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Potential hazards of metal-contaminated soils in an estuarine impoundment

机译:河口蓄水中金属污染土壤的潜在危害

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Purpose A recreational impoundment was constructed in the mid-nineteenth century on the mudflats reclaimed from the Plym Estuary (SW England) following salt marsh removal and infilling with waste soils from local catchments. Restoration of the salt marsh was attempted about 25 years ago when a regulated tidal exchange system was installed in the embankment separating the impoundment from the estuary. Currently, the embankment is disintegrating with the potential loss of the impounded soils, of unknown composition, to the estuary. Methods Cores were obtained from the impoundment and the adjoining estuary, sectioned, dried and analysed. The geochronology of the soils, and estuarine sediments, was established using gamma-ray spectroscopy to determine the activities of fallout radionuclides, Cs-137 and Pb-210. The concentrations of As, Co, Cr Cu, Fe, Mn, Ni, Pb, Rb, Sn, W and Zn in the core sections were determined by quantitative X-ray fluorescence spectrometry. Results Below a shallow surface layer ( 5 cm and post-1963), metal concentrations were high with several exceeding soil quality indices, and enrichment factors (EFs) were elevated, in the sequence Sn W approximate to As Cu Pb. Estimates of the total masses of particulate Sn, Pb, As and Cu available for down-estuary migration were significant. Conclusions Given the ecotoxicological implications resulting from a loss of metal-contaminated soils into the estuary, a strategy for the future management of the impoundment is required. The conditions at this site are compared with ageing estuarine impoundments at other locations, where polluted sediments, or soils, could be vulnerable to release.
机译:目的,在十九世纪中期,在盐沼地移除和从局部集水区的废物中排出盐渍土壤中的泥浆中中期的泥滩中的泥浆建造了娱乐蓄水。 25年前在将蓄水从河口分开的路堤中安装了规范的潮汐交换系统时,大约25年前恢复了盐沼。目前,堤防正在摧毁贫困土壤的潜在损失,未知的土壤,未知的组合物到河口。方法从蓄水和相邻的河口,切片,干燥和分析中获得核心。使用γ射线光谱建立土壤和河口沉积物的地理学,以确定辐射放射性核素,CS-137和PB-210的活性。通过定量X射线荧光光谱法测定芯部分中的浓度,CO,Cr Cu,Fe,Mn,Ni,Pb,Rb,Sn,W和Zn。结果低于浅表面层(> 5厘米和1963年),金属浓度高,几个超过土壤质量指数,浓缩因子(EF)升高,序列Sn> W近似为> Cu> Pb。可用于下浅月份迁移的颗粒状Sn,Pb,作为Cu的总质量的估计显着。结论鉴于由于金属污染的土壤损失导致的生态毒理学影响,需要对未来管理蓄积金的策略。将该网站的病症与其他位置的老化河口蓄水量进行比较,其中污染沉积物或土壤,可能易于释放。

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