2020
DOI: 10.1021/acs.est.0c02377
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Comparative Study for Interactions of Sulfate Radical and Hydroxyl Radical with Phenol in the Presence of Nitrite

Abstract: Sulfate radical (SO4 •–)- and hydroxyl radical (HO•)-based advanced oxidation processes (AOPs) are effective for the removal of organic pollutants in water treatment. This study compared the interactions of SO4 •– and HO• for the transformation of phenol in UV/peroxydisulfate (PDS) and UV/H2O2 with the presence of NO2 –, which is widely present in aquatic environments and transforms SO4 •– and HO• to •NO2. By using laser flash photolysis, the products of phenol reacting with SO4 •– and HO• were demonstrated to… Show more

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Cited by 109 publications
(100 citation statements)
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“…• generates 4-chloro-2-nitrocyclohexa-2,5-dienone ( Clewley et al, 1989 ). Such dienone is known to be unstable and undergoes rearrangement with the assistance of a H 2 O molecule, resulting in the formation of nitro-derivative ( Ji et al, 2017 ;Chen et al, 2020 ) (Scheme 3 of Fig. 3 ).…”
Section: Intermediate Products and Transformation Pathwaysmentioning
confidence: 99%
“…• generates 4-chloro-2-nitrocyclohexa-2,5-dienone ( Clewley et al, 1989 ). Such dienone is known to be unstable and undergoes rearrangement with the assistance of a H 2 O molecule, resulting in the formation of nitro-derivative ( Ji et al, 2017 ;Chen et al, 2020 ) (Scheme 3 of Fig. 3 ).…”
Section: Intermediate Products and Transformation Pathwaysmentioning
confidence: 99%
“… 19 However, NO 2 • possesses moderate E 0 (1.0 V) and small t 1/2 (1.4 μs) and therefore cannot be as efficient as NO 3 • in degrading pollutants. 21 , 22 Interestingly, NO 2 – experiences further dissection into O •– and NO • . 19 Despite having a lengthy lifetime ( t 1/2 of 10 7 μs), NO • is inactive in degrading contaminants ( E 0 of −0.4 V).…”
Section: Introductionmentioning
confidence: 99%
“…It should be noted that NO 2 – functionalities can be radicalized via the • OH → NO 2 • SUP route ( Figure 1 B) yet cannot be desirable in decomposing contaminant due to the demerits of NO 2 • stated above. 19 , 21 , 22 , 40 Nevertheless, these can suggest the merits of Mn oxides in activating • OH → NO 3 • SUP and pose the necessity to select the Mn oxide suitable to disperse Mn n + /O α species with desired properties. Mn species are multivalent in nature (Mn 2+ /Mn 3+ /Mn 4+ ) and therefore offer a variety of architectures including MnO, Mn 3 O 4 , Mn 2 O 3 , and MnO 2 , among which MnO 2 was reported to provide the largest quantities of O α and/or Mn n + species, 41 , 42 thereby being chosen herein.…”
Section: Introductionmentioning
confidence: 99%
“…As part of the so-called “brown carbon”, nitroaromatic compounds play a role in the absorption of sunlight by airborne aerosols and, by so doing, they affect to a potentially significant extent the still-debated and insufficiently defined climate feedback of the aerosols [ 10 , 11 , 12 , 13 , 14 , 15 , 16 ]. Another reason for the recent interest towards photonitration is the acknowledgement of the important role it may play in photochemical processes for water treatment, which are gaining increasing attention and where the occurrence of nitrate and nitrite under technical UV irradiation might favour the formation of harmful compounds [ 17 , 18 , 19 , 20 , 21 ].…”
Section: Introductionmentioning
confidence: 99%