PERFORMANCE AND MECHANISM OF CSB-BOC ACTIVATED PMS FOR REMOVAL OF TETRACYCLINE HYDROCHLORIDE IN WATER IN SLOW-GATHERING AREAS OF RIVER
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摘要: 利用浸渍-后热解法制备了Bi2O3-Bi7.90Mo0.10O12.15/Cu7S4生物碳催化剂(CSB-BOC),并采用X射线衍射仪(XRD)、场发射扫描电子显微镜(SEM)、X射线电子能谱仪(XPS)等对其晶格结构、形貌、表面元素及化学形态进行了表征和分析,随后探明其活化过一硫酸盐(PMS)去除新型污染物的催化性能及机理。以典型新型污染物盐酸四环素(TC)作为测试对象,研究了不同催化剂反应体系、PMS浓度、阴离子、腐植酸(HA)和pH对污染物去除的影响,考察了CSB-BOC循环使用的稳定性和异位去除河流缓集区水样中污染物的可行性,评估了TC降解产物的植物毒性。结果表明:CSB-BOC-5-1具有最佳催化性能,当其浓度为0.2 g/L,PMS浓度为0.2 g/L,TC浓度为20 mg/L,初始pH=6.8,温度为23℃,60 min内对TC去除率为95%左右,是生物碳(CSB)+PMS去除率的2.79倍;CSB-BOC-5-1循环使用4次后降解率仅降低了10百分点;自由基猝灭实验和电子自旋共振(ESR)结果表明1O2为降解TC主要活性物种;使用LC-MS鉴定了TC的降解产物并提出了2条可能的降解路径;植物毒性实验和实际水样实验表明CSB-BOC-5-1+PMS降解TC的处理溶液为无毒或低毒性,并且在用于异位去除河流缓集区水中的新型污染物时表现出良好效果。Abstract: Biochar-supported Bi2O3-Bi7.90Mo0.10O12.15/Cu4S7(CSB-BOC) composites were prepared by impregnation-post pyrolysis method and its lattice structure, morphology, surface elements, and chemical morphology were characterized and analyzed by XRD, SEM, XPS and other technologies. Subsequently, the performance and mechanism of CSB-BOC activated peroxymonosulfate(PMS) to remove emerging contaminants were explored. Tetracycline hydrochloride(TC), a typical emerging contaminant, was used as the target pollutant, and the effects of different catalyst reaction systems, PMS concentration, anions, humic acid(HA) and pH on pollutant's removal were studied; the stability of CSB-BOC recycling and the feasibility of removing pollutants in slow-gathering areas of river water were investigated; the phytotoxicity of TC degradation intermediates was evaluated. The results showed that CSB-BOC-5-1 had the best catalytic performance. When the concentration of CSB-BOC-5-1 was 0.2 g/L, the concentration of PMS was 0.2 g/L, the concentration of TC was 20 mg/L, pH=6.8, and the temperature was 23 ℃, the removal rate of TC reached 95% within 60 min at room temperature, 2.79 times that of coconut shell carbon(CSB)+PMS. The degradation efficiency after four degradation cycles only decreased by 10 percentage points. The results of the radical quenching experiment and electron spin resonance(ESR) showed that1O2 was the main active species for TC degradation. The degradation products of TC were identified by LC-MS, and two possible degradation pathways were proposed. The phytotoxicity test and the actual water tests showed that the treatment solution of CSB-BOC+PMS for TC degradation was non-toxic or low toxic, and it showed good effect when being used to remove emerging contaminants in the water samples of slow-gathering areas of a river.
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Key words:
- biochar /
- peroxymonosulfate /
- emerging contaminants /
- impregnation-post pyrolysis /
- slow-gathering areas
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