Introduction to Radical Singlet Oxygen

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10.1016/J.SEPPUR.2021.118466

Electron paramagnetic resonance (EPR) and quenching tests indicated that non-radical singlet oxygen (1O2) is the dominant contributor for HA degradation.

Enhanced humic acid degradation by Fe3O4/ultrasound-activated peroxymonosulfate : Synergy index, non-radical effect and mechanism

10.1016/J.APCATB.2021.120229

The active species capture experimental data and electron spin resonance (ESR) determinations revealed that both active radicals (like •SO4-, •OH, •O2-, h+) and nonradical singlet oxygen (1O2) participated in the CQ decomposition.

Photocatalysis-activated SR-AOP over PDINH/MIL-88A(Fe) composites for boosted chloroquine phosphate degradation: Performance, mechanism, pathway and DFT calculations

10.1007/s10971-021-05574-2

The scavenging experiments and electron paramagnetic resonance technologies revealed that non-radical singlet oxygen (1O2), sulfate radicals(SO4•−) were associated as active species in the SrCoO2.

Singlet oxygen produced SrCoO2.5 in environmental protection: extraordinary electronic properties and promoted catalytic performance

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10.1016/j.jcis.2019.07.002

Quenching experiments and electron paramagnetic resonance demonstrated that non-radical singlet oxygen (1O2) was the dominant species for the oxidation of organic pollutants via electron transfer in the g-C3N4@COF/PMS system.

Metal-free catalysts of graphitic carbon nitride-covalent organic frameworks for efficient pollutant destruction in water.

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An Overview of Radical Singlet Oxygen

Radical Singlet Oxygen
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What is/are Radical Singlet?

Radical Singlet - Electron paramagnetic resonance (EPR) and quenching tests indicated that non-radical singlet oxygen (1O2) is the dominant contributor for HA degradation. [1] The active species capture experimental data and electron spin resonance (ESR) determinations revealed that both active radicals (like •SO4-, •OH, •O2-, h+) and nonradical singlet oxygen (1O2) participated in the CQ decomposition. [2] The scavenging experiments and electron paramagnetic resonance technologies revealed that non-radical singlet oxygen (1O2), sulfate radicals(SO4•−) were associated as active species in the SrCoO2. [3] Quenching experiments and electron paramagnetic resonance demonstrated that non-radical singlet oxygen (1O2) was the dominant species for the oxidation of organic pollutants via electron transfer in the g-C3N4@COF/PMS system. [4]

radical singlet oxygen

Electron paramagnetic resonance (EPR) and quenching tests indicated that non-radical singlet oxygen (1O2) is the dominant contributor for HA degradation. [1] The active species capture experimental data and electron spin resonance (ESR) determinations revealed that both active radicals (like •SO4-, •OH, •O2-, h+) and nonradical singlet oxygen (1O2) participated in the CQ decomposition. [2] The scavenging experiments and electron paramagnetic resonance technologies revealed that non-radical singlet oxygen (1O2), sulfate radicals(SO4•−) were associated as active species in the SrCoO2. [3] Quenching experiments and electron paramagnetic resonance demonstrated that non-radical singlet oxygen (1O2) was the dominant species for the oxidation of organic pollutants via electron transfer in the g-C3N4@COF/PMS system. [4]