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Hydroxyl and sulfate radical-based degradation of ciprofloxacin using UV-C and/or Fe2+-catalyzed peroxymonosulfate: Effects of process parameters and toxicity evaluation
被引:12
作者:
Iqbal, Jibran
[1
]
Shah, Noor S.
[2
]
Khan, Javed Ali
[3
]
Khan, Kifayatullah
[4
]
Wakeel, Muhammad
[2
]
Abdelghani, Heba Taha M.
[5
]
Khan, Zia Ul Haq
[6
]
Boczkaj, Grzegorz
[7
,8
]
机构:
[1] Zayed Univ, Coll Interdisciplinary Studies, Abu Dhabi 144534, U Arab Emirates
[2] COMSATS Univ Islamabad, Dept Environm Sci, Vehari Campus, Islamabad 61100, Pakistan
[3] Abdul Wali Khan Univ, Dept Chem, Mardan 23200, Pakistan
[4] Univ Swat, Dept Environm & Conservat Sci, Swat 19120, Pakistan
[5] King Saud Univ, Coll Sport Sci & Phys Act, Dept Physiol Phys Act, Riyadh 11451, Saudi Arabia
[6] COMSATS Univ Islamabad, Dept Chem, Pk Rd, Islamabad 45550, Pakistan
[7] Gdansk Univ Technol, Fac Civil & Environm Engn, Dept Sanit Engn, G Narutowicza St 11-12, PL-80233 Gdansk, Poland
[8] Gdansk Univ Technol, EkoTech Ctr, G Narutowicza St 11-12, PL-80233 Gdansk, Poland
关键词:
Advanced oxidation technologies;
Ciprofloxacin;
Environmental sustainability;
PMS;
Degradation mechanism;
Water treatment;
AQUEOUS-SOLUTION;
PHOTOCHEMICAL DEGRADATION;
FENTON OXIDATION;
ACTIVATION;
PERSULFATE;
KINETICS;
H2O2;
IRON;
ANTIBIOTICS;
ENDOSULFAN;
D O I:
10.1016/j.jphotochem.2023.115246
中图分类号:
O64 [物理化学(理论化学)、化学物理学];
学科分类号:
070304 ;
081704 ;
摘要:
Ciprofloxacin (CIP) is a valuable antibiotic and discharged in huge quantities in aquatic environment. Different (OH)-O-center dot and SO4 center dot--based advanced oxidation technologies (AOTs), e.g., Fe2+/PMS, UV-C/PMS, and UV-C/Fe2+/PMS are developed for treatment of CIP. The removal of CIP by Fe2+/PMS, UV-C/PMS and UV-C/Fe2+/PMS was 63, 77, and 87 %, respectively, under identical conditions which showed better performance of UV-C/Fe2+/PMS. The UV-C/Fe2+/PMS also caused high removal of total organic carbon of CIP. This high performance of UV-C/Fe2+/PMS-based AOTs possibly looked due to dual activation of PMS by UV-C and Fe2+. The removal of CIP by the three AOTs was found due to (OH)-O-center dot and SO4 center dot- and the later showed high reactivities with CIP, i.e., 2.45 x 10(9) and 2.35 x 10(9) M-1 s(-1), respectively. The study of factors affecting the reactivities and/or yield of (OH)-O-center dot and SO4 center dot- diminished CIP degradation efficiency. The change in pH of solution and temperature and doses of Fe2+, PMS, and CIP exhibited significant impacts on the removal of CIP. The addition of inorganic ions showed strong inhibiting effects of NO2-, CO32-, and HCO3- while Cu2+ showed facilitating role. Analysis of degradation of CIP by GC-MS was used to develop proposed pathways. Acute and chronic toxicities of CIP and its products were measured by ECOSAR program and showed the resulting products to be non-toxic.
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