紫外-活性炭协同活化过硫酸氢钾对罗丹明B的降解

范星, 唐玉朝, 姚顺顺. 紫外-活性炭协同活化过硫酸氢钾对罗丹明B的降解[J]. 环境化学, 2018, 37(12): 2711-2720. doi: 10.7524/j.issn.0254-6108.2018052001
引用本文: 范星, 唐玉朝, 姚顺顺. 紫外-活性炭协同活化过硫酸氢钾对罗丹明B的降解[J]. 环境化学, 2018, 37(12): 2711-2720. doi: 10.7524/j.issn.0254-6108.2018052001
FAN Xing, TANG Yuchao, YAO Shunshun. Degradation of Rhodamine B by peroxymonosulfate synergistically activated by UV/activated carbon[J]. Environmental Chemistry, 2018, 37(12): 2711-2720. doi: 10.7524/j.issn.0254-6108.2018052001
Citation: FAN Xing, TANG Yuchao, YAO Shunshun. Degradation of Rhodamine B by peroxymonosulfate synergistically activated by UV/activated carbon[J]. Environmental Chemistry, 2018, 37(12): 2711-2720. doi: 10.7524/j.issn.0254-6108.2018052001

紫外-活性炭协同活化过硫酸氢钾对罗丹明B的降解

  • 基金项目:

    安徽省教育厅自然科学重点项目(KJ2015A109),住建部科学技术项目(2016-K4-077)和安徽省重点研究与开发计划(1704a0902006)资助.

Degradation of Rhodamine B by peroxymonosulfate synergistically activated by UV/activated carbon

  • Fund Project: Supported by Anhui Provincial Department of Education Natural Science Key Project(KJ2015A109), Ministry of Housing and Urban Development Science and Technology Project(2016-K4-077) and Anhui Province Key Research and Development Plan(1704a0902006).
  • 摘要: 利用紫外光(UV)和活性炭(AC)协同活化过硫酸氢钾(PMS)产生硫酸根自由基(SO4-·)对染料进行降解.以罗丹明B(RhB)作为目标污染物,考察了PMS浓度、AC用量、废水初始pH等因素对体系降解RhB的影响.实验表明,UV-AC体系能有效活化PMS.AC用量0.5 g· L-1,PMS浓度为2.0 mmol· L-1时,10 mg· L-1RhB的降解率在5 min达到89%,RhB的降解率随着初始PMS浓度和AC的用量增加而增大,但超过一定量时,对降解的促进就不明显.降解反应遵循准一级动力学.自由基清除的实验证明了硫酸根自由基(SO4-·)是主要的活性自由基,羟基自由基(HO·)也起到一定的作用,同时证明UV对PMS活化的贡献大于AC.通过紫外可见光谱和FT-IR光谱分析,初步推断RhB分子降解主要是由于共轭结构裂解和N-位脱乙基等作用.五次循环实验后RhB的脱色率仍能达到85%证明了降解体系的稳定性.
  • 加载中
  • [1] XU Y M, LU H Q. Degradation of the dye X-3B by UV/Fe(Ⅲ)-generated hydroxyl radicals in aqueous solution[J]. Journal of Photochemistry and Photobiology A:Chemistry, 2000, 136:73-77.
    [2] BUXTON G V. Critical review of rate constants for reactions of hydrated electrons, hydrogen atoms and hydroxyl radicals (·OH/·OH) in aqueous solution[J]. Journal of Physical & Chemical Reference Data, 1988, 17(2):513-886.
    [3] NETA P, HUIE R, ROSS A B. Rate constants for reactions of inorganic radicals in aqueous solution[J]. Journal of Physical & Chemical Reference Data, 1988, 17(3):1027-1284.
    [4] LIN H, WU J, ZHANG H. Degradation of bisphenol A in aqueous solution by a novel electro/Fe3+/peroxydisulfate process[J]. Separation & Purification Technology, 2013, 117(4):18-23.
    [5] ANTONIOU M G, DE LA CRUZ A A, DIONYSIOU D D. Degradation of microcystin-LR using sulfate radicals generated through photolysis, thermolysis and e- transfer mechanisms[J]. Applied Catalysis B:Environmental, 2010, 96(3-4):290-298.
    [6] 范斯娜, 吕文英, 姚坤, 等. 亚铁离子活化过硫酸氢钾复合盐降解水溶液中萘普生[J]. 环境工程学报, 2015, 9(6):2767-2770.

    FAN S N, LU W Y, YAO K, et al. Degradation of naproxen in aqueous by peroxymonosulfate activated by ferrous ion[J]. Chinese Journal of Environmental Engineering, 2015, 9(6):2767-2770(in Chinese).

    [7] SHARMA J, MISHRA I M, DIONYSIOU D D, et al. Oxidative removal of Bisphenol A by UV-C/peroxymonosulfate (PMS):Kinetics, influence of co-existing chemicals and degradation pathway[J]. Chemical Engineering Journal, 2015, 276:193-204.
    [8] YIN R, GUO W, WANG H, et al. Enhanced peroxymonosulfate activation for sulfamethazine degradation by ultrasound irradiation:Performances and mechanisms[J]. Chemical Engineering Journal, 2018, 335:145-153.
    [9] 刘曼, 李一兵, 王彦斌,等. 掺铜介孔碳活化过硫酸氢盐高效降解双酚A[J]. 中国环境科学, 2017, 37(11):4151-4158.

    LIU M, LI Y B, WANG Y B, et al. Activation of peroxymonosulfate by copper doped ordered mesoporous carbon for efficient destruction of bisphenol A.[J]. China Environmental Science, 2017, 37(11):4151-4158(in Chinese).

    [10] LAI L, YAN J, LI J, et al. Co/Al2O3 -EPM as peroxymonosulfate activator for sulfamethoxazole removal:Performance, biotoxicity, degradation pathways and mechanism[J]. Chemical Engineering Journal, 2018, 343:676-688.
    [11] LIU S, ZHAO X, ZENG H, et al. Enhancement of photoelectrocatalytic degradation of diclofenac with persulfate activated by Cu cathode[J]. Chemical Engineering Journal, 2017, 320:168-177.
    [12] TAN C,DONG Y, FU D, et al. Chloramphenicol removal by zero valent iron activated peroxymonosulfate system:Kinetics and mechanism of radical generation[J]. Chemical Engineering Journal, 2018, 334:1006-1015.
    [13] LIU Y, ZHANG N, KANG H, et al. WS2 Nanowires as a High-Performance Anode for Sodium-Ion Batteries[J]. Chemistry, 2015, 21(33):11878-11884.
    [14] YIN C, AROUA M, DAUD W. Review of modifications of activated carbon for enhancing contaminant uptakes from aqueous solutions[J]. Separation and Purification Technology, 2007, 52(3):403-415.
    [15] GUO C, XU J, HE Y, et al. Photodegradation of rhodamine B and methyl orange over one-dimensional TiO2 catalysts under simulated solar irradiation[J]. Applied Surface Science, 2011, 257(8):3798-3803.
    [16] VELASCO L F, FONSECA I M, PARRA J B, et al. Photochemical behaviour of activated carbons under UV irradiation[J]. Carbon, 2012, 50(1):249-258.
    [17] TAN C, GAO N, DENG Y, et al. Radical induced degradation of acetaminophen with Fe3O4 magnetic nanoparticles as heterogeneous activator of peroxymonosulfate[J]. Journal of Hazardous Materials, 2014, 276:452-460.
    [18] 冯善方, 邓思萍, 杜嘉雯, 等. 三维有序介孔Co3O4非均相活化单过硫酸氢钾降解罗丹明B[J]. 环境科学, 2016, 37(11):4247-4254.

    FENG S F, DENG S P, Du J W, et al. Heterogeneous activation of peroxymonosulfate with three-dimensional ordered mesoporous Co3O4 for the Degradation of Rhodamine B[J]. Environmental Science, 2016, 37(11):4247-4254(in Chinese).

    [19] WANG J, WANG S. Activation of persulfate (PS) and peroxymonosulfate (PMS) and application for the degradation of emerging contaminants[J]. Chemical Engineering Journal, 2018, 334:1502-1517.
    [20] ANIPSITAKIS G P, DIONYSIOU D D. Degradation of organic contaminants in water with sulfate radicals generated by the conjunction of peroxymonosulfate with cobalt[J]. Environmental Science & Technology, 2003, 37:4790-4797.
    [21] QI C, LIU X, MA J, et al. Activation of peroxymonosulfate by base:Implications for the degradation of organic pollutants[J]. Chemosphere, 2016, 151:280-288.
    [22] 葛勇建, 蔡显威, 林翰, 等. 碱活化过一硫酸盐降解水中环丙沙星[J]. 环境科学, 2017, 38(12):5116-5123.

    GE Y J, CAI X W, LIN H, et al. Base activation of peroxymonosulfate for the degradation of ciprofloxacin in water[J]. Environmental Science, 2017, 38(12):5116-5123(in Chinese).

    [23] 杨照荣, 崔长征, 李炳智, 等. 热激活过硫酸盐降解卡马西平和奥卡西平复合污染的研究[J]. 环境科学学报, 2013, 33(1):98-104.

    YANG Z R, CUI C Z, LI B Z, et al. Degradation of carbamazepine and oxcarbazepine by heat-activated persulfate[J]. Acta Scientiae Circumstantiae, 2013, 33(1):98-104(in Chinese).

    [24] LINDSEY M E, TARR M A. Inhibition of hydroxyl radical reaction with aromatics by dissolved natural organic matter[J]. Environmental Science & Technology, 2000, 34:444-449.
    [25] LI J P, ZHANG X,AI Z H,et al. Efficient visible light degradation of rhodamine b by a photo-electrochemical process based on a Bi2WO6 nanoplate film electrode[J]. Journal of Physical Chemistry C, 2007, 111:6832-6836.
    [26] VELO-GALA I, LOPEZ-PENALVER J J, NCHEZ-POLO M, et al. Role of activated carbon surface chemistry in its photocatalytic activity and the generation of oxidant radicals under UV or solar radiation[J]. Applied Catalysis B:Environmental, 2017, 207:412-423.
  • 加载中
计量
  • 文章访问数:  1644
  • HTML全文浏览数:  1610
  • PDF下载数:  41
  • 施引文献:  0
出版历程
  • 收稿日期:  2018-05-20
  • 刊出日期:  2018-12-15
范星, 唐玉朝, 姚顺顺. 紫外-活性炭协同活化过硫酸氢钾对罗丹明B的降解[J]. 环境化学, 2018, 37(12): 2711-2720. doi: 10.7524/j.issn.0254-6108.2018052001
引用本文: 范星, 唐玉朝, 姚顺顺. 紫外-活性炭协同活化过硫酸氢钾对罗丹明B的降解[J]. 环境化学, 2018, 37(12): 2711-2720. doi: 10.7524/j.issn.0254-6108.2018052001
FAN Xing, TANG Yuchao, YAO Shunshun. Degradation of Rhodamine B by peroxymonosulfate synergistically activated by UV/activated carbon[J]. Environmental Chemistry, 2018, 37(12): 2711-2720. doi: 10.7524/j.issn.0254-6108.2018052001
Citation: FAN Xing, TANG Yuchao, YAO Shunshun. Degradation of Rhodamine B by peroxymonosulfate synergistically activated by UV/activated carbon[J]. Environmental Chemistry, 2018, 37(12): 2711-2720. doi: 10.7524/j.issn.0254-6108.2018052001

紫外-活性炭协同活化过硫酸氢钾对罗丹明B的降解

  • 1. 安徽建筑大学, 水污染控制与废水资源化安徽省重点实验室, 合肥, 230601
基金项目:

安徽省教育厅自然科学重点项目(KJ2015A109),住建部科学技术项目(2016-K4-077)和安徽省重点研究与开发计划(1704a0902006)资助.

摘要: 利用紫外光(UV)和活性炭(AC)协同活化过硫酸氢钾(PMS)产生硫酸根自由基(SO4-·)对染料进行降解.以罗丹明B(RhB)作为目标污染物,考察了PMS浓度、AC用量、废水初始pH等因素对体系降解RhB的影响.实验表明,UV-AC体系能有效活化PMS.AC用量0.5 g· L-1,PMS浓度为2.0 mmol· L-1时,10 mg· L-1RhB的降解率在5 min达到89%,RhB的降解率随着初始PMS浓度和AC的用量增加而增大,但超过一定量时,对降解的促进就不明显.降解反应遵循准一级动力学.自由基清除的实验证明了硫酸根自由基(SO4-·)是主要的活性自由基,羟基自由基(HO·)也起到一定的作用,同时证明UV对PMS活化的贡献大于AC.通过紫外可见光谱和FT-IR光谱分析,初步推断RhB分子降解主要是由于共轭结构裂解和N-位脱乙基等作用.五次循环实验后RhB的脱色率仍能达到85%证明了降解体系的稳定性.

English Abstract

参考文献 (26)

返回顶部

目录

/

返回文章
返回