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Adsorption of arsenic from a Nova Scotia groundwater onto water treatment residual solids

机译:新斯科舍省地下水中砷吸附到水处理残留固体上

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Water treatment residual solids were examined in batch adsorption and column adsorption experiments using a groundwater from Halifax Regional Municipality that had an average arsenic concentration of 43 μg/L (±4.2 μg/L) and a pH of 8.1. The residual solids studied in this paper were from five water treatment plants, four surface water treatment plants that utilized either alum, ferric, or lime in their treatment systems, and one iron removal plant. In batch adsorption experiments, iron-based residual solids and lime-based residual solids pre-formed similarly to GFH, a commercially-available adsorbent, while alum-based residual solids performed poorly. Langmuir isotherm modeling showed that ferric residuals had the highest adsorptive capacity for arsenic (Q_(max) = 2230 mg/kg and 42,910 mg/kg), followed by GFH (Q_(max) = 640 mg/kg), lime (Q_(max) = 160 mg/kg) and alum (Q_(max) = <1 mg/kg and 3 mg/kg). Similarly, the maximum arsenic removal was >93% for the ferric and lime residuals and GFH, while the maximum arsenic removal was <49% for the alum residuals under the same conditions. In a column adsorption experiment, ferric residual solids achieved arsenic removal of >26,000 bed volumes before breakthrough past 10 μg As/L, whereas the effluent arsenic concentration from the GFH column was under the method detection limit at 28,000 bed volumes. Overall, ferric and lime water treatment residuals were promising adsorbents for arsenic adsorption from the groundwater, and alum water treatment residuals did not achieve high levels of arsenic adsorption.
机译:使用Halifax Regional Municipality的地下水进行分批吸附和柱吸附实验,对水处理残留固体进行了检查,该地下水的平均砷浓度为43μg/ L(±4.2μg/ L),pH值为8.1。本文研究的残余固体来自五家水处理厂,四家在其处理系统中使用明矾,铁或石灰的地表水处理厂和一台除铁厂。在分批吸附实验中,铁基残留固体和石灰基残留固体的形成与GFH(一种市售的吸附剂)相似,而明矾基残留固体的表现较差。 Langmuir等温线模型显示,铁残留物对砷的吸附能力最高(Q_(max)= 2230 mg / kg和42,910 mg / kg),其次是GFH(Q_(max)= 640 mg / kg),石灰(Q_(最大)= 160 mg / kg)和明矾(Q_(max)= <1 mg / kg和3 mg / kg)。类似地,在相同条件下,铁和石灰残留物和GFH的最大砷去除率> 93%,而明矾残留物的最大砷去除率<49%。在柱吸附实验中,铁残留固体在突破超过10μgAs / L之前实现了> 26,000床体积的砷去除,而GFH柱中的流出物砷浓度在28,000床体积下处于方法检测极限以下。总体而言,铁和石灰水处理残留物是从地下水中吸附砷的有希望的吸附剂,明矾水处理残留物并未实现高水平的砷吸附。

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