Nguyen H L, Leermakers M, Kurunczi S, Bozo L, Baeyens W
Laboratory of Analytical and Environmental Chemistry, Vrije Universiteit Brussel, Pleinlaan 2, 1050 Brussels, Belgium.
Sci Total Environ. 2005 Mar 20;340(1-3):231-46. doi: 10.1016/j.scitotenv.2004.08.016.
The distribution and speciation of mercury in air, rain, lake water, sediment, and zooplankton in Lake Balaton (Hungary) were investigated between 1999 and 2002. In air, total gaseous mercury (TGM) ranged from 0.4 to 5.9 ng m(-3) and particulate phase mercury (PPM) from 0.01 to 0.39 ng m(-3). Higher concentrations of both TGM and PPM occurred during daytime. Higher concentrations of PPM occurred in winter. In rain and snow, total mercury ranged from 10.8 to 36.7 ng L(-1) in summer but levels up to 191 ng L(-1) in winter. Monomethylmercury (MMHg) concentrations ranged from 0.09 to 1.26 ng L(-1) and showed no seasonal variations. Total Hg in the unfiltered lake water varied spatially, with concentrations ranging from 1.4 to 6.5 ng L(-1). Approximately 70% of the total Hg is dissolved. MMHg levels ranged from 0.08 to 0.44 ng L(-1) as total and from 0.05 to 0.37 ng L(-1) in the dissolved form. Lower Hg concentrations in the water column occurred in winter. In suspended particulate matter and in sediment, total mercury ranged from 9 to 160 ng g(-1) dw, and MMHg ranged from 0.07 to 0.84 ng g(-1) dw. In zooplankton, an average mercury level of 31.0+/-6.8 ng g(-1) dw occurred, with MMHg accounting for approximately 17%. In sediments, suspended-matter- and zooplankton-high Hg and MMHg levels occurred at the mouth of the River Zala, but, in the lake, higher concentrations occurred on the Northern side, and an increasing trend from north-west to north-east was observed. In general, regarding Hg, Lake Balaton can be considered as a relatively uncontaminated site. The high-pH and well-oxygenated water as well as the low organic matter content of the sediment does not favour the methylation of Hg. In addition, bioconcentration and bioaccumulation factors are relatively low compared to other aquatic systems.
1999年至2002年期间,对匈牙利巴拉顿湖的空气、雨水、湖水、沉积物和浮游动物中的汞分布及形态进行了调查。空气中,总气态汞(TGM)范围为0.4至5.9纳克/立方米,颗粒态汞(PPM)范围为0.01至0.39纳克/立方米。TGM和PPM在白天浓度较高。PPM在冬季浓度较高。雨雪中,夏季总汞范围为10.8至36.7纳克/升,而冬季可达191纳克/升。甲基汞(MMHg)浓度范围为0.09至1.26纳克/升,且无季节性变化。未过滤湖水中的总汞在空间上存在差异,浓度范围为1.4至6.5纳克/升。总汞中约70%为溶解态。MMHg总量范围为0.08至0.44纳克/升,溶解态范围为0.05至0.37纳克/升。水柱中汞浓度在冬季较低。悬浮颗粒物和沉积物中,总汞范围为9至160纳克/克干重,MMHg范围为0.07至0.84纳克/克干重。浮游动物中,汞平均水平为31.0±6.8纳克/克干重,其中MMHg约占17%。沉积物、悬浮物和浮游动物中高汞和MMHg水平出现在佐洛河河口,但在湖中,北侧浓度较高,且观察到从西北向东北呈上升趋势。总体而言,就汞而言,巴拉顿湖可被视为相对未受污染的地点。高pH值、富氧的水以及沉积物中低有机质含量不利于汞的甲基化。此外,与其他水生系统相比,生物浓缩和生物累积因子相对较低。