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铬、镉和铅对两种地中海土壤的生态毒性。

Ecotoxicity of Cr, Cd, and Pb on two Mediterranean soils.

机构信息

Laboratori d'Edafologia, Facultat de Farmàcia, Universitat de Barcelona, Barcelona, 08028, Spain.

出版信息

Arch Environ Contam Toxicol. 2013 Apr;64(3):377-87. doi: 10.1007/s00244-012-9841-9. Epub 2012 Dec 2.

DOI:10.1007/s00244-012-9841-9
PMID:23212577
Abstract

Three potentially toxic elements [chromium (Cr), lead (Pb), and cadmium (Cd)] were tested to assess their effects on two soils of different properties and origin. The soils were a granitic soil (Haplic Arenosol), which meets the requirements of OECD ecotoxicity testing, and a calcareous soil (Calcaric Regosol) with properties often found in the Mediterranean areas. The metal concentrations used ranged from 0.001 to 5,000 mg kg(-1) soil. The effects on soil microbial activity and community composition (respirometry and polymerase chain reaction-denaturing gradient gel electrophoresis analysis), as well as the effects on plant germination and elongation (Lactuca sativa), were assessed. The toxicity of the soil water extracts was also evaluated by the growth inhibition of algal populations (Pseudokirschneriella subcapitata). Cr showed the highest level of toxicity to soil organisms in the assays performed because this element remains in soil as anionic form and is less retained by the soil solid matrix than Cd and Pb. The lowest observed-adverse effect level for Cr ranged from approximately 0.1 mg kg(-1) [substrate induced respiration (SIR) test for the granitic soil] to 10 mg kg(-1) (basal respiration and SIR tests for the calcareous soil). For Pb (SIR) and Cd (SIR and alga tests), these levels were approximately 100 mg kg(-1). Germination and algal tests showed higher sensitivity in Regosol soil than in Arenosol soil for Cr due to differences in the bioavailability between the soils. In the cases or areas where alkaline soils are abundant, these should also be considered in laboratory ecotoxicity testing to avoid underestimation of ecotoxicological risks.

摘要

三种潜在有毒元素(铬、铅和镉)被检测以评估它们对两种不同性质和来源土壤的影响。这些土壤是一种满足 OECD 生态毒性测试要求的花岗岩土(Haplic Arenosol),和一种在地中海地区常见的钙质土壤(Calcaric Regosol)。使用的金属浓度范围从 0.001 到 5000mgkg(-1) 土壤。评估了对土壤微生物活性和群落组成(呼吸测定法和聚合酶链反应-变性梯度凝胶电泳分析)的影响,以及对植物发芽和伸长(生菜)的影响。还通过藻类种群(Pseudokirschneriella subcapitata)的生长抑制来评估土壤浸出液的毒性。在进行的测定中,Cr 对土壤生物表现出最高的毒性水平,因为这种元素以阴离子形式存在于土壤中,并且比 Cd 和 Pb 更少地被土壤固体基质保留。Cr 的最低观察到的不良效应水平范围大约从 0.1mgkg(-1)(用于花岗岩土的基质诱导呼吸(SIR)测试)到 10mgkg(-1)(用于钙质土壤的基础呼吸和 SIR 测试)。对于 Pb(SIR)和 Cd(SIR 和藻类测试),这些水平大约为 100mgkg(-1)。由于土壤之间的生物可利用性差异,Cr 的发芽和藻类测试在 Regosol 土壤中的敏感性高于 Arenosol 土壤。在碱性土壤丰富的地区或情况下,也应该在实验室生态毒性测试中考虑这些土壤,以避免低估生态毒性风险。

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