Yang Jinyan, Wang Mei, Jia Yanbo, Gou Min, Zeyer Josef
College of Architecture and Environment, Sichuan University, Chengdu 610065, China.
Hangzhou Institute for Food and Drug Control, Hangzhou 310022, China.
Environ Pollut. 2017 Dec;231(Pt 1):48-58. doi: 10.1016/j.envpol.2017.07.075. Epub 2017 Aug 4.
Vanadium(V) is present in trace amounts in most plants and widely distributed in soils. However, the environmental toxicity of V compound in soils is controversial. A greenhouse study with soybean from germination to bean production under exposure to pentavalent V [V(V)] was conducted to elucidate the interaction of plants and V fractions in soils and to evaluate the toxicity of V at different plant growth stages. Soybean growth has no effect on non-specific-bond and specific-bond fractions of V in soils, but V fractionation occurred in more extraction-resistant phases at high V concentrations. High concentrations of V(V) postponed the germination and growth of the soybeans. Bean production was less than half of that of the control at 500 mg kg spiked V(V). For the 0 mg kg spiked V(V) treated plants, the root was not the main location where V was retained. Vanadium in the soils at ≤ 250 mg kg did not significantly affect the V concentration in the shoot and leaf of soybeans. With the increase in V concentration in soil, V concentrations in roots increased, whereas those in beans and pods decreased. From vegetative growth to the reproductive growth, the soybeans adsorbed more V and accumulated more V in the roots, with <20% transported to the aboveground parts. Hence, the analysis of V concentration in vegetative tissues or beans may not be a useful indicator for V pollution in soil. Meanwhile, the ratio of V concentration in cell wall to the total V concentration in the root increased with the increase in V(V) concentration in soils. Our results revealed that high concentrations of V inhibited soybean germination and biomass production. However, plants may produce self-defense systems to endure V toxicity.
五价钒在大多数植物中含量甚微,且广泛分布于土壤中。然而,土壤中钒化合物的环境毒性存在争议。开展了一项温室研究,观察大豆从发芽到结荚过程中暴露于五价钒[V(V)]的情况,以阐明植物与土壤中钒组分的相互作用,并评估不同植物生长阶段钒的毒性。大豆生长对土壤中钒的非特异性结合态和特异性结合态组分没有影响,但在高钒浓度下,钒会在更难提取的相中发生分馏。高浓度的V(V)延缓了大豆的发芽和生长。在添加500 mg/kg V(V)时,豆荚产量不到对照的一半。对于添加0 mg/kg V(V)处理的植株,根部并非钒留存的主要部位。土壤中钒含量≤250 mg/kg时,对大豆地上部茎叶中的钒浓度没有显著影响。随着土壤中钒浓度的增加,根部钒浓度升高,而豆荚和豆粒中的钒浓度降低。从营养生长到生殖生长阶段,大豆吸收更多的钒并在根部积累更多的钒,转运到地上部分的钒不到20%。因此,分析营养组织或豆粒中的钒浓度可能并非土壤钒污染的有效指标。同时,随着土壤中V(V)浓度的增加,根部细胞壁中钒浓度与根部总钒浓度的比值升高。我们的结果表明,高浓度的钒抑制大豆发芽和生物量生产。然而,植物可能会产生自我防御系统来耐受钒的毒性。