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REMOVAL OF COPPER FROM AQUEOUS SOLUTIONS USING BIOCHARS PRODUCED THROUGH PYROLYSIS

机译:使用通过热解产生的生物脉管从水溶液中除去铜

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In this study, the biochars of three agricultural by-products (rice husks, olive pomace andorange waste) and compost are evaluated regarding their capability in Cu(ll) adsorptionfrom aqueous solutions.For each material, two kinds of biochars were produced, through pyrolysis at two different temperatures, 300°C and 600°C, respectively. The pyrolysis process was carried out under oxygen-limited conditions in a muffle furnace, where porcelain crucibles containing the materials were placed and kept for six hours.For the evaluation of the adsorption capability of the biochars and the raw materials,batch experiments were performed to investigate the influence of adsorbent dose, pH,contact time and initial Cu(ll) concentration. These experiments were carried out usingplastic flasks with a ratio of solid:liquid of 1:40 (g/mL). The resulting data were used tostudy the adsorption kinetics and adsorption equilibrium.The obtained results showed relatively high Cu(ll) adsorption efficiency onto all tested materials. It was observed that the adsorption process was highly dependent on the experimental conditions. It resulted that the optimum Cu(ll) adsorption conditions determined from this evaluation were: adsorbent dose 5-12.5 g/L, pH 5 - 6 and contact time 2 -4 h. The adsorption kinetics was properly fitted by the pseudo-second order model, for all tested materials. Regarding the adsorption equilibrium, the adsorption systems for five materials were best described by the linear isotherm, while the rest were best described by the Freundlich isotherm.Furthermore, it was also noticed that pyrolyzing the four studied materials at bothtemperatures, 300°C and 600°C respectively, led to a decrease in their adsorptioncapacity, in comparison with the raw materials. This is probably due to the destruction ofsome part of the active sites on the materials surface. However, the adsorption resultsobtained by the 300°C Pyrolysis biochars were higher and more sufficient compared tothe adsorption ability shown by the 600°C Pyrolysis biochars. This could be attributed tothe higher temperature of this process, which consequently caused the destruction ofmore active sites, compared to the 300°C Pyrolysis process.
机译:在这项研究中,评估了三种农业副产品(稻壳,橄榄饼和ororange废物)和堆肥的生物脉,关于它们在Cu(L1)吸附的能力。对于每种材料,通过热解产生两种生物脉冲在两个不同的温度下,300°C和600°C。在马弗炉中的氧有限条件下进行热解过程,其中含有含有材料的瓷坩埚并保持六个小时。对于生物触发器和原料的吸附能力的评估,进行分批实验研究吸附剂剂量,pH,接触时间和初始Cu(LL)浓度的影响。使用具有固体比例的血液烧瓶的使用比例:液体为1:40(g / ml)。所得到的数据被扭转了吸附动力学和吸附平衡。得到的结果显示出相对高的Cu(LL)吸附效率在所有测试材料上。观察到吸附过程高度依赖于实验条件。因此,由该评估确定的最佳Cu(LL)吸附条件是:吸附剂量5-12.5g / L,pH 5-6和接触时间2 -4 h。伪二次订单模型适用于所有测试材料的吸附动力学。关于吸附平衡,用于五种材料的吸附系统最好由线性等温线描述,而其余的是由Freundlich等温线最佳描述的,它还被注意到,热解四个在繁殖的四种研究中,300°C和600与原料相比,分别导致其吸附缓存降低。这可能是由于材料表面上有活跃点的部分部分的破坏。然而,通过300℃热解Biochars的吸附率为300℃热解Biochars所示的吸附能力较高,更易于足够的吸附能力。这可能归因于该过程的较高温度,因此与300℃的热解过程相比,该方法的较高温度导致了活性位点的破坏。

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