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水培茶树对铅的吸收与累积特性研究

  • 赵先明 ,
  • 汪艳霞 ,
  • 杜晓 ,
  • 李品武
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  • 1. 宜宾职业技术学院,四川 宜宾 644003;
    2. 四川农业大学园艺学院,四川 雅安 625014;
    3. 四川省茶业科学与工程重点实验室,四川 雅安 625014
赵先明(1963— ),男,重庆市人,副教授,主要从事茶叶加工方面的研究。

收稿日期: 2010-10-18

  修回日期: 2011-01-27

  网络出版日期: 2019-09-06

基金资助

四川省教育厅重点实验室项目(2006ZD010)、四川农业大学青年科技创新基金(00330300)

Uptake and Accumulation Characters of Lead in Tea Plants (Camellia sinensis) Grown in Hydroponics

  • ZHAO Xian-min ,
  • WANG Yan-xia ,
  • DU Xiao ,
  • LI Pin-wu
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  • 1. Yibin vocational and technical college, Yibin 644003, China;
    2. College of Horticulture, Sichuan Agricultural University, Ya’an 625014, China;
    3. Key Laboratory of Tea Science and Engineering in Sichuan province, Ya’an 625014, China;

Received date: 2010-10-18

  Revised date: 2011-01-27

  Online published: 2019-09-06

摘要

添加铅盐进行水培茶树试验,用火焰原子吸收光度法测定铅含量,研究茶树对铅的吸收、累积及分布特性。结果表明,铅离子能被根系或叶片大量吸收和累积,并按浓度差通过茎段转运与再分布;根施或叶部喷施2500mg/L的铅盐溶液,根系铅含量分别为8.00×104mg/kg和8.38×103mg/kg,叶片铅含量分别为551.79mg/kg和1.03×104mg/kg,两者的铅富集量很高,但仍未见茶树死亡;当铅盐质量浓度为800~2000mg/L时,茶树逐渐受到铅危害,早期吸收根转为透明状,再褐变,后期叶片部分脱落;当铅盐质量浓度为300~800mg/L,水培茶树35d,茶树长势良好,未见受害症状。研究表明,水培茶树对铅具有大量吸收与累积的能力,并对铅危害有很强的抵抗与耐受力。

本文引用格式

赵先明 , 汪艳霞 , 杜晓 , 李品武 . 水培茶树对铅的吸收与累积特性研究[J]. 茶叶科学, 2011 , 31(3) : 237 -246 . DOI: 10.13305/j.cnki.jts.2011.03.016

Abstract

Lead (Pb) concentration was investigated in tea plants (Camellia sinensis) grown in hydroponics by the FAAS method to understand the Pb uptake, accumulation and distribution characters in tea plants. The results showed that Pb ion can be uptaken and accumulated by roots in a large quantity, transported through stems along with concentration gradient, and redistributed. Cultured in 2500mg/L Pb solution or sprayed the same solution on leaves (cultured in distilled water), Pb concentration in roots were 8.00×104mg/kg and 8.38×103mg/kg, respectively, in leaves were 551.79mg/kg and 1.03×104mg/kg respectively. Even such high accumulation the tea plants were still alived. At the range of 800~2000mg/L Pb solution, tea plants were gradually damaged; in the early time, absorbing roots became transparent, and then turned brown, and leaves were defoliated in the latter period. Tea plant cultured under the 300~800mg/L Pb solution for 35d, these plants grew well, and no damaged symptoms can be observed. Results indicated that tea plants possessed a strong ability of Pb uptake, accumulation and tolerance.

参考文献

[1] 石元值, 马立峰. 铅在茶树中的吸收累积特性[J]. 中国农业科学, 2003, 36(11): 1272-1278.
[2] 陈英旭. 土壤重金属的植物污染化学[M]. 北京:科学出版社, 2008: 50.
[3] 石元值, 韩文炎, 马立峰, 等. 龙井茶中重金属元素 Pb含量的影响因子探究[J]. 农业环境科学学报, 2004, 23(5): 899-903.
[4] Baker AJM.Terrestrial higher plants which hyperaccumulate metallic elements: a review of their distribution ecology and phytochemistry[J]. Biorecovery, 1989(1): 81-89.
[5] Assuncao AGL, Da Costa Martins P, Folter S, et al. Elevated expression of metal transporter genes in three accessions of the metal hyperaccumulator Thlaspi caerulescens[J]. Plant Cell Environ, 2001(24):217-226.
[6] 秦菲, 陈文. 北京市售茶叶的铅和铜含量水平分析[J]. 食品科学, 2007, 28(11): 496-500.
[7] 韩文炎, 韩国柱, 蔡雪雄. 茶叶铅含量现状及其控制技术研究进展[J]. 中国茶叶, 2008, 30(4): 16-17.
[8] 韩文炎, 杨亚军, 梁月荣, 等. 茶树体内铅的吸收累积特性研究[J]. 茶叶科学, 2009, 29(3): 200-206.
[9] Han WY, Zhao FJ, Shi YZ, et al. Scale and causes of lead contamination in Chinese tea[J]. Environmental Pollution, 2006(139): 125-132.
[10] 兰海霞, 夏建国. 川西蒙山茶树中铅、镉元素的吸收累积特性[J]. 农业环境科学学报, 2008, 27(3): 1077-1083.
[11] 汤茶琴, 张定, 黎星辉. 茶树及成品茶叶中铅的研究进展[J]. 福建茶叶, 2006(2): 15-18.
[12] 郭巍. 铜、铅在土壤-植物系统中环境化学行为的研究[J]. 江苏环境科技, 2006(12): 10-12.
[13] 骆耀平, 康孟利, 任明兴. 铅污染对茶树生育及相关保护酶活性的影响[J]. 茶叶, 2004, 30(4): 213-216.
[14] 童启庆. 茶树栽培学[M]. 北京: 中国农业出版社, 2006: 93, 344.
[15] 康孟利, 骆耀平, 石元值. 茶树对铅的吸收和累积特性[J]. 茶叶, 2004, 30(2): 88-90.
[16] Narin I. Soylak M.Enrichment and determination of nickle, cadmium, copper, cobalt and lead ions in natural waters, table salts, tea and urine samples-Flame atomic absorption spectrometry combination[J]. Analy Chim Acta, 2003(493): 205-212.
[17] Sharma NC, Gardea-Torresdey JL, Parsons J, et al. Chemical speciation and cellular deposition of lead in Sesbania drummondii[J]. Environ Toxicol Chem, 2004(23): 2068-2073.
[18] Marmiroli M, Antonioli G, Maestria E, et al. Evidence of the involvement of plant lingo- cellulosic structure in the sequestration of Pb: an X - ray spectroscopy- based analysis[J]. Environ Pollut, 2005(134): 217-227.
[19] Gardea-Torresdey JL, Dokken K, Tiemann KJ, et al. Infrared and X- ray absorption spectroscopic studies on the mechanism of chromium binding to alfalfa biomass[J]. Microchem J, 2000(71): 157-166.
[20] Gupta M, Rai NU, Tripathi DR, et al. Lead induced changes in glutathione and phytochelatin in Hydrilla verticillata(L. f.) Royle[J]. Chemosphere, 1995, 30(10): 2011-2020.
[21] Pawlik S,Ronska B.Relationship between acid-soluble thliol peptidesand accumulated Pb in the green alga Stichococcus bacillaris[J]. Aquatic Toxicol, 2000, 50(1): 221-230.
[22] Lasat MM, Pence NS, Garvin DF, et al. Molecular physiology of zinc transport in the Zn hyperaccumulator Thlaspi caerulescens[J]. J Exp Bot, 2000(51): 71-79.
[23] Jin CW, Zheng SJ, He YF, et al. Lead contamination in tea garden soils and factors affecting its bioavailability[J]. Chemosphere, 2005(59): 1151-1159.
[24] Othman I, Aloudat M, Almasrim S.Lead levels in roadside soils and vegetation of Damascus city[J]. Sci Total Environ, 1997, 207(1): 43-48.
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