Oxidation of salicylic acid in water by the O3 and UV/O3 processes : removal and reaction byproducts

In this study, the removal of salicylic acid (SA) in water by ozone (O3) and ultraviolet/ozone (UV/O3) processes was investigated. Results showed that more than 50% of SA (10 mg/L) could be effectively removed after 1 min during these two processes. However, the UV/O3 process was much more effective...

Ausführliche Beschreibung

Bibliographische Detailangaben
Veröffentlicht in:Water science and technology : a journal of the International Association on Water Pollution Research. - 1986. - 81(2020), 4 vom: 11. Feb., Seite 753-762
1. Verfasser: Jing, Chang (VerfasserIn)
Weitere Verfasser: Shaopo, Wang, Yaxue, Zhang, Yibo, Wang, Wenjuan, Zhang, Jinfeng, Lu, Zhe, Wang
Format: Online-Aufsatz
Sprache:English
Veröffentlicht: 2020
Zugriff auf das übergeordnete Werk:Water science and technology : a journal of the International Association on Water Pollution Research
Schlagworte:Journal Article Water Pollutants, Chemical Water 059QF0KO0R Ozone 66H7ZZK23N Hydrogen Peroxide BBX060AN9V Salicylic Acid O414PZ4LPZ
LEADER 01000caa a22002652c 4500
001 NLM310422213
003 DE-627
005 20250227082451.0
007 cr uuu---uuuuu
008 231225s2020 xx |||||o 00| ||eng c
024 7 |a 10.2166/wst.2020.155  |2 doi 
028 5 2 |a pubmed25n1034.xml 
035 |a (DE-627)NLM310422213 
035 |a (NLM)32460278 
040 |a DE-627  |b ger  |c DE-627  |e rakwb 
041 |a eng 
100 1 |a Jing, Chang  |e verfasserin  |4 aut 
245 1 0 |a Oxidation of salicylic acid in water by the O3 and UV/O3 processes  |b removal and reaction byproducts 
264 1 |c 2020 
336 |a Text  |b txt  |2 rdacontent 
337 |a ƒaComputermedien  |b c  |2 rdamedia 
338 |a ƒa Online-Ressource  |b cr  |2 rdacarrier 
500 |a Date Completed 29.05.2020 
500 |a Date Revised 15.12.2020 
500 |a published: Print 
500 |a Citation Status MEDLINE 
520 |a In this study, the removal of salicylic acid (SA) in water by ozone (O3) and ultraviolet/ozone (UV/O3) processes was investigated. Results showed that more than 50% of SA (10 mg/L) could be effectively removed after 1 min during these two processes. However, the UV/O3 process was much more effective than the O3 process for SA mineralization, and the total organic carbon reduction after 30 min was 69.5% and 28.1%, respectively. In the two processes, the optimum pH value for SA removal was 4.3, while that for SA mineralization was 10.0. Both bicarbonate and dissolved organic carbon significantly inhibited SA removal during the two processes. Eleven oxidation byproducts were detected in O3 process, but only four byproducts were observed in UV/O3 process. Three hydroxylation aromatic products were identified as the initial byproducts during SA degradation. Glyoxylic acid monohydrate, glycolic acid, and oxalic acid were accumulated in O3 process but not observed in UV/O3 process. Oxalic acid was the only detected small molecular byproduct in UV/O3 process, and it could be further mineralized, thereby indicating that UV/O3 had a greater potential for degrading both SA and its reaction byproducts 
650 4 |a Journal Article 
650 7 |a Water Pollutants, Chemical  |2 NLM 
650 7 |a Water  |2 NLM 
650 7 |a 059QF0KO0R  |2 NLM 
650 7 |a Ozone  |2 NLM 
650 7 |a 66H7ZZK23N  |2 NLM 
650 7 |a Hydrogen Peroxide  |2 NLM 
650 7 |a BBX060AN9V  |2 NLM 
650 7 |a Salicylic Acid  |2 NLM 
650 7 |a O414PZ4LPZ  |2 NLM 
700 1 |a Shaopo, Wang  |e verfasserin  |4 aut 
700 1 |a Yaxue, Zhang  |e verfasserin  |4 aut 
700 1 |a Yibo, Wang  |e verfasserin  |4 aut 
700 1 |a Wenjuan, Zhang  |e verfasserin  |4 aut 
700 1 |a Jinfeng, Lu  |e verfasserin  |4 aut 
700 1 |a Zhe, Wang  |e verfasserin  |4 aut 
773 0 8 |i Enthalten in  |t Water science and technology : a journal of the International Association on Water Pollution Research  |d 1986  |g 81(2020), 4 vom: 11. Feb., Seite 753-762  |w (DE-627)NLM098149431  |x 0273-1223  |7 nnas 
773 1 8 |g volume:81  |g year:2020  |g number:4  |g day:11  |g month:02  |g pages:753-762 
856 4 0 |u http://dx.doi.org/10.2166/wst.2020.155  |3 Volltext 
912 |a GBV_USEFLAG_A 
912 |a SYSFLAG_A 
912 |a GBV_NLM 
912 |a GBV_ILN_350 
951 |a AR 
952 |d 81  |j 2020  |e 4  |b 11  |c 02  |h 753-762