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Water chemistry and nutrient release during the resuspension of FeS-rich sediments in a eutrophic estuarine system

机译:富营养化河口系统中富FeS沉积物重悬过程中的水化学和养分释放

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The objective of this study was to investigate the impact of resuspending FeS-rich benthic sediment on estuarine water chemistry. To address this objective, we conducted (1) a series of laboratory-based sediment resuspension experiments and (2) also monitored changes in surface water composition during field-based sediment resuspension events that were caused by dredging activities in the Peel-Harvey Estuary, Western Australia. Our laboratory resuspension experiments showed that the resuspension of FeS-rich sediments rapidly deoxygenated estuarine water. In contrast, dredging activities in the field did not noticeably lower O_2 concentrations in adjacent surface water. Additionally, while FeS oxidation in the laboratory resuspensions caused measurable decreases in pH, the field pH was unaffected by the dredging event and dissolved trace metal concentrations remained very low throughout the monitoring period. Dissolved ammonium (NH_4~+) and inorganic phosphorus (PO_4-P) were released into the water column during the resuspension of sediments in both the field and laboratory. Following its initial release, PO_4-P was rapidly removed from solution in the laboratory-based (<1 h) and field-based (<100m from sediment disposal point) investigations. In comparison to PO_4-P, NH_4~+ release was observed to be more prolonged over the 2-week period of the laboratory resuspension experiments. However, our field-based observations revealed that elevated NH_4~+ concentrations were localised to <100m from the sediment disposal point. This study demonstrates that alongside the emphasis on acidification, deoxygenation and metal release during FeS resuspension, it is important to consider the possibility of nutrient release from disturbed sediments in eutrophic estuaries.
机译:这项研究的目的是调查重悬富FeS底栖沉积物对河口水化学的影响。为了实现这一目标,我们进行了(1)一系列基于实验室的沉积物重悬实验,并且(2)还监测了由于Peel-Harvey河口疏dr活动导致的基于现场的沉积物重悬事件期间地表水成分的变化,澳大利亚西部。我们的实验室重悬实验表明,富FeS沉积物的重悬迅速使河口水脱氧。相反,在田间的疏activities活动并未显着降低相邻地表水中的O_2浓度。此外,尽管实验室悬浮液中的FeS氧化导致pH值可测量地降低,但现场pH值不受疏event事件的影响,并且在整个监测期间,溶解的痕量金属浓度仍然非常低。在田间和实验室中,沉积物的重悬过程中,溶解的铵(NH_4〜+)和无机磷(PO_4-P)被释放到水柱中。最初释放后,PO_4-P在实验室(<1 h)和野外(从沉积物处置点<100m)研究中迅速从溶液中去除。与PO_4-P相比,在实验室重悬实验的2周时间内,NH_4〜+的释放更加延长。但是,我们的实地观测表明,从沉积物处置点开始,NH_4〜+浓度升高的局限在<100m。这项研究表明,在重悬浮FeS的过程中,除了强调酸化,脱氧和金属释放外,重要的是要考虑富营养化河口受干扰沉积物释放养分的可能性。

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