Materials Reports 2020, Vol. 34 Issue (Z2): 507-512 |
POLYMERS AND POLYMER MATRIX COMPOSITES |
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Review on Removal of Polycyclic Aromatic Hydrocarbons in Aquatic Environment by Advanced Oxidation Technology |
WANG Dejun1,2,3, LI Hui4, JIANG Xiren1,2, ZHAO Chaocheng3, ZHAO Yuhui1,2, DENG Chunmei1,2, WANG Xinping1,2
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1 North China Sea Environmental Monitoring Center, State Oceanic Administration, Qingdao 266033, China 2 Shandong Provincial Key Laboratory of Marine Ecology and Environment & Disaster Prevention and Mitigation, Qingdao 266033, China 3 College of Chemical Engineering, China University of Petroleum, Qingdao 266580, China 4 Qingdao Technical College, Qingdao 266555, China |
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Abstract Polycyclic aromatic hydrocarbons (PAHs) are composed of two or more benzene rings with lipophilic properties and high desorption activation energy. They mainly have two combinations. One is non-fused ring type, that is, benzene ring and the benzene rings are connected by a carbon atom, such as biphenyl, terphenyl, etc.; the other is a fused ring type, that is, two carbon atoms are shared by two benzene rings, such as naphthalene, anthracene, etc. They are persistent compounds in the environment due to their chemically stable structure and low bioavailable fraction. PAHs are released into the environment because of natural activities such as terrestrial vegetation synthesis, microbial synthesis, and volcanic activity. However, PAHs released by these processes are minimal in comparison with those produced from forest fires, grass land fires and anthropogenic sources. Anthropogenic activities (such as military operations, vehicular emissions, agricultural production, residential waste burning, combustion of fossil fuels, leakage from the petroleum industry, manufacturing of carbon black, coal tar pitch and asphalt, heating and power generation, and emissions from internal combustion engines) release a significant amount of PAHs into the environment. Due to the toxic, mutagenic, and carcinogenic natures of PAHs, developing appropriate removal process through understanding remediation mechanisms have been researched to mitigate the possible risk of PAHs on the environment and human health. Physical, chemical, thermal, biological and phytoremediation processes (which comprise incineration, thermal desorption, radio frequency heating, oxidation, ion exchange, photolysis, adsorption, electrolysis, chemical precipitation, natural attenuation, biostimulation, bioaugmentation, rhizofiltration, phytoextraction, plant immobilization and phytodegradation techniques) are the major treatment methods of PAHs contaminated soil, sediment and waters. In general, it is the physical, biological, and chemical processes. It can be known that the PAHs removal process in practice is mostly biological or physical by referring to lots of references. However, most of these methods possess several disadvantages such as high investment and maintenance costs, complicated operating procedure. Addi-tionally, some of these treatment processes release the secondary by-products and some of them are carcinogenic and mutagenic compounds which further add an adverse impact on public health. Although the chemical process currently remains at the stage of laboratory, it has unique advantages over the other two processes, such as wider application, non-selective to pollutants, and complete mineralization of pollutants. Therefore, chemical process found to be a more efficient and promising technique to treat PAHs. The paper summarizes the past literature on PAHs removal by advanced oxidation technology, and reviews the latest research progress and reaction mechanism of various oxidation technologies.
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Published: 08 January 2021
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Fund:This work was financially supported by the Qingdao Postdoctoral Applied Research Project. |
About author:: Dejun Wang received his Ph.D. degree in Environmental Chemical Engineering from China University of Petroleum (East China) with a doctorate in engineering. He is currently conducting a postdoctoral research at the North China Sea Environmental Monitoring Center of the State Oceanic Administration. The research direction is advanced oxidation technology to treat marine pollution. Xiren Jiang, professor, mainly engaged in marine environment monitoring and evaluation, publishing a number of monographs, hosting a number of key projects, and participating in the preparation of multiple stan-dards, has extensive experience in the marine environment monitoring field. |
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1 Johnsen A R, Karlson U.Microbial Ecology, 2005, 50(4), 488. 2 Zhang Z L, Hong H S, Zhou J L, et al.Science of the Total Environment, 2004, 323(1), 71. 3 Shin K H, Kim K W, Ahn Y. Journal of Hazardous Materials, 2006, 137(3), 1831. 4 Manoli E, Samara C.Trac Trends in Analytical Chemistry, 1999, 18(6), 417. 5 Zhou W, Wang X, Chen C, et al.Chemical Engineering Journal, 2013, 233(11), 251. 6 Yun H, He Y, Wang X, et al. Applied Surface Science, 2014, 311(9), 825. 7 Li H, Qu R, Chao L, et al.Bioresour Technology, 2014, 163(7), 193. 8 Peng R H, Fu X Y, Zhao W, et al. Environmental Science & Technology, 2014, 48(21), 12824. 9 Sun K, Liu J, Gao Y, et al.Scientific Reports, 2013, 4(Suppl 1), 5462. 10 Jun W, Zaiming C, Baoliang C.Environmental Science & Technology, 2014, 48(9), 4817. 11 Lee H K.Journal of Chromatography A, 1995, 710(1), 79. 12 王连生,孔令仁,韩塑暌. 致癌有机物, 中国环境科学出版社, 1993. 13 唐森本,王欢畅,葛碧洲.环境有机污染物, 冶金工业出版社, 1995. 14 欧阳琼,方战强. 广东化工, 2017, 44(16), 107. 15 孔敏仪. 超声-芬顿降解印染废水中多环芳烃的研究. 硕士学位论文, 广东工业大学, 2018. 16 潘玉兰. Fenton试剂氧化降解水和土壤中多环芳烃. 硕士学位论文, 南京农业大学, 2014. 17 Cuypers C, Grotenhuis T, Joziasse J, et al.Environmental Science & Technology, 2000, 34(10), 2057. 18 Yen C H, Chen K F, Kao C M, et al. Journal of Hazardous Materials, 2011, 186(2-3), 2097. 19 Kun-Chang H, Zhiqiang Z, Hoag G E, et al.Chemosphere, 2005, 61(4), 551. 20 Liang C, Lai M C. Environmental Engineering Science, 2008, 25(7), 1071. 21 Chih-Feng C, Nguyen Thanh B, Chiu-Wen C, et al.Air Repair, 2015, 65(4), 375. 22 Yu S, Gu X, Lu S, et al.Chemical Engineering Journal, 2017, 333, 122. 23 Alvares A B C, Diaper C, Parsons S A.Environmental Technology Letters, 2001, 22(4), 409. 24 Hoigne J, Bader H. Water Research, 1983, 17(2), 173. 25 Elovitz M S, von Gunten U, Kaiser H. Ozone Science & Engineering, 2000, 22(2), 123. 26 Staehelin J, Hoigne J.Environmental Science & Technology, 1982, 10(16), 678. 27 Nemes A, Fábián I, Gordon G. Ozone: Science & Engineering, 2008, 3(22), 287. 28 林冲. 焦化废水外排水中残余组分的环境行为及臭氧氧化过程分析.博士学位论文, 华南理工大学, 2014. 29 Silva P T D S, Silva V L D, Neto B D B, et al. Journal of Hazardous Materials, 2009, 168(2-3), 1269. 30 Tan X M, Ji F Y, Wang X D, et al.Advanced Materials Research, 2012, 518-523, 784. 31 马虹. 油田采出水中多环芳烃的光催化氧化处理方法研究. 硕士学位论文, 华北电力大学, 2012. 32 Turro N J.Modern molecular photochemistry, CA: University Science Books, 1991. 33 Xiaowu, Shao Y. Procedia Earth & Planetary Science, 2017, 17, 348. 34 Shang J, Chen J, Shen Z, et al. Environmental Science & Pollution Research, 2015, 22(16), 12374. 35 Maria W, Wiśniowska E, Turek A, et al.Desalination and Water Treatment, 2016, 57, 1262. 36 Ge L, Na G, Chen C E, et al.Science of the Total Environment, 2016, 547, 166. 37 Verhoeven J. W. Pure and Applied Chemistry, 2009, 68(12), 2223. 38 王德军,赵朝成.材料导报:综述篇, 2015, 29(9), 57. 39 Fujishima A, Honda K.Nature, 1972, 238(5358), 37. 40 Carey J H, Lawrence J, Tosine H M. Bulletin of Environmental Contamination and Toxicology, 1976, 16(6), 697. 41 Karam F F, Hussein F H, Baqir S J, et al. International Journal of Photoenergy, 2014, 2014, 1. 42 Bo L, Bing C, Bai Y Z, et al. Journal of Environmental Engineering, 2016, 142(11), 4016054. 43 Mondal K, Bhattacharyya S, Sharma A. Industrial & Engineering Chemistry Research, 2014, 53(49), 18900. 44 Xiao Z, Cai Z, Wang T, et al.Applied Catalysis B Environmental, 2016, 187, 134. 45 Bai H, Zhou J, Zhang H, et al. Colloids and Surfaces B: Biointerfaces, 2016, 150, 68. 46 Grover I S, Prajapat R C, Singh S, et al.Particuology, 2017, 34(5), 156. 47 Karunakaran C, Kalaivani S, Vinayagamoorthy P, et al.Materials Science in Semiconductor Processing, 2014, 21, 122. 48 Wang X, Zhan S, Wang Y, et al. Journal of Colloid & Interface Science, 2014, 422, 30. 49 Reutergådh L B, Iangphasuk M.Chemosphere, 1997, 35(3), 585. 50 Mahmood M A, Baruah S, Dutta J. Materials Chemistry & Physics, 2011, 130(1-2), 531. 51 Chen H, Wen M, Huang Z, et al.Journal of Materials Chemistry A, 2015, 3(2), 600. 52 Teply' F.Collection of Czechoslovak Chemical Communications,2011, 76(7), 859. 53 王儒威. 环境中有机污染物的有机地球化学及其光催化降解研究.博士学位论文, 中国科学技术大学, 2012. 54 Jie F, Kyzas G Z, Cai Z, et al. Chemical Engineering Journal, 2017, 335, 290. 55 Yang X, Cai H, Bao M, et al.Chemical Engineering Journal, 2017, 334. 56 胡春,贺泓,李俊华,等. 环境催化—原理及应用, 科学出版社, 2008. 57 曲久辉. 水处理电化学原理与技术, 科学出版社, 2007. 58 Feng Z, Feng C, Li W, et al. International Journal of Electrochemical Science, 2014, 9(2), 943. 59 Machado C F C, Gomes M A, Silva R S, et al. Journal of Electroanalytical Chemistry, 2018, 816, 232. 60 Herrada R A, Acosta-Santoyo G, Sepúlveda-Guzmán S, et al.Electrochimica Acta, 2018, 263, 353. 61 Herrada R A, Medel A, Manríquez F, et al. Journal of Hazardous Mate-rials, 2016, 319, 102. 62 Yaqub A, Isa M H, Ajab H, et al.Ecological Chemistry & Engineering, 2017, 24(3), 6672. 63 Asim Y, Hasnain I M, Huma A, et al. Electrochemical Energy Technology, 2018, 4(1), 1. 64 Yaqub A, Isa M H, Ajab H, et al.Petroleum Chemistry, 2017, 57(5), 457. 65 张峰.光催化水处理技术, 化学工业出版社, 2015. 66 Vela N, Martínez-Menchón M, Navarro G, et al. Journal of Photochemistry and Photobiology A: Chemistry, 2012, 232, 32. 67 刘博川,王丽娟,乔梦,等. 环境科学研究, 2017, 30(2), 322. |
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