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Does control of soil erosion inhibit aquatic eutrophication?

机译:控制土壤侵蚀是否抑制了水体富营养化?

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Much of the phosphorus (P) from erosive soils is transported to water bodies together with eroded soil. Studies clarifying the impact of soil erosion on eutrophication have sought largely to quantify the reserves of P in soil particles that can be desorbed in different types of receiving waters. Aquatic microbiology has revealed that the cycling of P is coupled to the availability of common electron acceptors, Fe oxides and SO4, through anaerobic mineralization in sediments. Eroded soil is also rich in Fe oxides, and their effect on the coupled cycling of C, Fe, S, and P has been neglected in eutrophication research. Soil erosion, and its control, should therefore be studied by considering not only the processes occurring in the water phase but also those taking place after the soil particles have settled to the bottom. We propose that in SC>4-rich systems, Fe oxides transported by eroded soil may promote Fe cycling, inhibit microbial SO4 reduction and maintain the ability of sediment to retain P. We discuss the mechanisms through which eroded soil may affect benthic mineralization processes and the manner in which soil erosion may contribute to or counteract eutrophication.
机译:来自侵蚀性土壤的大部分磷(P)与侵蚀性土壤一起被输送到水体。澄清土壤侵蚀对富营养化影响的研究在很大程度上试图量化土壤颗粒中磷的含量,这些颗粒可以在不同类型的接收水中解吸。水生微生物学表明,磷的循环通过沉积物中的厌氧矿化作用与常见电子受体,Fe氧化物和SO4的可用性相关。侵蚀的土壤也富含铁氧化物,在富营养化研究中忽略了它们对碳,铁,硫和磷的耦合循环的影响。因此,不仅应考虑在水相中发生的过程,而且还应考虑在土壤颗粒沉降到底部之后发生的过程,以研究土壤侵蚀及其控制方法。我们建议在富含SC> 4的系统中,受侵蚀的土壤输送的铁氧化物可能促进铁的循环,抑制微生物的SO4还原并保持沉积物保留P的能力。我们讨论了侵蚀的土壤可能通过哪些机制影响底栖矿化过程和土壤侵蚀可能导致或抵消富营养化的方式。

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