磁性氧化铁纳米颗粒在不同性质分散剂作用下的聚合状态

徐其静, Ghosh Saikat, 王朋, 郭秉林, 郭倩月, 郭进. 磁性氧化铁纳米颗粒在不同性质分散剂作用下的聚合状态[J]. 环境化学, 2018, 37(2): 327-334. doi: 10.7524/j.issn.0254-6108.2017071202
引用本文: 徐其静, Ghosh Saikat, 王朋, 郭秉林, 郭倩月, 郭进. 磁性氧化铁纳米颗粒在不同性质分散剂作用下的聚合状态[J]. 环境化学, 2018, 37(2): 327-334. doi: 10.7524/j.issn.0254-6108.2017071202
XU Qijing, GHOSH Saikat, WANG Peng, GUO Binglin, GUO Qianyue, GUO Jin. Aggregation of magnetic iron oxide nanoparticles under dispersants with differentproperties[J]. Environmental Chemistry, 2018, 37(2): 327-334. doi: 10.7524/j.issn.0254-6108.2017071202
Citation: XU Qijing, GHOSH Saikat, WANG Peng, GUO Binglin, GUO Qianyue, GUO Jin. Aggregation of magnetic iron oxide nanoparticles under dispersants with differentproperties[J]. Environmental Chemistry, 2018, 37(2): 327-334. doi: 10.7524/j.issn.0254-6108.2017071202

磁性氧化铁纳米颗粒在不同性质分散剂作用下的聚合状态

  • 基金项目:

    国家自然科学基金(41573100)资助.

Aggregation of magnetic iron oxide nanoparticles under dispersants with differentproperties

  • Fund Project: Supported by the National Natural Science Foundation of China(41573100).
  • 摘要: 磁性氧化铁(γFe2O3)纳米颗粒广泛应用导致其进入环境中引起环境风险.由于本身固有的磁极力作用,γFe2O3纳米颗粒在水相环境中极易聚合沉降.然而,自然环境中广泛存在的有机物,包括胡敏酸(HA)和球状蛋白质如牛血清蛋白(BSA),能够极大地加强其胶体稳定性,使之易于在环境中迁移转化,进而增加了环境风险.本研究考察在pH=4时,HA和BSA分别作用下,γFe2O3纳米颗粒胶体稳定性的相对变化.运用动态光散射原理(DLS)分析颗粒的平均水合直径(DH)变化,原位原子力显微镜(AFM)及非原位透射电镜(TEM)等手段考察颗粒的分散情况.结果证实:此pH条件下,两种物质均能在不同程度上使γFe2O3分散.然而,相比于BSA,环境中广泛存在具有低pKa且吸附亲和力较强的HA,能够使γFe2O3纳米颗粒的分散性更好,其产生的环境风险也更大.
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  • [1] LOOSLI F,VITORAZI L,BERRET J O,et al. Isothermal titration calorimetry as a powerful tool to quantify and better understand agglomeration mechanisms during interaction processes between TiO2 nanoparticles and humic acids[J]. Environmental Science Nano,2015,2(5):541-550.
    [2] AUFFAN M,ROSE J,BOTTERO J Y,et al. Towards a definition of inorganic nanoparticles from an environmental,health and safety perspective[J]. Nature Nanotechnology,2009,4(10):634-641.
    [3] CHALOUPKA K,MALAM Y,SEIFALIAN A M. Nanosilver as a new generation of nanoproduct in biomedical applications[J]. Trends Biotechnol,2010,28(11):580-588.
    [4] BENN T M,WESTERHOFF P. Nanoparticle silver released into water from commercially available sock fabrics[J]. Environmental Science & Technology,2008,42(11):4133-4139.
    [5] YEVGEN N,HAN T W,PAUL J,et al. Potential for exposure to engineered nanoparticles from nanotechnology-based consumer spray products[J]. J Expo Sci Environ Epidemiol,2011,21(5):515-528.
    [6] STEFAN L,SCHNEIDER O D,TOBIAS M,et al. Micro-organism-triggered release of silver nanoparticles from biodegradable oxide carriers allows preparation of self-sterilizing polymer surfaces[J]. Small,2008,4(6):824-832.
    [7] SAYES C M,FORTNER J D,GUO W,et al. The differential cytotoxicity of water-soluble fullerenes[J]. Nano Letters,2004,4(10):1881-1887.
    [8] OBERDRSTER E,ZHU S,BLICKLEY T M,et al. Ecotoxicology of carbon-based engineered nanoparticles:Effects of fullerene (C60) on aquatic organisms[J]. Carbon,2006,44(6):1112-1120.
    [9] LAM U T,KIYONORI S,MAMMUCARI R,et al. Processing of iron oxide nanoparticles by supercritical fluids.[J]. American Chemical Society,2008,47(3):599-614.
    [10] WEAVER T,NOGINOVA N,KING M,et al. NMR and spin relaxation in systems with magnetic nanoparticles[J]. Journal of Physics Condensed Matter An Institute of Physics Journal,2006,984(25):255301.
    [11] MOSLEY L M,HUNTER K A,DUCKER W A. Forces between colloid particles in natural waters[J]. Environmental Science & Technology,2003,37(15):3303-3308.
    [12] MYLON S E,CHEN K L,ELIMELECH M. Influence of natural organic matter and ionic composition on the kinetics and structure of hematite colloid aggregation:Implications to iron depletion in estuaries[J]. Langmuir,2004,20(21):9000-9006.
    [13] HEIDMANN I,CHRISTL I,KRETZSCHMAR R. Aggregation kinetics of kaolinite-fulvic acid colloids as affected by the sorption of Cu and Pb[J]. Environmental Science & Technology,2005,39(3):807-813.
    [14] WILKINSON K J,JOZ-ROLAND A,BUFFLE J. Different roles of pedogenic fulvic acids and aquagenic biopolymers on colloid aggregation and stability in freshwaters[J]. Limnology & Oceanography,1997,42(8):1714-1724.
    [15] GHOSH S,MASHAYEKHI H,BHOWMIK P,et al. Colloidal stability of Al2O3 nanoparticles as affected by coating of structurally different humic acids[J]. Langmuir,2010,26(2):873-879.
    [16] GHOSH S,WEI J D,XING B S,et al. Colloidal stability of magnetic iron oxide nanoparticles:Influence of nature organic matter and synthetic polyelectrolytes[J]. Langmuir,2011:27(13):8036-8043.
    [17] DU P,ZHAO J,MASHAYEKHI H,et al. Adsorption of bovine serum albumin and lysozyme on functionalized carbon nanotubes[J]. Journal of Physical Chemistry C,2014,118(38):22249-22257.
    [18] CARNAL F,CLAVIER A,STOLL S. Polypeptide-nanoparticle interactions and corona formation investigated by monte carlo simulations[J]. Polymers,2016,8(6):203.
    [19] BARBOSA L R S,ORTORE M G,SPINOZZI F,et al. The importance of protein-protein interactions on the pH-induced conformational changes of bovine serum albumin:A Small-Angle X-Ray Scattering Study[J]. Biophysical Journal,2010,98(1):147-157.
    [20] LYNCH I,DAWSON K A. Protein-nanoparticle interactions[J]. Nano Today,2008,3(1):40-47.
    [21] SRIVASTAVA S,SAMANTA B,ARUMUGAM P,et al. DNA-mediated assembly of iron platinum (FePt) nanoparticles[J]. Journal of Materials Chemistry,2007,17(1):52-55.
    [22] SAMANTA B,YAN H,FISCHER N O,et al. Protein-passivated Fe3O4 nanoparticles:Low toxicity and rapid heating for thermal therapy[J]. Journal of Materials Chemistry,2008,18(11):1204-1208.
    [23] MATTHEW N M,ANDREW J A,MACCUSPIE R I,et al. Dissolution,agglomerate morphology,and stability limits of protein-coated silver nanoparticles[J]. Langmuir the Acs Journal of Surfaces & Colloids,2014,30(38):11442-11452.
    [24] KANG S,XING B. Phenanthrene sorption to sequentially extracted soil humic acids and humins[J]. Environmental Science & Technology,2005,39(1):134-140.
    [25] WANG L,LIANG N,LI H,et al. Quantifying the dynamic fluorescence quenching of phenanthrene and ofloxacin by dissolved humic acids[J]. Environmental Pollution,2015,196:379-385.
    [26] OU Y H,CHANG Y J,LIN F Y,et al. Competitive sorption of bisphenol A and phenol in soils and the contribution of black carbon[J]. Ecological Engineering,2016,92(2):270-276.
    [27] PHENRAT T,SALEH N,SIRK K,et al. Stabilization of aqueous nanoscale zerovalent iron dispersions by anionic polyelectrolytes:adsorbed anionic polyelectrolyte layer properties and their effect on aggregation and sedimentation[J]. Journal of Nanoparticle Research,2008,10(5):795-814.
    [28] RAFIGH S M,YAZDI A V,SAFEKORDI A A,et al. Protein adsorption using novel carboxymethyl-curdlan microspheres[J]. International Journal of Biological Macromolecules,2016,87:603-610.
    [29] KOSMULSKI M,PR CHNIAK P,ROSENHOLM J B. Electrokinetic study of adsorption of ionic surfactants on titania from organic solvents[J]. Colloids & Surfaces A Physicochemical & Engineering Aspects,2009,348(1-3):298-300.
    [30] BISHOP K J,WILMER C E,SOH S,et al. Nanoscale forces and their uses in self-assembly[J]. Small,2009,5(14):1600-1630.
    [31] SCHNITZER M,SCHUPPLI P,SCHULTEN H R,et al. Organic matter extraction from soils with water at high pressure and temperatures[J]. Soil Science Society of America Journal,1991,55(1):102-108.
    [32] GULLEYSTAHL H,ND H P,SCHMIDT W L,et al. Surface complexation of catechol to metal oxides:An ATR-FTIR,adsorption,and dissolution study[J]. Environmental Science & Technology,2010,44(16):6517-6518.
    [33] KANG S,XING B. Humic acid fractionation upon sequential adsorption onto goethite[J]. Langmuir the Acs Journal of Surfaces & Colloids,2008,24(6):2525-2531.
    [34] OLIVEIRA L K,MOLINA E F,MOURA A L,et al. Synthesis,characterization,and environmental applications of hybrid materials based on humic acid obtained by the Sol-Gel Route[J]. ACS Appl Mater Interfaces,2016,8(2):1478-1485.
    [35] GHOSH S,PRADHAN N R,MASHAYEKHI H,et al. Colloidal aggregation and structural assembly of aspect ratio variant goethite (α-FeOOH) with nC60 fullerene in environmental media[J]. Environmental Pollution,2016,219:1049-1059.
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  • 收稿日期:  2017-07-12
  • 刊出日期:  2018-02-15

磁性氧化铁纳米颗粒在不同性质分散剂作用下的聚合状态

  • 1.  昆明理工大学, 环境科学与工程学院, 昆明, 650500;
  • 2.  云南省红河哈尼族彝族自治州环境保护局, 红河, 661100
基金项目:

国家自然科学基金(41573100)资助.

摘要: 磁性氧化铁(γFe2O3)纳米颗粒广泛应用导致其进入环境中引起环境风险.由于本身固有的磁极力作用,γFe2O3纳米颗粒在水相环境中极易聚合沉降.然而,自然环境中广泛存在的有机物,包括胡敏酸(HA)和球状蛋白质如牛血清蛋白(BSA),能够极大地加强其胶体稳定性,使之易于在环境中迁移转化,进而增加了环境风险.本研究考察在pH=4时,HA和BSA分别作用下,γFe2O3纳米颗粒胶体稳定性的相对变化.运用动态光散射原理(DLS)分析颗粒的平均水合直径(DH)变化,原位原子力显微镜(AFM)及非原位透射电镜(TEM)等手段考察颗粒的分散情况.结果证实:此pH条件下,两种物质均能在不同程度上使γFe2O3分散.然而,相比于BSA,环境中广泛存在具有低pKa且吸附亲和力较强的HA,能够使γFe2O3纳米颗粒的分散性更好,其产生的环境风险也更大.

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