Abstract:The degradation of the chloracetamide herbicide acetochlor has been studied under simulated ozonation treatment plant conditions. The degradation of acetochlor included the formation of several degradation products that were identified using GC/ion‐trap mass spectrometry with EI and CI and HPLC/electrospray‐QqTOF mass spectrometry. Thirteen ozonation products of acetochlor have been identified. Ozonation of the deuterated herbicide combined to MSn and high‐resolution mass measurement allowed effective characte… Show more
“…6(d)). This result suggests that UV-A radiation is not energetic enough to excite 1 and thus to cause its conversion into the subsequent intermediates (2)(3)(4)(5)(6)(7)(8)(9)(10)(11), as observed for the other systems (TiO 2 / UV-C, TiO 2 /UV-A and UV-C) evaluated herein.…”
Section: Identification Of By-products: Proposal Of a Degradation Routesupporting
confidence: 49%
“…It is important to mention that some of these intermediates (1, 2, 6, 8 and 9) have been previously reported by several research groups. [25,32,36,38,45,51,53,54] The evolution of each intermediate (1)(2)(3)(4)(5)(6)(7)(8)(9)(10)(11) formed during the photodegradation processes could then be monitored by LC-HRMS. The results from the extracted-ion chromatograms ( Fig.…”
Section: Identification Of By-products: Proposal Of a Degradation Routementioning
confidence: 99%
“…To improve the efficiency of removal of pharmaceutical compounds in aqueous media, novel and powerful technologies have been developed, especially the so‐called advanced oxidation processes (AOPs). Moreover, there has been a growing interest in the detection and identification of degradation products resulting from the application of AOPs . Among the AOPs, the following processes are noteworthy: photolysis, photocatalysis, electrochemistry and photoelectrochemistry .…”
Section: Introductionmentioning
confidence: 99%
“…Moreover, there has been a growing interest in the detection and identification of degradation products resulting from the application of AOPs. [9,10] Among the AOPs, the following processes are noteworthy: photolysis, [11][12][13][14][15][16] photocatalysis, [17] electrochemistry and photoelectrochemistry. [18,19] However, many challenging issues still remain, which are mainly related to the fact that products arising from the degradation of pollutants may present higher toxicity than their predecessors.…”
The degradation of the pharmaceutical compound ibuprofen (IBP) in aqueous solution induced by direct photolysis (UV-A and UV-C radiation) and photocatalysis (TiO2 /UV-A and TiO2 /UV-C systems) was evaluated. Initially, we observed that whereas photocatalysis (both systems) and direct photolysis with UV-C radiation were able to cause an almost complete removal of IBP, the mineralization rates achieved for all the photodegradation processes were much smaller (the highest value being obtained for the TiO2 /UV-C system: 37.7%), even after an exposure time as long as 120 min. Chemical structures for the by-products formed under these oxidative conditions (11 of them were detected) were proposed based on the data from liquid chromatography coupled to high-resolution mass spectrometry (LC-HRMS) analyses. Taking into account these results, an unprecedented route for the photodegradation of IBP could thus be proposed. Moreover, a fortunate result was achieved herein: tests against Artemia salina showed that the degradation products had no higher ecotoxicities than IBP, which possibly indicates that the photocatalytic (TiO2 /UV-A and TiO2 /UV-C systems) and photolytic (UV-C radiation) processes can be conveniently employed to deplete IBP in aqueous media.
“…6(d)). This result suggests that UV-A radiation is not energetic enough to excite 1 and thus to cause its conversion into the subsequent intermediates (2)(3)(4)(5)(6)(7)(8)(9)(10)(11), as observed for the other systems (TiO 2 / UV-C, TiO 2 /UV-A and UV-C) evaluated herein.…”
Section: Identification Of By-products: Proposal Of a Degradation Routesupporting
confidence: 49%
“…It is important to mention that some of these intermediates (1, 2, 6, 8 and 9) have been previously reported by several research groups. [25,32,36,38,45,51,53,54] The evolution of each intermediate (1)(2)(3)(4)(5)(6)(7)(8)(9)(10)(11) formed during the photodegradation processes could then be monitored by LC-HRMS. The results from the extracted-ion chromatograms ( Fig.…”
Section: Identification Of By-products: Proposal Of a Degradation Routementioning
confidence: 99%
“…To improve the efficiency of removal of pharmaceutical compounds in aqueous media, novel and powerful technologies have been developed, especially the so‐called advanced oxidation processes (AOPs). Moreover, there has been a growing interest in the detection and identification of degradation products resulting from the application of AOPs . Among the AOPs, the following processes are noteworthy: photolysis, photocatalysis, electrochemistry and photoelectrochemistry .…”
Section: Introductionmentioning
confidence: 99%
“…Moreover, there has been a growing interest in the detection and identification of degradation products resulting from the application of AOPs. [9,10] Among the AOPs, the following processes are noteworthy: photolysis, [11][12][13][14][15][16] photocatalysis, [17] electrochemistry and photoelectrochemistry. [18,19] However, many challenging issues still remain, which are mainly related to the fact that products arising from the degradation of pollutants may present higher toxicity than their predecessors.…”
The degradation of the pharmaceutical compound ibuprofen (IBP) in aqueous solution induced by direct photolysis (UV-A and UV-C radiation) and photocatalysis (TiO2 /UV-A and TiO2 /UV-C systems) was evaluated. Initially, we observed that whereas photocatalysis (both systems) and direct photolysis with UV-C radiation were able to cause an almost complete removal of IBP, the mineralization rates achieved for all the photodegradation processes were much smaller (the highest value being obtained for the TiO2 /UV-C system: 37.7%), even after an exposure time as long as 120 min. Chemical structures for the by-products formed under these oxidative conditions (11 of them were detected) were proposed based on the data from liquid chromatography coupled to high-resolution mass spectrometry (LC-HRMS) analyses. Taking into account these results, an unprecedented route for the photodegradation of IBP could thus be proposed. Moreover, a fortunate result was achieved herein: tests against Artemia salina showed that the degradation products had no higher ecotoxicities than IBP, which possibly indicates that the photocatalytic (TiO2 /UV-A and TiO2 /UV-C systems) and photolytic (UV-C radiation) processes can be conveniently employed to deplete IBP in aqueous media.
“…From the analysis of the obtained peaks identified by the value of m/z ratios, based on the molecular weight and the nature of the chemical bond in the molecule of DMA-P, the occurrence of transformation products can be confirmed, which is illustrated in Figure 7. The efficiency of LC-MS hyphenated techniques for the characterization of various photodegradation [30,31] products has been recently reported for chloracetamide herbicide acetochlor, which has similar structure as the investigated dimethenamide-P. HPLC/MS analysis of the reaction mixture after 10 minutes of the photocatalytic degradation, revealed the presence of one degradation product with m/z of 110.5. From the structural analysis of DMA-P it can be assumed that the cleavage of C-N bond occurred (path I) and that the dimethylthiophenyl cation has been formed, as shown in Figure 7.…”
Article Highlights • Photocatalytic degradation of dimethenamid-P herbicide is presented • Degradation was studied in deionised and ground water under different conditions • Photocatalytic degradation of dimethenamid-P is much faster in ground water • HPLC showed almost complete removal of herbicide after 90 min in both water • TOC showed herbicide was mineralized 64% in deionised and 50% in ground water
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