ATMOSPHERIC EMISSION AND PLANT UPTAKE OF MERCURY FROM AGRICULTURAL SOILS NEAR THE ALMADEN MERCURY MINE

被引:210
作者
LINDBERG, SE
JACKSON, DR
HUCKABEE, JW
JANZEN, SA
LEVIN, MJ
LUND, JR
机构
[1] BATTELLE MEM INST,COLUMBUS LABS,ECOL & ECOSYST SECT,COLUMBUS,OH 43201
[2] OAK RIDGE NATL LAB,DIV ANALYT CHEM,OAK RIDGE,TN 37830
关键词
D O I
10.2134/jeq1979.00472425000800040026x
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Surface soils collected near the Almaden, Spain, mercury mine reflected increasing concentrations of mercury (Hg) with proximity to the mine due to weathered mineral deposits and to atmospheric deposition of Hg from the smelter. Density gradient centrifugation indicated a significant fraction of the Hg to be associated with a high-density mineral fraction, presumably cinnabar. Accumulation of Hg by alfalfa suggested a dual mechanism of uptake; roots accumulated Hg in proportion to the soil levels, while aerial plant material absorbed Hg vapor directly from the atmosphere. Soil fertilization with and without liming significantly increased total Hg uptake, largely due to plant growth stimulation. Liming itself had no significant effect.; Surface soils collected near the Almaden, Spain, mercury mine reflected increasing concentrations of mercury (Hg) with proximity to the mine due to weathered mineral deposits and to atmospheric deposition of Hg from the smelter. Extractions with NaHCO3 or NH4OAc removed small amounts of Hg from both control (20 km from the mine; total Hg = 2.3 μg/g) and mine site soils (1 km; total Hg = 97 μg/g). Density gradient centrifugation indicated a significant fraction of the Hg to be associated with a high-density mineral fraction, presumably cinnabar. Accumulation of Hg by alfalfa suggested a dual mechanism of uptake; roots accumulated Hg in proportion to the soil levels, while serial plant material absorbed Hg vapor directly from the atmosphere. Soil fertilization with and without liming significantly increased total Hg uptake, largely due to plant growth stimulation. Liming itself had no significant effect. The rate of volatilization of elemental Hg from both soils (~0.13 and 0.33 μg/m2 per hour at 25°C, for control and mine site, respectively) exceeded reported background emission rates by factors of 4 to 10, increasing with surface temperature and Hg content and decreasing with increased plant cover.
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页码:572 / 578
页数:7
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