The University of Queensland, School of Land, Crop and Food Sciences, St Lucia, Queensland, Australia, 4072.
J Exp Bot. 2010 Feb;61(4):945-54. doi: 10.1093/jxb/erp385. Epub 2010 Jan 6.
Solution culture has been used extensively to determine the phytotoxic effects of trace metals. A review of the literature from 1975 to 2009 was carried out to evaluate the effects of As(V), Cd(II), Co(II), Cu(II), Hg(II), Mn(II), Ni(II), Pb(II), and Zn(II) on plants grown in solution. A total of 119 studies was selected using criteria that allowed a valid comparison of the results; reported toxic concentrations varied by five orders of magnitude. Across a range of plant species and experimental conditions, the phytotoxicity of the trace metals followed the trend (from most to least toxic): Pb approximately Hg >Cu >Cd approximately As >Co approximately Ni approximately Zn >Mn, with median toxic concentrations of (muM): 0.30 Pb, 0.47 Hg, 2.0 Cu, 5.0 Cd, 9.0 As, 17 Co, 19 Ni, 25 Zn, and 46 Mn. For phytotoxicity studies in solution culture, we suggest (i) plants should be grown in a dilute solution which mimics the soil solution, or that, at a minimum, contains Ca and B, (ii) solution pH should be monitored and reported (as should the concentrations of the trace metal of interest), (iii) assessment should be made of the influence of pH on solution composition and ion speciation, and (iv) both the period of exposure to the trace metal and the plant variable measured should be appropriate. Observing these criteria will potentially lead to reliable data on the relationship between growth depression and the concentration of the toxic metal in solution.
溶液培养已被广泛用于确定痕量金属的植物毒性效应。对 1975 年至 2009 年的文献进行了综述,以评估 As(V)、Cd(II)、Co(II)、Cu(II)、Hg(II)、Mn(II)、Ni(II)、Pb(II)和 Zn(II)对溶液中生长的植物的影响。使用允许对结果进行有效比较的标准,共选择了 119 项研究;报告的毒性浓度相差五个数量级。在一系列植物物种和实验条件下,痕量金属的植物毒性遵循以下趋势(从最毒到最不毒):Pb≈Hg>Cu>Cd≈As>Co≈Ni≈Zn>Mn,毒性浓度中位数(μM)为:0.30 Pb、0.47 Hg、2.0 Cu、5.0 Cd、9.0 As、17 Co、19 Ni、25 Zn 和 46 Mn。对于溶液培养中的植物毒性研究,我们建议(i)植物应在稀溶液中生长,该溶液模拟土壤溶液,或至少含有 Ca 和 B,(ii)应监测和报告溶液 pH 值(以及感兴趣的痕量金属的浓度),(iii)应评估 pH 值对溶液组成和离子形态的影响,以及(iv)应适当考虑暴露于痕量金属和测量的植物变量的时间。遵守这些标准将有可能获得关于生长抑制与溶液中毒性金属浓度之间关系的可靠数据。