• 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

通过对木屑基生物炭进行臭氧-三亚乙基四胺改性提高其对亚甲基蓝的水相吸附性能。

Improved methylene blue adsorption from an aqueous medium by ozone-triethylenetetramine modification of sawdust-based biochar.

作者信息

Hassaan Mohamed A, Yılmaz Murat, Helal Mohamed, El-Nemr Mohamed A, Ragab Safaa, El Nemr Ahmed

机构信息

National Institute of Oceanography and Fisheries (NIOF), Kayet Bey, Elanfoushy, Alexandria, Egypt.

Department of Chemical Engineering, Faculty of Engineering, Osmaniye Korkut Ata University, 80000, Osmaniye, Turkey.

出版信息

Sci Rep. 2023 Aug 1;13(1):12431. doi: 10.1038/s41598-023-39495-7.

DOI:10.1038/s41598-023-39495-7
PMID:37528164
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC10394039/
Abstract

In this study, sawdust biochar-O-TETA (SDBT), a novel biochar, was prepared via treatment with 80% sulfuric acid, followed by oxidation by ozone and subsequent treatment with boiling Triethylenetetramine (TETA). Characterization studies of the prepared SDBT adsorbent were performed with SEM-EDX, BET, XRD, BJH, FT-IR, DTA and TGA analyses. The adsorption efficiency of MB dye by SDBT biochar from water was investigated. Methylene Blue (MB) dye absorption was most effective when the solution pH was 12. The maximum removal % of MB dye was 99.75% using 20 mg/L as starting MB dye concentration and 2.0 g/L SDBT dose. The Q of the SDBT was 568.16 mg/g. Actual results were fitted to Temkin (TIM), Freundlich (FIM), and Langmuir (LIM) isotherm models. The experimental results for SDBT fitted well with all three models. Error function equations were used to test the results obtained from these isotherm models, which showed that the experimental results fit better with TIM and FIM. Kinetic data were investigated, and the pseudo-second-order (PSOM) had R > 0.99 and was mainly responsible for guiding the absorption rate. The removal mechanism of the MB dye ions in a base medium (pH 12) may be achieved via physical interaction due to electrostatic interaction between the SDBT surface and the positive charge of the MB dye. The results show that SDBT effectively removes the MB dye from the aqueous environment and can be used continually without losing its absorption efficiency.

摘要

在本研究中,通过用80%的硫酸处理,随后用臭氧氧化并接着用沸腾的三亚乙基四胺(TETA)处理,制备了一种新型生物炭——锯末生物炭-O-TETA(SDBT)。采用扫描电子显微镜-能谱仪(SEM-EDX)、比表面积分析仪(BET)、X射线衍射仪(XRD)、巴雷特-乔伊纳-哈尔达瓦方法(BJH)、傅里叶变换红外光谱仪(FT-IR)、差示热分析仪(DTA)和热重分析仪(TGA)对制备的SDBT吸附剂进行了表征研究。研究了SDBT生物炭从水中吸附亚甲基蓝(MB)染料的效率。当溶液pH值为12时,亚甲基蓝(MB)染料的吸附效果最佳。以20 mg/L作为初始MB染料浓度,2.0 g/L的SDBT剂量时,MB染料的最大去除率为99.75%。SDBT的吸附量(Q)为568.16 mg/g。将实际结果拟合到坦金(TIM)、弗伦德利希(FIM)和朗缪尔(LIM)等温线模型。SDBT的实验结果与这三种模型都拟合得很好。使用误差函数方程来检验从这些等温线模型获得的结果,结果表明实验结果与TIM和FIM拟合得更好。对动力学数据进行了研究,准二级动力学模型(PSOM)的R大于0.99,主要负责指导吸附速率。在碱性介质(pH 12)中,MB染料离子的去除机制可能是通过SDBT表面与MB染料正电荷之间的静电相互作用实现物理吸附。结果表明,SDBT能有效从水环境中去除MB染料,并且可以持续使用而不丧失其吸附效率。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ff3c/10394039/d8a3ad85838d/41598_2023_39495_Fig15_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ff3c/10394039/4b45cf765d29/41598_2023_39495_Fig1_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ff3c/10394039/138b2289f140/41598_2023_39495_Fig2_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ff3c/10394039/d5f13d9bcba4/41598_2023_39495_Fig3_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ff3c/10394039/ca137a6bc2a4/41598_2023_39495_Fig4_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ff3c/10394039/0be4a7014591/41598_2023_39495_Fig5_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ff3c/10394039/22b10836f1d1/41598_2023_39495_Fig6_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ff3c/10394039/9473c42f1fc4/41598_2023_39495_Fig7_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ff3c/10394039/e35c27808c22/41598_2023_39495_Fig8_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ff3c/10394039/1d740b4b5257/41598_2023_39495_Fig9_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ff3c/10394039/cff7981e4835/41598_2023_39495_Fig10_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ff3c/10394039/8b9d5648f6f1/41598_2023_39495_Fig11_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ff3c/10394039/edf01a55c244/41598_2023_39495_Fig12_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ff3c/10394039/59c8fd46fc5c/41598_2023_39495_Fig13_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ff3c/10394039/d87b2c79204e/41598_2023_39495_Fig14_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ff3c/10394039/d8a3ad85838d/41598_2023_39495_Fig15_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ff3c/10394039/4b45cf765d29/41598_2023_39495_Fig1_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ff3c/10394039/138b2289f140/41598_2023_39495_Fig2_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ff3c/10394039/d5f13d9bcba4/41598_2023_39495_Fig3_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ff3c/10394039/ca137a6bc2a4/41598_2023_39495_Fig4_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ff3c/10394039/0be4a7014591/41598_2023_39495_Fig5_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ff3c/10394039/22b10836f1d1/41598_2023_39495_Fig6_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ff3c/10394039/9473c42f1fc4/41598_2023_39495_Fig7_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ff3c/10394039/e35c27808c22/41598_2023_39495_Fig8_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ff3c/10394039/1d740b4b5257/41598_2023_39495_Fig9_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ff3c/10394039/cff7981e4835/41598_2023_39495_Fig10_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ff3c/10394039/8b9d5648f6f1/41598_2023_39495_Fig11_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ff3c/10394039/edf01a55c244/41598_2023_39495_Fig12_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ff3c/10394039/59c8fd46fc5c/41598_2023_39495_Fig13_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ff3c/10394039/d87b2c79204e/41598_2023_39495_Fig14_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ff3c/10394039/d8a3ad85838d/41598_2023_39495_Fig15_HTML.jpg

相似文献

1
Improved methylene blue adsorption from an aqueous medium by ozone-triethylenetetramine modification of sawdust-based biochar.通过对木屑基生物炭进行臭氧-三亚乙基四胺改性提高其对亚甲基蓝的水相吸附性能。
Sci Rep. 2023 Aug 1;13(1):12431. doi: 10.1038/s41598-023-39495-7.
2
Isotherm and kinetic investigations of sawdust-based biochar modified by ammonia to remove methylene blue from water.氨改性木屑基生物炭对水中亚甲基蓝吸附的等温线及动力学研究
Sci Rep. 2023 Aug 5;13(1):12724. doi: 10.1038/s41598-023-39971-0.
3
Mandarin Biochar-TETA (MBT) prepared from Citrus reticulata peels for adsorption of Acid Yellow 11 dye from water.从柑橘皮制备的普通话生物炭-TETA(MBT)用于从水中吸附酸性黄 11 染料。
Sci Rep. 2022 Oct 22;12(1):17797. doi: 10.1038/s41598-022-22359-x.
4
Fabrication of date palm kernel biochar-sulfur (DPKB-S) for super adsorption of methylene blue dye from water.用于从水中高效吸附亚甲基蓝染料的枣椰核生物炭-硫(DPKB-S)的制备
Sci Rep. 2024 Mar 21;14(1):6830. doi: 10.1038/s41598-024-56939-w.
5
Isotherm and kinetic studies of acid yellow 11 dye adsorption from wastewater using Pisum Sativum peels microporous activated carbon.用豌豆皮微孔活性炭从废水中吸附酸性黄 11 染料的等温线和动力学研究。
Sci Rep. 2023 Mar 15;13(1):4268. doi: 10.1038/s41598-023-31433-x.
6
Fabrication of N-doping activated carbons from fish waste and sawdust for Acid Yellow 36 dye removal from an aquatic environment.由鱼废弃物和木屑制备 N 掺杂活性炭用于从水相中去除酸性黄 36 染料。
Sci Rep. 2023 Apr 11;13(1):5892. doi: 10.1038/s41598-023-33075-5.
7
Thermodynamic, kinetic, and isotherm studies of Direct Blue 86 dye absorption by cellulose hydrogel.纤维素水凝胶对直接蓝 86 染料的吸附热力学、动力学和等温线研究。
Sci Rep. 2023 Apr 11;13(1):5910. doi: 10.1038/s41598-023-33078-2.
8
Efficiency of iron modified peels biochar as a novel adsorbent for methylene blue dye abatement from aqueous phase: equilibrium and kinetic studies.铁改性果皮生物炭作为新型吸附剂去除水相中亚甲基蓝染料的效率:平衡和动力学研究。
Int J Phytoremediation. 2022;24(11):1173-1183. doi: 10.1080/15226514.2021.2021848. Epub 2022 Jan 6.
9
Electrospun cellulose acetate/activated carbon composite modified by EDTA (rC/AC-EDTA) for efficient methylene blue dye removal.静电纺丝纤维素醋酸酯/活性炭复合改性乙二胺四乙酸(rC/AC-EDTA)用于高效去除亚甲基蓝染料。
Sci Rep. 2023 Jun 19;13(1):9919. doi: 10.1038/s41598-023-36994-5.
10
Methylene blue and Congo red dye elimination from synthetic wastewater using seed pod powder: isotherm and kinetic and mechanistic studies.采用豆荚粉去除合成废水中亚甲基蓝和刚果红染料:等温线和动力学及机理研究。
Int J Phytoremediation. 2024;26(14):2366-2377. doi: 10.1080/15226514.2024.2390190. Epub 2024 Aug 14.

引用本文的文献

1
Isotherm, kinetics and ANN analysis of methylene blue adsorption onto nitrogen doped Ulva lactuca Biochar.亚甲基蓝在氮掺杂石莼生物炭上吸附的等温线、动力学及人工神经网络分析
Sci Rep. 2025 Mar 27;15(1):10642. doi: 10.1038/s41598-025-92973-y.
2
Modelling of a new form of nitrogen doped activated carbon for adsorption of various dyes and hexavalent chromium ions.一种新型氮掺杂活性炭对各种染料和六价铬离子吸附的建模
Sci Rep. 2025 Jan 31;15(1):3896. doi: 10.1038/s41598-025-87398-6.
3
Adsorption of Acid Yellow 36 and direct blue 86 dyes to Delonix regia biochar-sulphur.

本文引用的文献

1
Ecological and human health risk assessment of polycyclic aromatic hydrocarbons (PAH) in Tigris river near the oil refineries in Iraq.伊拉克炼油厂附近底格里斯河多环芳烃(PAH)的生态和人体健康风险评估。
Environ Res. 2023 Jun 15;227:115791. doi: 10.1016/j.envres.2023.115791. Epub 2023 Mar 28.
2
Isotherm and kinetic studies of acid yellow 11 dye adsorption from wastewater using Pisum Sativum peels microporous activated carbon.用豌豆皮微孔活性炭从废水中吸附酸性黄 11 染料的等温线和动力学研究。
Sci Rep. 2023 Mar 15;13(1):4268. doi: 10.1038/s41598-023-31433-x.
3
Ketoprofen and aspirin removal by laccase immobilized on date stones.
酸性黄36和直接蓝86染料在凤凰木生物炭-硫磺上的吸附
Sci Rep. 2025 Jan 27;15(1):3448. doi: 10.1038/s41598-025-85405-4.
4
Microwave-induced degradation of Congo red dye in the presence of 2D TiCT MXene as a catalyst.二维TiCT MXene作为催化剂存在下微波诱导刚果红染料的降解。
Sci Rep. 2025 Jan 3;15(1):634. doi: 10.1038/s41598-024-82911-9.
5
Advancements in application of modified biochar as a green and low-cost adsorbent for wastewater remediation from organic dyes.改性生物炭作为一种绿色低成本吸附剂用于去除有机染料废水中污染物的应用进展。
R Soc Open Sci. 2024 May 15;11(5):232033. doi: 10.1098/rsos.232033. eCollection 2024 May.
6
Potent and Versatile Biogenically Synthesized Alumina/Nickel Oxide Nanocomposite Adsorbent for Defluoridation of Drinking Water.用于饮用水除氟的高效多功能生物合成氧化铝/氧化镍纳米复合吸附剂
ACS Omega. 2024 May 23;9(22):23220-23240. doi: 10.1021/acsomega.3c09076. eCollection 2024 Jun 4.
7
Green algae Ulva lactuca-derived biochar-sulfur improves the adsorption of methylene blue from water.绿藻浒苔衍生生物炭-硫可改善水中亚甲基蓝的吸附。
Sci Rep. 2024 May 21;14(1):11583. doi: 10.1038/s41598-024-61868-9.
8
Removal of Cr ions and mordant violet 40 dye from liquid media using Pterocladia capillacea red algae derived activated carbon-iron oxides.利用海萝属红藻衍生的活性炭-铁氧化物从液体介质中去除铬离子和媒染剂紫40染料。
Sci Rep. 2023 Oct 25;13(1):18306. doi: 10.1038/s41598-023-45464-x.
固定在椰枣核上的漆酶对酮洛芬和阿司匹林的去除
Chemosphere. 2023 Jan;311(Pt 2):137133. doi: 10.1016/j.chemosphere.2022.137133. Epub 2022 Nov 4.
4
Mandarin Biochar-TETA (MBT) prepared from Citrus reticulata peels for adsorption of Acid Yellow 11 dye from water.从柑橘皮制备的普通话生物炭-TETA(MBT)用于从水中吸附酸性黄 11 染料。
Sci Rep. 2022 Oct 22;12(1):17797. doi: 10.1038/s41598-022-22359-x.
5
Magnetic biochar derived from biosolids via hydrothermal carbonization: Enzyme immobilization, immobilized-enzyme kinetics, environmental toxicity.通过水热碳化从生物固体中衍生的磁性生物炭:酶固定化、固定化酶动力学、环境毒性。
J Hazard Mater. 2020 Feb 15;384:121272. doi: 10.1016/j.jhazmat.2019.121272. Epub 2019 Sep 21.
6
Mechanisms and reutilization of modified biochar used for removal of heavy metals from wastewater: A review.改性生物炭去除废水中重金属的机制及再利用:综述。
Sci Total Environ. 2019 Jun 10;668:1298-1309. doi: 10.1016/j.scitotenv.2019.03.011. Epub 2019 Mar 4.
7
Removal of azo dye from water via adsorption on biochar produced by the gasification of wood wastes.通过在气化木质废弃物产生的生物炭上吸附去除水中偶氮染料。
Environ Sci Pollut Res Int. 2019 Oct;26(28):28558-28573. doi: 10.1007/s11356-018-3833-x. Epub 2019 Jan 3.
8
Investigation of dye adsorption onto activated carbon from the shells of Macoré fruit.关于从马科雷果壳制备的活性炭对染料吸附的研究。
J Environ Manage. 2015 Jun 1;156:10-4. doi: 10.1016/j.jenvman.2015.03.006. Epub 2015 Mar 16.
9
Removal of arsenic by magnetic biochar prepared from pinewood and natural hematite.由松木和天然赤铁矿制备的磁性生物炭去除砷。
Bioresour Technol. 2015 Jan;175:391-5. doi: 10.1016/j.biortech.2014.10.104. Epub 2014 Oct 28.
10
Polyethylenimine modified biochar adsorbent for hexavalent chromium removal from the aqueous solution.聚乙烯亚胺改性生物炭吸附剂用于从水溶液中去除六价铬。
Bioresour Technol. 2014 Oct;169:403-408. doi: 10.1016/j.biortech.2014.07.014. Epub 2014 Jul 10.