School of Earth and Environment, The University of Western Australia, Crawley, WA 6009, Australia.
Sci Total Environ. 2012 Aug 15;432:47-56. doi: 10.1016/j.scitotenv.2012.05.065. Epub 2012 Jun 15.
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 (<1h) and field-based (<100 m 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 <100 m 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.
本研究旨在探讨再悬浮富铁硫底层沉积物对河口水质化学的影响。为了达到这一目标,我们进行了(1)一系列基于实验室的沉积物再悬浮实验,以及(2)还监测了西澳大利亚皮尔-哈维河口疏浚活动引起的现场沉积物再悬浮事件期间地表水成分的变化。我们的实验室再悬浮实验表明,富铁硫沉积物的再悬浮会迅速使河口水质脱氧。相比之下,现场的疏浚活动并没有明显降低相邻地表水的氧气浓度。此外,尽管实验室再悬浮过程中铁硫的氧化导致 pH 值可测量地降低,但现场 pH 值不受疏浚事件影响,并且整个监测期间溶解痕量金属浓度仍非常低。在沉积物再悬浮过程中,溶解态铵(NH(4)(+)和无机磷(PO(4)-P)被释放到水柱中,无论是在现场还是实验室。在初始释放后,PO(4)-P 在实验室 (<1h) 和现场 (<100 米从沉积物处置点) 研究中均迅速从溶液中去除。与 PO(4)-P 相比,NH(4)(+)的释放在为期两周的实验室再悬浮实验中观察到更为持久。然而,我们的现场观测表明,NH(4)(+)浓度升高仅限于距沉积物处置点 <100 米的范围内。本研究表明,除了强调铁硫再悬浮过程中的酸化、脱氧和金属释放外,还需要考虑富营养化河口受干扰沉积物中营养物释放的可能性。