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Atmospheric mercury emissions from polluted gold mining areas (Venezuela)

机译:污染金矿区(委内瑞拉)的大气汞排放

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Soil, waste rock and mud from mercury-gold amalgamation mining areas of El Callao (Venezuela) are highly enriched in Hg (0.5-500 μg g~(-1)) relative to natural background concentrations ( < 0.1 μg g~(-1)). Mercury fluxes to the atmosphere from twelve polluted sites of this area were measured in situ (6 a.m. to 8 p.m.) using a Plexiglas flux chamber connected to a portable mercury analyzer (model RA-915+; Lumex, St. Petersburg, Russia). Mercury fluxes ranged between 0.65 and 420.1 μg m~(-2) h~(-1), and the average flux range during the diurnal hours was 9.1-239.2 μg m~(-2) h~(-1). These flux values are five orders of magnitude higher than both reported world background Hg fluxes (1-69 ng m~(-2) h~(-1)) and the regional values, which are in the range 2-10 ng m~(-2) h~(-1). The flux results obtained in this study are, however, similar to those measured at Hg polluted sites such as chloro-alkali plants or polymetallic ore mining districts ( > 100,000 ng m~(-2) h~(-1)). The results from this study also show that Hg emissions from the soil are influenced by solar radiation, soil temperature and soil Hg concentration. Our data suggest that solar radiation may be the dominant factor affecting Hg° emission since the major species of mercury in polluted soil is Hg° (85-97% of total Hg). The simple release of Hg° vapor is probably the dominant process occurring with incident light in the field. The apparent activation energy for mercury emission indicates that the volatilization of mercury mainly occurred as a result of the vaporization of elemental mercury in soil. The degree of Hg emission differed significantly among the soil sites studied, which may be due to variations in soil texture, organic matter content and soil compaction.
机译:相对于自然本底浓度(<0.1μgg〜(-1),来自El Callao(委内瑞拉)汞金合并矿产区的土壤,废石和泥土富含Hg(0.5-500μgg〜(-1))。 ))。使用连接到便携式汞分析仪(型号RA-915 +; Lumex,圣彼得堡,俄罗斯)的有机玻璃通量室,从该地区的十二个污染点向大气中的汞通量进行了现场测量(上午6点至晚上8点)。汞通量范围为0.65至420.1μgm〜(-2)h〜(-1),日间平均通量范围为9.1-239.2μgm〜(-2)h〜(-1)。这些通量值比报道的世界背景汞通量(1-69 ng m〜(-2)h〜(-1))和区域值都高5个数量级,后者在2-10 ng m〜范围内(-2)h〜(-1)。但是,本研究中获得的通量结果与在汞污染场所(如氯碱厂或多金属矿产区)(> 100,000 ng m〜(-2)h〜(-1))所测得的通量结果相似。这项研究的结果还表明,土壤中汞的排放受太阳辐射,土壤温度和土壤汞浓度的影响。我们的数据表明,太阳辐射可能是影响Hg°排放的主要因素,因为污染土壤中汞的主要种类是Hg°(占总Hg的85-97%)。汞蒸气的简单释放可能是场中入射光发生的主要过程。汞释放的表观活化能表明,汞的挥发主要是由于土壤中元素汞的蒸发所致。汞排放的程度在所研究的土壤位点之间存在显着差异,这可能是由于土壤质地,有机质含量和土壤压实度的变化所致。

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