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首页> 外文期刊>International Journal of Energy Engineering >Modeling Lateral Distribution of Heavy Metal and Bio-accumulation in Earthworm in the Varying Acidic Surface Horizon of Waste- Polluted Soil
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Modeling Lateral Distribution of Heavy Metal and Bio-accumulation in Earthworm in the Varying Acidic Surface Horizon of Waste- Polluted Soil

机译:废物污染土壤在酸性表面范围内worm中重金属横向分布和生物富集的模拟

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Heavy metal concentrations and its distributions in the soil have been a source of concern to soil usage, particularly to agriculture as concentration and distribution of heavy metal determine to a large extent, the soil quality and consequently that of the crops. The ability to quantify the amount of heavy metal in the soil is of immense importance to soil management. The use of accurate model is essential to estimate the actual soil heavy metal values and its distribution for efficient management. In this study, soil and earthworm samples of the battery-waste-polluted site and that of the background site were collected from five different locations(A,B,C,D and E) along the gradient of decreasing pollution .With five replicates each form one sampling location, twenty–five soil and fifty earthworms samples (two earthworms from each replicate) were collected using stratified random sampling technique. Lead(pb), Cadmium(Cd), Chromium(Cr), Nickel(Ni), Manganese(Mn), Arsenic(As), pH and Mercury(Hg) were analyzed using standard methods. The same process was replicated for the background site. Values of the heavy metals in soil and earthworms were natural and typical of Ameki-Nanka-soil formation. The average range of heavy metals concentrations in soil and earthworm samples from the polluted site were; pb(1025-695 mg/kg), Cd(11.34-6.3 mg/kg), Mn(290-81 mg/kg), pH(2.3-6.9mg/kg), Cr(185-3.7 mg/kg), Ni(12.87-1.7 mg/kg), As(72-4.5 mg/kg), Hg(1.7-0.002mg/kg) and pb(193-37.98 mg/kg), Cd(14.04-0.01 mg/kg), Mn(17.34-1.10mg/kg), pH(6.9-2.3mg/kg), Cr(8.45-0.01 mg/kg), Ni(1.41-0.03 mg/kg), As(0.75-0.01 mg/kg) , Hg(0.4-0.009mg/kg) respectively. Concentrations of heavy metals for soil and earthworm samples decreased along the gradient of decreasing pollution of the polluted site. Three models(Linear , Logarithmic and quadratic models) were developed to test their suitability to the data in which Ph was correlated with heavy metals. Inverse correlation was observed with coefficient R2 of between 0.77-0.95 and lowest percentage deviation of the field from the predicted values.
机译:重金属的浓度及其在土壤中的分布已成为土壤使用特别是农业关注的问题,因为重金属的浓度和分布在很大程度上决定了土壤质量,进而决定了农作物的质量。量化土壤中重金属含量的能力对土壤管理极为重要。准确模型的使用对于估算土壤重金属的实际价值及其分布对于有效管理至关重要。在这项研究中,沿污染减少的梯度从五个不同的位置(A,B,C,D和E)收集了电池废物污染站点和背景站点的土壤和earth样本,每个样本重复了五次在一个采样点,使用分层随机采样技术收集了25个土壤和50个earth样品(每个重复样品中有2个earth)。使用标准方法分析了铅(pb),镉(Cd),铬(Cr),镍(Ni),锰(Mn),砷(As),pH和汞(Hg)。对于后台站点,复制了相同的过程。土壤和earth中的重金属是自然的,是Ameki-Nanka土壤形成的典型特征。污染地点的土壤和earth样品中重金属的平均浓度范围为:铅(1025-695 mg / kg),镉(11.34-6.3 mg / kg),锰(290-81 mg / kg),pH(2.3-6.9mg / kg),铬(185-3.7 mg / kg),镍(12.87-1.7 mg / kg),砷(72-4.5 mg / kg),汞(1.7-0.002mg / kg)和铅(193-37.98 mg / kg),镉(14.04-0.01 mg / kg),锰(17.34-1.10mg / kg),pH(6.9-2.3mg / kg),铬(8.45-0.01 mg / kg),镍(1.41-0.03 mg / kg),砷(0.75-0.01 mg / kg),汞(0.4-0.009mg / kg)。土壤和earth样品中重金属的浓度随着污染地点污染的减少而降低。开发了三种模型(线性模型,对数模型和二次模型)以测试它们对Ph与重金属相关的数据的适用性。观察到反相关,系数R2在0.77-0.95之间,并且场与预测值的最低百分比偏差。

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