Oxidation of Pharmaceuticals and Personal-Care Products in Water using Hydrodynamic Cavitation 245th American Chemical Society Meeting April 10, 2013
Authors
Greg Loraine and Georges L. Chahine Dynaflow, Inc. 10621-J Iron Bridge Road Jessup, MD 20794 U.S.A.
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Outline Cavitation and Formation of Free Radicals Acoustic (Ultrasonic) Cavitation vs. Hydrodynamic Cavitation Hydrodynamic Cavitating Jets Chloramphenicol Pharmaceuticals and Personal-Care-Products in Wastewater Conclusions
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6000 V spark. Collapse is analogous to cavitation
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Cavitation Bubble nuclei in water expand & collapse when the local pressure changes very quickly. Collapsing bubbles produce tremendous pressures & temperatures in localized area (~5,200 K, ~200 Atm). Water vapor dissociates into OH• and H• H2O → OH• + H• Volatile compounds can also dissociate into radicals CCl4 → Cl• + Cl3C• www.dynaflow-inc.com
Radius of Bubble
Pressure
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Reaction Location Collapsing Bubble
Parent Concentration
Reactions occur inside collapsing bubble or at interface OH• and H• concentrations highest in center, decrease toward bubble wall Hydrophobic compounds partition to air-water interface Local depletion of starting compound and build up of products Volatile compounds enter the expanding bubble and decompose during collapse
OH• H• Products
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Products 4-10-13
Hydrodynamic & Ultrasonic Cavitation Ultrasonic (US) cavitation produced by mechanical vibration in a liquid localized at the face of the probe. US- high intensity, localized cavitation, energy intensive, scaling up difficult Hydrodynamic Cavitation (HD) is produced by motion of fluid. All liquid is forced through cavitation region Large pressure fluctuations in shear layer of the liquid cause cavitation. HD – wider area of cavitation, 1/10 – 1/100 energy required, easy to scale www.dynaflow-inc.com
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US
HD
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DYNAJETS® Cavitating Jets Specially designed nozzles intensify cavitation and generate cavitation at lower pump pressures This is achieved through: Bluff body Swirling the flow Passive acoustic excitation Enhance vorticity and reduce pressure in the vortices
DYNASwirl®
Area of Cavitation
Centerbody CAVIJET® www.dynaflow-inc.com
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Hydrodynamic Cavitation for Oxidation Hydrodynamic cavitation can be 10 – 100 times more energy efficient than acoustic cavitation No addition of oxidizer Optical opacity or particulates are no problem Other than nozzle no special equipment required Specially designed submerged nozzles (DYNAJETS®) Cavitation at lower pressures Lower pressures lower electrical requirements Hydraulic Energy = Flow Rate x Pressure Change x Time Cavitation in wider area Easier to scale up than US www.dynaflow-inc.com
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C/C0 P-Nitrophe nol
1
Note Much More Rapid Concentration Drop with the DYNAJETS ® .
0.8 ULTRASONIC
0.6 DYNAJETS®
0.4 0.2
Oxidation Efficency, mg/MJ
Energy: Acoustic & Hydrodynamic 10 Note High Oxidation Efficency and Short Oxidation Time for DYNAJETS ® . 1
DYNAJETS®
0.1 ULTRASONIC 0.01 0
0 0
10
20 Time, Hours
30
40
5
10
15
20
25
30
35
Time, Hours
25 ppm p-Nitrophenol
Hydrodynamic cavitation can be 10 – 100 times more energy efficient than acoustic cavitation* *K.Kalumuck, G. Chahine, J. Fluids Eng., 122,(2000) 465. S. Majumdar, P. S. Kumar, A. Pandit, Ultra. Sonochem., 5 (1998) 113. K. Jyoti, A. Pandit, Water Res., 38 (2004), 2249.
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Previous Work using DYNAJETS® Oxidation Pharmaceuticals and Personal Care Products Chlorinated solvents Toluene, Acetone Pesticides: Malathion, Carbaryl, 2,4-D Disinfection Water Wastewater Storm water Recovery of Cellular Matter – Algae Pretreatment of lignocellulose biomass Biodiesel production www.dynaflow-inc.com
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Selectivity of HD Cavitation Oxidation Volatile (high vapor pressure) can be oxidized easily Hydrophobic compounds (high octanol-water partition coefficient log KOW) oxidize faster than hydrophilic compounds pH can be used to adjust degree of ionization of weak acids and bases Reaction intermediates are formed in regions of high radical concentrations, lower by-product concentrations Operating parameters (pump pressure, jet velocity, etc.), and nozzle design can be varied to improve oxidation performance
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Chloroamphenicol 2,2-dichloro-N-[1,3-dihydroxy-1-(4-nitrophenyl) propan-2-yl acetamide Broad spectrum antibiotic Log KOW = 1.14, pKa = 9.61 Experimental Oxidized using two types of nozzles Pressure drops across nozzle 30 – 90 psi (2 – 6.2 bar) [CA]0 = 30 mg/L in DI water (10 L) Analytical Extracted using SDB solid phase extraction disks GC/MS analysis LOD 2.4 mg/L & 95% recovery www.dynaflow-inc.com
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Effects of Operating Pressure - DYNASWIRL® Operating pressure had a large effect on the removal rate, Nozzle design and geometry also affect performance. DYNASWIRL
30
30 psi 90 psi
25
Chloramphenicol mg/L
60 psi
20
15
10
5 0
20
40
60
80
100
120
140
Oxidation Time, mins.
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Effects of Operating Pressure – Centerbody CAVIJET® Operating pressure again affected the removal rate, 91% removal centerbody-CAVIJET 30
Chloramphenicol, mg/L
25 65 psi 45 psi
20
15 10 5 0 0
20
40
60
80
100
120
140
Oxidation Time, mins. www.dynaflow-inc.com
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Chloramphenicol Removal per kiloJoule 1.2
Chloramphenicol [C]/[C]0
CAVIJET 65 PSI CAVIJET 45 PSI
1
DYNASWIRL 30 PSI DYNASWIRL 60 PSI
0.8
DYNASWIRL 90 PSI
0.6 0.4 0.2
0 0
100
200
300
400
500
600
kJ
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Chloramphenicol: Product Formation and Mass Balance 120
120 Mass Balance
100
80
80 Chloramphenicol
60
60 4-Dichloromethyl Oxazoline
40
40 Nitrobenzaldehyde
20
Mass Balance
Concentration, mM
100
20
0
0 0
50
100
150
Time (mins.) www.dynaflow-inc.com
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Proposed Mechanism of Chloramphenicol Oxidation Cl
Cl N
NO2
C Cl
C
NO2
+ •OH
•
C O
Cl
NO2
+
•
N
Cl
N
C
C
Cl
O
OH
H2O +
C C
4-Nitrobenzaldehyde
C
Cl
C
OH
OH
O
N
Cl
N
C
O
Cl
C Cl
C
OH
O
2-dichloromethyl oxazoline www.dynaflow-inc.com
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Selective Oxidation of Mixtures: log KOW Seven
PPCP spiked into filtered wastewater TP effluent Oxidized using a DYNASWIRL® nozzle Range of Log KOW Compound
Primary Use
Spiked concentration
MDL g/L*
g/L
Concentration Range in Wastewater Effluent ug/L
Log KOW
14.4
1.44
1.9 – 6.9
2.48
Triclosan
Pharmaceutic al Anti-microbial
3.46
0.346
0.6 – 4.7
4.79
Chloroxylenol
Anti-microbial
0.146
0.015
0.03 – 0.05
5.9
Galaxolide
Fragrance
6.14
0.614
0.7 – 2.6
5.9
Musk Ketone
Fragrance
0.33
0.034
0.06 – 0.11
4.31
Oxybenzone
Sun-screen
0.6
0.06
0.18 – 0.35
3.79
Tris (2chloroethyl) Phosphate
Flame retardant
1.79
0.35
0.35 – 0.39
1.44
Ibuprofen
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Oxidation of Mixture of PPCP in Wastewater 1.100
Log KOW 1.44 2.48
1.000
4.31
C/C0
0.900
3.79 4.76
0.800
Chloroxylenol Tris(2-chloroethyl)Phosphate
5.9
Galaxolide Musk Ketone
0.700
5.9
Oxybenzone Triclosan Ibuprofen
0.600 0
5
10
15
20
25
30
Time (mins.)
DYNASWIRL® nozzle at 60 psi www.dynaflow-inc.com
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Log KOW and Reaction Extent 0.35 y = 0.05x - 0.0385 R2 = 0.7906
0.3
(1-C/C0)
0.25 0.2 0.15 0.1 0.05 0 0
1
2
3
4
5
6
7
log Kow
In a mixture more hydrophobic compounds react faster www.dynaflow-inc.com
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Conclusions Cavitation initiated reactions are similar regardless of how the cavitation is initiated Hydrodynamic cavitation can be more energy efficient and easier to scale up than ultrasonic devices Selective removal of volatile and hydrophobic compounds can be accomplished Oxidation rates have non-linear dependence on pump pressure Nozzle geometry can affect oxidation rates www.dynaflow-inc.com
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Acknowledgements & Contact Information US Environmental Protection Agency NASA Office Naval Research NOAA NIEHS
DYNAFLOW, INC. www.dynaflow-inc.com 10621-J Iron Bridge Road, Jessup, MD 20794. USA Dr. Greg Loraine Sr. Research Scientist (301) 604-3688
[email protected] Dr. Georges L. Chahine President (301) 604-3688
[email protected]
Business POC: Dr. Jin-Keun Choi Principal Research Scientist (301) 604-3688
[email protected] www.dynaflow-inc.com
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