
HN
H3C
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Results-GAC Effect
Freundlich Isotherm(GAC effect)
-500
50100150200250
0 50 100 150 200
Ceq
q
pH=3,Temp15C,Calgon
pH=3, Temp15C,Norit
Log.(pH=3,Temp15C,Calgon)Log. (pH=3,Temp15C,Norit)
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Results-Temperature Effects for pH = 3
Freundlich Isotherm (Temp effect)
-500
50100150200250
0 100 200 300 400
Ceq
q
pH=3, Temp 5CpH=3,Temp 25CpH=3,Temp15C
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Results-pH Effects at 15 C
Freundlich Isotherm (pH effect)
-500
50100150200250
0 50 100 150 200
Ceq
q
pH=3, Temp 15CpH=1, temp15CpH=5, temp15C
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Results-Discussion
N
NH
HN
H3C
+
N
N
HN
H3CpKa = 2.0N
N
N
H3C
-pKa =8.8
•GAC Effects
- pH = 7.2 and 8.5
•pH Effects
•Temperature Effects
-Below pKa, temperature is less important
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Isotherm ResultsSummary
Experiment pH Temp Carbon KF Value1 1 5 Calgon 42.152 1 15 Calgon 35.483 1 25 Calgon 45.104 3 5 Calgon 34.535 3 15 Calgon 54.216 3 25 Calgon 48.197 3 15 Norit 39.048 5 15 Calgon 59.09
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Metals
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Research ObjectiveMetals
N
N
HN
N
N
HN
N
N
HN
N
N
HN
N
N
HN
N
N
HN
R
M+x
electronegativecharge density
δ-
N
N
HN
N
N
HN
N
N
HN
N
N
HN
N
N
HN
N
N
HN
RM
complexation reduces negative charge density
Zn+
NN
HN
NN
HN
NN
HN
NN
HN
NN
HN
NN
HN
NN
HN
NN
HN
NN
HNN
NHN
NN
HN
NN
HN
Cu
CuZnN
NHN
NN
HN
NN
HN
Zn
GranularActivatedCarbon A
B
Zn+
NN
HN
NN
HN
NN
HN
NN
HN
NN
HN
NN
HN
NN
HN
NN
HN
NN
HN
NN
HN
NN
HN
NN
HN
NN
HN
NN
HN
NN
HN
NN
HN
NN
HN
NN
HNN
NHN
NN
HN
NN
HN
NN
HN
NN
HN
NN
HN
Cu
CuZnN
NHN
NN
HN
NN
HN
Zn NN
HN
NN
HN
NN
HN
NN
HN
NN
HN
NN
HN
Zn
GranularActivatedCarbon A
B
Hydrophilic Side Hydrophobic Side
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Immobilization of Metals to GAC using Benzotriazole
NH
NN
H3C
N
N
N
Cu
HN
N N
CH3
N
N
N
Cu
CuN
NN
H3C
B
A
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Research ApproachMetals
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Research Approach-Metals
pH = 1
pH = 2
pH = 2.3
pH = 3
pH = 5
5MeBT, ppm10 20Cu, ppm
500
Copper added initially
50010 20
Copper added after adsorption
010 20
A B Control
Copper added initially
1% Granular Activated Carbon
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Research Approach-Sample Analysis 5MeBT concentrations determined using HPLC Copper concentrations analyzed in the University
of Colorado’s Geology laboratory using Inductive Coupled Plasma/Atomic Emission Spectroscopy (ICP/AES)
Results were confirmed using differential pulse polarography (DPP)
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Results - Metals
20 ppm Copper + 500 ppm 5MeBT
020406080
100
1 2 2.3 3 5
pH
% R
emov
al Scenario1Scenario2Control
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Results - Metals
10 ppm Copper + 500 ppm 5MeBT
020406080
100
1 2 2.3 3 5
pH
% R
emov
al Scenario1Scenario2Control
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Conclusions & Acknowledgements
Adsorption of 5-MeBT onto GAC can be accurately predicted by the Freundlich model
Further research should be done– Metals other than Cu
Thanks to Muna, Mark, JoAnn, Jenny…
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Questions?