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Waterlogging and soil reduction affect the amount and apparent molecular weight distribution of dissolved organic matter in wetland soil: a laboratory study

机译:涝渍和土壤还原对湿地土壤溶解有机物的量和表观分子量分布:实验室研究

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The release of dissolved organic matter (DOM) from wetland soils is an important pathway for the input of organic compounds into adjacent aquatic environments. In the present study we investigated, under controlled laboratory conditions, the quantity and quality of DOM released from a wetland soil subject to waterlogging and reducing conditions. Three soil redox conditions (oxic, moderately reducing and advanced reducing) were distinguished based on nitrate, ferrous ions and sulfate concentrations in soil solution. Under each redox condition, the quantity (dissolved organic carbon (DOC), humic substances and peptides plus proteins (P-PN) and quality (aromaticity; specific ultraviolet absorbance at 254 nm (SUVA254nm)) and apparent molecular weight (aMW) distribution) of DOM were investigated. The results showed that soil redox condition affects the amount and properties of mobilised DOM. The rate of DOM release and SUVA254 values were highest during the transition from oxic to moderately reducing conditions, whereas both stabilised during progression to advanced reducing conditions. In addition, the mobilised DOM is expected to be more reactive because of an increase in polar substituents in aromatic structures between oxic and moderately reducing conditions. During the development of moderately reducing conditions, dissolved humic substances increased significantly, whereas their aMW distribution (between 500 and 6000) remained constant for each of the three different redox conditions. In contrast, the quantity of dissolved P-PN remained low and steady under the three redox conditions, whereas the aMW distribution of protein-like and microbial by-product-like compounds decreased during the development of reducing conditions (aMW of compounds between 100 and 100 000).
机译:来自湿地土壤的溶解有机物质(DOM)的释放是将有机化合物输入到相邻的水生环境中的重要途径。在本研究中,我们调查了受控实验室条件,从湿地土壤释放的DOM的数量和质量受到涝渍和减少条件。基于硝酸铁,铁离子和土壤溶液中的硫酸盐浓度来区分三种土壤氧化还原条件(氧化,中度减少和晚期还原)。在每种氧化还原条件下,量(溶解有机碳(DOC),腐殖物质和肽加蛋白质(P-P-PN)和质量(芳香性;特定的紫外线吸收,在254nm(suva254nm))和表观分子量(AMW)分布) DOM被调查了。结果表明,土壤氧化还原病症影响动员的DOM的量和性质。在从氧化物到中度还原条件的转变期间,DOM释放和SUVA254值的速率最高,而均在进展期间稳定到晚期的还原条件。此外,由于氧和中等减少条件之间的芳族结构中的极性取代基增加,所动力化的DOM预期更能反应。在中度减少条件的发展期间,溶解的腐殖质物质显着增加,而它们的AMW分布(在500和6000之间)对于三种不同的氧化还原条件中的每一个保持恒定。相比之下,在三种氧化还原条件下溶解的p-p-pn的量仍然低且稳定,而在还原条件下发生蛋白质样和微生物副产物样化合物的AMW分布减少(100个和100之间的化合物的AMW & 100 000)。

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