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多元统计分析鉴定修复湿地中控制磷形态和迁移性的环境因素。

Identification of environmental factors controlling phosphorus fractions and mobility in restored wetlands by multivariate statistics.

机构信息

Key Laboratory of Wetland Ecology and Environment, Northeast Institute of Geography and Agroecology, Chinese Academy of Sciences, Changchun, 130102, China.

University of Chinese Academy of Sciences, Beijing, 101408, China.

出版信息

Environ Sci Pollut Res Int. 2019 Jun;26(16):16014-16025. doi: 10.1007/s11356-019-05028-x. Epub 2019 Apr 9.

Abstract

Phosphorus is a dominant environmental factor in fostering eutrophication, and its biogeochemical behavior has attracted much attention. This study investigated the distribution of phosphorus fractions and the adsorption-desorption characteristic in the soils of wetlands converted from paddy fields with a restoration duration of 1, 2, 3, 5, 13, or 19 years. The results demonstrated the content of total phosphorus (TP) first increased, which was then reversed until the process stabilized after 5 restoration years. Labile inorganic phosphorus (L-Pi), labile organic phosphorus (L-Po), iron-aluminum-bound phosphorus (Fe.Al-P), and humic phosphorus (Hu-P) peaked at 1-3 restoration years, respectively, while moderately labile organic phosphorus (Ml-Po), calcium-magnesium-bound phosphorus (Ca.Mg-P), and residual phosphorus (Re-P) decreased within 0-5 restoration years. During the 5th to 19th restoration years, the contents of all phosphorus fractions stabilized within a minor fluctuating range. Redundancy analysis (RDA) results indicated that total nitrogen (TN) and soil organic matter (SOM) are the important environmental factors controlling redistribution of phosphorus fractions. The capability of restored wetlands to retain phosphorus increased first and then decreased with the extension of the restoration duration. Path analysis (PA) results demonstrated that pH, TN, and Fe are the primary factors for the capacity of soil to retain phosphorus, followed by SOM, Mn, and electrical conductivity(EC). Fe.Al-P and Hu-P had a higher release risk with approximate amounts of 197.25-337.25 and 113.28-185.72 mg/kg during the first stage of restoration, which needs to be focused.

摘要

磷是促进富营养化的主要环境因素,其生物地球化学行为受到了广泛关注。本研究调查了从稻田恢复 1、2、3、5、13 或 19 年的湿地中磷素形态的分布和吸附解吸特性。结果表明,总磷(TP)含量先增加,然后在 5 年恢复后稳定下来。活性无机磷(L-Pi)、活性有机磷(L-Po)、铁铝结合磷(Fe.Al-P)和腐殖质磷(Hu-P)分别在 1-3 年恢复期间达到峰值,而中等活性有机磷(Ml-Po)、钙镁结合磷(Ca.Mg-P)和残余磷(Re-P)在 0-5 年恢复期间减少。在第 5 至 19 年恢复期间,所有磷素形态的含量在较小的波动范围内稳定下来。冗余分析(RDA)结果表明,总氮(TN)和土壤有机质(SOM)是控制磷素形态再分配的重要环境因素。随着恢复时间的延长,恢复湿地对磷的保留能力先增加后减少。路径分析(PA)结果表明,pH、TN 和 Fe 是土壤保持磷能力的主要因素,其次是 SOM、Mn 和电导率(EC)。Fe.Al-P 和 Hu-P 在恢复的最初阶段具有较高的释放风险,释放量分别约为 197.25-337.25 和 113.28-185.72 mg/kg,需要重点关注。

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