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Degradation of chloroethenes in aqueous solution by ultrasound

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SONOCHEMICAL DEGRADATION OF HALOCOMPOUNDS AN OVERVIEW Chlorinated organocompounds are usually used as industrial solvents: CCl4, CHCl3, C2Cl4, C2HCl3 , among others, withspread environmental pollutants in the subsurface aquatic environment Development of new technologies - Air stripping - Incineration - Biodegradation - Oxidation with chemicals - Carbon adsorption SONOCHEMICAL DEGRADATION OF HALOCOMPOUNDS AN OVERVIEW Development of new technologies (Advanced Oxidation Processes AOPs) Production of hydroxyl radical (OH·) as a primary oxidant: -Photochemical treatment (UV, UV/H2O2) -Ozonolysis -Fenton reaction Fe2+ + H2O2 Fe(OH)2+ + OH· Application of ultrasound field is a successful tecnology for environmental clean-up SONOCHEMICAL DEGRADATION OF HALOCOMPOUNDS AN OVERVIEW Ultrasound field Physical effects (solution agitation) Cavitation (highT,P ) Chemical effects (solvent sonolysis) Pyrolytic degradation Radicals generation H 2O  → H• + OH• ))))) OH • + OH • → H 2 O 2 H• + O 2 → HO • 2 Pollutants oxidation SONOCHEMICAL DEGRADATION OF HALOCOMPOUNDS AN OVERVIEW During the cavitational collapse of single, isolated bubbles, extreme temperatures and pressures are achieved. " #$$$ % #$$ & '( → ', - ', ! )*+ → ', - )*+→ ! )*+ . "($$$% ', - ) /+ ! /+ → ) /+ ! /+ → ( ', → '( ( ! " . "0$$% ', '( → ! ! () /+ ) /+ /+ → ) /+ /+ The main chemical pathways for organic compound degradation include: - Hydroxyl chemical oxidation - Direct pyrolytic degradation -Supercritical water reactions: Water vapor splits during bubble cavitation to yield H· and OH· Several organic compounds have been degradated using an ultrasonic field: - Aromatic compounds (phenol, chlorophenols) - Organic dyes - Herbicides and pesticides - Aliphatic carboxilic acids - Surfactants SONOCHEMICAL DEGRADATION OF HALOCOMPOUNDS OBJECTIVES Study of the degradation of chlorinated organic compounds in aqueous solution using a 20 and 850 kHz ultrasound field Cl Cl Cl Cl # Degradation of perchloroethylene as a model molecule in aqueous solution " $"! " ! "" ═"" % ! SONOCHEMICAL DEGRADATION OF HALOCOMPOUNDS RESULTS $ Properties perchloroethylene : 6&.2- ' : 9," 8 ," 7 ," ) + .6 Excellent solvent 0 ' ( Applications * &," & '( $ Hazardous toxic compound * ( ( -Dry-cleaning industry -Metal cleaning -Vapor degreasing 1 1 -./ . .0 3 2./0 US EPA Persistent pollutant &," 5 &," .2 4 -' Table of physical and chemical properties of perchloroethylene SONOCHEMICAL DEGRADATION OF HALOCOMPOUNDS EXPERIMENTAL PROCEDURE Perchloroethylene (Aldrich 99%) used as received. -Solutions were prepared with purified water obtained from a Milli-Q system, 18.2 MΩ cm and previously deoxygenated by bubbling argon before addition of pechloroethylene. - The solution was left stirring overnight. -Temperature was kept at 20 ±1 ºC with a refrigerated bath and circulator. -Ultrasonic irradiation was carried out at maximum volume (minimum headspace in the sonochemical reactor). -Samples were analyzed inmediately after collection SONOCHEMICAL DEGRADATION OF HALOCOMPOUNDS RESULTS The degradation of perchloroethylene was studied by: Analysis of aqueous phase A) Following the chloride concentration formation in solution Chromatography by Ion Exchange B) Monitoring of PCE and byproducts by High Performance Liquid Chromatograph (HPLC) C) Detection and quantification of PCE and products from the degradation obtained at the end of each experiment was carried out using Purge and Trap Gas Chromatography Mass Spectrometry (PT-GC-MS) Analysis of gaseous phase A) Analysis CO/CO2 by Gas Cromatographic with TCD (GC-TCD) B) Anaysis of PCE and intermediates by Gas Cromatographic with FID (GC-FID) SONOCHEMICAL DEGRADATION OF HALOCOMPOUNDS RESULTS Experimental set-up Sonoreactor ( Undatim) Frequency: 20kHz Maximum power output: 100W Hastelloy ultrasound horn: 3 cm diam. Cell dimensions: diameter 68mm depth 84mm Sonicated volume: 200cm3 (1) ultrasonic probe (2) transducer (3) gas passing (4) electrolyte (5) cooling jacket (6) Teflon adaptor (7) O-ring joints. SONOCHEMICAL DEGRADATION OF HALOCOMPOUNDS RESULTS Characterization of the sonoreactor, 20kHz, 100W Ultrasonic power input was measured using standard calorimetric procedures 10 -2 I/ W cm 8 $ $ # $ ' 6 ' '+ + ( + 4 2 ; - .2/ . 6& / ; / -.-9 . 6 ; -6 &. 9 . 2 2 ; /& 6.-6 . ; &/ 0.6/ . 0 0 0 20 40 60 80 100 Amplitude/ % & SONOCHEMICAL DEGRADATION OF HALOCOMPOUNDS RESULTS Initial concentration of PCE 1.0 [PCE]/[PCE]0 PCE concentration/ ppm 120 100 Concentration decay is uneffected by initial concentration of PCE 0.8 80 0.6 60 0.4 40 0.2 20 0.0 0 0 50 100 150 200 250 300 insonation time/min 0 50 100 150 200 250 300 insonation time/min ● [PCE]0 = 14ppm ■ [PCE]0 = 64ppm ▲[PCE]0 = 100ppm 6.4 W cm-2 5h 20kHz 20ºC Ultrasonic intensity SONOCHEMICAL DEGRADATION OF HALOCOMPOUNDS RESULTS 1.0 [PCE]/[PCE]0 -2 1.84 W cm -2 3.39 W cm -2 5.09 W cm -2 6.36 W cm -2 7.64 W cm 0.8 The pH was found to decrease in all cases due to the HCl formation 0.6 0.4 =' + < '; 0.2 0.0 0 50 100 150 200 250 300 insonation time/min [PCE]0 ≈ 75ppm 20kHz 5h 20ºC .2/ / -.-9 9 &. 9 6.-6 0.6/ & SONOCHEMICAL DEGRADATION OF HALOCOMPOUNDS RESULTS Ultrasonic intensity 0.0 -0.2 0.020 log(c(t)/c(0) -0.4 -0.6 k/ min-1 0.016 -0.8 0.012 -1.0 1,84 W 3,39 W 5,09 W 6,36 W 7,64 W -1.2 -1.4 -1.6 -1.8 -2 cm -2 cm -2 cm -2 cm -2 cm 0.008 0.004 0.000 0 1 2 3 I/ W cm -2.0 -2.2 0 50 100 150 200 250 300 350 t/ min Experimental results show that sonochemical destruction of PCE follows pseudo first-order kinetics 4 -2 5 6 SONOCHEMICAL DEGRADATION OF HALOCOMPOUNDS RESULTS Main products from perchloroethylene sonochemical degradation: Cl Cl H Cl H Products detected by P&T-GC-MS after 5h: Cl H Cl H Cl CHCl3 CCl4 Hexachloroethane Hexachlorobutadiene Hexachloropropene H Cl SONOCHEMICAL DEGRADATION OF HALOCOMPOUNDS RESULTS 45 70 80 50 [TCE],[DCE],[Cl-]/ ppm 50 80 [TCE],[DCE],[Cl-]/ ppm [PCE]/ ppm [PCE]/ ppm Ultrasonic intensity 45 70 40 60 40 60 35 50 30 25 40 20 30 35 50 30 25 40 20 30 15 20 Sonochemical treatment leads to TCE and DCE and chloride anions as major by-products 15 20 10 10 5 0 0 100 200 time/ min 1.84 W cm-2 0 300 10 10 5 0 0 100 200 time/ min 3.39 W cm-2 0 300 -■-■-▲-×- [PCE] [TCE] [DCE] [Cl-] SONOCHEMICAL DEGRADATION OF HALOCOMPOUNDS RESULTS Mechanism: Cl Cl Cl Cl H CHCl3 Cl · · + H + Cl Cl Cl Cl Cl Cl )))))) C-C ·H Cl )))))) Cl 2 CCl2 Cl + Cl · CCl ·Cl 3 + )))))) ·Cl C-Cl Cl Cl Cl Cl Cl · + CCl3 Cl Cl ·Cl + + Cl ·H Cl H Cl Cl Cl CCl4 )))))) x2 Cl C-Cl · Cl · + 2 Cl Cl Cl · Cl · · Cl + Cl Cl Cl Cl Cl Cl H Cl + ·H H H Cl Cl Experimental set-up SONOCHEMICAL DEGRADATION OF HALOCOMPOUNDS RESULTS Sonoreactor Meinhardt Ultraschalltechnik, K80-5 Frequency: 850kHz Maximum power output: 140W Sonicated volume: 200cm3 1) Transducer, 2) bulk solution, 3) glass cell, 4) sample withdrawing system, 5) temperature probe, 6) lid, 7) inlet and outlet of the cooling jacket and 8) interface SONOCHEMICAL DEGRADATION OF HALOCOMPOUNDS RESULTS Characterization of the sonoreactor, 850kHz, 140W Ultrasonic power output was measured using standard calorimetric procedures 50 power output 40 30 20 10 0 0 1 2 3 4 5 amplitude Power input/ watts W cm-2 W cm-3 2.2±0.2 0.11 0.01 4.7±0.1 0.24 0.02 17.2±0.9 0.88 0.07 37.9±4.4 1.93 0.15 SONOCHEMICAL DEGRADATION OF HALOCOMPOUNDS RESULTS Effect of PCE concentration 80 150ppm perchloroethylene 60 150ppm PCE Saturation conditions!! 75ppm perchloroethylene [Chloride]final/ ppm 100 40 80 60 38ppm perchloroethylene 20 40 20 0 0 1 2 3 4 5 insonation time/ hours 0 0 25 50 75 100 125 150 [PCE] initial/ ppm 100 yield Chloride conc/ ppm 100 80 Initial Perchloroethylene concentration/ ppm 150 75 38 60 40 20 0 0 25 50 75 100 125 150 p e rc h lo ro e th yle n e in itia l c o n c e n tra tio n / p p m Yield of C l - formation/ % 58 73 91 60 3 8 w att 1 7 w att 40 5 w a tt 20 2 w att Yield of chloride formation / % Chloride concentration/ ppm SONOCHEMICAL DEGRADATION OF HALOCOMPOUNDS RESULTS Effect of ultrasound power 80 60 40 20 0 0 5 10 Power output / Wh 0 0 30 60 90 120 150 in s o n a tio n tim e / m in Ultrasonic power / watts 38 17 5 2 Yield of Cl- formation/ % 70 62 50 26 15 SONOCHEMICAL DEGRADATION OF HALOCOMPOUNDS RESULTS ! H Cl Cl H H Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl " # Cl Cl Cl $ % SONOCHEMICAL DEGRADATION OF HALOCOMPOUNDS CONCLUSIONS Perchloroethylene sonochemical degradation can be carried out Different behaviour has been detected with the frequency Sonochemical degradation seems mainly to follow a pyrolytic radical mechanism Total degradation can not be stablished from the results coming from Cl- detection Differences in the by-products obtained with different frequencies are still under study ACKNOWLEDGEMENTS Coventry University Generalidad Valenciana Finantial Support Alicante University COST D32/004 (Electrochemistry with Ultrasound) Thank you!