• 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

紫外/过一硫酸盐工艺降解二氯乙腈:基于响应面法(RSM)的建模与优化

Degradation of dichloroacetonitrile by a UV/peroxymonosulfate process: modeling and optimization based on response surface methodology (RSM).

作者信息

Zhang Xing, Yao Jilun, Peng Wei, Xu Wensi, Li Zhongguo, Zhou Chong, Fang Zhendong

机构信息

Department of Military Facilities, Army Logistics University of PLA Chongqing 401331 China.

Engineering and Technological Research Center of National Disaster Relief Equipment, Army Logistics University of PLA Chongqing 401331 China

出版信息

RSC Adv. 2018 Oct 1;8(59):33681-33687. doi: 10.1039/c8ra07009a. eCollection 2018 Sep 28.

DOI:10.1039/c8ra07009a
PMID:35548810
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC9086566/
Abstract

Response surface methodology (RSM) was utilized to model and optimize the dichloroacetonitrile (DCAN) degradation process by UV/PMS. A quadratic function between DCAN degradation efficiency and three factors including dosage of PMS, UV power and retention time was obtained. The model fitted very well according to high the value of (0.9919) and Adj- (0.9814). Additionally, the analysis of variance showed the influence of factors on degradation efficiency followed: retention time > UV power > dosage of PMS. Finally, the optimum conditions were suggested under this model. The degradation efficiency reached the maximum value of 96.2% with the optimum conditions: dosage of PMS = 0.2 mM, UV power = 7.95 W, retention time = 80 min.

摘要

采用响应面法(RSM)对紫外光/过一硫酸氢钾复合盐(PMS)降解二氯乙腈(DCAN)的过程进行建模和优化。得到了DCAN降解效率与PMS投加量、紫外光功率和停留时间这三个因素之间的二次函数关系。根据较高的决定系数(R² = 0.9919)和调整后的决定系数(Adj-R² = 0.9814),该模型拟合效果良好。此外,方差分析表明各因素对降解效率的影响顺序为:停留时间>紫外光功率>PMS投加量。最后,在此模型下给出了最佳条件。在最佳条件下:PMS投加量 = 0.2 mM,紫外光功率 = 7.95 W,停留时间 = 80 min时,降解效率达到最大值96.2%。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4fd4/9086566/8bc4e5c2c83c/c8ra07009a-f9.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4fd4/9086566/71cf572c585b/c8ra07009a-f1.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4fd4/9086566/da31ac3f69c2/c8ra07009a-f2.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4fd4/9086566/358e564a3494/c8ra07009a-f3.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4fd4/9086566/989131482214/c8ra07009a-f4.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4fd4/9086566/98d901284553/c8ra07009a-f5.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4fd4/9086566/12d5fda4db4a/c8ra07009a-f6.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4fd4/9086566/76cbc6fc118a/c8ra07009a-f7.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4fd4/9086566/83d727a95158/c8ra07009a-f8.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4fd4/9086566/8bc4e5c2c83c/c8ra07009a-f9.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4fd4/9086566/71cf572c585b/c8ra07009a-f1.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4fd4/9086566/da31ac3f69c2/c8ra07009a-f2.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4fd4/9086566/358e564a3494/c8ra07009a-f3.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4fd4/9086566/989131482214/c8ra07009a-f4.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4fd4/9086566/98d901284553/c8ra07009a-f5.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4fd4/9086566/12d5fda4db4a/c8ra07009a-f6.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4fd4/9086566/76cbc6fc118a/c8ra07009a-f7.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4fd4/9086566/83d727a95158/c8ra07009a-f8.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4fd4/9086566/8bc4e5c2c83c/c8ra07009a-f9.jpg

相似文献

1
Degradation of dichloroacetonitrile by a UV/peroxymonosulfate process: modeling and optimization based on response surface methodology (RSM).紫外/过一硫酸盐工艺降解二氯乙腈:基于响应面法(RSM)的建模与优化
RSC Adv. 2018 Oct 1;8(59):33681-33687. doi: 10.1039/c8ra07009a. eCollection 2018 Sep 28.
2
Sono-photo-assisted heterogeneous activation of peroxymonosulfate by Fe/CMK-3 catalyst for the degradation of bisphenol A, optimization with response surface methodology.声-光辅助铁/CMK-3 催化剂活化过一硫酸盐降解双酚 A 的多相反应,采用响应面法进行优化。
Water Environ Res. 2020 Feb;92(2):189-201. doi: 10.1002/wer.1181. Epub 2019 Oct 6.
3
A novel Fe(II)/citrate/UV/peroxymonosulfate process for micropollutant degradation: Optimization by response surface methodology and effects of water matrices.一种用于微污染物降解的新型铁(II)/柠檬酸盐/紫外线/过氧单硫酸盐工艺:响应面法优化及水基质的影响
Chemosphere. 2017 Oct;184:417-428. doi: 10.1016/j.chemosphere.2017.06.004. Epub 2017 Jun 4.
4
Degradation of oxytetracycline in aqueous solution by heat-activated peroxydisulfate and peroxymonosulfate oxidation.热活化过二硫酸盐和过一硫酸盐氧化法降解水溶液中的土霉素
Environ Sci Pollut Res Int. 2022 Feb;29(6):9110-9123. doi: 10.1007/s11356-021-16157-7. Epub 2021 Sep 8.
5
CoFe-LDO nanoparticles as a novel catalyst of peroxymonosulfate (PMS) for histidine removal.CoFe-LDO 纳米粒子作为过一硫酸盐(PMS)的新型催化剂用于组氨酸去除。
Environ Sci Pollut Res Int. 2022 Mar;29(11):16517-16528. doi: 10.1007/s11356-021-16853-4. Epub 2021 Oct 14.
6
UV/ peroxymonosulfate process for degradation of chloral hydrate: Pathway and the role of radicals.UV/过一硫酸盐工艺降解水合氯醛:途径和自由基的作用。
J Hazard Mater. 2021 Jan 5;401:123837. doi: 10.1016/j.jhazmat.2020.123837. Epub 2020 Sep 2.
7
Synergistic mechanism and degradation kinetics for atenolol elimination via integrated UV/ozone/peroxymonosulfate process.通过集成 UV/臭氧/过一硫酸盐工艺去除阿替洛尔的协同机制和降解动力学。
J Hazard Mater. 2021 Apr 5;407:124393. doi: 10.1016/j.jhazmat.2020.124393. Epub 2020 Nov 2.
8
Kinetics and reaction mechanism of photochemical degradation of diclofenac by UV-activated peroxymonosulfate.紫外光活化过一硫酸盐光化学降解双氯芬酸的动力学及反应机理
RSC Adv. 2021 Feb 10;11(12):6804-6817. doi: 10.1039/d0ra10178h. eCollection 2021 Feb 4.
9
Degradation of bisphenol A by persulfate coupled with dithionite: Optimization using response surface methodology and pathway.过硫酸盐耦合连二亚硫酸钠降解双酚 A:响应面法优化及途径。
Sci Total Environ. 2020 Jan 10;699:134258. doi: 10.1016/j.scitotenv.2019.134258. Epub 2019 Sep 2.
10
Photo-assisted catalytic degradation of acetaminophen using peroxymonosulfate decomposed by magnetic carbon heterojunction catalyst.采用磁性碳异质结催化剂分解过一硫酸盐实现对扑热息痛的光辅助催化降解。
Chemosphere. 2019 Oct;232:140-151. doi: 10.1016/j.chemosphere.2019.05.070. Epub 2019 May 16.

引用本文的文献

1
Activating peroxymonosulfate by halogenated and methylated quinones: performance and mechanism.卤代醌和甲基化醌活化过一硫酸盐:性能与机制
RSC Adv. 2019 Aug 30;9(47):27224-27230. doi: 10.1039/c9ra04789a. eCollection 2019 Aug 29.

本文引用的文献

1
Formation and estimated toxicity of trihalomethanes, haloacetonitriles, and haloacetamides from the chlor(am)ination of acetaminophen.对乙酰氨基酚的氯化(氨化)生成三卤甲烷、卤乙腈和卤乙酰胺及其估算毒性。
J Hazard Mater. 2018 Jan 5;341:112-119. doi: 10.1016/j.jhazmat.2017.07.049. Epub 2017 Jul 25.
2
Photodegradation of haloacetonitriles in water by vacuum ultraviolet irradiation: Mechanisms and intermediate formation.真空紫外光辐照下水相中卤乙腈的光降解:机理与中间产物形成。
Water Res. 2016 Jul 1;98:160-7. doi: 10.1016/j.watres.2016.04.010. Epub 2016 Apr 11.
3
Seasonal variation in drinking water concentrations of disinfection by-products in IZMIR and associated human health risks.
伊兹密尔饮用水中消毒副产物的季节性变化及相关的人类健康风险。
Sci Total Environ. 2008 Dec 15;407(1):286-96. doi: 10.1016/j.scitotenv.2008.08.019. Epub 2008 Sep 20.
4
Haloacetonitriles vs. regulated haloacetic acids: are nitrogen-containing DBPs more toxic?卤代乙腈与受管制的卤乙酸:含氮消毒副产物毒性更强吗?
Environ Sci Technol. 2007 Jan 15;41(2):645-51. doi: 10.1021/es0617441.
5
Occurrence of a new generation of disinfection byproducts.新一代消毒副产物的出现。
Environ Sci Technol. 2006 Dec 1;40(23):7175-85. doi: 10.1021/es060353j.