Nash D M, Mc Dowell R W, Kleinman P J A, Moore P A, Duncan J M, Haygarth P M, Smith D R, Iho A
School of Agriculture and Food, Faculty of Veterinary and Agricultural Sciences, The University of Melbourne, Parkville, Victoria, Australia.
Soil and Allied Services Pty. Ltd., Port Welshpool, Victoria, Australia.
J Environ Qual. 2025 Mar-Apr;54(2):303-318. doi: 10.1002/jeq2.70003. Epub 2025 Feb 20.
Excessive phosphorus (P) concentrations can lead to conditions that limit the amenity of freshwater resources. This problem is particularly acute in agricultural catchments, where P fertilizer and manure amendments have been used to increase soil fertility and productivity. In these catchments, P indices are often used to help target critical source areas in order to reduce P exports. However, the overall impact of agricultural mitigation efforts on receiving waters has not always been consistent with declines in total P exports from catchments. In this paper we propose a model of dissolved P mobilization (i.e., entrainment) in surface runoff that accounts for this outcome and examine modifications to P indices that better accommodate dissolved P mobilization. We suggest that dissolved P mobilization commences near the soil surface and has two phases. When water is first applied, labile P is mostly mobilized by dissolution and advection. Subsequently, as the supply of readily accessible P is exhausted, diffusion and hydrodynamic dispersion mobilize P from other sources at a near constant rate for the remainder of the event. As most P exports occur in larger (i.e., longer) events, the second phase appears responsible for most dissolved P exports. Such a model of dissolved P mobilization is consistent with runoff monitoring data under natural and simulated rainfall, suggesting that on low (shallow) slopes where the interaction between surface soil and water may be prolonged, dissolved P concentrations are likely to be higher. Dissolved P mobilization from low-slope areas is not well represented in P indices at present. We suggest that there needs to be a more complex, mechanistic structure to P indices that involves additional compartmentalization. Further, we suggest that this can be achieved without losing the simplicity of P indices or flexibility to integrate research data and experiential knowledge into tools that are relevant to specific regions.
过量的磷(P)浓度会导致限制淡水资源适宜性的情况。这个问题在农业集水区尤为严重,在这些地区,磷肥和粪肥改良剂被用于提高土壤肥力和生产力。在这些集水区,磷指数常被用来帮助确定关键源区,以减少磷的输出。然而,农业缓解措施对受纳水体的总体影响并不总是与集水区总磷输出的下降相一致。在本文中,我们提出了一个地表径流中溶解磷迁移(即夹带)的模型,该模型解释了这一结果,并研究了对磷指数的修改,以更好地适应溶解磷的迁移。我们认为溶解磷的迁移始于土壤表层附近,分为两个阶段。当首次加水时,不稳定磷主要通过溶解和平流作用被迁移。随后,随着易于获取的磷供应耗尽,扩散和水动力弥散在事件的剩余时间内以接近恒定的速率从其他来源迁移磷。由于大多数磷的输出发生在较大(即较长)的降雨事件中,第二阶段似乎是大多数溶解磷输出的原因。这种溶解磷迁移模型与自然降雨和模拟降雨条件下的径流监测数据一致,表明在低(浅)坡度地区,表层土壤与水之间的相互作用可能会延长,溶解磷浓度可能会更高。目前,低坡度地区溶解磷的迁移在磷指数中没有得到很好的体现。我们认为磷指数需要一个更复杂的机制结构,涉及额外的分区。此外,我们认为可以在不失去磷指数的简单性或灵活性的情况下实现这一点,即将研究数据和经验知识整合到与特定区域相关的工具中。