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Air – Borne Heavy Metal Contamination to River Ganga (India)

机译:空气–重金属污染到恒河(印度)

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A two year study was undertaken at Ganges basin of India to evaluate theatmospheric input of six heavy metals to river Ganga. Atmospheric bulk deposition wascollected on a fortnightly basis at 8 river sites from April 2006 through March 2008 todetermine atmospheric loading of heavy metals to river Ganga. The sampling protocolconsisted of bulk collectors placed at 24 locations (3 at each site) selected along a 20 kmlong tract of river Ganga at Varanasi, India. The atmospheric fluxes of six heavy metalsto river Ganga were estimated as (g ha~(-1) y~(-1)) : Cd – 0.56 – 20.15; Cr – 0.34 – 8.87; Cu –1.63 – 58.17; Ni – 0.21 – 7.32; Pb – 1.80 – 124.00; Zn – 124.15 – 477.18. Atmosphericdeposition of all the elements was lowest at Adalpura (site 1) and highest at Rajghatdownstream site (site 8) receiving maximum down – wind urban industrial emissions.Zinc alone contributed to more than 68 % of total measured heavy metal input. Forseason, the atmospheric fluxes were measured highest during winter followed by summerand rainy seasons. Data on heavy metal concentrations in mid – stream water showedsignificant correlation with their respective values received through atmosphericdeposition. Corresponding to the atmospheric deposition, except for Zn, highestconcentrations of Cd, Cr, Cu, Ni and Pb in mid – stream were recorded during winterfollowed by summer and rainy seasons. Concentrations were recorded highest for Znfollowed by Ni, Cr, Pb, Cu and Cd. Concentrations of all the heavy metals were high indown – stream sampling locations. Although the concentrations of Cr, Cu and Znremained well below their maximum admissible concentrations (MAC), more than 80 %of water samples of 7 out of 8 locations sampled, showed Cd, Ni and Pb levels abovetheir respective MAC. Heavy metal loading to mid – stream implicates the adjoiningurban agglomeration of Varanasi as the principal emission source area. The atmosphericloading to the river will continue to rise with the completion of Ganga Express highway.This may lead to serious health implications in long – run since Ganga water is also usedfor drinking purpose by a large population.
机译:在印度恒河盆地进行了为期两年的研究,以评估 恒河中六种重金属的大气输入。大气整体沉积为 从2006年4月到2008年3月,每两周收集8个河流站点, 确定恒河中重金属的大气负荷。采样协议 由在20公里内选定的24个地点(每个地点3个)中放置的大量收集器组成 河在印度瓦拉纳西的恒河。六种重金属的大气通量 到恒河的估计为(g ha〜(-1)y〜(-1)):Cd – 0.56 – 20.15;铬-0.34-8.87;铜– 1.63 – 58.17; Ni – 0.21 – 7.32;铅– 1.80 – 124.00;锌– 124.15 – 477.18。大气层 所有元素的沉积在Adalpura(站点1)最低,在Rajghat最高 下游站点(站点8)获得最大的下降–风能城市工业排放。 仅锌就占重金属总投入量的68%以上。为了 季节,冬季和夏季之后的大气通量被测得最高 和雨季。中游水中重金属浓度的数据显示 与它们各自通过大气获得的值有显着相关性 沉积。对应于大气沉积,除锌外,最高 冬季中游记录了Cd,Cr,Cu,Ni和Pb的浓度 其次是夏季和雨季。锌的浓度最高 其次是镍,铬,铅,铜和镉。所有重金属的浓度都很高 下行–采样位置。虽然Cr,Cu和Zn的浓度 仍远低于其最大允许浓度(MAC)(超过80%) 在8个采样点中有7个采样点的水样中Cd,Ni和Pb含量高于 它们各自的MAC。重金属负载到中游–暗示着毗邻 瓦拉纳西城市群是主要的排放源区域。大气 随着Ganga Express高速公路的竣工,河水的装载量将继续增加。 从长远来看,这可能会导致严重的健康影响,因为还使用了恒河水 用于大量人群的饮酒目的。

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