2018
DOI: 10.1021/acs.est.7b05563
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Fe(III)-Doped g-C3N4 Mediated Peroxymonosulfate Activation for Selective Degradation of Phenolic Compounds via High-Valent Iron-Oxo Species

Abstract: Herein, we proposed a new peroxymonosulfate (PMS) activation system employing the Fe(III) doped g-CN (CNF) as catalyst. Quite different from traditional sulfate radical-based advanced oxidation processes (SR-AOPs), the PMS/CNF system was capable of selectively degrading phenolic compounds (e.g., p-chlorophenol, 4-CP) in a wide pH range (3-9) via nonradical pathway. The generated singlet oxygen (O) in the PMS/CNF3 (3.46 wt % Fe) system played negligible role in removing 4-CP, and high-valent iron-oxo species fi… Show more

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Cited by 720 publications
(238 citation statements)
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“…When incorporating a small amount of metal into the precursors, the g‐C 3 N 4 nanosheets doped with individual metal atoms can be facilely obtained. For instance, Sr, Co, and Fe doped g‐C 3 N 4 have been synthesized without defining the structure of the metal atoms in g‐C 3 N 4 matrix . In a modified strategy reported by Chen et al, the as‐prepared silver tricyanomethanide was used as a miscible and reactive metal precursor to cocondensation with cyanamide, which ensured the homogeneity of the single atom dispersed Ag coordinated with g‐C 3 N 4 .…”
Section: Synthesis Of Sacs In 2d Materialsmentioning
confidence: 99%
“…When incorporating a small amount of metal into the precursors, the g‐C 3 N 4 nanosheets doped with individual metal atoms can be facilely obtained. For instance, Sr, Co, and Fe doped g‐C 3 N 4 have been synthesized without defining the structure of the metal atoms in g‐C 3 N 4 matrix . In a modified strategy reported by Chen et al, the as‐prepared silver tricyanomethanide was used as a miscible and reactive metal precursor to cocondensation with cyanamide, which ensured the homogeneity of the single atom dispersed Ag coordinated with g‐C 3 N 4 .…”
Section: Synthesis Of Sacs In 2d Materialsmentioning
confidence: 99%
“…A large number of studies have focused on waste water purification contaminated by phenols, and various techniques have been developed to efficiently remove them. At present, the most widely used methods for phenol removal have included biological degradation [2,3], photocatalytic decomposition [4,5], chemical oxidation [6,7], 2 of 13 hydrodynamic cavitation [8,9] and adsorption [10][11][12][13]. Among these approaches, adsorption seem to have a particular advantage due to its relatively low cost, speed and convenience of operation.…”
Section: Introductionmentioning
confidence: 99%
“…The reactive species generated in L 1.15 FO/H 2 O 2 system were confirmed by the quenching tests and in situ EPR technique as shown in Figure a–c. Ethanol (EtOH) and furfuryl alcohol (FFA) were chosen as the scavengers of hydroxyl radical ( • OH) and singlet oxygen ( 1 O 2 ), respectively . Figure a witnessed that FFA (0.05 m ) exhibited more serious inhibition on MO degradation and only 72% of MO was removed in 70 min, compared with EtOH (0.05 m ).…”
Section: Resultsmentioning
confidence: 99%