Photolysis and photooxidation of typical gaseous VOCs by UV Irradiation: Removal performance and mechanisms

In-Sun Kang , Jinying Xi , Hong-Ying Hu

Front. Environ. Sci. Eng. ›› 2018, Vol. 12 ›› Issue (3) : 8

PDF (892KB)
Front. Environ. Sci. Eng. ›› 2018, Vol. 12 ›› Issue (3) : 8 DOI: 10.1007/s11783-018-1032-0
RESEARCH ARTICLE
RESEARCH ARTICLE

Photolysis and photooxidation of typical gaseous VOCs by UV Irradiation: Removal performance and mechanisms

Author information +
History +
PDF (892KB)

Abstract

UV photodegradation of 27 typical VOCs was systematically investigated.

Contribution of photolysis and photooxidation to VOCs removal was identified.

Gaseous VOC could be partially converted to particles by 185/254 nm UV irradiation.

The mineralization and conversion of 27 VOCs by UV irradiation were reported.

Photodegradation by ultraviolet irradiation (UV) is increasingly applied in volatile organic compound (VOC) and odor gas treatments. In this study, 27 typical VOCs, including 11 hydrocarbons and 16 hydrocarbon derivatives, at 150–200 ppm in air and nitrogen gas were treated by a laboratory-scale UV reactor with 185/254 nm irradiation to systematically investigate their removal and conversion by UV irradiation. For the tested 27 VOCs, the VOC removal efficiencies in air were within the range of 13%–97% (with an average of 80%) at a retention time of 53 s, which showed a moderate positive correlation with the molecular weight of the VOCs (R = 0.53). The respective contributions of photolysis and photooxidation to VOC removal were identified for each VOC. According to the CO2 results, the mineralization rate of the tested VOCs was within the range of 9%–90%, with an average of 41% and were negatively correlated to the molecular weight (R = -0.63). Many of the tested VOCs exhibited high concentration particulate matters in the off-gases with a 3–283 mg/m3 PM10 range and a 2–40 mg/m3 PM2.5 range. The carbon balance of each VOC during UV irradiation was analyzed based on the VOC, CO2 and PM10 concentrations. Certain organic intermediates and 23–218 ppm ozone were also identified in the off-gases. Although the UV technique exhibited a high VOC removal efficiency, its drawbacks, specifically low mineralization, particulate matters production, and ozone emission, must be considered prior to its application in VOC gas treatments.

Graphical abstract

Keywords

VOCs / UV photodegradation / Particulate matters / Ozone

Cite this article

Download citation ▾
In-Sun Kang, Jinying Xi, Hong-Ying Hu. Photolysis and photooxidation of typical gaseous VOCs by UV Irradiation: Removal performance and mechanisms. Front. Environ. Sci. Eng., 2018, 12(3): 8 DOI:10.1007/s11783-018-1032-0

登录浏览全文

4963

注册一个新账户 忘记密码

References

[1]

Duan H, Liu X, Yan M, Wu Y, Liu Z. Characteristics of carbonyls and volatile organic compounds (VOCs) in residences in Beijing, China. Frontiers of Environmental Science and Engineering, 2016, 10(1): 73–84

[2]

Niu H, Mo Z, Shao M, Lu S, Xie S. Screening the emission sources of volatile organic compounds (VOCs) in China by multi-effects evaluation. Frontiers of Environmental Science and Engineering, 2016, 10(5): 1

[3]

Zhao P, Zhu L. Optimized porous clay heterostructure for removal of acetaldehyde and toluene from indoor air. Frontiers of Environmental Science and Engineering, 2016, 10(2): 219–228

[4]

Qiao N, Zhang X, He C, Li Y, Zhang Z, Cheng J, Hao Z. Enhanced performances in catalytic oxidation of o-xylene over hierarchical macro-/mesoporous silica-supported palladium catalysts. Frontiers of Environmental Science and Engineering, 2016, 10(3): 458–466

[5]

Berenjian A, Chan N, Malmiri H J. Volatile organic compounds removal methods: A review. American Journal of Biochemistry and Biotechnology, 2012, 8(4): 220–229

[6]

Parmar G R, Rao N N. Emerging control technologies for volatile organic compounds. Critical Reviews in Environmental Science and Technology, 2008, 39(1): 41–78

[7]

Wekhof A. Treatment of contaminated water, air and soil with UV flash lamps. Environment and Progress, 1991, 10(4): 241–247

[8]

Bhowmick M, Semmens M J. Ultraviolet photooxidation for the destruction of VOCs in air. Water Research, 1994, 28(11): 2407–2415

[9]

Hay S O, Obee T, Luo Z, Jiang T, Meng Y, He J, Murphy S C, Suib S. The viability of photocatalysis for air purification. Molecules (Basel, Switzerland), 2015, 20(1): 1319–1356

[10]

George C, Beeldens A, Barmpas F, Doussin J F, Manganelli G, Herrmann H, Kleffmann J, Mellouki A. Impact of photocatalytic remediation of pollutants on urban air quality. Frontiers of Environmental Science & Engineering, 2016, 10(5): 2

[11]

Wang J H, Ray M B. Application of ultraviolet photooxidation to remove organic pollutants in the gas phase. Separation and Purification Technology, 2000, 19(1–2): 11–20

[12]

Kang I S, Xi J Y, Hu H Y. Effects of different operating conditions on the VOCs removal performance of UV irradiation reactors. Journal of Odor and Indoor Environment, 2017, 16(1): 72–80

[13]

Feiyan C, Pehkonen S O, Ray M B. Kinetics and mechanisms of UV-photodegradation of chlorinated organics in the gas phase. Water Research, 2002, 36(17): 4203–4214

[14]

Yu J, Cai W, Chen J, Feng L, Jiang Y, Cheng Z. Conversion characteristics and mechanism analysis of gaseous dichloromethane degraded by a VUV light in different reaction media. Journal of Environmental Sciences-China, 2012, 24(10): 1777–1784

[15]

Shen Y S, Ku Y. Treatment of gas-phase volatile organic compounds (VOCs) by the UV/O3 process. Chemosphere, 1999, 38(8): 1855–1866

[16]

Chou M S, Chang K L. UV/ozone degradation of gaseous hexamethyldisilazane (HMDS). Chemosphere, 2007, 69(5): 697–704

[17]

Mahmoudkhani F, Rezaei M, Asili V, Atyabi M, Vaisman E, Langford C H, De Visscher A. Benzene degradation in waste gas by photolysis and photolysis-ozonation: experiments and modeling. Frontiers of Environmental Science & Engineering, 2016, 10(6): 10

[18]

Cheng Z W, Sun P F, Jiang Y F, Yu J M, Chen J M. Ozone-assisted UV254 nm photodegradation of gaseous ethylbenzene and chlorobenzene: Effects of process parameters, degradation pathways, and kinetic analysis. Chemical Engineering Journal, 2013, 228 (3): 1003–1010

[19]

Koh L H, Kuhn C S, Mohseni M, Allen D G. Utilizing ultraviolet Photolysis as a pre-treatment of volatile organic compounds upstream of a biological gas cleaning operation. Journal of Chemical Technology and Biotechnology (Oxford, Oxfordshire), 2004, 79(6): 619–625

[20]

Wang C, Xi J Y, Hu H Y, Yao Y. Advantages of combined UV photodegradation and biofiltration processes to treat gaseous chlorobenzene. Journal of Hazardous Materials, 2009, 171(1–3): 1120–1125

[21]

Braslavskys S E. Glossary of terms used in photochemistry, 3rd ed. Pure and Applied Chemistry, 2007, 79(3): 293–465

[22]

Kang I S, Xi J Y, Wang C, Hu H Y. UV Photodegradation of chlorinated VOCs: Removal efficiency and products. Journal of Korean Society for Atmospheric Environment, 2017, 33(2): 87–96

[23]

Ji J, Xu Y, Huang H, He M, Liu S, Liu G, Xie R, Feng Q, Shu Y, Zhan Y, Fang R, Ye X, Leung D Y C. Mesoporous TiO2 under VUV irradiation: Enhanced photocatalytic oxidation for VOCs degradation at room temperature. Chemical Engineering Journal, 2017, 327: 490–499

[24]

Mohseni M. Gas phase trichloroethylene (TCE) photooxidation and byproduct formation: Photolysis vs. titania/silica based photocatalysis. Chemosphere, 2005, 59(3): 335–342

[25]

Huang H, Huang H, Zhan Y, Liu G, Wang X, Lu H, Xiao L, Feng Q, Leung D Y C. Efficient degradation of gaseous benzene by VUV photolysis combined with ozone-assisted catalytic oxidation: Performance and mechanism. Applied Catalysis B: Environmental, 2016, 186: 62–68

[26]

Jeong T S, Shin C H, Kim J S, Longzhe C. A study on the treatment of toluene and pilot test by using UV and ozone. Journal of Korean Society of Environmental Technology, 2007, 8: 33–39

[27]

Holzinger R, Millet D B, Williams B, Lee A, Kreisberg N, Hering S V, Jimenez J, Allan J D, Worsnop D R, Goldstein A H. Emission, oxidation, and secondary organic aerosol formation of volatile organic compounds as observed at Chebogue Point, Nova Scotia. Journal of Geophysical Research, 2007, 112(D10): D10S24

[28]

Camredon M, Aumont B, Lee-Taylor J, Madronich S. The SOA/VOC/NOx system: An explicit model of secondary organic aerosol formation. Atmospheric Chemistry and Physics Discussions, 2007, 7: 5599–5610

[29]

Lee S B, Bae G N, Moon K C. Smog chamber measurements. In: Kim Y J, Platt U, Gu M B, Iwahashi H, eds. Atmospheric and Biological Environmental Monitoring. Dordrecht: Springer, 2009, 105–136

[30]

Vaden T D, Song C, Zaveri R A, Imre D, Zelenyuk A. Morphology of mixed primary and secondary organic particles and the adsorption of spectator organic gases during aerosol formation. Proceedings of the National Academy of Sciences of the United States of America, 2010, 107(15): 6658–6663

[31]

Tie X, Madronich S, Li G H, Ying Z, Zhang R, Garcia A R, Lee-Taylor J, Liu Y. Characterizations of chemical oxidants in Mexico City: A regional chemical/dynamical model (WRF-Chem) study. Atmospheric Environment, 2007, 41(9): 1989–2008

RIGHTS & PERMISSIONS

Higher Education Press and Springer–Verlag GmbH Germany, part of Springer Nature

AI Summary AI Mindmap
PDF (892KB)

3199

Accesses

0

Citation

Detail

Sections
Recommended

AI思维导图

/