• 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

非热等离子体去除地下水中的Pb(II)、Cd(II)和Ni(II)离子

Removal of Pb(II), Cd(II) and Ni(II) Ions from Groundwater by Nonthermal Plasma.

作者信息

Jabłońska Beata, Dróżdż Tomasz, Jabłoński Paweł, Kiełbasa Paweł

机构信息

Faculty of Infrastructure and Environment, Czestochowa University of Technology, Brzeźnicka St. 60a, 42-200 Częstochowa, Poland.

Faculty of Production and Power Engineering, University of Agriculture in Krakow, Al. Mickiewicza 21, 31-120 Krakow, Poland.

出版信息

Materials (Basel). 2022 Aug 6;15(15):5426. doi: 10.3390/ma15155426.

DOI:10.3390/ma15155426
PMID:35955360
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC9369537/
Abstract

The removal of Pb(II), Cd(II) and Ni(II) ions from aqueous solutions by means of nonthermal plasma with a dielectric barrier discharge is investigated. Aqueous solutions with metal ion concentrations from 10 to 100 mg/dm in spring water were used. In the first stage, the optimization of the solution flow rate, generator modulation frequency and duty cycle was made in terms of the removal efficiency of the considered metals. The removal was then investigated as a function of the number of passes of the solution through the cold plasma reactor. The effect of the initial concentration of ions in the solution was studied. Techniques such as composite central design, least squares method and Fourier transform infrared spectroscopy were used. The physical and chemical parameters of the solutions, such as electrical conductivity, pH, temperature, concentration of metal ions and the content of other substances (e.g., total organic carbon), were measured, and the presence of microorganisms was also examined. It was found that each pass of the solution through the cold plasma reactor causes a decrease in the concentration of Cd(II) and Ni(II); the concentration of Pb(II) drops rapidly after one pass, but further passes do not improve its removal. The removal percentage was 88% for Cd(II) after six passes and 72% for Pb(II) after one pass, whereas 19% for Ni(II). The purification mechanism corresponds to the precipitation of metal ions due to the increasing pH of the solution after exposure to cold plasma.

摘要

研究了利用具有介质阻挡放电的非热等离子体从水溶液中去除Pb(II)、Cd(II)和Ni(II)离子的方法。使用了金属离子浓度为10至100 mg/dm³的泉水溶液。在第一阶段,根据所考虑金属的去除效率对溶液流速、发生器调制频率和占空比进行了优化。然后研究了去除率与溶液通过冷等离子体反应器次数的函数关系。研究了溶液中离子初始浓度的影响。使用了复合中心设计、最小二乘法和傅里叶变换红外光谱等技术。测量了溶液的物理和化学参数,如电导率、pH值、温度、金属离子浓度和其他物质的含量(如总有机碳),并检测了微生物的存在。结果发现,溶液每次通过冷等离子体反应器都会导致Cd(II)和Ni(II)浓度降低;Pb(II)的浓度在一次通过后迅速下降,但进一步通过并不能提高其去除率。经过六次通过后,Cd(II)的去除率为88%,Pb(II)一次通过后的去除率为72%,而Ni(II)为19%。净化机制对应于由于溶液在暴露于冷等离子体后pH值升高导致金属离子沉淀。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2ad6/9369537/37e7e46676a3/materials-15-05426-g013.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2ad6/9369537/f81b286b7fc3/materials-15-05426-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2ad6/9369537/e15a4430154a/materials-15-05426-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2ad6/9369537/078bf7b3a861/materials-15-05426-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2ad6/9369537/9dd854e23047/materials-15-05426-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2ad6/9369537/c27df9c8905e/materials-15-05426-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2ad6/9369537/ae4802ebf362/materials-15-05426-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2ad6/9369537/77ad8a8e40ed/materials-15-05426-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2ad6/9369537/dfd5d619d652/materials-15-05426-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2ad6/9369537/40f85b687e7e/materials-15-05426-g009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2ad6/9369537/850f3224ae47/materials-15-05426-g010.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2ad6/9369537/35fb86c5ab98/materials-15-05426-g011.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2ad6/9369537/d7f28678c102/materials-15-05426-g012.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2ad6/9369537/37e7e46676a3/materials-15-05426-g013.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2ad6/9369537/f81b286b7fc3/materials-15-05426-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2ad6/9369537/e15a4430154a/materials-15-05426-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2ad6/9369537/078bf7b3a861/materials-15-05426-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2ad6/9369537/9dd854e23047/materials-15-05426-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2ad6/9369537/c27df9c8905e/materials-15-05426-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2ad6/9369537/ae4802ebf362/materials-15-05426-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2ad6/9369537/77ad8a8e40ed/materials-15-05426-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2ad6/9369537/dfd5d619d652/materials-15-05426-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2ad6/9369537/40f85b687e7e/materials-15-05426-g009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2ad6/9369537/850f3224ae47/materials-15-05426-g010.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2ad6/9369537/35fb86c5ab98/materials-15-05426-g011.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2ad6/9369537/d7f28678c102/materials-15-05426-g012.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2ad6/9369537/37e7e46676a3/materials-15-05426-g013.jpg

相似文献

1
Removal of Pb(II), Cd(II) and Ni(II) Ions from Groundwater by Nonthermal Plasma.非热等离子体去除地下水中的Pb(II)、Cd(II)和Ni(II)离子
Materials (Basel). 2022 Aug 6;15(15):5426. doi: 10.3390/ma15155426.
2
Ion-exchange of Pb2+, Cu2+, Zn2+, Cd2+, and Ni2+ ions from aqueous solution by Lewatit CNP 80.用Lewatit CNP 80从水溶液中离子交换Pb2+、Cu2+、Zn2+、Cd2+和Ni2+离子。
J Hazard Mater. 2007 Feb 9;140(1-2):299-307. doi: 10.1016/j.jhazmat.2006.09.011. Epub 2006 Sep 14.
3
The stability of the compounds formed in the process of removal Pb(II), Cu(II) and Cd(II) by steelmaking slag in an acidic aqueous solution.炼钢渣在酸性水溶液中去除 Pb(II)、Cu(II)和 Cd(II)过程中形成的化合物的稳定性。
J Environ Manage. 2019 Feb 1;231:41-48. doi: 10.1016/j.jenvman.2018.10.028. Epub 2018 Oct 13.
4
Application of mucilage from Dicerocaryum eriocarpum plant as biosorption medium in the removal of selected heavy metal ions.毛果双角果藜植物黏液作为生物吸附介质在去除特定重金属离子中的应用。
J Environ Manage. 2016 Jul 15;177:365-72. doi: 10.1016/j.jenvman.2016.04.011. Epub 2016 May 2.
5
Procion Green H-4G immobilized poly(hydroxyethylmethacrylate/chitosan) composite membranes for heavy metal removal.用于去除重金属的Procion Green H-4G固定化聚(甲基丙烯酸羟乙酯/壳聚糖)复合膜。
J Hazard Mater. 2003 Feb 28;97(1-3):111-25. doi: 10.1016/s0304-3894(02)00259-5.
6
Removal and recovery of lead(II) from single and multimetal (Cd, Cu, Ni, Zn) solutions by crop milling waste (black gram husk).利用农作物碾磨废料(黑豆皮)从单一金属(铅(II))和多金属(镉、铜、镍、锌)溶液中去除和回收铅(II)
J Hazard Mater. 2005 Jan 14;117(1):65-73. doi: 10.1016/j.jhazmat.2004.09.008.
7
Removal of Pb(II) and Cd(II) ions from aqueous solution by thiosemicarbazide modified chitosan.硫代氨基脲改性壳聚糖对水溶液中Pb(II)和Cd(II)离子的去除
Int J Biol Macromol. 2016 May;86:876-84. doi: 10.1016/j.ijbiomac.2016.02.027. Epub 2016 Feb 12.
8
Removal and recovery of heavy metals from aqueous solution using Ulmus carpinifolia and Fraxinus excelsior tree leaves.利用榆叶和欧洲白蜡树叶从水溶液中去除和回收重金属
J Hazard Mater. 2008 Jul 15;155(3):513-22. doi: 10.1016/j.jhazmat.2007.11.110. Epub 2007 Dec 4.
9
Efficiency of extremophilic microbial mats for removing Pb(II), Cu(II), and Ni(II) ions from aqueous solutions.极端微生物垫去除水溶液中 Pb(II)、Cu(II) 和 Ni(II)离子的效率。
Environ Sci Pollut Res Int. 2021 Oct;28(38):53365-53378. doi: 10.1007/s11356-021-14571-5. Epub 2021 May 24.
10
Alginate modified graphitic carbon nitride composite hydrogels for efficient removal of Pb(II), Ni(II) and Cu(II) from water.海藻酸钠改性石墨相氮化碳复合水凝胶用于高效去除水中的 Pb(II)、Ni(II) 和 Cu(II)。
Int J Biol Macromol. 2020 Apr 1;148:1298-1306. doi: 10.1016/j.ijbiomac.2019.10.105. Epub 2019 Nov 15.

本文引用的文献

1
Heavy metal adsorption using structurally preorganized adsorbent.使用结构预组织吸附剂吸附重金属
RSC Adv. 2020 Feb 19;10(12):7259-7264. doi: 10.1039/d0ra00125b. eCollection 2020 Feb 13.
2
Editorial: Heavy Metal Toxicity in Plants: Recent Insights on Physiological and Molecular Aspects.社论:植物中的重金属毒性:生理和分子方面的最新见解
Front Plant Sci. 2022 Feb 18;12:830682. doi: 10.3389/fpls.2021.830682. eCollection 2021.
3
Potential Application of Pin-to-Liquid Dielectric Barrier Discharge Structure in Decomposing Aqueous Phosphorus Compounds for Monitoring Water Quality.
针-液介质阻挡放电结构在分解水中磷化合物以监测水质方面的潜在应用。
Materials (Basel). 2021 Dec 9;14(24):7559. doi: 10.3390/ma14247559.
4
Removal of metal ions from water using oxygen plasma.利用氧等离子体去除水中的金属离子。
Sci Rep. 2021 Apr 28;11(1):9175. doi: 10.1038/s41598-021-88466-3.
5
The assessment of cadmium, chromium, copper, and nickel tolerance and bioaccumulation by shrub plant Tetraena qataranse.灌木植物 Tetraena qataranse 对镉、铬、铜和镍的耐受性和生物积累能力的评估。
Sci Rep. 2019 Apr 4;9(1):5658. doi: 10.1038/s41598-019-42029-9.
6
Water consumption management in polyethylene terephthalate (PET) bottles washing process via wastewater pretreatment and reuse.通过废水预处理和回用管理聚对苯二甲酸乙二醇酯(PET)瓶洗濯过程中的用水量。
J Environ Manage. 2018 Oct 15;224:215-224. doi: 10.1016/j.jenvman.2018.07.054. Epub 2018 Jul 24.
7
A novel two-level dielectric barrier discharge reactor for methyl orange degradation.一种用于甲基橙降解的新型两级介质阻挡放电反应器。
J Environ Manage. 2016 Dec 15;184(Pt 3):480-486. doi: 10.1016/j.jenvman.2016.10.038. Epub 2016 Oct 23.
8
Removal of copper from water using a thermally regenerative electrodeposition battery.使用热再生电沉积电池从水中去除铜。
J Hazard Mater. 2017 Jan 15;322(Pt B):551-556. doi: 10.1016/j.jhazmat.2016.10.022. Epub 2016 Oct 13.
9
Toxicity, mechanism and health effects of some heavy metals.某些重金属的毒性、作用机制及对健康的影响。
Interdiscip Toxicol. 2014 Jun;7(2):60-72. doi: 10.2478/intox-2014-0009. Epub 2014 Nov 15.
10
Degradation of pharmaceutical compounds in water by non-thermal plasma treatment.水相中药物化合物的非热等离子体降解。
Water Res. 2015 Sep 15;81:124-36. doi: 10.1016/j.watres.2015.05.037. Epub 2015 Jun 5.