Formation of carbonaceous and nitrogenous disinfection by-products during monochloramination of oxytetracycline including N-Nitrosodimethylamine

被引:4
作者
Tian, Fu-xiang [1 ]
Xu, Bin [1 ]
Tian, Kang-ning [1 ]
Hu, Chen-yan [2 ]
Xia, Sheng-ji [1 ]
Gao, Nai-yun [1 ]
Ye, Tao [1 ]
机构
[1] Tongji Univ, Coll Environm Sci & Engn, State Key Lab Pollut Control & Resources Reuse, Key Lab Yangtze River Water Environm,Minist Educ, Shanghai 200092, Peoples R China
[2] Shanghai Univ Elect Power, Coll Environm & Chem Engn, Shanghai 200090, Peoples R China
关键词
N-Nitrosodimethylamine (NDMA); Nitrogenous disinfection by-products (N-DBPs); Oxytetracycline (OTC); Monochloramination; Carbonaceous disinfection by-products (C-DBPs); TRIHALOMETHANE FORMATION; VETERINARY ANTIBIOTICS; KINETICS; WATER; NDMA; DECOMPOSITION; PHARMACEUTICALS; CHLORINATION; PATHWAYS; BROMIDE;
D O I
10.1080/19443994.2014.899518
中图分类号
TQ [化学工业];
学科分类号
0817 ;
摘要
Formation of typical volatile carbonaceous and nitrogenous disinfection by-products (C-DBPs and N-DBPs) during aqueous monochloramination of oxytetracycline (OTC) was investigated in this study. Impact factors including reaction time, pH, monochloramine (NH2Cl) dosages, and bromide concentrations were examined. The results showed that six DBPs including chloroform, dichloroacetonitrile, trichloronitromethane, 1,1-dichloropropanone, 1,1,1-trichloropropanone, especially extreme toxic N-Nitrosodimethylamine were found. Formation of these DBPs increased over time and monochloramine dosages with maximum yields given as 14.2, 4.3, 0.8, 2.1, 0.7, and 4.1 mu g/mg at pH 7, respectively (mu g/mg represents DBPs yields per mg of OTC). Solution pH exerted significant influence on the formation of all the DBPs species. Peak yields were found under circumneutral conditions. Production of bromine-substituted DBPs increased in the presence of bromide. Removal of presented OTC in waters should be implemented before chloramination disinfection process in drinking water treatment.
引用
收藏
页码:2299 / 2306
页数:8
相关论文
共 42 条
[1]  
[Anonymous], 2010, OXIDATION PHARM PERS
[2]  
[Anonymous], 1995, 5511 USEPA
[3]  
[Anonymous], THESIS U MASSACHUSET
[4]  
APHA, 1998, Standard methods for the examination of water and wastewater, V20
[5]   Simultaneous analysis of multiple classes of antibiotics by ion trap LC/MS/MS for assessing surface water and groundwater contamination [J].
Batt, AL ;
Aga, DS .
ANALYTICAL CHEMISTRY, 2005, 77 (09) :2940-2947
[6]   Monochloramination of Oxytetracycline: Kinetics, Mechanisms, Pathways, and Disinfection By-Products Formation [J].
Bi, Xiangyu ;
Xu, Bin ;
Lin, Yi-Li ;
Hu, Chen-Yan ;
Ye, Tao ;
Qin, Cao .
CLEAN-SOIL AIR WATER, 2013, 41 (10) :969-975
[7]   RATE OF HYPOBROMITE FORMATION IN CHLORINATED SEAWATER [J].
BOUSHER, A ;
BRIMBLECOMBE, P ;
MIDGLEY, D .
WATER RESEARCH, 1986, 20 (07) :865-870
[8]   REACTION PATHWAYS OF TRIHALOMETHANE FORMATION FROM THE HALOGENATION OF DIHYDROXYAROMATIC MODEL COMPOUNDS FOR HUMIC-ACID [J].
BOYCE, SD ;
HORNIG, JF .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1983, 17 (04) :202-211
[9]   Behavior of pharmaceuticals, cosmetics and hormones in a sewage treatment plant [J].
Carballa, M ;
Omil, F ;
Lema, JM ;
Llompart, M ;
García-Jares, C ;
Rodríguez, I ;
Gómez, M ;
Ternes, T .
WATER RESEARCH, 2004, 38 (12) :2918-2926
[10]   Effects of bromide on the formation of THMs and HAAs [J].
Chang, EE ;
Lin, YP ;
Chiang, PC .
CHEMOSPHERE, 2001, 43 (08) :1029-1034