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Catalytic ozonation process using a MgO nano-catalyst to degrade methotrexate from aqueous solutions and cytotoxicity studies in human lung epithelial cells (A549) after treatment

机译:使用MgO纳米催化剂的催化臭氧氧化工艺可从水溶液中降解甲氨蝶呤和治疗后人肺上皮细胞(A549)的细胞毒性研究

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Pharmaceutical compounds which enter the environment are classified as emerging pollutants. Among different drug compounds, anti-cancer drugs like methotrexate are of more concern due to their mutagenic, carcinogenic, and genotoxic properties. Therefore, the main objective of this study was to use catalytic ozonation processes (COPs) as novel advanced oxidation processes to degrade methotrexate from aqueous solutions. The calcination method was used to obtain a nitrate magnesium oxide nano-catalyst. The main variables considering the effect of single ozonation processes (SOPs) and COPs on the target pollutant were initial methotrexate concentration, contact time, solution pH, and MgO dosage. The BET results indicated that the surface area of the MgO nano-catalyst was 140.031 m ~(2) g ~(?1) . Based on the BJH plot, the size of the MgO nano-catalyst and average pore volume were 44.5 nm and 0.4454 cm ~(3) g ~(?1) , respectively. The weight percent of Mg and O was 61.09% and 38.91%, respectively. In acidic and alkaline pH, the degradation rate of methotrexate showed a higher increase in SOPs and COPs than at neutral pH. The degradation rate of methotrexate decreased with increasing concentration. By increasing the contact time, the degradation rate of methotrexate of both SOPs and COPs increased. Actually, the methotrexate degradation in COPs was faster than in SOPs. When using tert -butanol as a scavenger, the reduced removal efficiency in SOPs and COPs was 32% and 31%, respectively.
机译:进入环境的药物化合物被分类为新兴污染物。在不同的药物化合物中,甲氨蝶呤等抗癌药物因其诱变,致癌和遗传毒性特性而倍受关注。因此,本研究的主要目的是使用催化臭氧氧化工艺(COPs)作为新型的高级氧化工艺来降解水溶液中的甲氨蝶呤。煅烧方法用于获得硝酸镁氧化物纳米催化剂。考虑单一臭氧化过程(SOP)和COP对目标污染物的影响的主要变量是甲氨蝶呤的初始浓度,接触时间,溶液pH值和MgO剂量。 BET结果表明,MgO纳米催化剂的表面积为140.031m·(2)g·(Δ1)。基于BJH图,MgO纳米催化剂的尺寸和平均孔体积分别为44.5nm和0.4454cm〜(3)g〜(?1)。 Mg和O的重量百分比分别为61.09%和38.91%。在酸性和碱性pH下,甲氨蝶呤的降解速率显示出SOP和COP的增加要高于中性pH。甲氨蝶呤的降解率随浓度增加而降低。通过增加接触时间,SOP和COP的甲氨蝶呤的降解率均增加。实际上,COP中的甲氨蝶呤降解速度比SOP中的快。当使用叔丁醇作为清除剂时,降低的SOP和COP去除效率分别为32%和31%。

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