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      카본나노튜브에 흡착된 휴믹산의 탈착에 관한 연구 = Desorption of Adsorbed Humic Acid on Carbon nano Tubes

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      https://www.riss.kr/link?id=A101661990

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      다국어 초록 (Multilingual Abstract) kakao i 다국어 번역

      Concerns have been raised over the impact of nano materials on soil and groundwater environment with the increasing attention to the potential applications of carbon nano materials in various fields. Particularly, carbon nano materials introduced into water environment readily make complexes with humic acid (HA) due to their hydrophobic nature, so there have been increasing numbers of studies on the interaction between HA and carbon nano materials. In this study, we investigated the solubility of HA and multiwalled carbon nanotubes (MWCNT) in three different surfactant solutions of sodium dodecyl sulfate (SDS), Brij 30 and Triton X-100, and evaluated whether the HA can be effectively desorbed from the surface of MWCNT by surfactant. The objective of this study was to determine the optimal adsorption condition for HA to MWCNT. Futhermore, sodium dodecyl sulfate (SDS), Brij 30, Triton X-100 were used to elucidate the effect of desorption and separation on adsorbed HA on MWCNT. As a result, HA solution with 12.7 mg of total organic carbon (TOC) and 5 mg of MWCNT showed the highest adsorption capacity at pH 3 reacted for 72 hrs. Weight solubilizing ratio (WSR) of surfactants on HA and MWCNT was calculated. HA had approximately 2 times lower adsorption capacity for the applied three surfactants compared to those of MWCNT, implying that the desorption of HA may occur from the HA/MWCNT complex. According to the results of adsorption isotherm and weight solubilizing ratio (WSR), the most effective surfactants was the SDS 1% soluiton, showing 53.63% desorption of HA at pH 3.
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      Concerns have been raised over the impact of nano materials on soil and groundwater environment with the increasing attention to the potential applications of carbon nano materials in various fields. Particularly, carbon nano materials introduced into...

      Concerns have been raised over the impact of nano materials on soil and groundwater environment with the increasing attention to the potential applications of carbon nano materials in various fields. Particularly, carbon nano materials introduced into water environment readily make complexes with humic acid (HA) due to their hydrophobic nature, so there have been increasing numbers of studies on the interaction between HA and carbon nano materials. In this study, we investigated the solubility of HA and multiwalled carbon nanotubes (MWCNT) in three different surfactant solutions of sodium dodecyl sulfate (SDS), Brij 30 and Triton X-100, and evaluated whether the HA can be effectively desorbed from the surface of MWCNT by surfactant. The objective of this study was to determine the optimal adsorption condition for HA to MWCNT. Futhermore, sodium dodecyl sulfate (SDS), Brij 30, Triton X-100 were used to elucidate the effect of desorption and separation on adsorbed HA on MWCNT. As a result, HA solution with 12.7 mg of total organic carbon (TOC) and 5 mg of MWCNT showed the highest adsorption capacity at pH 3 reacted for 72 hrs. Weight solubilizing ratio (WSR) of surfactants on HA and MWCNT was calculated. HA had approximately 2 times lower adsorption capacity for the applied three surfactants compared to those of MWCNT, implying that the desorption of HA may occur from the HA/MWCNT complex. According to the results of adsorption isotherm and weight solubilizing ratio (WSR), the most effective surfactants was the SDS 1% soluiton, showing 53.63% desorption of HA at pH 3.

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      참고문헌 (Reference)

      1 박인정, "음이온성 계면활성제(DBS)와 비이온성 계면활성제(Brij 30과 Brij 35) 와의 혼합미셀화에 대한 비교연구" 대한화학회 53 (53): 491-498, 2009

      2 엄하늬, "나노물질의 환경 매질별 노출 사례 조사" 한국화학공학회 50 (50): 1056-1063, 2012

      3 Chiou, C. T., "Water solubility enhancement of some organic pollutants and pesticides by dissolved humic and fulvic acids" 20 : 502-507, 1986

      4 Maris, K., "Study of interaction between humic acids and fullerene C60 using fluorescence quenching approach" 17 (17): 351-362, 2009

      5 Liu, Z., "Sorption of nonionic surfactants onto soil" 26 (26): 1337-1345, 1992

      6 Fei, W., "Sorption of humic acid to functionalized multi-walled carbon nanotubes" 180 : 1-6, 2013

      7 Wang, X., "Sorption and Competition of Aromatic Compounds and Humic Acid on Multiwalled Carbon Nanotubes" 43 (43): 6214-6219, 2009

      8 Li, J.L., "Solubilization of model polycyclic aromatic hydrocarbons by nonionic surfactants" 57 : 2825-2835, 2002

      9 Ahna, C. K., "Soil washing using various nonionic surfactants and their recovery by selective adsorption with activated carbon" 154 (154): 153-160, 2008

      10 Wanless, E.J., "Organization of sodium dodecyl sulfate at the graphitesolution interface" 100 (100): 3207-3214, 1996

      1 박인정, "음이온성 계면활성제(DBS)와 비이온성 계면활성제(Brij 30과 Brij 35) 와의 혼합미셀화에 대한 비교연구" 대한화학회 53 (53): 491-498, 2009

      2 엄하늬, "나노물질의 환경 매질별 노출 사례 조사" 한국화학공학회 50 (50): 1056-1063, 2012

      3 Chiou, C. T., "Water solubility enhancement of some organic pollutants and pesticides by dissolved humic and fulvic acids" 20 : 502-507, 1986

      4 Maris, K., "Study of interaction between humic acids and fullerene C60 using fluorescence quenching approach" 17 (17): 351-362, 2009

      5 Liu, Z., "Sorption of nonionic surfactants onto soil" 26 (26): 1337-1345, 1992

      6 Fei, W., "Sorption of humic acid to functionalized multi-walled carbon nanotubes" 180 : 1-6, 2013

      7 Wang, X., "Sorption and Competition of Aromatic Compounds and Humic Acid on Multiwalled Carbon Nanotubes" 43 (43): 6214-6219, 2009

      8 Li, J.L., "Solubilization of model polycyclic aromatic hydrocarbons by nonionic surfactants" 57 : 2825-2835, 2002

      9 Ahna, C. K., "Soil washing using various nonionic surfactants and their recovery by selective adsorption with activated carbon" 154 (154): 153-160, 2008

      10 Wanless, E.J., "Organization of sodium dodecyl sulfate at the graphitesolution interface" 100 (100): 3207-3214, 1996

      11 박은정, "Induction of Inflammatory Responses by Carbon Fullerene (C60) in Cultured RAW264.7 Cells and in Intraperitoneally Injected Mice" 한국독성학회 26 (26): 267-273, 2010

      12 Stevenson, F.J., "Humus chemistry-genesis, composition reaction" John Wiley & Sons, Inc 1994

      13 Islam, M. F., "High weight fraction surfactant solubilization of single- wall carbon nanotubes in water" 3 (3): 269-273, 2003

      14 Schwarzenbach, R.P., "Environmental organic chemistry" Wiley Interscience 1993

      15 Cho, H. H., "Effects of dissolved matters and anionic surfactant on the solubility of hydrophobic organic contaminants" Ewha Womans University 2000

      16 Moore, M. N., "Do nanoparticles present ecotoxicologiocal risks for the health of the aquatic environment?" 32 : 967-976, 2006

      17 Manne, S., "Direct visualization of surfactant hemimicelles by force microscopy of the electrical double layer" 10 (10): 4409-4413, 1994

      18 Kun, Y., "Desorption of polycyclic aromatic hydrocarbons from carbon nanomaterials in water" 145 : 529-537, 2007

      19 Buffle, J., "Complexation reactions in aquatic systems, an analytical approach" Ellis Horwood 692-, 1990

      20 Arnaud M., "Cellular toxicity of carbon-based nanomaterials" 6 (6): 1121-1125, 2006

      21 Luuk, K. K., "Binding of ionic surfactants to purified humic acid" 275 (275): 360-367, 2004

      22 Chen, W., "Adsorption of polar and nonpolar organic chemicals to carbon nanotubes" 41 : 8295-8300, 2007

      23 Lin, D.H., "Adsorption of phenolic compounds by carbon nanotubes: role of aromaticity and substitution of hydroxyl groups" 42 (42): 7254-7259, 2008

      24 Jianfei L., "Adsorption of mixed polycyclic aromatic hydrocarbons in surfactant solutions by activated carbon" 2013

      25 Wang, P., "Adsorption of hydrophobic organic compounds onto a hydrophobic carbonaceous geosorbent in the presence of surfactants" 27 (27): 1237-1243, 2008

      26 Park, E., "A single instillation of amorphous Silica nanoparticles induced inflammatory responses and tissue damage until day 28 after exposure" 57 (57): 60-71, 2011

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      기준연도 WOS-KCI 통합IF(2년) KCIF(2년) KCIF(3년)
      2016 0.3 0.3 0.35
      KCIF(4년) KCIF(5년) 중심성지수(3년) 즉시성지수
      0.35 0.36 0.568 0.05
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