Ali Nadia Ait, Ater Mohammed, Sunahara Geoffrey I, Robidoux Pierre Yves
Applied Ecotoxicology Group, Biotechnology Research Institute, National Research Council of Canada, 6100 Royalmount Avenue, Montreal, QC, Canada H4P 2R2.
Ecotoxicol Environ Saf. 2004 Mar;57(3):363-74. doi: 10.1016/S0147-6513(03)00074-5.
The toxicities of two heavy metals, copper (Cu2+) and chromium (Cr6+), to barley (Hordeum vulgare L.) were evaluated using two types of substrates: artificial and natural forest soils. Phytotoxicity was assessed using a standardized toxicity test. Endpoints included plant emergence and shoot and root growth. Shoot and root concentrations of Cu and Cr were also measured. Data indicated that the root biomass was the most sensitive endpoint. The results showed that toxicity of Cr to root growth (IC50=6.6 microg/g in artificial soil; IC50=61.8 microg/g in forest soil) was higher than that of Cu (IC50=13.7 microg/g in artificial soil; IC50>322 microg/g in forest soil). Data also indicated that the toxicity of Cu and Cr was significantly decreased in the spiked forest soil, suggesting lower metal bioavailability to barley in the natural soil. Analysis of tissue concentrations in barley showed that Cu and Cr were mainly accumulated in the roots. Toxicity was correlated with Cr residues in shoots (< or =11.2 microg Cr/g and < or =5.3 microg Cr/g for artificial and natural soils, respectively) and roots (< or =161 microg Cr/g and < or =51.7 microg Cr/g for artificial and natural soils, respectively) and Cu residues in roots (< or =61.8 microg Cu/g and < or =91.3 microg Cu/g for artificial and natural soils, respectively). Cu concentration in shoot tissues was < or =61.8 microg Cu/g. Since it may overestimate toxicity, effect and risk assessment using spiked soils, particularly in artificial soil, must be used with diligence.
使用两种类型的基质(人工土壤和天然森林土壤)评估了两种重金属铜(Cu2+)和铬(Cr6+)对大麦(Hordeum vulgare L.)的毒性。采用标准化毒性试验评估植物毒性。终点指标包括植株出苗率以及地上部和根部生长情况。还测量了地上部和根部的铜和铬浓度。数据表明,根生物量是最敏感的终点指标。结果显示,铬对根生长的毒性(在人工土壤中IC50 = 6.6微克/克;在森林土壤中IC50 = 61.8微克/克)高于铜(在人工土壤中IC50 = 13.7微克/克;在森林土壤中IC50>322微克/克)。数据还表明,在添加了重金属的森林土壤中,铜和铬的毒性显著降低,这表明在天然土壤中金属对大麦的生物有效性较低。对大麦组织浓度的分析表明,铜和铬主要积累在根部。毒性与地上部铬残留量(人工土壤和天然土壤中分别≤11.2微克铬/克和≤5.3微克铬/克)以及根部铬残留量(人工土壤和天然土壤中分别≤161微克铬/克和≤51.7微克铬/克)和根部铜残留量(人工土壤和天然土壤中分别≤61.8微克铜/克和≤91.3微克铜/克)相关。地上部组织中的铜浓度≤61.8微克铜/克。由于使用添加了重金属的土壤(特别是人工土壤)可能会高估毒性,因此在进行效应和风险评估时必须谨慎使用。