Fe(Ⅲ)-Salen功能化纳米Fe3O4复合材料的合成及其对三氯苯的催化降解性能

蒋琦, 姜哲昊, 陈荣, 郭素芳, 冯锦秀, 沈昊宇, 胡美琴, 夏清华. Fe(Ⅲ)-Salen功能化纳米Fe3O4复合材料的合成及其对三氯苯的催化降解性能[J]. 环境化学, 2017, 36(8): 1744-1751. doi: 10.7524/j.issn.0254-6108.2017010901
引用本文: 蒋琦, 姜哲昊, 陈荣, 郭素芳, 冯锦秀, 沈昊宇, 胡美琴, 夏清华. Fe(Ⅲ)-Salen功能化纳米Fe3O4复合材料的合成及其对三氯苯的催化降解性能[J]. 环境化学, 2017, 36(8): 1744-1751. doi: 10.7524/j.issn.0254-6108.2017010901
JIANG Qi, JIANG Zhehao, CHEN Rong, GUO Sufang, FENG Jinxiu, SHEN Haoyu, HU Meiqin, XIA Qinghua. Preparation of Fe(Ⅲ)-Salen-functionalized nano-Fe3O4 magnetic composite and its catalytic degradation of 2,4,6-trichlorophenol[J]. Environmental Chemistry, 2017, 36(8): 1744-1751. doi: 10.7524/j.issn.0254-6108.2017010901
Citation: JIANG Qi, JIANG Zhehao, CHEN Rong, GUO Sufang, FENG Jinxiu, SHEN Haoyu, HU Meiqin, XIA Qinghua. Preparation of Fe(Ⅲ)-Salen-functionalized nano-Fe3O4 magnetic composite and its catalytic degradation of 2,4,6-trichlorophenol[J]. Environmental Chemistry, 2017, 36(8): 1744-1751. doi: 10.7524/j.issn.0254-6108.2017010901

Fe(Ⅲ)-Salen功能化纳米Fe3O4复合材料的合成及其对三氯苯的催化降解性能

  • 基金项目:

    国家自然科学基金(51608479),浙江省自然科学基金(LY14B04003),宁波市自然科学基金(2014A610092),国家级大学生创新创业训练计划项目(201513022009)和浙江省新苗计划项目(2015R401181)资助.

Preparation of Fe(Ⅲ)-Salen-functionalized nano-Fe3O4 magnetic composite and its catalytic degradation of 2,4,6-trichlorophenol

  • Fund Project: Supported by the National Natural Science Foundation (51608479),National Natural Science Foundation of Zhejiang Province (LY14B04003),National Natural Science Foundation of Ningbo (2014A610092),National College Students' Innovation and Entrepreneurship Training Program (201513022009) and Xinmiao Students' Innovation Training Program of Zhejiang Province (2015R401181).
  • 摘要: 采用溶剂热制备了氨基功能化纳米Fe3O4 磁性复合材料(NH2-nFe3O4), 并进一步通过缩合、配位等反应得到Fe(Ⅲ)-Salen功能化纳米Fe3O4复合材料(nFe3O4@Fe(Ⅲ)Salen). 通过元素分析(EA)、X-射线衍射(XRD)、红外光谱(FTIR)、透射电镜(TEM)、振动样品磁强计(VSM)等手段对其进行了组成、结构、形貌、磁性等表征. 结果表明, nFe3O4@Fe(Ⅲ)Salen平均粒径为约200 nm, 饱和磁化强度为24.8 emu·g-1. 催化剂为nFe3O4@Fe(Ⅲ)Salen, 研究了其在可见光/H2O2类Fenton体系催化降解水中2,4,6-三氯酚(2,4,6-TCP)的性能.研究发现, 当nFe3O4@Fe(Ⅲ)Salen用量 ≥ 0.8 g·L-1,溶液pH值为4.0-7.0, H2O2浓度为 8.16-40.8 mmol·L-1时, nFe3O4@Fe(Ⅲ)Salen/H2O2/可见光体系可以实现对浓度-1(253.2 mg·L-1)的TCP溶液在5 min内近100%降解,较普通Fenton反应体系有更宽的pH适用范围. 循环使用5次后, 该催化体系对TCP的降解率仍能保持95%以上, nFe3O4@Fe(Ⅲ)Salen是有优异潜力的水中TCP绿色催化剂.
  • 加载中
  • [1] CAGNETTA G, ROBERTSON J, HUANG J, et al. Mechanochemical destruction of alogenated organic pollutants:A critical review[J]. Journal of Hazardous Materials, 2016, 313:85-102.
    [2] CZAPLICKA M. Sources and transformations of chlorophenols in the natural environment[J]. Science of the Tolal Environment, 2004, 322:21-29.
    [3] GUO J Q, WU C H, LV S L, et al. Associations of prenatal exposure to five chlorophenols with adverse birth outcomes[J]. Environmental Pollution, 2016, 214:478-484.
    [4] LIMAM I, LIMAM R D, MEZNI M, et al. Penta-and 2,4,6-tri-chlorophenol biodegradation during municipal solid waste anaerobic digestion[J]. Ecotoxicology and Environmental Safety, 2016, 130:270-278.
    [5] ANGELUCCI D M, TOMEI M C. Ex situ bioremediation of chlorophenol contaminated soil:Comparison of slurry and solid-phase bioreactors with the two-step polymer extraction-bioregeneration process[J]. Journal of Chemical Technology and Biotechnology, 2016, 91:1577-1584.
    [6] 张佳丽,叶然,徐潇潇, 等. 分子印迹氨基功能化磁性复合材料的合成及其对海水中2,4,6-三氯苯酚的吸附性能[J]. 复合材料学报, 2015, 4:1201-1210. ZHANG J L, YE R, XU X X, et al. Preparation of molecular printed amino-functionalized nano-Fe3

    O4-polymer magnetic composite material and its adsorption properties on 2,4,6-trichlorophenol in seawater[J]. Acta Material Composite Sinica, 2015, 4:1201-1210(in Chinese).

    [7] 孙亚锡, 沙布, 王晓东, 等. 膜生物反应器去除原水中微量2,4,6-三氯酚的研究[J]. 水处理技术, 2007, 33(12):42-45.

    SUN Y X, SHA B, WANG X D, et al. Removal of trace from surface water by membrane bioreactor[J]. Technology of Water Treatment, 2007, 33(12):42-45(in Chinese).

    [8] HUANG W J, FANG G C, WANG C C. A nanometer-ZnO catalyst to enhance the ozonation of 2,4,6-trichlorophenol in water[J]. Colloids and Surfaces A:Physicochemical Engineering Aspects, 2005, 260:45-51.
    [9] 杨静, 崔世海, 陈慧慧, 等. 磁载纳米TiO2复合光催化材料的研究进展[J]. 环境化学,2014,33(11):1930-1935.

    YANG J, CUI S H, CHEN H H, et al. Research progress on magnetic TiO2 composite nano-photocatalysts[J]. Environmental Chemistry, 2014, 33(11):1930-1935(in Chinese).

    [10] HU M Q, WANG Y, XIONG Z G, et al. Iodine-sensitized degradation of 2,4,6-trichlorophenol under visible light[J]. Environmental Science and Technology, 2012, 46:9005-9011.
    [11] 饶志, 顾彦,黄春迎,等.FeVO4可见光光催化降解有毒有机污染物[J]. 环境化学,2013,32(4):564-570.

    RAO Z, GU Y, HUANG C Y, et al. Photodegradation of toxic organic pollutants by FeVO4 under visible light irradiation[J]. Environmental Chemistry, 2013, 32(4):564-570(in Chinese).

    [12] GOLDSTEIN N S, MEYERSTEIN D. Comments on the mechanism of the "Fenton-Like" reaction[J]. Accounts Chemical Research, 1999, 32(7):547-549.
    [13] HUANG Y, MA W, ZHAO J. A novel β-CD-Hemin complex photocatalyst for efficient degradation of organic pollutants at neutral pHs under visible irradiation[J]. Journal of Physical Chemistry, 2003, 107(35):9409-9414.
    [14] COLLINS T J. TAML oxidant activators:A new approach to the activation of hydrogen peroxide for environmentally significant problems[J]. Accounts Chemical Research, 2002, 35(9):782-790.
    [15] GUPTA S S, STADLER M, NOSER C, et al. Rapid total destruction of chlorophenols by activated hydrogen peroxide[J]. Science, 2002, 296:326-328.
    [16] SHEN H Y, ZHU Y, WEN X E, et al. Preparation of Fe3O4-C18 nano-magnetic composite materials and their cleanup properties for organophosphorous pesticides[J]. Analytic Bioanalytic Chemistry, 2007, 387:2227-2237.
    [17] 陈君良, 姚屠鹏, 朱宏亮, 等. 巯基功能化纳米Fe3O4磁性高分子复合材料的合成及其对水中亚甲基蓝的吸附作用[J]. 复合材料学报,2014,31(2):323-330.

    CHEN J L, YAO T P, ZHU H L, et al. Preparation of thiol-functionalized nano-Fe3O4-polymer magnetic composite material and its adsorption properties on methylene blue in water[J]. Acta Material Composite Sinica, 2014,31(2):323-330(in Chinese).

    [18] SHEN H Y, CHEN Z X, LI Z H, et al. Controlled synthesis of 2,4,6-trichlorophenol-imprinted amino-functionalized nano-Fe3O4-polymer magnetic composite for highly selective adsorption[J]. Colloids and Surfaces A:Physicochemical Engineering Aspects, 2015, 481:439-450.
    [19] 张蕴, 奚晓青, 许姗妮, 等. 氨基功能化纳米复合材料对水中磷酸盐的吸附研究[J]. 化学学报, 2012, 70(17):1839-1846.

    ZHANG Y, XI X Q, XU S N, et al. Adsorption studies on phosphate by amino-functionalized nano-size composite materials[J]. Acta Chimica Sinica, 2012, 70(17):1839-1846(in Chinese).

    [20] PAN S D, SHEN H Y, ZHOU L X, et al. Controlled synthesis of pentachlorophenol imprinted polymers on the surface of magnetic graphene oxide for highly selective adsorption[J]. Journal of Material Chemistry A, 2014, 2:15345-15356.
    [21] 杨军,谢晟瑜,陈扬,等. μ-O-桥联均相铁(Ⅲ)催化剂的合成及其对邻苯二甲酸二丁酯的降解性能[J]. 环境化学,2016,35(9):1745-1752.

    YANG J, XIE S Y, CHEN Y, et al. Synthesis of homogeneous μ-H2O-Fe(Ⅲ) catalyst and its application in degradation of dibutyl phthalate (DBP)[J]. Environmental Chemistry, 2016,35(9):1745-1752(in Chinese).

    [22] 焦利敏, 黄鑫, 廖学品, 等. 胶原纤维负载铁Fe(Ⅲ)催化剂对邻苯二甲酸二甲酯的光助催化降解[J]. 化工学报, 2011, 69(12):3419-3427.

    JIAO L M, HUANG X, LIAO X P, et al. Catalytic degradation of dimethyl phthalate by photo-assisted Fe(Ⅲ) immobilized collagen fiber[J]. Journal of Chemical Industry and Engineering (China), 2011, 69(12):3419-3427(in Chinese).

  • 加载中
计量
  • 文章访问数:  1946
  • HTML全文浏览数:  1893
  • PDF下载数:  370
  • 施引文献:  0
出版历程
  • 收稿日期:  2017-01-09
  • 刊出日期:  2017-08-15

Fe(Ⅲ)-Salen功能化纳米Fe3O4复合材料的合成及其对三氯苯的催化降解性能

  • 1.  浙江大学宁波理工学院, 生物与化学工程学院, 宁波, 315100;
  • 2.  湖北大学, 有机化工新材料湖北省协同创新中心, 有机功能分子合成与应用教育部重点实验室, 武汉, 430062
基金项目:

国家自然科学基金(51608479),浙江省自然科学基金(LY14B04003),宁波市自然科学基金(2014A610092),国家级大学生创新创业训练计划项目(201513022009)和浙江省新苗计划项目(2015R401181)资助.

摘要: 采用溶剂热制备了氨基功能化纳米Fe3O4 磁性复合材料(NH2-nFe3O4), 并进一步通过缩合、配位等反应得到Fe(Ⅲ)-Salen功能化纳米Fe3O4复合材料(nFe3O4@Fe(Ⅲ)Salen). 通过元素分析(EA)、X-射线衍射(XRD)、红外光谱(FTIR)、透射电镜(TEM)、振动样品磁强计(VSM)等手段对其进行了组成、结构、形貌、磁性等表征. 结果表明, nFe3O4@Fe(Ⅲ)Salen平均粒径为约200 nm, 饱和磁化强度为24.8 emu·g-1. 催化剂为nFe3O4@Fe(Ⅲ)Salen, 研究了其在可见光/H2O2类Fenton体系催化降解水中2,4,6-三氯酚(2,4,6-TCP)的性能.研究发现, 当nFe3O4@Fe(Ⅲ)Salen用量 ≥ 0.8 g·L-1,溶液pH值为4.0-7.0, H2O2浓度为 8.16-40.8 mmol·L-1时, nFe3O4@Fe(Ⅲ)Salen/H2O2/可见光体系可以实现对浓度-1(253.2 mg·L-1)的TCP溶液在5 min内近100%降解,较普通Fenton反应体系有更宽的pH适用范围. 循环使用5次后, 该催化体系对TCP的降解率仍能保持95%以上, nFe3O4@Fe(Ⅲ)Salen是有优异潜力的水中TCP绿色催化剂.

English Abstract

参考文献 (22)

目录

/

返回文章
返回