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UV/H_(2)O_(2)和UV/NaClO工艺降解吉非罗齐的比较 被引量:1

Comparative investigation of gemfibrozil degradation by UV/H_(2)O_(2)and UV/NaClO processes
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摘要 对比了吉非罗齐(GEM)在UV/H_(2)O_(2)和UV/NaClO系统中的降解,两个高级氧化系统均可以有效降解GEM,与UV/H_(2)O_(2)相比,UV/NaClO对GEM的去除速率更快。在UV/H_(2)O_(2)和UV/NaClO系统内,目标物的降解速率随着氧化剂浓度的增加而加快,由于pH会影响OH的氧化能力和UV/NaClO系统内自由基的组成比例,因此溶液的p H对两个系统均有显著的影响,当溶液pH从5增加到11时,GEM在UV/H_(2)O_(2)系统和UV/NaClO系统内的k_(obs)分别从0.2115min^(-1)和1.3115min^(-1)降低到0.1064min^(-1)和0.2283min^(-1)。Cl^(-)和HCO_(3)^(-)可以稍微加快GEM在UV/NaClO系统内的降解速率,却减慢了GEM在UV/H_(2)O_(2)系统内的降解速率;HA可以通过竞争效应和滤光效应抑制GEM在两个系统内的降解,但由于HClO/ClO^(-)的摩尔吸光系数高于H_(2)O_(2),HA对GEM在UV/NaClO系统内降解的抑制效应较小。OH和Cl是UV/NaClO系统内降解GEM的主要氧化物种,GEM在两个高级氧化系统内降解过程主要包括羟基化、去甲基化、H提取和C—O键断裂步骤。经济效益评估可知,UV/NaClO系统比UV/H_(2)O_(2)系统更具有成本效益。 The degradation of gemfibrozil(GEM)by UV/H_(2)O_(2)and UV/NaClO processes was comparatively evaluated.Both advanced oxidation systems can effectively degrade GEM.Compared with UV/H_(2)O_(2)system,the degradation rate of GEM in UV/NaClO system was faster.In UV/H_(2)O_(2)and UV/NaClO systems,the degradation rate of the target increased with the increase of oxidant concentrations.Because pH could affect the oxidation capacity of‧OH and the composition ratio of free radicals in UV/NaClO system,the pH of the solutions had a significant impact on both systems.When pH was increased from 5 to 11,the kobs in UV/H_(2)O_(2)and UV/NaClO decreased from 0.2115min^(-1)and 1.3115min^(-1)to 0.1064min^(-1)and 0.2283min^(-1),respectively.Cl^(-)and HCO_(3)^(-)can slightly accelerate the degradation of GEM in UV/NaClO system,but slightly slow down the degradation of GEM in UV/H_(2)O_(2)system.HA can inhibit GEM degradation in both systems through competition and filter effect.Because the molar absorption coefficient of HClO/ClO^(-)was higher than H_(2)O_(2),HA had less inhibitory effect on GEM degradation in UV/NaClO system compared with UV/H_(2)O_(2)system.The main oxidation species degrading GEM in UV/NaClO system were‧OH and Cl^(-).The degradation path of GEM in both systems mainly included hydroxylation,demethylation,H-extraction and C-O bond breakage steps.In terms of economic benefits,UV/NaClO system was more cost-effective than UV/H_(2)O_(2)system.
作者 闫博引 韩春宇 夏晶晶 王松雪 武桂芝 夏文香 李金成 YAN Boyin;HAN Chunyu;XIA Jingjing;WANG Songxue;WU Guizhi;XIA Wenxiang;LI Jincheng(School of Environmental and Municipal Engineering,Qingdao University of Technology,Qingdao 266033,Shandong,China)
出处 《化工进展》 EI CAS CSCD 北大核心 2023年第11期6102-6112,共11页 Chemical Industry and Engineering Progress
基金 山东省自然科学基金(ZR2021QE234) 国家自然科学基金(52100010) 河海大学浅水湖泊综合治理与资源开发教育部重点实验室开放项目。
关键词 自由基 紫外/过氧化氢 紫外/次氯酸钠 高级氧化 降解路径 反应动力学 radical UV/H_(2)O_(2) UV/NaClO advanced oxidation degradation path reaction kinetics
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  • 1Acero J L, Stemmler K, Von Gunten U. 2000. Degradation kinetics of atrazine and its degradation products with ozone and OH radicals: a predictive tool for drinking water treatment [ J ]. Environmental Science & Technology, 34 (4): 591-597.
  • 2Anipsitakis G P, Dionysiou D D. 2004. Radical generation by the interaction of transition metals with common oxidants [ J ]. Environmental Science & Technology, 38 (13): 3705-3712.
  • 3Antoniou M G, Armah A, Dionysiou D D. 2010. Degradation of microcystin-LR using sulfate radicals generated through photolysis, thermolysis and e- transfer mechanisms [ J ]. Applied Catalysis B : Environmental, 96 (3): 290-298.
  • 4Araujo L, Villa N, Camargo N, et al. 2011. Persistence of gemfibrozil, naproxen and mefenamic acid in natural waters [ J ]. Environmental Chemistry Letters, 9 (1) : 13-18.
  • 5Bendz D, Paxeus N A, Ginn T R, et al. 2005. Occurrence and fate of pharmaceutically active compounds in the environment, a case study: H6je River in Sweden [ J ]. Journal of Hazardous Materials, 122 (3) : 195-204.
  • 6Bennedsen L R, Muff J, Sogaard E G.2012. Influence of chloride and carbonates on the reactivity of activated persulfate [ J ]. Chemosphere, 86(11) : 1092-1097.
  • 7Boyd G R, Reemtsma H, Grimm D A, et al. 2003. Pharmaceuticals andpersonal care products (PPCPs) in surface and treated waters of Louisiana, USA and Ontario, Canada [ J ]. Science of the Total Environment, 311 (1) : 135-149.
  • 8Buxton G V, Greenstock C L, Helman W P, et al. 1988. Critical review of rate constants for reactions of hydrated electrons, hydrogen atoms and hydroxyl radicals ( ~ Oil/-O-in aqueous solution [ J ]. Journal of Physical and Chemical Reference data, 17 (2) : 513-886.
  • 9Cermola M, DellaGreca M, Iesce M R, et al. 2005. Phototransformation of fibrate drugs in aqueous media [ J ]. Environmental Chemistry Letters, 3 ( 1 ) : 43-47.
  • 10Clifton C L, Huie R E. 1989. Rate constants for hydrogen abstraction reactions of the sulfate radical, SO4"- Alcohols [ J ]. International Journal of Chemical Kinetics, 21 (8) : 677-687.

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