Shoham-Frider E, Shelef G, Kress N
Israel Oceanographic and Limnological Research, National Institute of Oceanography, P.O. Box 8030, Haifa 31080, Israel.
Mar Environ Res. 2007 Dec;64(5):601-15. doi: 10.1016/j.marenvres.2007.06.003. Epub 2007 Jul 5.
Mercury speciation was performed in excess activated sewage sludge (ASS) and in marine sediments collected at the AAS disposal site off the Mediterranean coast of Israel in order to characterize the spatial and vertical distribution of different mercury species and assess their environmental impact. Total Hg (HgT) concentrations ranged between 0.19 and 1003ng/g at the polluted stations and 5.7 and 72.8ng/g at the background station, while the average concentration in ASS was 1181+/-273ng/g. Only at the polluted stations did HgT concentrations decrease exponentially with sediment depth, reaching background values at 16-20cm, the vertical distribution resulting from mixing of natural sediment with ASS solids and bioturbation by large populations of polycheates. Average Methyl Hg (MeHg) concentration in ASS was 39.7+/-7.1ng/g, ca. 3% of the HgT concentration, while the background concentrations ranged between 0.1 and 0.61ng/g. MeHg concentrations in surficial polluted sediments were 0.7-5.9ng/g (ca. 0.5% of the HgT) and decreased vertically, similar to HgT. A positive correlation between MeHg and Hg only at the polluted stations, higher MeHg concentrations at the surface of the sediment and not below the redoxline, and no seasonality in the concentrations suggest that the MeHg originated from the ASS and not from in situ methylation. By doing selective extractions, we found that ca. 80% of the total Hg in ASS and polluted sediments was strongly bound to amorphous organo-sulfur and to inorganic sulfide species that are not bioavailable. The fractions with potential bioaccessible Hg had maximal concentrations in the range in which biotic effects should be expected. Therefore, although no bioaccumulation was found in the biota in the area, the concentration in the polluted sediments are not negligible and should be carefully monitored.
对过量的活性污水污泥(ASS)以及在以色列地中海沿岸AAS处置场采集的海洋沉积物进行汞形态分析,以表征不同汞形态的空间和垂直分布,并评估其环境影响。在受污染站点,总汞(HgT)浓度在0.19至1003纳克/克之间,在背景站点为5.7至72.8纳克/克,而ASS中的平均浓度为1181±273纳克/克。仅在受污染站点,HgT浓度随沉积物深度呈指数下降,在16 - 20厘米处达到背景值,这种垂直分布是自然沉积物与ASS固体混合以及大量多毛纲动物生物扰动的结果。ASS中甲基汞(MeHg)的平均浓度为39.7±7.1纳克/克,约占HgT浓度的3%,而背景浓度在0.1至0.61纳克/克之间。受污染表层沉积物中的MeHg浓度为0.7 - 5.9纳克/克(约占HgT的0.5%),并随深度下降,与HgT情况相似。仅在受污染站点,MeHg与Hg呈正相关,沉积物表面而非氧化还原线以下的MeHg浓度更高,且浓度无季节性变化,这表明MeHg源自ASS而非原位甲基化。通过选择性萃取,我们发现ASS和受污染沉积物中约80%的总汞与无定形有机硫和无机硫化物物种紧密结合,这些物种不可生物利用。具有潜在生物可及性汞的组分在预期会产生生物效应的范围内浓度最高。因此,尽管该区域的生物群中未发现生物累积现象,但受污染沉积物中的浓度不可忽视,应予以仔细监测。