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Colloid-facilitated and dissolved cadmium transport through layered soil columns with subsurface cracks

机译:胶体促进和溶解的镉通过具有地下裂缝的分层土壤柱传输

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Cadmium is among the most toxic heavy metals in soil, but its mobility in contaminated soils is not fully understood. The objectives of this study were (i) to investigate relative contribution of colloid- facilitated and dissolved Cd transport to the total flux in contaminated soils with subsurface cracks, and (ii) to identify key processes controlling the downward transport of Cd from contaminated soils. Simulated rainfall experiments were conducted using single-layer columns repacked with topsoil spiked with 3 or 30 mg·kg<'-1> of Cd, and dual-layer columns composed of the repacked Cd-spiked topsoil and undisturbed subsurface soil with visible cracks. Distilled water or 5 mM CaCl<,2> was applied to the columns at a rainfall intensity of 7mm·h<'-1> for 5h on 6 consecutive days. The colloid concentration in the column effluent not only showed a quick response to the concentrations of coexisting ions, but was also affected by the remobilization of once-deposited particles, probably due to shearing force exerted by the water flow. Infiltration of CaCl<,2> completely suppressed the discharge of colloidal particles and colloid-associated Cd while significantly enhancing dissolved Cd transport. Although Cd transport was predominantly in the dissolved form, colloid-associated transport accounted for 30%-80% of the total transport when the ionic strength was lowered by the infiltration of distilled water. The addition of Ca (OH)<,2> to the soil substantially reduced the dissolved Cd concentration, while the colloid particle transport was not appreciably affected. The colloid-associated Cd can be the main form of total Cd transport in limed soils with subsurface cracks.
机译:镉是土壤中毒性最强的重金属之一,但其在污染土壤中的迁移性尚不完全清楚。这项研究的目的是(i)研究胶体促进和溶解的Cd迁移对具有地下裂缝的污染土壤中总通量的相对贡献,以及(ii)确定控制Cd从污染土壤向下迁移的关键过程。模拟降雨实验使用的是单层填充有3或30 mg·kg'-1的Cd的表土再填充的单层柱,以及由重新填充的Cd的表层土壤和未受干扰的具有可见裂缝的地下土壤组成的双层柱。连续6天以7mm·h -1的降雨强度将蒸馏水或5 mM CaCl 2施加到色谱柱上5小时。柱流出物中的胶体浓度不仅显示出对共存离子浓度的快速响应,而且还受到曾经沉积的颗粒迁移的影响,这可能是由于水流施加的剪切力所致。 CaCl 2的渗透完全抑制了胶体颗粒和胶体相关的Cd的排放,同时显着增强了溶解Cd的传输。尽管Cd的运输主要以溶解形式进行,但当离子强度因蒸馏水的渗透而降低时,胶体相关的运输占总运输的30%-80%。向土壤中添加Ca(OH),2大大降低了溶解的Cd浓度,而胶体颗粒的传输没有受到明显影响。胶体相关的Cd可能是镉在具有地下裂缝的石灰土壤中总Cd运移的主要形式。

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