Degradation of Anthraquinone dye wastewater by sodium percarbonate with CoO heterogeneous activation

降级(电信) 化学 蒽醌 废水 有机化学 环境科学 环境工程 计算机科学 电信
作者
Haoyu Fan,Yanzhao Xia,Cuizhen Sun,Rupeng Liu,Feiyong Chen,Meng Li,Weichen Zhu,Xinpeng Yang,Zheng Zhang
出处
期刊:Journal of Chemical Technology & Biotechnology [Wiley]
卷期号:99 (8): 1821-1836 被引量:3
标识
DOI:10.1002/jctb.7684
摘要

Abstract BACKGROUND Anthraquinone dyes have an anthraquinone structure as their nucleus, with one or more substituents forming different organic dyes. Anthraquinone dyes have a complex structure that allows them to exist stably in water environment, but also makes them more toxic than azo dyes. This results in varying degrees of harm to both humans and the environment as a result of residual dyes in the water or on the material’ surface. Sodium percarbonate (SPC) is a highly promising oxidant due to its green end product. Therefore, in this study, the catalytic performance and kinetic study of cobalt oxide (CoO) on SPC under different conditions were systematically investigated using RB19 as the target pollutant. The Box–Behnken Design (BBD) model was used to model the degradation of RB19 by CoO/SPC system, which gives the basis for practical application. The types of reactive oxygen species that effectively degrade RB19 and the potential degradation mechanism of the CoO/SPC system were revealed. At the same time, the CoO/SPC system was evaluated in terms of its practicality. RESULTS In this work, the activation of SPC using CoO towards reactive blue 19 (RB19) degradation was explored. Experimental results showed that nearly 93.8% of RB19 could be removed within 30 min using 1 mmol L −1 SPC and 30 mg L −1 CoO. The three‐factor interaction effects of SPC concentration, CoO dosage and initial pH were investigated. The BBD model was set up to obtain the optimum working conditions of 1.039 mmol L −1 SPC, 33.35 mg L −1 CoO and the initial pH of 7.82, which gave a degradation rate of 95.372%. Additionally, it was confirmed that the solubility of Co 2+ is consistently <150 μg L −1 , meeting the emission standard (1 ppm). The presence of Cl − , NO 3– , and HA had a similar profile, with a slight promoting effect in small amounts and an inhibitory effect when introduced in excess. The introduction of SO 4 2– had a negligible effect on RB19 degradation, whereas the presence of HCO 3 − produced a slight inhibitory effect. Furthermore, the presence of PO 4 3– showed a strong inhibitory effect. The CoO/SPC system is suitable for other organic dyes (32.7%–100%) and antibiotics (97.1–100%). Electron paramagnetic resonance (EPR) analysis and quenching experiments confirmed the presence and relative contribution of free radicals in the CoO/SPC system as CO 3 •‐ (88.12%) >O 2 •‐ (51.11%) >1O 2 (37.21%) >•OH (5.27%) > SPC (3.33%) >CoO (0.09%). It has been confirmed that CoO activates SPC through electron transfer. CONCLUSION The present study describes a less time‐consuming, and more efficient method of treating anthraquinone dye wastewater that requires less oxidizer and catalyst, making it more economical. This proposes a straightforward, cost‐effective and efficient technique using SPC triggered by transition metal oxides. © 2024 Society of Chemical Industry (SCI).
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