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1994年至1996年英国亨伯河口系统中悬浮颗粒、碳和氮的通量与转化:综合观测与建模研究结果

The fluxes and transformations of suspended particles, carbon and nitrogen in the Humber estuarine system (UK) from 1994 to 1996: results from an integrated observation and modelling study.

作者信息

Tappin A D, Harris J R W, Uncles R J

机构信息

Plymouth Marine Laboratory, Prospect Place, Plymouth PL1 3DH, UK.

出版信息

Sci Total Environ. 2003 Oct 1;314-316:665-713. doi: 10.1016/s0048-9697(03)00078-0.

Abstract

Results from the first multi-constituent dynamic modelling study of the Humber estuarine system over seasonal time scales are presented. The model, constructed within the ECoS3 simulation software, has been calibrated using data obtained from 27 surveys of the Yorkshire Ouse and Humber estuaries during 1994-1996. The model is tidally averaged, and is one-dimensional in the vertical and in cross-section. Daily-varying longitudinal concentration profiles of SPM, POC, nitrate, nitrite and ammonium have been simulated, and these have been compared with the observations used for model calibration (model confirmation). The fits are generally good. The model captures the marked seasonal variability in concentrations of the particulate constituents (SPM, POC), and places the turbidity maximum in approximately the correct region of the estuary. There was a high degree of scatter in the SPM and POC concentrations measured due to tidal resuspension, which was not reproduced by the tidally averaged model. Comparisons between measured and simulated nitrate+nitrite are satisfactory, although for a number of surveys the modelled values are systematically too low in the lower Yorkshire Ouse and upper Humber. These discrepancies are not readily explained, but may be linked to inadequately characterised source terms for this nitrogen. The general trends in the concentrations and distributions of ammonium are reproduced by the model, despite the plethora of external inputs of this constituent, and significant modifications to ammonium transport by in situ nitrification and benthic exchange. The simulated concentrations and distributions have also been tested against independent data encapsulating axial transects in the Trent and Humber estuaries, and temporal variations at fixed sites on the Trent and Yorkshire Ouse estuaries. With some exceptions, the fits between the model results and these data are also good. The model has also been used to construct constituent budgets (external/internal sources and sinks) for each estuary for 1994, 1995 and 1996. Riverine inputs of SPM, POC, nitrate, nitrite and ammonium decreased over the 3 years, presumably reflecting changing patterns of terrestrial runoff coupled to a reduction in effluent inputs. This trend was also observed in the point discharges of these constituents direct to the estuary. The simulated estuary was a source of sediments to the North Sea during 1994 and 1996, but a sink during 1995. The difference has been ascribed to the exceptionally dry summer and autumn of 1995, in which up-estuary tidal 'pumping' of SPM was dominant over down-estuary flushing by river water. Fluvial inputs represent an important external source of POC to the model estuary (27-55%), as does the North Sea (26-58%). These inputs are exceeded by POC loss via bacterial remineralisation, suggesting that the estuarine bed is a net source of POC. Riverine inputs account for 76-77% of the external inputs of nitrate. This constituent behaves quasi-conservatively in the estuary, reflecting the dilution of nitrate-rich river waters with low-nitrate coastal water, although nitrification is a significant input (approx. 21%). Denitrification is small, and consequently all nitrate added to the estuary is lost to the North Sea. External loads of nitrite are small and ammonium nitrification accounts for approximately 93% of its annual input. Practically all of the nitrite is oxidised to nitrate, and little escapes to the North Sea. The fluvial and direct waste inputs of ammonium to the estuary are of similar size. Most of the ammonium in the model is nitrified (98-100%) and only a few tons are exported to the North Sea. In 1996 the estuary appears to have been a sink for coastal water ammonium. Constituent budgets are compared with independently evaluated fluxes. There is good agreement in a number of cases, but the comparison highlights the main uncertainties in the simulated fluxes. It is concluded that the model as currently formulated provides an excellent basis for heuristic studies of the Humber estuarine system.

摘要

本文展示了亨伯河口系统在季节时间尺度上的首个多成分动态建模研究结果。该模型是在ECoS3模拟软件中构建的,已使用1994 - 1996年期间对约克郡乌斯河和亨伯河口进行的27次调查所获得的数据进行了校准。该模型是潮汐平均的,在垂直方向和横截面上均为一维。已模拟了悬浮颗粒物(SPM)、颗粒有机碳(POC)、硝酸盐、亚硝酸盐和铵的逐日变化纵向浓度剖面,并将其与用于模型校准(模型验证)的观测值进行了比较。拟合效果总体良好。该模型捕捉到了颗粒成分(SPM、POC)浓度明显的季节变化,并将浊度最大值置于河口大致正确的区域。由于潮汐再悬浮,测量的SPM和POC浓度存在高度离散性,这在潮汐平均模型中未得到再现。实测与模拟的硝酸盐 + 亚硝酸盐之间的比较结果令人满意,尽管在一些调查中,在约克郡乌斯河下游和亨伯河上游,模拟值系统性地偏低。这些差异难以解释,但可能与该氮源项特征描述不足有关。尽管该成分有大量外部输入,且原位硝化和底栖交换对铵的输运有显著改变,但模型再现了铵浓度和分布的总体趋势。模拟的浓度和分布也已针对包含特伦特河和亨伯河河口轴向断面的独立数据以及特伦特河和约克郡乌斯河河口固定站点的时间变化进行了测试。除了一些例外情况,模型结果与这些数据之间的拟合也很好。该模型还被用于构建1994年、1995年和1996年每个河口的成分收支(外部/内部源和汇)。在这3年中,河流输入的SPM、POC、硝酸盐、亚硝酸盐和铵有所减少,这可能反映了陆地径流模式的变化以及污水输入的减少。在这些成分直接排入河口的点排放中也观察到了这一趋势。1994年和1996年模拟的河口是北海沉积物的一个源,但1995年是一个汇。这种差异归因于1995年异常干燥的夏秋季节,其中河口上游SPM的潮汐“抽吸”作用超过了河水的下游冲刷作用。河流输入是模型河口POC的一个重要外部源(27 - 55%),北海也是(26 - 58%)。通过细菌再矿化导致的POC损失超过了这些输入,这表明河口床是POC的净源。河流输入占硝酸盐外部输入的76 - 77%。该成分在河口表现为准保守行为,反映了富含硝酸盐的河水与低硝酸盐沿海水的稀释,尽管硝化作用是一个重要输入(约21%)。反硝化作用较小,因此添加到河口的所有硝酸盐都流入了北海。亚硝酸盐的外部负荷较小,铵硝化作用约占其年输入的93%。实际上所有的亚硝酸盐都被氧化为硝酸盐,很少有亚硝酸盐排入北海。河流和直接废物向河口输入的铵量大致相同。模型中的大部分铵被硝化(98 - 100%),只有几吨铵输出到北海。1996年,河口似乎是沿海水铵的一个汇。将成分收支与独立评估的通量进行了比较。在一些情况下有很好的一致性,但这种比较突出了模拟通量中的主要不确定性。得出的结论是,当前形式的模型为亨伯河口系统的启发式研究提供了一个极好的基础。

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