USDA-ARS, Soil Drainage Research Unit, 590 Woody Hayes Dr., Columbus, OH, 43210, USA.
J Environ Qual. 2020 May;49(3):675-687. doi: 10.1002/jeq2.20070. Epub 2020 Apr 27.
Legacy phosphorus (P) in agricultural soils can be transported to surface waters via runoff and tile drainage, where it contributes to the development of harmful and nuisance algal blooms and hypoxia. However, a limited understanding of legacy P loss dynamics impedes the identification of mitigation strategies. Edge-of-field data from 41 agricultural fields in northwestern Ohio, USA, were used to develop regressions between legacy P concentrations (C) and discharge (Q) for two P fractions: total P (TP) and dissolved reactive P (DRP). Tile drainage TP concentration (C ) and DRP concentration (C ) both increased as Q increased, and C tended to increase at a greater rate than C . Surface runoff showed greater variation in C-Q regressions, indicating that the response of TP and DRP to elevated Q was field specific. The relative variability of C and Q was explored using a ratio of CVs (CV /CV ), which indicated that tile drainage TP and DRP losses were chemodynamic, whereas losses via surface runoff demonstrated both chemodynamic and chemostatic behavior. The chemodynamic behavior indicated that legacy P losses were strongly influenced by variation in P source availability and transport pathways. In addition, legacy P source size influenced C, as demonstrated by a positive relationship between soil-test P and the C and C in both tile drainage and surface runoff. Progress towards legacy P mitigation will require further characterization of the drivers of variability in C and C , including weather-, soil-, and management-related factors.
农业土壤中的磷素残留(P)可以通过径流和排水渠输送到地表水中,从而导致有害和滋扰性藻类水华和缺氧的发生。然而,对磷素残留损失动态的有限理解阻碍了缓解策略的确定。利用美国俄亥俄州西北部 41 个农业田块的田间边缘数据,建立了总磷(TP)和溶解反应性磷(DRP)两个磷素分数与流量(Q)之间的回归关系。排水中 TP 浓度(C )和 DRP 浓度(C )随流量(Q)的增加而增加,C 增加的速率往往大于 C 。地表径流的 C-Q 回归表现出更大的变化,表明 TP 和 DRP 对升高 Q 的响应具有田块特异性。利用变异系数(CV )的比值(CV /CV )来探索 C 和 Q 的相对变异性,这表明排水 TP 和 DRP 的损失是化学动力的,而通过地表径流的损失则表现出化学动力和化学静态行为。化学动力行为表明,磷素残留损失受到磷素源供应和运输途径变化的强烈影响。此外,磷素源大小影响 C ,这表现为土壤测试磷与排水和地表径流中 C 和 C 之间存在正相关关系。要实现磷素残留的缓解,就需要进一步描述 C 和 C 变异性的驱动因素,包括天气、土壤和管理相关因素。