• 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

采用高级氧化与吸附混合工艺处理制药工业废水

Treatment of a Pharmaceutical Industrial Effluent by a Hybrid Process of Advanced Oxidation and Adsorption.

作者信息

Patel Surabhi, Mondal Somen, Majumder Subrata Kumar, Das Papita, Ghosh Pallab

机构信息

Department of Chemical Engineering, Indian Institute of Technology Guwahati, Guwahati 781039, Assam, India.

Department of Chemical Engineering, Jadavpur University, Kolkata 700032, West Bengal, India.

出版信息

ACS Omega. 2020 Dec 10;5(50):32305-32317. doi: 10.1021/acsomega.0c04139. eCollection 2020 Dec 22.

DOI:10.1021/acsomega.0c04139
PMID:33376867
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC7758896/
Abstract

In the present study, a combined approach of ozone-based advanced oxidation and adsorption by activated char was employed for the treatment of a pharmaceutical industrial effluent. Ozone is a selective oxidant, but the addition of HO generated hydroxyl radicals, which is a non-selective stronger oxidant than ozone. The effluent obtained from the pharmaceutical industry mainly contained anti-cancer drugs, anti-psychotic drugs, and some pain killers. The peroxone process had 75-88.5% chemical oxygen demand (COD) reduction efficiency at pH 5-11 in 3 h. Adsorption by activated char further reduced the COD to 85.4-92.7% for pH 5-11 in 2.5 h. All other water quality parameters were significantly decreased (>73% removal) during ozonation. The primary operational parameters (system pH and HO concentration) were also varied, and their effects were analyzed. The pseudo-first-order rate constants for ozonation were calculated, and they were found to be in the range of 1.42 × 10 to 3.35 × 10 s for pH 5-11. The kinetic parameters for adsorption were calculated for the pseudo-first-order, pseudo-second-order, and Elovich models. The fit of the pseudo-first-order kinetic model to the experimental data was the best.

摘要

在本研究中,采用基于臭氧的高级氧化与活性炭吸附相结合的方法来处理制药工业废水。臭氧是一种选择性氧化剂,但羟基自由基(HO)的生成产生了比臭氧更强的非选择性氧化剂。制药工业产生的废水主要含有抗癌药物、抗精神病药物和一些止痛剂。在pH值为5 - 11的条件下,过氧臭氧工艺在3小时内的化学需氧量(COD)降低效率为75 - 88.5%。在pH值为5 - 11的条件下,活性炭吸附在2.5小时内进一步将COD降低至85.4 - 92.7%。在臭氧化过程中,所有其他水质参数均显著降低(去除率>73%)。还改变了主要操作参数(系统pH值和HO浓度),并分析了它们的影响。计算了臭氧化的伪一级速率常数,发现在pH值为5 - 11时,其范围为1.42×10至3.35×10 s。针对伪一级、伪二级和埃洛维奇模型计算了吸附的动力学参数。伪一级动力学模型对实验数据的拟合效果最佳。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7d44/7758896/2446f14621c0/ao0c04139_0014.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7d44/7758896/c4d1891fef69/ao0c04139_0002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7d44/7758896/f6d2f4efc5ad/ao0c04139_0003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7d44/7758896/91d324f29e25/ao0c04139_0004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7d44/7758896/23cf0851e8b5/ao0c04139_0005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7d44/7758896/f9a6cb343ca6/ao0c04139_0006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7d44/7758896/8d44e8f5d9b8/ao0c04139_0007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7d44/7758896/8c56eba4ae16/ao0c04139_0008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7d44/7758896/1cf3aae50a12/ao0c04139_0009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7d44/7758896/cb301552de1f/ao0c04139_0010.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7d44/7758896/08d4db7b9aaf/ao0c04139_0011.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7d44/7758896/62baa5a13aa8/ao0c04139_0012.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7d44/7758896/6a798b7c992a/ao0c04139_0013.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7d44/7758896/2446f14621c0/ao0c04139_0014.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7d44/7758896/c4d1891fef69/ao0c04139_0002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7d44/7758896/f6d2f4efc5ad/ao0c04139_0003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7d44/7758896/91d324f29e25/ao0c04139_0004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7d44/7758896/23cf0851e8b5/ao0c04139_0005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7d44/7758896/f9a6cb343ca6/ao0c04139_0006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7d44/7758896/8d44e8f5d9b8/ao0c04139_0007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7d44/7758896/8c56eba4ae16/ao0c04139_0008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7d44/7758896/1cf3aae50a12/ao0c04139_0009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7d44/7758896/cb301552de1f/ao0c04139_0010.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7d44/7758896/08d4db7b9aaf/ao0c04139_0011.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7d44/7758896/62baa5a13aa8/ao0c04139_0012.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7d44/7758896/6a798b7c992a/ao0c04139_0013.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7d44/7758896/2446f14621c0/ao0c04139_0014.jpg

相似文献

1
Treatment of a Pharmaceutical Industrial Effluent by a Hybrid Process of Advanced Oxidation and Adsorption.采用高级氧化与吸附混合工艺处理制药工业废水
ACS Omega. 2020 Dec 10;5(50):32305-32317. doi: 10.1021/acsomega.0c04139. eCollection 2020 Dec 22.
2
Effect of operational and water quality parameters on conventional ozonation and the advanced oxidation process O/HO: Kinetics of micropollutant abatement, transformation product and bromate formation in a surface water.操作和水质参数对常规臭氧氧化和高级氧化工艺 O/HO 的影响:地表水中微污染物去除、转化产物和溴酸盐形成的动力学。
Water Res. 2017 Oct 1;122:234-245. doi: 10.1016/j.watres.2017.05.018. Epub 2017 May 11.
3
Combined chemical and biological oxidation of penicillin formulation effluent.青霉素制剂废水的化学与生物联合氧化
J Environ Manage. 2004 Nov;73(2):155-63. doi: 10.1016/j.jenvman.2004.06.007.
4
Optimization of the Electro-Peroxone Process for Micropollutant Abatement Using Chemical Kinetic Approaches.采用化学动力学方法优化电过硫酸盐工艺去除水中微量污染物。
Molecules. 2019 Jul 20;24(14):2638. doi: 10.3390/molecules24142638.
5
Peroxone mineralization of chemical oxygen demand for direct potable water reuse: Kinetics and process control.过一硫酸氢钾复合盐对化学需氧量的矿化作用及其在直接饮用水回用中的应用:动力学及过程控制。
Water Res. 2015 Apr 15;73:362-72. doi: 10.1016/j.watres.2015.01.030. Epub 2015 Jan 31.
6
Advanced treatment of biotreated textile industry wastewater with ozone, virgin/ozonated granular activated carbon and their combination.采用臭氧、原生/臭氧化颗粒活性炭及其组合对生物处理后的纺织工业废水进行深度处理。
J Environ Sci Health A Tox Hazard Subst Environ Eng. 2004;39(7):1681-94. doi: 10.1081/ese-120037869.
7
Comparison of pharmaceutical abatement in various water matrices by conventional ozonation, peroxone (O/HO), and an electro-peroxone process.比较常规臭氧氧化、过氧单硫酸盐(O/HO)和电过氧单硫酸盐工艺在各种水基质中药物去除的效果。
Water Res. 2018 Mar 1;130:127-138. doi: 10.1016/j.watres.2017.11.054. Epub 2017 Nov 27.
8
Kinetics of pulp mill effluent treatment by ozone-based processes.基于臭氧工艺处理纸浆厂废水的动力学
J Hazard Mater. 2009 Sep 15;168(2-3):875-81. doi: 10.1016/j.jhazmat.2009.02.111. Epub 2009 Mar 3.
9
Stabilized leachates: ozone-activated carbon treatment and kinetics.稳定化渗滤液:臭氧-活性炭处理及动力学
Water Res. 2003 Dec;37(20):4823-34. doi: 10.1016/j.watres.2003.08.007.
10
Effect of some operational parameters on the decolorization of textile effluents and dye solutions by ozonation.一些操作参数对纺织废水和染料溶液臭氧氧化脱色的影响。
Environ Technol. 2005 Feb;26(2):135-43. doi: 10.1080/09593332608618573.

引用本文的文献

1
Safeguarding drinking water: A brief insight on characteristics, treatments and risk assessment of contamination.保障饮用水安全:关于污染特征、处理和风险评估的简要见解。
Environ Monit Assess. 2024 Jan 20;196(2):180. doi: 10.1007/s10661-024-12311-z.
2
Removal of Non-Steroidal Anti-Inflammatory Drugs from Drinking Water Sources by GO-SWCNT Buckypapers.GO-SWCNT 碳纳米纸去除饮用水源中的非甾体抗炎药。
Molecules. 2022 Nov 8;27(22):7674. doi: 10.3390/molecules27227674.
3
Regeneration of dye-saturated activated carbon through advanced oxidative processes: A review.

本文引用的文献

1
Integrated ozonation assisted electrocoagulation process for the removal of cyanide from steel industry wastewater.臭氧协同电混凝工艺去除钢铁工业废水中的氰化物。
Chemosphere. 2021 Jan;263:128370. doi: 10.1016/j.chemosphere.2020.128370. Epub 2020 Sep 18.
2
Antimicrobial Resistance: Implications and Costs.抗菌药物耐药性:影响与成本
Infect Drug Resist. 2019 Dec 20;12:3903-3910. doi: 10.2147/IDR.S234610. eCollection 2019.
3
A hybrid process of Fe-based catalytic ozonation and biodegradation for the treatment of industrial wastewater reverse osmosis concentrate.
通过高级氧化工艺实现染料饱和活性炭的再生:综述
Heliyon. 2022 Aug 13;8(8):e10205. doi: 10.1016/j.heliyon.2022.e10205. eCollection 2022 Aug.
4
Coconut Fiber Decorated with Bismuth Vanadate for Enhanced Photocatalytic Activity.负载钒酸铋的椰壳纤维用于增强光催化活性
ACS Omega. 2022 Mar 3;7(10):8854-8863. doi: 10.1021/acsomega.1c07169. eCollection 2022 Mar 15.
铁基催化臭氧化和生物降解的混合工艺处理工业废水反渗透浓缩液。
Chemosphere. 2020 Jan;238:124639. doi: 10.1016/j.chemosphere.2019.124639. Epub 2019 Aug 22.
4
Pharmaceutical Compounds in Drinking Water.饮用水中的药物化合物。
J Xenobiot. 2016 Jun 10;6(1):5774. doi: 10.4081/xeno.2016.5774.
5
Adsorption of selected endocrine disrupting compounds and pharmaceuticals on activated biochars.吸附选定的内分泌干扰化合物和药物在活性生物炭上。
J Hazard Mater. 2013 Dec 15;263 Pt 2:702-10. doi: 10.1016/j.jhazmat.2013.10.033. Epub 2013 Oct 24.
6
Treatment of micropollutants in municipal wastewater: ozone or powdered activated carbon?城市污水中微污染物的处理:臭氧还是粉末活性炭?
Sci Total Environ. 2013 Sep 1;461-462:480-98. doi: 10.1016/j.scitotenv.2013.05.034. Epub 2013 Jun 8.
7
Oxidation and biodegradability enhancement of 1,4-dioxane using hydrogen peroxide and ozone.使用过氧化氢和臭氧增强1,4-二氧六环的氧化及生物降解性
Environ Sci Technol. 1994 Oct 1;28(11):1812-8. doi: 10.1021/es00060a010.
8
Adverse effects in wild fish living downstream from pharmaceutical manufacture discharges.制药厂排放物下游野生鱼类的不良反应。
Environ Int. 2011 Nov;37(8):1342-8. doi: 10.1016/j.envint.2011.06.002. Epub 2011 Jun 30.
9
Occurrence and concentrations of pharmaceutical compounds in groundwater used for public drinking-water supply in California.加利福尼亚州用于公共饮用水供应的地下水中药物化合物的出现和浓度。
Sci Total Environ. 2011 Aug 15;409(18):3409-17. doi: 10.1016/j.scitotenv.2011.05.053.
10
Development and optimization of a HPLC-DAD method for the determination of diverse pharmaceuticals in estuarine surface waters.一种用于测定河口表层水中多种药物的高效液相色谱 - 二极管阵列检测法的开发与优化
J Chromatogr Sci. 2010 Mar;48(3):176-82. doi: 10.1093/chromsci/48.3.176.