Agricultural Catchments Programme, Teagasc, Johnstown Castle, Wexford, Ireland; Environment Section, Wexford County Council, Carricklawn, Wexford, Ireland.
Microbiology, School of Natural Sciences and Ryan Institute, National University of Ireland, Galway, Ireland.
Sci Total Environ. 2017 Jul 15;590-591:469-483. doi: 10.1016/j.scitotenv.2017.02.100. Epub 2017 Mar 9.
Stormflow and baseflow phosphorus (P) concentrations and loads in rivers may exert different ecological pressures during different seasons. These pressures and subsequent impacts are important to disentangle in order to target and monitor the effectiveness of mitigation measures. This study investigated the influence of stormflow and baseflow P pressures on stream ecology in six contrasting agricultural catchments. A five-year high resolution dataset was used consisting of stream discharge, P chemistry, macroinvertebrate and diatom ecology, supported with microbial source tracking and turbidity data. Total reactive P (TRP) loads delivered during baseflows were low (1-7% of annual loads), but TRP concentrations frequently exceeded the environmental quality standard (EQS) of 0.035mgL during these flows (32-100% of the time in five catchments). A pilot microbial source tracking exercise in one catchment indicated that both human and ruminant faecal effluents were contributing to these baseflow P pressures but were diluted at higher flows. Seasonally, TRP concentrations tended to be highest during summer due to these baseflow P pressures and corresponded well with declines in diatom quality during this time (R=0.79). Diatoms tended to recover by late spring when storm P pressures were most prevalent and there was a poor relationship between antecedent TRP concentrations and diatom quality in spring (R=0.23). Seasonal variations were less apparent in the macroinvertebrate indices; however, there was a good relationship between antecedent TRP concentrations and macroinvertebrate quality during spring (R=0.51) and summer (R=0.52). Reducing summer point source discharges may be the quickest way to improve ecological river quality, particularly diatom quality in these and similar catchments. Aligning estimates of P sources with ecological impacts and identifying ecological signals which can be attributed to storm P pressures are important next steps for successful management of agricultural catchments at these scales.
河流的暴雨和基流磷(P)浓度和负荷在不同季节可能会产生不同的生态压力。为了有针对性地监测和监测缓解措施的有效性,需要厘清这些压力及其后续影响。本研究调查了暴雨和基流 P 压力对六个具有对比性农业流域的河流生态的影响。使用了一个包含五年高分辨率数据集的研究,包括河流流量、P 化学、大型底栖无脊椎动物和硅藻生态学,以及微生物来源追踪和浊度数据的支持。基流期间输送的总反应性 P(TRP)负荷较低(占年负荷的 1-7%),但在这些流量下,TRP 浓度经常超过环境质量标准(EQS)0.035mgL(在五个流域中有 32-100%的时间)。在一个流域进行的试点微生物来源追踪实验表明,人类和反刍动物粪便污水都对这些基流 P 压力有贡献,但在较高流量下被稀释。季节性地,由于这些基流 P 压力,TRP 浓度在夏季往往最高,与这段时间硅藻质量的下降非常吻合(R=0.79)。当暴雨 P 压力最为普遍时,硅藻通常会在春末恢复,而春季的前溯 TRP 浓度与硅藻质量之间的关系较差(R=0.23)。在宏观无脊椎动物指数中,季节性变化不太明显;然而,在春季(R=0.51)和夏季(R=0.52),前溯 TRP 浓度与宏观无脊椎动物质量之间存在很好的关系。减少夏季点源排放可能是改善生态河流质量的最快方法,特别是在这些和类似流域的硅藻质量。将 P 源的估计与生态影响联系起来,并确定可以归因于暴雨 P 压力的生态信号,是在这些规模上成功管理农业流域的重要下一步。