Guelke Monika, Von Blanckenburg Friedhelm
Leibniz University of Hannover, Institute of Mineralogy, Callinstrasse 3, 30167 Hannover, Germany.
Environ Sci Technol. 2007 Mar 15;41(6):1896-901. doi: 10.1021/es062288j.
Although the fractionation of stable iron isotopes by biological processes in the environment is currently a matter of intense debate, the isotope fractionation associated with the growth of higher plants has, to date, not been characterized. We show that iron isotope fractionation induced by higher plants is substantial and also generates systematic plant-specific patterns. We suggest a hypothesis in which these patterns mirror the two different strategies that plants have developed to incorporate iron from the soil: reduction of Fe(III) in soils by strategy I plants results in the uptake of iron, which is depleted in 56Fe by up to 1.6 per mil relative to 54Fe when compared to the available Fe in soils; complexation with siderophores by strategy II plants results in the uptake of iron that is 0.2 per mil heavier than that in soils. Furthermore, younger parts of strategy I plants get increasingly depleted in heavy isotopes as the plant grows, while strategy II plants incorporate nearly the same isotope composition throughout. This points to entirely different translocation mechanisms between strategy I and II plants. Such presumably redox-related differences in translocation have been under debate up to now. We conclude that plant metabolism represents an important cause of isotopic variation in the biogeochemical cycling of Fe. Therefore, heavy stable metal isotope systems now start to be viable indicators of geosphere-biosphere metal transfer processes.
尽管环境中生物过程对稳定铁同位素的分馏作用目前仍是激烈争论的焦点,但迄今为止,与高等植物生长相关的同位素分馏尚未得到表征。我们表明,高等植物诱导的铁同位素分馏作用显著,并且还产生了系统的植物特异性模式。我们提出了一个假设,即这些模式反映了植物从土壤中吸收铁所采用的两种不同策略:I型植物通过还原土壤中的Fe(III)来吸收铁,与土壤中可利用的铁相比,所吸收的铁中56Fe相对于54Fe的含量最多可贫化1.6‰;II型植物通过与铁载体络合来吸收铁,所吸收的铁比土壤中的铁重0.2‰。此外,随着植物生长,I型植物较幼嫩的部分重同位素含量越来越低,而II型植物在整个生长过程中吸收的同位素组成几乎相同。这表明I型和II型植物之间的转运机制完全不同。迄今为止,这种推测与氧化还原相关的转运差异一直存在争议。我们得出结论,植物代谢是铁生物地球化学循环中同位素变化的一个重要原因。因此,重稳定金属同位素体系现在开始成为地球圈层-生物圈金属转移过程的可行指标。