低剂量三氯生和三氯卡班对嗜热四膜虫的毒性研究

白琦锋, 高礼, 袁涛. 低剂量三氯生和三氯卡班对嗜热四膜虫的毒性研究[J]. 环境化学, 2012, 31(5): 720-725.
引用本文: 白琦锋, 高礼, 袁涛. 低剂量三氯生和三氯卡班对嗜热四膜虫的毒性研究[J]. 环境化学, 2012, 31(5): 720-725.
BAI Qifeng, GAO Li, YUAN Tao. Toxicity of low concentration exposures of triclosan and triclocarban on Tetrahymena thermophila[J]. Environmental Chemistry, 2012, 31(5): 720-725.
Citation: BAI Qifeng, GAO Li, YUAN Tao. Toxicity of low concentration exposures of triclosan and triclocarban on Tetrahymena thermophila[J]. Environmental Chemistry, 2012, 31(5): 720-725.

低剂量三氯生和三氯卡班对嗜热四膜虫的毒性研究

  • 基金项目:

    上海科委基础研究重点项目(10JC1407800)资助.

Toxicity of low concentration exposures of triclosan and triclocarban on Tetrahymena thermophila

  • Fund Project:
  • 摘要: 研究了环境相关浓度水平(μg·L-1)的三氯生(TCS)和三氯卡班(TCC)暴露对嗜热四膜虫的生长抑制效应,并尝试探索这两种新生污染物对四膜虫细胞活性的影响.结果表明,μg·L-1水平的TCS和TCC对四膜虫的生长存在明显抑制作用,24 h-EC50分别为141 μg·L-1、728 μg·L-1;最低无效应浓度(NOEC)分别为2 μg·L-1、30 μg·L-1;最低效应浓度(LOEC)分别为4 μg·L-1、61 μg·L-1.其中,TCC在1—10 μg·L-1水平表现出促进作用,可能是hormesis效应的体现.另外,在TCS和TCC浓度达到1000 μg·L-1时均对四膜虫细胞膜产生明显损伤;TCS和TCC也影响其溶酶体活性,1 μg·L-1暴露2 h时,荧光值(RFU)百分比分别降低至对照样品的88.62%、95.75%.本研究结果有助于进一步从亚细胞和分子水平认识环境污染水平TCS和TCC的生态毒性,也为这两种新生污染物在环境中的生态风险评价提供重要参考依据.
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  • [1] Sabaliunas D, Webb S F, Hauk A, et al. Environmental fate of triclosan in the River Aire basin, UK[J]. Water Research, 2003,37(13):3145-3154
    [2] Pkota A, Heldler J, Halden R U. Detection of triclocarban and two co-contaminating chlorocarbanilides in US aquatic environments using isotope dilution liquid chromatography tandem mass spectrometry[J]. Environmental Research, 2007, 103(1): 21-29
    [3] Talia E A, Halder R U. Environmental exposure of aquatic and terrestrial biota to triclosan and triclocarban[J]. Journal of the American Water Resources Association, 2009, 45(1):4-13
    [4] Kolpin D W, Furlong E T,Meyer M T, et al. Pharmaceuticals, hormones and other organic wastewater contaminants in U.S. streams, 1999—2000: anationalreconnaissance[J]. Environ Sci Technol, 2002, 36(6):1202-1211
    [5] Xu W H, Zhang G, Zou S, et al. Determination of selected antibiotics in the Victoria Harbour and the Pearl River, South China using high-performance liquid chromatography-electrospray ionization tandem mass spectrometry[J]. Environmental Pollution, 2007, 145(3):672-679
    [6] Peng X Z, Yu Y Y, Tang C M, et al. Occurrence of steroid estrogens,endocrine-disrupting phenols,and acid pharmaceutical residues in urban river in water of the Pearl River Delta, South China[J]. Sci Total Environ,2008, 397(1/3):158-166
    [7] Margaretha A, Maria P, Jari P, et al. Triclosan, a commonly used bactericide found in humanmilk and in the aquatic environment in Sweden[J]. Chemosphere,2002, 46(9-10):1485-1489
    [8] Mats A, Margaretha A, Michael S M, et al.Triclosan in plasma and milk from Swedish nursing mothers and their exposure via personal care products[J]. Sci Total Environ,2006, 372(1):87-93
    [9] Miller T J, Heidler S, Chillrud A, et al. Fate of triclosan and triclocarban in estuarine sediment[J]. Environ Sci Technol, 2008, 42(12):4570-4576
    [10] Snyder E H, O'Connor G A, McAvoy D C.Measured physicochemical characteristics and biosolids-borne concentrations of the antimicrobial triclocarban(TCC)[J]. Sci Total Environ, 2010,48 (13):2667-2673
    [11] Chen J G, Ahn K C, Gee N A, et al. Triclocarban enhances testosterone action: a new type of endocrine disruptor?[J]. Endocrinology, 2008, 149(3): 1173-1179
    [12] 吕妍,袁涛,王文华,等.个人护理用品(PCPs)生态风险评价研究进展[J].环境与健康杂志,2007,24(8):650-653
    [13] David R O, Donald J V, Josff I,et al. Aquatic toxicity of triclosan[J]. Environmental Toxicology and Chemistry, 2002, 21(7):1338-1349
    [14] Foran C M, Bennett E R, Benson W H. Developmental evaluation of a potential non-steroidal estrogen: triclosan[J]. Marine Environmental Research, 2000, 50(1/5): 153-156
    [15] Consortium T. Iuclid Data Set.TCC Consortium. New York: 2002: 44
    [16] Ben D G,Thomas M Y.The antimicrobial triclocarban stimulates embryo production in the freshwater mudsnail Potamopyrgus antipodarum[J]. Environmental Toxicology and Chemistry, 2010, 29(4):966-970
    [17] Chen X J, Feng W S, Miao W, et al. A microcalorimetric assay of Tetrahymena thermophila for assessing tributyltin acute tovicity[J].Journal of Thermal Analysis and Calorimetry, 2008, 94 (3):779-784
    [18] Vivian R, Dayeh S L, Chow K S, et al. Evaluating the toxicity of Triton X-100 to protozoan, fish, and mammalian cells using fluorescent dyes as indicators of cell viability[J]. Ecotoxicology and Environmental Safety, 2004, 57:375-382
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  • 收稿日期:  2011-09-21
白琦锋, 高礼, 袁涛. 低剂量三氯生和三氯卡班对嗜热四膜虫的毒性研究[J]. 环境化学, 2012, 31(5): 720-725.
引用本文: 白琦锋, 高礼, 袁涛. 低剂量三氯生和三氯卡班对嗜热四膜虫的毒性研究[J]. 环境化学, 2012, 31(5): 720-725.
BAI Qifeng, GAO Li, YUAN Tao. Toxicity of low concentration exposures of triclosan and triclocarban on Tetrahymena thermophila[J]. Environmental Chemistry, 2012, 31(5): 720-725.
Citation: BAI Qifeng, GAO Li, YUAN Tao. Toxicity of low concentration exposures of triclosan and triclocarban on Tetrahymena thermophila[J]. Environmental Chemistry, 2012, 31(5): 720-725.

低剂量三氯生和三氯卡班对嗜热四膜虫的毒性研究

  • 1.  上海交通大学环境科学与工程学院, 上海, 200240;
  • 2.  宁夏大学资源与环境学院, 银川, 750021
基金项目:

上海科委基础研究重点项目(10JC1407800)资助.

摘要: 研究了环境相关浓度水平(μg·L-1)的三氯生(TCS)和三氯卡班(TCC)暴露对嗜热四膜虫的生长抑制效应,并尝试探索这两种新生污染物对四膜虫细胞活性的影响.结果表明,μg·L-1水平的TCS和TCC对四膜虫的生长存在明显抑制作用,24 h-EC50分别为141 μg·L-1、728 μg·L-1;最低无效应浓度(NOEC)分别为2 μg·L-1、30 μg·L-1;最低效应浓度(LOEC)分别为4 μg·L-1、61 μg·L-1.其中,TCC在1—10 μg·L-1水平表现出促进作用,可能是hormesis效应的体现.另外,在TCS和TCC浓度达到1000 μg·L-1时均对四膜虫细胞膜产生明显损伤;TCS和TCC也影响其溶酶体活性,1 μg·L-1暴露2 h时,荧光值(RFU)百分比分别降低至对照样品的88.62%、95.75%.本研究结果有助于进一步从亚细胞和分子水平认识环境污染水平TCS和TCC的生态毒性,也为这两种新生污染物在环境中的生态风险评价提供重要参考依据.

English Abstract

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