氮掺杂纳米洋葱碳/PMS体系去除水中抗生素与抗性菌研究
PDF下载 (155)胡 莹,蒋晓孟,高豆豆,俞梦飞,沈柯妙,甘慧慧.氮掺杂纳米洋葱碳/PMS体系去除水中抗生素与抗性菌研究[J].宁波大学学报(理工版),2024,37(3):80-87.DOI:10.20098/j.cnki.1001-5132.2024.0203
HU Ying,JIANG Xiaomeng,GAO Doudou,YU Mengfei,SHEN Kemiao,GAN Huihui.
Elimination of complex pollutants of antibiotics and antibiotic-resistant bacteria in water using magnetic nano onion carbon/PMS systems
| Title: | Elimination of complex pollutants of antibiotics and antibiotic-resistant bacteria in water using magnetic nano onion carbon/PMS systems
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| 作者: | 胡 莹, 蒋晓孟, 高豆豆, 俞梦飞, 沈柯妙, 甘慧慧 |
| Author(s): | HU Ying, JIANG Xiaomeng, GAO Doudou, YU Mengfei, SHEN Kemiao, GAN Huihui |
| 关键词: | 磁性碳结构; 抗生素; 抗性菌; 过一硫酸盐 |
| Keywords: | magnetic carbon structure; antibiotics; resistant bacteria; peroxymonosulfate |
| 分类号: | X705 |
| DOI: | 10.20098/j.cnki.1001-5132.2024.0203 |
| 文献标识码: | A |
| 摘要: | 水环境中抗生素持续和长期残留将对细菌产生选择性压力, 诱导产生抗性菌和抗生素抗性基因, 对水体生态系统和人类健康带来威胁. 本文采用具有磁性功能的氮掺杂纳米洋葱碳耦合过一硫酸盐氧化体系(NCNO/PMS), 用于处理水中抗生素磺胺甲恶唑(SMX)和带有磺胺类抗生素抗性菌(ARB). 通过X射线衍射(XRD)、透射电子显微镜(TEM)、磁滞回线等表征NCNO的表面结构和功能, 考察不同环境条件下NCNO/PMS对水中SMX降解和ARB灭活效率的作用. 实验结果表明, NCNO可以有效提升PMS对水中SMX降解的效率, 同时NCNO/PMS对病原菌具有极强的灭活能力. |
| Abstract: | The continuous and long-term residues of antibiotics in the aquatic environment are suggested to exert selective pressure on bacteria, induce the generation of resistant bacteria and antibiotic resistance genes, and bring threats to aquatic ecosystems and human health. In the present study, a magnetic nitrogen-doped nano- onion carbon coupled PMS oxidation system (NCNO/PMS) was used to treat the antibiotic sulfamethoxazole (SMX) and pathogens with sulfonamides resistance genes (ARB) in water at the same time. The surface structure and function of NCNO were analyzed by XRD, TEM and hysteresis loop characterization. The degradation efficiency of SMX in water and the inactivation efficiency of ARG by NCNO/PMS were investigated under different environmental conditions. The experimental results showed that NCNO could effectively improve the degradation efficiency of SMX in water by PMS. In addition, NCNO/PMS had excellent inactivation ability to pathogenic bacteria. This study provides a new idea and theoretical reference for the application and development of peroxymonosulfate oxidation technology for the removal of new biological risk pollutants. |
| 参考文献 /References: | [1] CHEN Z M, XIAO X, XING B S, et al. pH-dependent sorption of sulfonamide antibiotics onto biochars: sorption mechanisms and modeling[J]. Environmental Pollution, 2019, 248:48-56.
[2] PENG J, WU E H, WANG N N, et al. Removal of sulfonamide antibiotics from water by adsorption and persulfate oxidation process[J]. Journal of Molecular Liquids, 2019, 274:632-638.
[3] CLARA M, STRENN B, KREUZINGER N. Carbamazepine as a possible anthropogenic marker in the aquatic environment: investigations on the behaviour of carbamazepine in wastewater treatment and during groundwater infiltration[J]. Water Research, 2004, 38(4): 947-954.
[4] PALLARES-VEGA R, BLAAK H, VAN DER PLAATS R, et al. Determinants of presence and removal of antibiotic resistance genes during WWTP treatment: a cross-sectional study[J]. Water Research, 2019, 161:319- 328.
[5] MOMPELAT S, LE BOT B, THOMAS O. Occurrence and fate of pharmaceutical products and by-products, from resource to drinking water[J]. Environment International, 2009, 35(5):803-814.
[6] PETROVIC M. Analysis and removal of emerging contaminants in wastewater and drinking water[J]. TrAC Trends in Analytical Chemistry, 2003, 22(10):685-696.
[7] YANG Y, OK Y S, KIM K H, et al. Occurrences and removal of pharmaceuticals and personal care products (PPCPs) in drinking water and water/sewage treatment plants: a review[J]. The Science of the Total Environment, 2017, 596/597:303-320.
[8] STACKELBERG P E, FURLONG E T, MEYER M T, et al. Persistence of pharmaceutical compounds and other organic wastewater contaminants in a conventional drinking-water-treatment plant[J]. The Science of the Total Environment, 2004, 329(1/2/3):99-113.
[9] KUMAR M, RAM B, SEWWANDI H, et al. Treatment enhances the prevalence of antibiotic-resistant bacteria and antibiotic resistance genes in the wastewater of
Sri Lanka, and India[J]. Environmental Research, 2020, 183:109179.
[10] HAN X, ZHOU C L, CHEN Y J, et al. Preparation of Yb-Sb co-doped Ti/SnO2 electrode for electrocatalytic degradation of sulfamethoxazole (SMX)[J]. Chemosphere, 2023, 339:139633.
[11] SONG Y L, LI Z Y, LI S B, et al. Enhancing the photocatalytic efficiency of sulfamethoxazole by regulating the band gap structure of g-C3N4 through phosphorus element doping[J]. Journal of Water Process Engineering, 2024, 58:104936.
[12] 章强, 辛琦, 朱静敏, 等. 中国主要水域抗生素污染现状及其生态环境效应研究进展[J]. 环境化学, 2014, 33(7):1075-1083.
[13] ZHANG Z Y, ZHANG Q, WANG T Z, et al. Assessment of global health risk of antibiotic resistance genes[J]. Nature Communications, 2022, 13(1):1553.
[14] AL-JASSIM N, ANSARI M I, HARB M, et al. Removal of bacterial contaminants and antibiotic resistance genes by conventional wastewater treatment processes in Saudi Arabia: is the treated wastewater safe to reuse for agricultural irrigation?[J]. Water Research, 2015, 73:277- 290.
[15] ZHUANG Y, REN H Q, GENG J J, et al. Inactivation of antibiotic resistance genes in municipal wastewater by chlorination, ultraviolet, and ozonation disinfection[J]. Environmental Science and Pollution Research International, 2015, 22(9):7037-7044.
[16] CHENG C F, LIN H H H, TUNG H H, et al. Enhanced solar photodegradation of a plasmid-encoded extracellular antibiotic resistance gene in the presence of free chlorine [J]. Journal of Environmental Chemical Engineering, 2022, 10(1):106984.
[17] ZHAO M J, ZHOU X Q, LI Z F, et al. The dynamics and removal efficiency of antibiotic resistance genes by UV- LED treatment: an integrated research on single- or dual- wavelength irradiation[J]. Ecotoxicology and Enviro- nmental Safety, 2023, 263:115212.
[18] YAO S J, HU Y R, YE J F, et al. Disinfection and mechanism of super-resistant Acinetobacter sp. and the plasmid-encoded antibiotic resistance gene blaNDM-1 by UV/peroxymonosulfate[J]. Chemical Engineering Journal, 2022, 433:133565.
[19] HU Y R, ZHANG T Y, JIANG L, et al. Removal of sulfonamide antibiotic resistant bacterial and intracellular antibiotic resistance genes by UVC-activated peroxymonosulfate[J]. Chemical Engineering Journal, 2019, 368:888-895.
[20] CHU L B, CHEN D, WANG J L, et al. Degradation of antibiotics and inactivation of antibiotic resistance genes (ARGs) in cephalosporin C fermentation residues using ionizing radiation, ozonation and thermal treatment[J]. Journal of Hazardous Materials, 2020, 382:121058.
[21] ÖSTMAN M, BJÖRLENIUS B, FICK J, et al. Effect of full-scale ozonation and pilot-scale granular activated carbon on the removal of biocides, antimycotics and antibiotics in a sewage treatment plant[J]. The Science of the Total Environment, 2019, 649:1117-1123.
[22] DING D H, YANG S J, CHEN L W, et al. Degradation of norfloxacin by CoFe alloy nanoparticles encapsulated in nitrogen doped graphitic carbon (CoFe@N-GC) activated peroxymonosulfate[J]. Chemical Engineering Journal, 2020, 392:123725.
[23] CHEN F, HUANG G X, YAO F B, et al. Catalytic degradation of ciprofloxacin by a visible-light-assisted peroxymonosulfate activation system: performance and mechanism[J]. Water Research, 2020, 173:115559.
[24] JIN C Y, WANG M, LI Z L, et al. Two dimensional Co3O4/g-C3N4 Z-scheme heterojunction: mechanism insight into enhanced peroxymonosulfate-mediated visible light photocatalytic performance[J]. Chemical Engineering Journal, 2020, 398:125569.
[25] JIANG Q J, GAN H H, HUANG Y, et al. Peroxymonosulfate activation on carbon nano-onions modified graphitic carbon nitride via light-tuning radical and nonradical pathways[J]. Journal of Environmental Chemical Engineering, 2021, 9(6):106592.
[26] MYKHAILIV O, ZUBYK H, PLONSKA-BRZEZINSKA M E. Carbon nano-onions: unique carbon nanostructures with fascinating properties and their potential applications [J]. Inorganica Chimica Acta, 2017, 468:49-66.
[27] YUN E T, PARK S W, SHIN H J, et al. Peroxymonosulfate activation by carbon-encapsulated metal nanoparticles: switching the primary reaction route and increasing chemical stability[J]. Applied Catalysis B: Environmental, 2020, 279:119360.
[28] HAN L J, ZHANG P, LI L, et al. Nitrogen-containing carbon nano-onions-like and graphene-like materials derived from biomass and the adsorption and visible photocatalytic performance[J]. Applied Surface Science, 2021, 543:148752.
[29] ZHANG H, JIA L H, WU P, et al. Improved H2O2 photogeneration by KOH-doped g-C3N4 under visible light irradiation due to synergistic effect of N defects and K modification[J]. Applied Surface Science, 2020, 527: 146584.
[30] CAO S H, FAN B, FENG Y C, et al. Sulfur-doped g-C3N4 nanosheets with carbon vacancies: general synthesis and improved activity for simulated solar-light photocatalytic nitrogen fixation[J]. Chemical Engineering Journal, 2018, 353:147-156.
[31] BOUHOUCH L, FADEL M, HILALI E. Magnetic properties of the electrolytic super alloys Ni-Fe[J]. Physica Status Solidi C, 2006, 3(9):3253-3256.
[32] 邓钏, 张卫珂, 杨艳青, 等. 磁性纳米洋葱碳基复合材料的制备及其吸波性能[J]. 新型炭材料, 2019, 34(2): 170-180.
[33] GOCLON J, BANKIEWICZ B, KOLEK P, et al. Role of nitrogen doping in stoichiometric and defective carbon nano-onions: structural diversity from DFT calculations [J]. Carbon, 2021, 176:198-208.
[34] YANG P Z, JI Y F, LU J H, et al. Formation of nitrophenolic byproducts during heat-activated peroxydisulfate oxidation in the presence of natural organic matter and nitrite[J]. Environmental Science & Technology, 2019, 53(8):4255-4264. |
| 备注/Memo: | 收稿日期: 2024−02−12. 宁波大学学报（理工版）网址: http://journallg.nbu.edu.cn/ 基金项目: 宁波市水利科技计划重点项目（NSKA202210）; 浙江省自然科学基金（LY21E090004）; 国家自然科学基金（52070103）. 第一作者: 胡莹, 硕士研究生, 主要研究方向: 新型污染物控制. E-mail: hy18296628309@163.com *通信作者: 甘慧慧, 博士/副教授, 主要研究方向: 环境功能材料与新污染物控制技术. E-mail: ganhuihui@nbu.edu.cn 宁波大学学报（理工版）网址：http://journallg.nbu.edu.cn/ |
