Nanoconfinement-triggered oligomerization pathway for efficient removal of phenolic pollutants via a Fenton-like reaction

被引:58
作者
Zhang, Xiang [1 ]
Tang, Jingjing [1 ]
Wang, Lingling [1 ]
Wang, Chuan [1 ]
Chen, Lei [2 ]
Chen, Xinqing [3 ]
Qian, Jieshu [1 ,2 ,4 ]
Pan, Bingcai [2 ]
机构
[1] Nanjing Univ Sci & Technol, Sch Environm & Biol Engn, Jiangsu Key Lab Chem Pollut Control & Resources R, Nanjing 210094, Peoples R China
[2] Nanjing Univ, Sch Environm, Res Ctr Environm Nanotechnol ReCENT, State Key Lab Pollut Control & Resources Reuse, Nanjing 210023, Peoples R China
[3] Chinese Acad Sci, Shanghai Adv Res Inst, CAS Key Lab Low Carbon Convers Sci & Engn, Shanghai, Peoples R China
[4] Wuxi Univ, Sch Environm Engn, Wuxi 214105, Jiangsu, Peoples R China
基金
中国国家自然科学基金;
关键词
METAL-ORGANIC FRAMEWORK; OXIDATION; DEGRADATION; CATALYSIS; SITES; IRON; ACID;
D O I
10.1038/s41467-024-45106-4
中图分类号
O [数理科学和化学]; P [天文学、地球科学]; Q [生物科学]; N [自然科学总论];
学科分类号
07 ; 0710 ; 09 ;
摘要
Heterogeneous Fenton reaction represents one of the most reliable technologies to ensure water safety, but is currently challenged by the sluggish Fe(III) reduction, excessive input of chemicals for organic mineralization, and undesirable carbon emission. Current endeavors to improve the catalytic performance of Fenton reaction are mostly focused on how to accelerate Fe(III) reduction, while the pollutant degradation step is habitually overlooked. Here, we report a nanoconfinement strategy by using graphene aerogel (GA) to support UiO-66-NH2-(Zr) binding atomic Fe(III), which alters the carbon transfer route during phenol removal from kinetically favored ring-opening route to thermodynamically favored oligomerization route. GA nanoconfinement favors the Fe(III) reduction by enriching the reductive intermediates and allows much faster phenol removal than the unconfined analog (by 208 times in terms of first-order rate constant) and highly efficient removal of total organic carbon, i.e., 92.2 +/- 3.7% versus 3.6 +/- 0.3% in 60min. Moreover, this oligomerization route reduces the oxidant consumption for phenol removal by more than 95% and carbon emission by 77.9%, compared to the mineralization route in homogeneous Fe2++H2O2 system. Our findings may upgrade the regulatory toolkit for Fenton reactions and provide an alternative carbon transfer route for the removal of aqueous pollutants.
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页数:9
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