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Mercury in soil near a long-term air emission source in southeastern Idaho

机译:爱达荷州东南部长期空气排放源附近土壤中的汞

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At the Idaho National Engineering and Environmental Laboratory in southeastern Idaho, a 500℃ fluidized bed calciner was intermittently operated for 37 years, with measured Hg emission rates of 9-11g/h. Surface soil was sampled at 57 locations around the facility to determine the spatial distribution of Hg fallout and surface Hg variability, and to predict the total residual Hg mass in the soil from historical emissions. Measured soil concentrations were slightly higher (p<0.05) within 5km of the source but were overall very low (15-20 ng/g) compared to background Hg levels published for similar soils in the USA (50-70 ng/g). Concentrations decreased 4%/cm with depth and were found to be twice as high under shrubs and in depressions. Mass balance calculations accounted for only 2.5-20% of the estimated total Hg emitted over the 37-year calciner operating history. These results suggest that much of the Hg deposited from calciner operations may have been reduced in the soil and re-emitted as Hg(0) to the global atmospheric pool.
机译:在爱达荷州东南部的爱达荷州国家工程和环境实验室,一台500℃的流化床煅烧炉间歇运行了37年,测得的汞排放速率为9-11g / h。在设施周围的57个位置对表层土壤进行采样,以确定汞沉降的空间分布和表层汞的变异性,并根据历史排放量预测土壤中的总残留汞量。与美国公布的类似土壤中的背景汞含量(50-70 ng / g)相比,在距污染源5 km处测得的土壤浓度略高(p <0.05),但总体上非常低(15-20 ng / g)。浓度随深度降低4%/ cm,在灌木和洼地中浓度是后者的两倍。在37年的煅烧炉运行历史中,质量平衡计算仅占估算的总汞排放量的2.5-20%。这些结果表明,煅烧炉操作中沉积的大部分汞可能已在土壤中减少,并以Hg(0)的形式重新排放到全球大气池中。

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