椰壳活性炭处理亚甲蓝的性能

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摘要

选择椰子壳作为原材料,通过物理和化学活化方法合成活性炭,并评估亚甲基蓝处理的性能。 物理活化方法是将椰子壳放入 400°C 的炉中加热,化学活化方法是使用磷酸。使用傅立叶变换红外光谱(FTIR)对制备的椰壳活性炭(CSAC)进行分析,以确定是否存在官能团及其组成。亚甲基蓝(MB)被认为是纺织工业废水中的主要污染物。它是一种有毒的致癌染料,对接触或食用它的生物体有害。由于 CSAC 对甲基溴的去除效率较高,因此采用 CSAC 吸附法处理亚甲基蓝。在本研究中,使用不同剂量的 CSAC(15 克、20 克、25 克)处理亚甲基蓝样品。为评估 CSAC 处理亚甲基蓝的性能,进行了脱色率(CR%)分析、化学需氧量分析和浊度分析。使用 15 克、20 克和 25 克 CSAC 的色度去除率(CR%)分别为 95.59%、97.40% 和 98.23%。在 COD 分析中,使用 15 克、20 克和 25 克 CSAC 时,COD 去除率分别为 55.41%、64.33% 和 80.25%。使用 15 克、20 克和 25 克 CSAC 时,浊度去除率分别为 81.48%、85.19% 和 92.59%。因此,由于样品中存在的表面积,当 CSAC 的用量增加时,甲基溴的吸附过程也随之增加。
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Performance of Coconut-shell Activated Carbon on Methylene Blue Treatment
Coconut shell was chosen as a raw material to synthesize activated carbon through physical and chemical activation methods and to evaluate the performance of methylene blue treatment Physical activation method was done by heating the coconut shell in the furnace at 400°C and the chemical activation method was done by using phosphoric acid. Prepared coconut-shell activated carbon (CSAC) was analysed using Fourier-transform infrared spectroscopy (FTIR) to determine the presence of functional groups and their composition. Methylene blue (MB) was chosen as a dye that can be considered as a major pollutant in textile industries’ wastewater. It is a toxic and carcinogenic dye that is harmful to organisms that are exposed to or consumed. The adsorption method using CSAC was used to treat methylene blue due to its higher MB removal efficiency. In this study, methylene blue samples were treated using different dosages of CSAC (15g, 20g, 25g). Color removal (CR%) analysis, COD analysis, and turbidity analysis were done to evaluate the performance of CSAC on methylene blue treatment. 95.59%, 97.40%, and 98.23% of color removal (CR%) were achieved using CSAC dosages of 15g, 20g, and 25g respectively. For COD analysis, 55.41%, 64.33%, and 80.25% of COD removal (%) were achieved when 15g, 20g and 25 g of CSAC dosages were used. 81.48%, 85.19%, and 92.59% of turbidity removal (%) were achieved using CSAC dosages of 15g, 20g, and 25 g respectively. Hence, the adsorption process of MB increases when the dosage of CSAC increases due to surface areas present in the sample.
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