Effects and mechanism on the removal of neurotoxin β-N-methylamino-L-alanine (BMAA) by chlorination

被引:4
|
作者
Yan, Boyin [1 ]
Liu, Zhiquan [1 ,2 ]
Liu, Ying [1 ]
Huang, Rui [1 ]
Xu, Yongpeng [1 ]
Liu, Dongmei [1 ]
Cui, Fuyi [3 ]
Shi, Wenxin [3 ]
机构
[1] Harbin Inst Technol, State Key Lab Urban Water Resource & Environm, Harbin 150090, Peoples R China
[2] Guangzhou Univ, Minist Educ, Key Lab Water Qual & Conservat Pearl River Delta, Inst Environm Res Greater Bay, Guangzhou 510006, Peoples R China
[3] Chongqing Univ, Sch Environm & Ecol, Chongqing 400044, Peoples R China
基金
中国国家自然科学基金;
关键词
BMAA; Kinetic model; Rate of constants; Reaction pathway; CYANOBACTERIAL NEUROTOXIN; REACTION PATHWAYS; DRINKING-WATER; AMINO-ACIDS; KINETICS; CYANOTOXINS; SHELLFISH; TOXICITY; PRODUCTS; TOXINS;
D O I
10.1016/j.scitotenv.2019.135513
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
beta-N-Methylamino-t-alanine (BMAA), a new cyanobacterial toxin, is found in different aquatic ecosystems world-wide and is to threaten the human nervous system. Therefore, it is important for water plants to develop feasible methods to counter the effects of BMAA. In this study, the removal of BMAA by chlorine, as well as its intermediate products, at different pH values and the mechanism of pH on the removal BMAA were investigated. The results showed that the chlorination of BMAA is in accordance with the second-order kinetics model. The reaction rate of chlorinated BMAA increased with the increase in the concentration of chlorine. The pH of the solution significantly affected the reaction rate. The apparent kinetic constant (k(app)) decreased from 6.00 x 10(3) M-1 . min(-1) to 35.5 M-1 . min(-1) when the pH increased from 4.5 to 9 in the chlorine concentration of 32.23 mu M. It is probable that the species distribution and proportion of BMAA and chlorine at different pH values were the main causes of this phenomenon. Additionally, the chlorination reaction consisted of four elementary reactions and hydrogen ions were beneficial to the reaction. The temperature also affected the reaction rate and the activation energy of the reaction was 16.6 +/- 1.99 kJ . M-1. A variety of degradation products were detected and the path of degradation was speculated. Chlorination, dechlorination, and decarboxylation were the main processes of oxidative degradation. Furthermore, the composition of the degradation products was the same at different pH values. (C) 2019 Published by Elsevier B.V.
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页数:8
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