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土壤性质和老化对砷植物毒性的影响。

Influence of soil properties and aging on arsenic phytotoxicity.

作者信息

Song Jing, Zhao Fang-Jie, McGrath Steve P, Luo Yong-Ming

机构信息

Soil and Environment Bioremediation Research Centre, State Key Laboratory of Soil and Sustainable Agriculture, Institute of Soil Science, Chinese Academy of Sciences, P.O. Box 821, Nanjing, People's Republic of China.

出版信息

Environ Toxicol Chem. 2006 Jun;25(6):1663-70. doi: 10.1897/05-480r2.1.

DOI:10.1897/05-480r2.1
PMID:16764487
Abstract

Bioavailability of As varies among soils, and this needs to be taken into account during environmental risk assessment. Using a standardized barley root elongation assay, we investigated the phytotoxicity of arsenate added to 16 European soils that varied widely in their physicochemical properties. The effective concentrations of As causing 10% (EC10) and 50% (EC50) inhibition were estimated based on the concentrations of total added As or As extracted with 0.05 M (NH4)2SO4 or 0.05 M NH4H2PO4. In addition, four soils were used to evaluate changes in arsenate phytotoxicity over a three-month period. The EC10s and EC50s of added As varied from 4.2 to 206.7 mg/kg and from 26.6 to 458.2 mg/kg, respectively. Multiple-regression analysis showed that the variability in the EC10 and EC50 was largely (>89%) explained by the contents of amorphous Mn oxide and clay and, to a lesser extent, Fe oxide, indicating that arsenate adsorption was a key factor controlling its bioavailability. Neither (NH4)2SO4 nor NH4H2PO4 extraction could explain arsenate phytotoxicity independently of soil properties. Furthermore, arsenate phytotoxicity decreased significantly after aging for three months, although the extent of aging differed among soils. This aging effect should be taken into account during the risk assessment.

摘要

不同土壤中砷的生物有效性存在差异,在进行环境风险评估时需要考虑这一点。我们使用标准化的大麦根伸长试验,研究了添加到16种理化性质差异很大的欧洲土壤中的砷酸盐的植物毒性。基于添加的总砷浓度或用0.05M硫酸铵或0.05M磷酸二氢铵提取的砷浓度,估算了导致10%(EC10)和50%(EC50)抑制率的砷的有效浓度。此外,使用四种土壤评估了三个月内砷酸盐植物毒性的变化。添加砷的EC10和EC50分别在4.2至206.7mg/kg和26.6至458.2mg/kg之间变化。多元回归分析表明,EC10和EC50的变异性在很大程度上(>89%)可由无定形氧化锰和粘土的含量解释,其次是氧化铁,这表明砷酸盐吸附是控制其生物有效性的关键因素。硫酸铵和磷酸二氢铵提取都不能独立于土壤性质来解释砷酸盐的植物毒性。此外,尽管不同土壤的老化程度不同,但老化三个月后砷酸盐的植物毒性显著降低。在风险评估过程中应考虑这种老化效应。

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