First photocatalytic investigation on Cd–Mn–O nanocomposites for the degradation of Eriochrome Black T
摘要
The use of photocatalysts for water purification is of great interest. The photocatalysts use solar energy to degrade organic pollutants. In this work, Cd-Mn–O nanocomposites (CMO NCs) were synthesized through simple co-precipitation and hydrothermal routes. The co-precipitation synthesis was fabricated without and also with capping agents, CTAB, PEG4000 and PVA. The hydrothermal synthesis was promoted without surfactant at 120, 150 and 180 °C for the different times. We also investigated effects some parameters, including, the surfactant, temperature and time in this synthesis. SEM images showed that multifaceted structures with diameters 10–300 nm, and clumps of the semi-spherical and multifaceted structures with different sizes (50–400 nm) were formed via co-precipitation and hydrothermal methods, respectively. With the hydrothermal route, nanorods and nanowires with diameters less than 50 nm could also be seen among these structures. TEM images confirmed SEM results and showed the formation of the spherical and multifaceted structures with diameters ranging from 2 to 30 nm, for the product prepared via co-precipitation. XRD patterns showed the formation of CdMn2O4 and CdO phases. The peaks at 500–700 cm−1 in FT-IR were related to the vibrations of Mn‒O and Cd‒O bonds. The presence of Cd, Mn, and O peaks in EDS confirmed the formation of CdMn2O4. Also, we highlighted the photocatalytic activities of CMO NCs, for the first time. To optimize the photocatalytic activities, we utilized both cationic and anionic dyes, including Rhodamine B (RB), Malachite green (MG), and Eriochrome Black T (EBT). We investigated the effects of some parameter to assess the UV-assisted photocatalytic activity of the CMO NCs. Maximum decolorization was achieved for the degradation of 5 ppm of EBT, with 0.05 g photocatalyst dosage, under UV irradiation after 120 min. It was selected as an optimum condition. The optimum CMO NC could catalyze the degradation of EBT by about 95.5%.