Abstract:The problem of organic pollution in wastewater is an important challenge due to its negative impact on the aquatic environment and human health. This review provides an outline of the research status for a sulfate-based advanced oxidation process in the removal of organic pollutants from water. The progress for metal catalyst activation and electrochemical activation is summarized including the use of catalyst-activated peroxymonosulfate (PMS) and peroxydisulfate (PDS) to generate hydroxyl radicals and sulfate… Show more
“…− hydrolysis produced H 2 O 2 (Equation ( 5)). Next, HO 2 • − was produced by the H 2 O 2 and •OH through Equation (6). Subsequently, the HO 2 • − decomposed to produce O 2 • − (Equation ( 7)).…”
Section: Electron-transfer Pathwaysmentioning
confidence: 99%
“…In particular, transition-metal-based catalysts are widely used as PMS activators due to their low toxicity, high abundance, and high catalytic activity [5]. Transition-metal oxides, such as Cu x O y , Mn x O y etc., have been proven to effectively activate peroxymonosulfate (PMS) [6]. For example, the Mn 3 O 4 /CuBi 2 O 4 composite material designed by Zhang et al [7], used for the catalytic activation of PMS, exhibits high phenol (almost 100%) and TOC (74.3%) degradation rates within 10 min.…”
Degradation efficiency and catalyst stability are crucial issues in the control of organic compounds in wastewater by advanced oxidation processes (AOPs). However, it is difficult for catalysts used in AOPs to have both high catalytic activity and high stability. Combined with the excellent activity of cobalt/copper oxides and the good stability of carbon, highly dispersed cobalt-oxide and copper-oxide nanoparticles embedded in carbon-matrix composites (Co-Cu@C) were prepared for the catalytic activation of peroxymonosulfate (PMS). The catalysts exhibited a stable structure and excellent performance for complete phenol degradation (20 mg L−1) within 5 min in the Cu-Co@C-5/PMS system, as well as low metal-ion-leaching rates and great reusability. Moreover, a quenching test and an EPR analysis revealed that ·OH, O2·−, and 1O2 were generated in the Co-Cu@C/PMS system for phenol degradation. The possible mechanism for the radical and non-radical pathways in the activation of the PMS by the Co-Cu@C was proposed. The present study provides a new strategy with which to construct heterostructures for environmentally friendly and efficient PMS-activation catalysts.
“…− hydrolysis produced H 2 O 2 (Equation ( 5)). Next, HO 2 • − was produced by the H 2 O 2 and •OH through Equation (6). Subsequently, the HO 2 • − decomposed to produce O 2 • − (Equation ( 7)).…”
Section: Electron-transfer Pathwaysmentioning
confidence: 99%
“…In particular, transition-metal-based catalysts are widely used as PMS activators due to their low toxicity, high abundance, and high catalytic activity [5]. Transition-metal oxides, such as Cu x O y , Mn x O y etc., have been proven to effectively activate peroxymonosulfate (PMS) [6]. For example, the Mn 3 O 4 /CuBi 2 O 4 composite material designed by Zhang et al [7], used for the catalytic activation of PMS, exhibits high phenol (almost 100%) and TOC (74.3%) degradation rates within 10 min.…”
Degradation efficiency and catalyst stability are crucial issues in the control of organic compounds in wastewater by advanced oxidation processes (AOPs). However, it is difficult for catalysts used in AOPs to have both high catalytic activity and high stability. Combined with the excellent activity of cobalt/copper oxides and the good stability of carbon, highly dispersed cobalt-oxide and copper-oxide nanoparticles embedded in carbon-matrix composites (Co-Cu@C) were prepared for the catalytic activation of peroxymonosulfate (PMS). The catalysts exhibited a stable structure and excellent performance for complete phenol degradation (20 mg L−1) within 5 min in the Cu-Co@C-5/PMS system, as well as low metal-ion-leaching rates and great reusability. Moreover, a quenching test and an EPR analysis revealed that ·OH, O2·−, and 1O2 were generated in the Co-Cu@C/PMS system for phenol degradation. The possible mechanism for the radical and non-radical pathways in the activation of the PMS by the Co-Cu@C was proposed. The present study provides a new strategy with which to construct heterostructures for environmentally friendly and efficient PMS-activation catalysts.
“…SO 4 •– are typically derived from peroxymonosulfate (PMS) and peroxydisulfate (PDS) with PMS activating more readily due to its asymmetric structure and longer O–O bond compared to PDS. , Various PMS activation methods have been demonstrated, including ultrasonic, thermal, alkali, UV radiation, transition metals, and carbon materials activation. − However, external energy activation encounters practical limitations due to the extra energy input required, which increases water treatment costs. Co 2+ has shown superior PMS activation efficiency in homogeneous reactions, but the performance of transition metal ions in PMS activation is affected by water system pH, and their homogeneous catalytic use poses recovery challenges, potentially leading to secondary water pollution. , Heterogeneous catalysts, such as Co 3 O 4 , are more suitable for large-scale wastewater treatment, evidenced by their effective activation of PMS for 2,4-dichlorophenol degradation and reduced metal ion concentration in effluent .…”
The Mn–Co dual-metal oxide is recognized as an
effective
activator for peroxymonosulfate (PMS), but its activation mechanism
remains controversial. In this study, a Co/Mn–C–N (CMCN)
nanocatalyst was synthesized using a simple pyrolysis method, and
its catalytic activity along with the PMS activation mechanism was
comprehensively explored. The findings indicated that the synergistic
effect of Mn and Co within the bimetallic composition significantly
enhanced the catalytic efficiency of CMCN compared to those of individual
metal oxides (Mn–C–N and Co–C–N). Bisphenol
A underwent successful degradation within 3 min in a neutral environment,
with a degradation kinetic rate of 1.59 min–1 and
a total organic carbon removal efficiency of 63.8%. Moreover, CMCN
nanoparticles demonstrated remarkable stability and reusability, maintaining
their efficacy over four cycles. Employing a series of experiments
and analytical characterizations, a novel activation mechanism for
PMS was proposed, involving both radical and nonradical pathways.
This mechanism involves the oxidation of organic pollutants through
a direct electron transfer process from metastable intermediate complexes.
Notably, the CMCN/PMS system exhibited a robust resistance to interference
factors. This research provides novel insights into the development
of bimetallic oxide composites for the effective removal of recalcitrant
water pollutants.
“…Persulfate can be activated through energy input (thermal, radiation, sonochemical/electrochemical), transition metal ions (iron, cobalt, copper, silver), alkali [5], and heterogeneous activators [6]. In addition, today sonochemical activation has sparked increasing interest as an alternative activation method.…”
Section: Introductionmentioning
confidence: 99%
“…Such materials are considered promising persulfate activators as they provide a high surface area, facilitating the interaction between persulfate and target pollutants [14]; (ii) Catalytic materials such as metal oxides [15], metal phosphides [16], metal-organic frameworks [17] or monolith catalysts with 3D hierarchical structures like δ-MnO 2 immobilized on 3D nickel foam or 3D α-Co(OH) 2 nanosheets developed on robust nickel foam (NF) [18,19]. These catalysts can enhance sulfate radicals production through redox reactions with persulfate, accelerating the oxidation of contaminants [6].…”
The development of efficient heterogeneous persulfate activators is one of the main research topics in the wastewater treatment area. The present work deals with the heterogeneous activation of sodium persulfate (SPS) using nickel oxide/strontium carbonate (NiO/SrCO3) for the degradation of sulfamethoxazole (SMX), a representative compound from the group of antibiotics. Results showed that NiO/SrCO3 exhibited high performance towards the activation of SPS, leading to SMX elimination in brief time spans. The impact of SPS (25–100 mg/L), NiO/SrCO3 (50–250 mg/L), and SMX (0.25–3.00 mg/L) concentration, and initial pH on the decomposition of SMX was further examined. Experiments were also conducted in real matrices such as secondary effluent and bottled water, revealing the existence of retarding phenomena compared to ultrapure water. This behavior was further investigated with the addition of bicarbonates, chlorides, or humic acid in ultrapure water. It was found that organic matter significantly hampered SMX removal. The role of the main radicals (hydroxyl and sulfate radicals) was determined using appropriate radical traps (methanol and tert-butanol). These quenching experiments combined with the conducted electrochemical measurements revealed that both a radical and a non-radical mechanism contribute to the decomposition of SMX.
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