南京大学学报(自然科学版) ›› 2014, Vol. 50 ›› Issue (4): 405–.

• • 上一篇    下一篇

碳纳米管在水溶液中的聚集和沉降行为研究

张淑娟,周丽霞,潘丙才   

  • 出版日期:2014-08-22 发布日期:2014-08-22
  • 作者简介: 南京大学环境学院,污染控制与资源化研究国家重点实验室,南京,210023
  • 基金资助:
     国家自然科学基金(21107045)、江苏省自然科学基金(BK2011575)、教育部新世纪优秀人才(NCET-10-0489)

The aggregation and deposition of carbon nanotubes in aquatic environment

 Zhou Lixia, Zhang Shujuan *, Pan Bingcai   

  • Online:2014-08-22 Published:2014-08-22
  • About author: State Key Laboratory of Pollution Control and Resource Reuse,
    School of the Environment, Nanjing University, Nanjing, 210023, China

摘要:  作为一种新型的碳质纳米材料,碳纳米管因其独特的物理和化学性能被广泛应用于各种高性能材料或器件。碳纳米管一旦被排放到水体中,因其巨大的比表面积将导致水环境中共存物质形态的改变,碳纳米管自身的赋存状态也将因共存物质的吸附而改变,从而直接或间接影响水体的毒理学特性。因此,有关碳纳米管聚集和沉降行为的研究对预测和评价其在自然水体中的环境效应具有重要的意义。本文通过描述胶体作用力的经典Derjaguin-Landau-Verwey-Overbeek (DLVO) 理论和非DLVO作用力,并借助时间分辨的动态光散射、石英晶体微天平和柱过滤测试,探讨了碳纳米管在水溶液中的聚集和沉降动力学,分析了碳纳米管的结构特性、电解质、溶液pH和天然有机质等因素对碳纳米管在水溶液中分散稳定性的影响及原因,阐明了控制碳纳米管颗粒在水溶液中聚集和沉降行为的作用机制,指出了在碳纳米管的聚集和沉降行为研究中存在的技术难点,并对未来碳纳米管的实验研究进行了展望。

Abstract:  As a novel nanoscale carbonaceous materials, carbon nanotubes (CNTs) have attracted extensive interests. Due to their unique electronic, optical, thermal, and mechanical properties, CNTs have been an ideal materials for industrial application. The ever rising demand and the decreasing cost lead to increased release of CNTs into natural waters. Once exposed to water environment, owing to their large specific surface areas, CNTs will inevitably adsorb the coexsited organic contaminations. Due to their nanoscale, CNTs are easily penetrated into human body, thus becoming a latent threate to both the environment and human being. The bioavailability and the toxicity of CNTs largely depend on their particle size in aquatic environment. In other words, the dispersion stability of CNTs is a key factor in determining their transport and fate in aquatic environment. Therefore, studies on the aggregation and deposition behavior of CNTs is of great significance to predict their environmental effects on water bodies. In this review, the mechanisms for the aggregation and deposition behaviors of CNTs were elucidated by describing the interactions between CNT colloidals with the classical Derjaguin-Landau-Verwey-Overbeek (DLVO) theory and the non-DLVO forces. The aggregation and deposition kinetics of CNTs was probed with the aid of time-resolved dynamic light scattering, quartz crystal microbalance, and column filtration analysis. The effects of some influencing factors, such as the physiochemical properties of CNTs (diameter, length, the content of surface functional groups), ionic strength, solution pH, and natural organic matters, on the dispersion stability of CNTs were evaluated. Moreover, the main difficulties in the study of the aggregation and deposition behavior of CNTs were pointed out. The complexity of matters in natural water and the lack of suitable experimental approach aggravated the difficulties in the current investigation on CNTs. The possible development of experimental research on CNTs in the near future was put forward.

 [1] Rosen R, Simendinger W, Debbault C, et al. Application of carbon nanotubes as electrodes in gas discharge tubes. Applied Physics Letters, 2000,76(13):1668~1670.
[2] Che G L, Lakshmi B B, Fisher E R, et al. Carbon nanotubule membranes for electrochemical energy storage and production. Nature,1998,393:346~ 349.
[3] Ajayan P M, Stephan O, Colliex C, et al. Aligned carbon nanotube arrays formed by cutting a polymer resin-nanotube composite. Science,1994, 265(5176):1212~1214.
[4] Baughman R H, Cui C, Zakhidov A A, et al. Carbon nanotube actuators. Science,1999,284(5418):1340~1344.
[5] Cientifica “Nanotubes Report 2004,” Cientifica, 2004.
[6] Bystrzejewski M, Huczko A, Büchner G B, et al. Dispersion and diameter separation of multi-wall carbon nanotubes in aqueous solutions. Journal of Colloid and Interface. Science,2010,345(2):138~142.
[7] Saleh N B, Pfefferle L D, Elimelech M. Aggregation kinetics of multiwalled carbon nanotubes in aquatic systems: Measurements and environmental implications. Environmental Science and Technology,2008,42(21):7963~ 7969.
[8] Shi B, Zhuang X, Yan X, et al. Adsorption of atrazine by natural organic matter and surfactant dispersed carbon nanotubes. Journal of Environmental Sciences,2010,22(8):1195~1202.
[9] Hyung H, Frotner J D, Hughes J B, et al. Natural organic matter stabilizes carbon nanotubes in the aqueous sphase. Environmental Science and Technology,2007,41(1):179~184.
[10] Wang Y G, Kim J-H, Baek J-B, et al. Transport behavior of functionalized multi-wall carbon nanotubes in water-saturated quartz sand as a function of tube length. Water Research,2012,46(14):4521~4531.
[11] Klaine S J, Alvarez P J J, Batley G E, et al. Nanomaterials in the environment: Behavior, fate, bioavailability, and effects. Environmental Toxicology and Chemistry,2008,27(9):1825~1851.
[12] Müller T J J, Bunz U H F. Functional organic materials: syntheses, strategies and applications. John Wiley & Sons,2005,193~237.
[13] Chen K L, Elimelech M. Aggregation and deposition kinetics of fullerene (C60) nanoparticles. Langmuir,2006,22(26):10994~11001.
[14] Chen K L, Smith B A, Ball W P et al. Assessing the colloidal properties of engineered nanoparticles in water: case studies from fullerene C60 nanoparticles and carbon nanotubes. Environmental Chemistry,2010, 7:10~27.
[15] Li Y S, Wang Y G, Pennell K D, et al. Investigation of the transport and deposition of fullerene (C60) nanoparticles in quartz sands under varying flow conditions. Environmental Science & Technology,2008,42(19): 7174~7180.
[16] Saleh N B, Pfefferle, L D, Elimelech, M. Influence of biomacromolecules and humic acid on the aggregation kinetics of single-walled carbon nanotubes. Environmental Science & Technology,2010,44(7):2412~2418.
[17] Chen K L, Mylon, S E, Elimelech, M. Aggregation kinetics of alginate-coated hematite nanoparticles in monovalent and divalent electrolytes. Environmental Science & Technology,2006,40(5):1516~1523.
[18] Hunter R J. Foundations of colloid science, Oxford, UK: Oxford University Press, 2002.
[19] Dickinson E, Eriksson L. Particle flocculation by adsorbing polymers. Advances in Colloid Interface Science,1991,34:1~29.
[20] Zhang S J, Shao T, Karanfil T. The effects of dissolved natural organic matter on the adsorption of synthetic organic chemicals by activated carbons and carbon anotubes. Water Research,2011,45(3):1378~1386.
[21] King S M, Jarvie H P. Exploring how organic matter controls structural transformations in natural aquatic nanocolloidal dispersions. Environmental Science & Technology,2012,46(13):6959~6967.
[22] Zhou X, Zhao H, Guo X, et al. Suspending multi-walled carbon nanotubes by humic acids from a peat soil. Environmental Science & Technology, 2012,46(7):3891~3897.
[23] Healy T W, Homola A, James R O, et al. Coagulation of amphoteric latex colloids: reversibility and specific ion effects. Faraday Discuss of the Chemical Society,1978,65:156~163.
[24] Elimelech M, Jia X D, Gregory O, et al. Particle deposition and aggregation: measurement, modelling and simulation. Oxford, UK: Butterworth-Heinemann, 1995.
[25] Bouchard D, Zhang W, Powell T, et al. Aggregation kinetics and transport of single-walled carbon nanotubes at low surfactant concentrations. Environmental Science & Technology,2012,46(8):4458~4465.
[26] Pautler B G, Woods G C, Dubnick A, et al. Molecular characterization of dissolved organic matter in glacial ice: coupling natural abundance H NMR and fluorescence spectroscopy. Environmental Science & Technology,2012,46(7):3753~3761.
[27] Chae S R, Xiao Y, Noeiaqhaei T, et al. Effects of humic acid and electrolytes on photocatalytic reactivity and transport of carbon nanoparticle aggregates in water. Water Research,2012,46(13):4053~4062.
[28] Azoubel S, Magdassi S. The formation of carbon nanotube dispersions by high pressure homogenization and their rapid characterization by analytical centrifuge. Carbon,2010,48(12):3346~3352.
[29] Yi P, Chen K L. Influence of solution chemistry on the release of multiwalled carbon nanotubes from silica surfaces. Environmental Science & Technology,2013,47(21):12211~12218.
[30] Harel Y, Azoubel S, Magdassi S, et al. A dispersability study on poly (thiophen-3-yl-acetic acid) and PEDOT multi-walled carbon nanotube composites using an analytical centrifuge. Journal of Colloid and Interface Science,2013,390(1):62~69.
[31] Smith B, Wepasnick K, Schrote K E, et al. Colloidal properties of aqueous suspensions of acid-treated, multi-walled carbon nanotubes. Environmental Science & Technology,2009,43(3):819~825.
[32] Tufenkji N, Elimelech M. Correlation equation for predicting single-collector efficiency in physicochemical filtration in saturated porous media. Environmental Science & Technology,2004,38(2):529~536.
[33] Lecoanet H F, Bottero J Y, Wiesner M R. Laboratory assessment of themobility of nanomaterials in porousmedia. Environmental Science & Technology,2004,38(19):5164~5169.
[34] Petosa A R, Jaisi D P, Quevedo I R, et al. Aggregation and deposition of engineered nanomaterials in aquatic environments: role of physicochemical interactions. Environmental Science & Technology,2010, 44(17):6532~6549.
[35] Bradford S A, Yates S R, Bettahar M, et al. Physical factors affecting the transport and fate of colloids in saturated porous media. Water Resource Research,2002,38(12):63-1~63-12.
[36] Bradford S A, Simunek J, Bettahar M, et al. Modeling colloid attachment, straining, and exclusion in saturated porous media. Environmental Science & Technology.,2003,37(10):2242~2250.
[37] Fatisson J, Domingos R F, Wilkinson K J, et al. Deposition of TiO2 nanoparticles onto silica measured using a quartz crystal microbalance with dissipation monitoring. Langmuir,2009,25(11):6062~6069.
[38] Sirk K M, Saleh N B, Phenrat T, et al. Effect of adsorbed polyelectrolytes on nanoscale zero-valent iron particle attachment to soil surface models. Environmental Science & Technology,2009,43(10):3803~3808.
[39] Saleh N, Sirk K, Liu Y Q, et al. Surface modifications enhance nanoiron transport and NAPL targeting in saturated porous media. Environmental Engineering Science,2007,24(1):45~57.
[40] Lin D H, Xing B S. Tannic acid adsorption and its role for stabilizing carbon nanotube suspensions. Environmental Science & Technology.,2008, 42(16):5917~5923.
[41] Smith B, Wepasnick K, Schrote K E, et al. Influence of surface oxides on the colloidal stability of multiwalled carbon nanotubes: a structure-property relationship. Langmuir,2009,25(17):9767~9776.
[42] Hu H, Yu A, Kim E, et al. Influence of the zeta potential on the dispersability and purification of single-walled carbon nanotubes. Journal of Physical Chemistry B,2005,109(23):11520~11524.
[43] Summers R S, Roberts P V. Activated carbon adsorption of humic substances: II. Size exclusion and electrostatic interactions. Journal of Colloid and Interface Science,1988,122(2):382~397.
[44] Lin D H, Liu N, Yang K, et al. The effect of ionic strength and pH on the stability of tannic acid-facilitated carbon nanotube suspensions. Carbon, 2009,47(12):2875~2882.
[45] Wang X L, Tao S, Xing B S. Sorption and competition of aromatic compounds and humic acid on multiwalled carbon nanotubes. Environmental Science & Technology,2009,43(16):6214~6219.
[46] Yang K, Xing B S. Adsorption of fulvic acid by carbon nanotubes from water. Environmental Pollution,2009,157(4):1095~1100.
[47] Hyung H, Kim J H. Natural organic matter (NOM) adsorption to multi-walled carbon nanotubes: effect of NOM characteristics and water quality parameters. Environmental Science & Technology,2008,45(12):4416~4421.
[48] Gotovac S, Honda H, Hattori Y, et al. Effect of nanoscale curvature of single-walled carbon nanotubes on adsorption of polycyclic aromatic hydrocarbons. Nano Letters,2007,7(3):583~587.
No related articles found!
Viewed
Full text


Abstract

Cited

  Shared   
  Discussed   
No Suggested Reading articles found!