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Assessment of gross and net mineralization rates of soil organic phosphorus - A review

机译:土壤有机磷总矿化率和净矿化率评估-综述

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The quantification of net soil organic P mineralization rates is hampered by the potentially rapid sorption of released phosphate. Here, isotopic dilution approaches to assess gross and net organic P mineralization rates under steady-state conditions are reviewed, including different analytical and numerical solutions to assess P transformation rates based on incubation experiments with P-32- or P-33-labeled soils. Non-isotopic approaches are also commented on. Published isotopic dilution studies show that isotopically exchangeable P during incubation can partly or even predominantly (20-90%) result from biological and biochemical rather than physicochemical processes. The relative contribution of biological and biochemical processes tends to be lower in arable soils than under grassland and forests and is negatively related to the availability of inorganic P and positively to concentrations of soil organic carbon. Typical basal gross organic P mineralization rates range between 0.1 and 2.5 mg P kg(-1) d(-1), but rates up to 12.6 mg P kg(-1) d(-1) have been observed in grassland and forest soils. The further partitioning of gross organic P mineralization remains uncertain, but a dominance of microbial immobilization and remineralization is likely under most conditions, at least during the initial weeks of incubation. Over longer time periods, the relative importance of mineralization of non-living soil organic P increases, with the contribution of extracellular hydrolysis remaining to be elucidated. This requires other approaches than enzyme activity assays, since measurements of phosphomonoesterase activity in soil render organic P mineralization rates that are one to two orders of magnitude greater than those determined by isotopic dilution. The numerical modeling approach will enable assessment of soil P transformation rates under non-steady-state conditions, where P fluxes are likely to be greater than under steady-state conditions. Ultimately, an improved understanding of the biological and biochemical processes in soil P dynamics may help to improve P management in agroecosystems. (C) 2015 Elsevier Ltd. All rights reserved.
机译:净土壤有机磷矿化速率的量化受到释放磷酸盐的潜在快速吸附的阻碍。在此,对评估稳态条件下总磷和净有机磷矿化速率的同位素稀释方法进行了综述,包括基于与P-32或P-33标记的土壤孵育实验得出的评估P转化率的不同分析和数值解决方案。还对非同位素方法进行了评论。已发表的同位素稀释研究表明,在孵育过程中同位素可交换的P可能部分或什至主要(20-90%)来自生物和生化过程而不是物理化学过程。耕作土壤中生物和生化过程的相对贡献往往低于草原和森林,并且与无机磷的有效性负相关,与土壤有机碳的浓度负相关。典型的基础有机磷总矿化速率介于0.1和2.5 mg P kg(-1)d(-1)之间,但在草地和森林土壤中已观察到高达12.6 mg P kg(-1)d(-1)的矿化速率。 。总有机磷矿化的进一步划分仍然不确定,但是在大多数条件下,至少在孵育的最初几周内,微生物固定化和再矿化有可能占据主导地位。在更长的时期内,非活性土壤有机磷矿化的相对重要性增加,而胞外水解的贡献仍有待阐明。这需要酶活性测定法以外的其他方法,因为对土壤中磷酸单酯酶活性的测量结果使有机磷矿化速率比同位素稀释法测定的高了一到两个数量级。数值建模方法将能够评估非稳态条件下的土壤磷转化率,在非稳态条件下,P通量可能大于稳态条件下的通量。最终,对土壤磷动力学中生物和生化过程的更好理解可能有助于改善农业生态系统中的磷管理。 (C)2015 Elsevier Ltd.保留所有权利。

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