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Distribution of heavy metals in the water column, suspended particulate matters and the sediment under hydrodynamic conditions using an annular flume

机译:使用环形水槽在水力条件下水柱中重金属,悬浮颗粒物和沉积物的分布

摘要

Sediment resuspension plays an important role in the transport and fate of heavy metals in the aquatic environment. In the present study, the release and binding forms of Cr, Cu, Zn, Pb under hydrodynamic conditions were investigated using an annular flume. Two sediments located at YLZ and GBD from Liangshui River, Beijing were resuspended for 10 hr at 0.159 and 0.267 m/sec, respectively. The concentrations of suspended particulate matters of YLZ were higher than those of GBD during resuspension, indicating that the former sediment is more sensitive to the velocity. Cr in the dissolved phase stayed nearly constant at about 2.25 and 1.84 mu g/L for YLZ and GBD, respectively, due to the high percentage of its stable binding fractions in both sediments, while Cu, Zn, and Pb showed a fast release in the initial period of time. However, their concentrations in SPM generally decreased with time and were higher at the lower velocity of 0.159 m/sec, which resulted from the entrainment and depressing effect of larger size particles with lower heavy metal content, commonly referred to as the "particle concentration effect". In addition, the binding form and heavy metal fractions were also found to vary during the resuspension event. A decrease in the sulphide/organic matters bounded form in GBD sediment was observed, whereas no visible changes were perceived in YLZ site samples. This phenomenon is due to the oxidation of heavy metal-sulphide binding forms, which originated from its high acid volatile sulphide content in GBD sediment.
机译:沉积物的再悬浮在水生环境中重金属的运输和命运中起着重要作用。在本研究中,使用环形水槽研究了在水力条件下Cr,Cu,Zn,Pb的释放和结合形式。来自北京凉水河的YLZ和GBD的两种沉积物分别以0.159和0.267 m / sec的速度重悬了10小时。悬浮过程中YLZ悬浮颗粒物的浓度高于GBD,表明前者对速度更敏感。对于YLZ和GBD,溶解相中的Cr分别保持在约2.25和1.84μg / L的几乎恒定不变,这是由于在两种沉积物中其稳定的结合分数所占的百分比很高,而Cu,Zn和Pb在沉积物中快速释放。初始时间段。但是,它们在SPM中的浓度通常随时间降低,并在较低速度0.159 m / sec时较高,这是由于重金属含量较低的大尺寸颗粒的夹带和抑制作用,通常称为“颗粒浓度效应”。 ”。另外,在再悬浮过程中,还发现了结合形式和重金属分数是变化的。观察到GBD沉积物中硫化物/有机物结合形式的减少,而YLZ站点样品中未观察到可见的变化。这种现象是由于重金属-硫化物结合形式的氧化所致,该结合形式源自GBD沉积物中酸性高的挥发性硫化物含量。

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