• 文献检索
  • 文档翻译
  • 深度研究
  • 学术资讯
  • Suppr Zotero 插件Zotero 插件
  • 邀请有礼
  • 套餐&价格
  • 历史记录
应用&插件
Suppr Zotero 插件Zotero 插件浏览器插件Mac 客户端Windows 客户端微信小程序
定价
高级版会员购买积分包购买API积分包
服务
文献检索文档翻译深度研究API 文档MCP 服务
关于我们
关于 Suppr公司介绍联系我们用户协议隐私条款
关注我们

Suppr 超能文献

核心技术专利:CN118964589B侵权必究
粤ICP备2023148730 号-1Suppr @ 2026

文献检索

告别复杂PubMed语法,用中文像聊天一样搜索,搜遍4000万医学文献。AI智能推荐,让科研检索更轻松。

立即免费搜索

文件翻译

保留排版,准确专业,支持PDF/Word/PPT等文件格式,支持 12+语言互译。

免费翻译文档

深度研究

AI帮你快速写综述,25分钟生成高质量综述,智能提取关键信息,辅助科研写作。

立即免费体验

利用 MgO 纳米粒子的吸附和光降解过程对甲硝唑残留进行处理的区分。

Differentiation Between Metronidazole Residues Disposal by Using Adsorption and Photodegradation Processes Onto MgO Nanoparticles.

机构信息

Central Laboratory for Environmental Quality Monitoring (CLEQM), National Water Research Center (NWRC), El Qanater El Khayria, Egypt.

出版信息

Int J Nanomedicine. 2020 Sep 28;15:7117-7141. doi: 10.2147/IJN.S265739. eCollection 2020.

DOI:10.2147/IJN.S265739
PMID:33061371
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC7533914/
Abstract

BACKGROUND

Metronidazole (MNZ) is an antibiotic form that is considered as a dangerous environmental pollutant due to its widespread use as growth promoters in livestock and aquaculture operations along with its therapeutic application for humans.

PURPOSE

The objective of this work was to conduct a comparative study between the efficiency of the adsorption and photocatalytic degradation of MNZ in an aqueous solution by using magnesium oxide nanoparticles (MgO NP) under different effects, as well as evaluate the performance, reusability and cost study.

MATERIALS AND METHODS

Several instruments such as XRD, EDX, SEM, and TEM were used to characterize the chemical composition and morphological properties of the synthesized MgO NP, while the GC-MS analysis was used to monitor the degradation pathway of MNZ particles within 180 min. The simple photo-batch reactor was used to investigate the degradation of MNZ under the effect of UV radiation, initial concentration of MNZ, pH, catalyst loading, inorganic salts addition, time, and temperature.

RESULTS

The degradation efficiency is mainly divided into two steps: 35.7% for maximum adsorption and 57.5% for photodegradation. Adsorption isotherm models confirmed that the process nature is chemisorption and appropriate Langmuir model, as well as to be a nonspontaneous and endothermic reaction according to the thermodynamic study. Adsorption constant during dark condition is smaller than typical adsorption equilibrium constant derived from the Langmuir-Hinshelwood kinetic model through photodegradation of MNZ that follows pseudo-first-order kinetics. Toxicity rates were reduced considerably after the photodegradation process to 88.21%, 79.84%, and 67.32% and 57.45%, 51.98%, and 43.87% by heamolytic and brine shrimp assays, respectively, for initial MNZ concentrations (20, 60, and 100 mg/L).

CONCLUSION

We significantly recommend using MgO NP as a promising catalyst in the photodegradation applications for other organic pollutants in visible light.

摘要

背景

甲硝唑(MNZ)是一种抗生素形式,由于其在畜牧业和水产养殖中的广泛用作生长促进剂以及在人类中的治疗应用,被认为是一种危险的环境污染物。

目的

本工作的目的是在不同影响下,通过使用氧化镁纳米粒子(MgO NP)比较研究在水溶液中 MNZ 的吸附和光催化降解的效率,并评估其性能、可重复使用性和成本研究。

材料和方法

使用 XRD、EDX、SEM 和 TEM 等多种仪器对合成的 MgO NP 的化学组成和形态特性进行了表征,而 GC-MS 分析则用于监测 180 分钟内 MNZ 颗粒的降解途径。简单的光批式反应器用于研究在 UV 辐射、MNZ 的初始浓度、pH 值、催化剂负载、无机盐添加、时间和温度的影响下 MNZ 的降解。

结果

降解效率主要分为两个步骤:最大吸附率为 35.7%,光降解率为 57.5%。吸附等温线模型证实,该过程的性质为化学吸附,适宜的 Langmuir 模型,以及根据热力学研究,是一个非自发和吸热反应。在黑暗条件下的吸附常数小于从 MNZ 光降解的 Langmuir-Hinshelwood 动力学模型推导出来的典型吸附平衡常数,该模型遵循准一级动力学。光降解后,毒性率大大降低,对于初始 MNZ 浓度(20、60 和 100mg/L),溶血和盐水虾试验的毒性率分别降低到 88.21%、79.84%和 67.32%和 57.45%、51.98%和 43.87%。

结论

我们强烈推荐使用 MgO NP 作为一种有前途的催化剂,用于可见光下其他有机污染物的光降解应用。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5e8d/7533914/b5fd70dd5b7a/IJN-15-7117-g0014.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5e8d/7533914/b62cf8d3ab9e/IJN-15-7117-g0001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5e8d/7533914/5734c7ee579b/IJN-15-7117-g0002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5e8d/7533914/1596e13484e6/IJN-15-7117-g0003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5e8d/7533914/508e9e62ce9e/IJN-15-7117-g0004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5e8d/7533914/fbc66aa6ec82/IJN-15-7117-g0005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5e8d/7533914/7f0497f042e0/IJN-15-7117-g0006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5e8d/7533914/79092b6ccdec/IJN-15-7117-g0007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5e8d/7533914/b882e27601a2/IJN-15-7117-g0008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5e8d/7533914/2f80fdb65d85/IJN-15-7117-g0009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5e8d/7533914/9788b067e6b4/IJN-15-7117-g0010.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5e8d/7533914/bba0e2376669/IJN-15-7117-g0011.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5e8d/7533914/065c72f13bcb/IJN-15-7117-g0012.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5e8d/7533914/d00551f5e4ab/IJN-15-7117-g0013.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5e8d/7533914/b5fd70dd5b7a/IJN-15-7117-g0014.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5e8d/7533914/b62cf8d3ab9e/IJN-15-7117-g0001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5e8d/7533914/5734c7ee579b/IJN-15-7117-g0002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5e8d/7533914/1596e13484e6/IJN-15-7117-g0003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5e8d/7533914/508e9e62ce9e/IJN-15-7117-g0004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5e8d/7533914/fbc66aa6ec82/IJN-15-7117-g0005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5e8d/7533914/7f0497f042e0/IJN-15-7117-g0006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5e8d/7533914/79092b6ccdec/IJN-15-7117-g0007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5e8d/7533914/b882e27601a2/IJN-15-7117-g0008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5e8d/7533914/2f80fdb65d85/IJN-15-7117-g0009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5e8d/7533914/9788b067e6b4/IJN-15-7117-g0010.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5e8d/7533914/bba0e2376669/IJN-15-7117-g0011.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5e8d/7533914/065c72f13bcb/IJN-15-7117-g0012.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5e8d/7533914/d00551f5e4ab/IJN-15-7117-g0013.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5e8d/7533914/b5fd70dd5b7a/IJN-15-7117-g0014.jpg

相似文献

1
Differentiation Between Metronidazole Residues Disposal by Using Adsorption and Photodegradation Processes Onto MgO Nanoparticles.利用 MgO 纳米粒子的吸附和光降解过程对甲硝唑残留进行处理的区分。
Int J Nanomedicine. 2020 Sep 28;15:7117-7141. doi: 10.2147/IJN.S265739. eCollection 2020.
2
Enhancement of the adsorption capacity of the light-weight expanded clay aggregate surface for the metronidazole antibiotic by coating with MgO nanoparticles: Studies on the kinetic, isotherm, and effects of environmental parameters.通过用 MgO 纳米粒子涂覆来增强轻质膨胀粘土骨料表面对甲硝唑抗生素的吸附能力:动力学、等温线和环境参数影响的研究。
Chemosphere. 2017 May;175:8-20. doi: 10.1016/j.chemosphere.2017.02.043. Epub 2017 Feb 9.
3
Photocatalytic degradation of metronidazole and oxytetracycline by novel l-Arginine (C, N codoped)-TiO/g-CN: RSM optimization, photodegradation mechanism, biodegradability evaluation.新型 L-精氨酸(C,N 共掺杂)-TiO/g-CN 光催化降解甲硝唑和土霉素:响应面法优化、光降解机制、可生物降解性评价。
Chemosphere. 2023 Oct;337:139282. doi: 10.1016/j.chemosphere.2023.139282. Epub 2023 Jun 20.
4
Metronidazole removal in powder-activated carbon and concrete-containing graphene adsorption systems: Estimation of kinetic, equilibrium and thermodynamic parameters and optimization of adsorption by a central composite design.粉末活性炭和含石墨烯混凝土吸附体系中甲硝唑的去除:动力学、平衡和热力学参数的估算以及通过中心复合设计对吸附进行优化
J Environ Sci Health A Tox Hazard Subst Environ Eng. 2017 Dec 6;52(14):1269-1283. doi: 10.1080/10934529.2017.1357406. Epub 2017 Sep 18.
5
Green synthesis of Ag nanoparticles from Argemone mexicana L. leaf extract coated with MOF-5 for the removal of metronidazole antibiotics from aqueous solution.从 Argemone mexicana L. 叶中提取的 Ag 纳米粒子的绿色合成,用 MOF-5 进行涂层,用于从水溶液中去除甲硝唑抗生素。
J Environ Manage. 2023 Sep 15;342:118161. doi: 10.1016/j.jenvman.2023.118161. Epub 2023 May 19.
6
Enhanced activation of persulfate by CuCoFe2O4@MC/AC as a novel nanomagnetic heterogeneous catalyst with ultrasonic for metronidazole degradation.CuCoFe2O4@MC/AC 作为一种新型纳米磁性多相催化剂,通过超声增强过硫酸盐对甲硝唑的降解。
Chemosphere. 2022 Jan;286(Pt 3):131872. doi: 10.1016/j.chemosphere.2021.131872. Epub 2021 Aug 12.
7
Microwave-assisted preparation of ZnFeO@methyl cellulose as a new nano-biomagnetic photocatalyst for photodegradation of metronidazole.微波辅助制备 ZnFeO@甲基纤维素作为一种新型的纳米生物磁性光催化剂用于甲硝唑的光降解。
Int J Biol Macromol. 2020 Jul 1;154:1036-1049. doi: 10.1016/j.ijbiomac.2020.03.069. Epub 2020 Apr 4.
8
Electrochemical synthesis, photodegradation and antibacterial properties of PEG capped zinc oxide nanoparticles.PEG 封端的氧化锌纳米粒子的电化学合成、光降解和抗菌性能。
J Photochem Photobiol B. 2018 Oct;187:25-34. doi: 10.1016/j.jphotobiol.2018.07.022. Epub 2018 Aug 2.
9
Oxidative removal of metronidazole from aqueous solution by thermally activated persulfate process: kinetics and mechanisms.热激活过硫酸盐工艺氧化去除水溶液中的甲硝唑:动力学和机制。
Environ Sci Pollut Res Int. 2018 Jan;25(3):2466-2475. doi: 10.1007/s11356-017-0518-9. Epub 2017 Nov 10.
10
On the adsorption/photodegradation of amoxicillin in aqueous solutions by an integrated photocatalytic adsorbent (IPCA): experimental studies and kinetics analysis.在水溶液中通过集成光催化吸附剂(IPCA)对阿莫西林的吸附/光降解作用:实验研究与动力学分析。
Photochem Photobiol Sci. 2011 Jun;10(6):1014-22. doi: 10.1039/c0pp00368a. Epub 2011 Mar 7.

本文引用的文献

1
Antimicrobial pharmaceuticals in the aquatic environment - occurrence and environmental implications.水环境中的抗菌药物 - 存在及其环境影响。
Eur J Pharmacol. 2020 Jan 5;866:172813. doi: 10.1016/j.ejphar.2019.172813. Epub 2019 Nov 18.
2
Environmental Remediation Applications of Carbon Nanotubes and Graphene Oxide: Adsorption and Catalysis.碳纳米管和氧化石墨烯在环境修复中的应用:吸附与催化
Nanomaterials (Basel). 2019 Mar 15;9(3):439. doi: 10.3390/nano9030439.
3
The Side Effects of the Most Commonly Used Group of Antibiotics in Periodontal Treatments.
牙周治疗中最常用抗生素组的副作用。
Med Sci (Basel). 2018 Jan 18;6(1):6. doi: 10.3390/medsci6010006.
4
Fabrication of MgO nanostructures and its efficient photocatalytic, antibacterial and anticancer performance.MgO 纳米结构的制备及其高效的光催化、抗菌和抗癌性能。
J Photochem Photobiol B. 2019 Jan;190:8-20. doi: 10.1016/j.jphotobiol.2018.11.001. Epub 2018 Nov 12.
5
Antibiotic Use in Agriculture and Its Consequential Resistance in Environmental Sources: Potential Public Health Implications.农业中的抗生素使用及其在环境源中的抗药性后果:对公共卫生的潜在影响。
Molecules. 2018 Mar 30;23(4):795. doi: 10.3390/molecules23040795.
6
Presence of antibiotic residues in various environmental compartments of Shandong province in eastern China: Its potential for resistance development and ecological and human risk.中国东部山东省不同环境介质中抗生素残留的存在:其产生耐药性的潜力及生态和人类风险。
Environ Int. 2018 May;114:131-142. doi: 10.1016/j.envint.2018.02.003. Epub 2018 Mar 2.
7
Designer carbon nanotubes for contaminant removal in water and wastewater: A critical review.用于水和废水中污染物去除的设计碳纳米管:批判性评价。
Sci Total Environ. 2018 Jan 15;612:561-581. doi: 10.1016/j.scitotenv.2017.08.132. Epub 2017 Sep 1.
8
Atrazine degradation through PEI-copper nanoparticles deposited onto montmorillonite and sand.通过将聚醚酰亚胺-铜纳米颗粒沉积在蒙脱石和沙子上来降解莠去津。
Sci Rep. 2017 May 3;7(1):1415. doi: 10.1038/s41598-017-01429-5.
9
Supporting of coupled silver halides onto clinoptilolite nanoparticles as simple method for increasing their photocatalytic activity in heterogeneous photodegradation of mixture of 4-methoxy aniline and 4-chloro-3-nitro aniline.将卤化银耦合负载到斜发沸石纳米颗粒上作为提高其在4-甲氧基苯胺和4-氯-3-硝基苯胺混合物的多相光降解中光催化活性的简便方法。
J Colloid Interface Sci. 2017 Mar 15;490:478-487. doi: 10.1016/j.jcis.2016.11.087. Epub 2016 Nov 29.
10
Synergistic effect of p-n heterojunction, supporting and zeolite nanoparticles in enhanced photocatalytic activity of NiO and SnO.p-n异质结、载体与沸石纳米颗粒对增强NiO和SnO光催化活性的协同作用。
J Colloid Interface Sci. 2017 Mar 15;490:314-327. doi: 10.1016/j.jcis.2016.11.069. Epub 2016 Nov 21.