Guo Yang, Lin Qiaoxin, Xu Bingbing, Qi Fei
Beijing Key Lab for Source Control Technology of Water Pollution, College of Environmental Science and Engineering, Beijing Forestry University, Beijing, 100083, People's Republic of China.
State Key Laboratory of Environmental Criteria and Risk Assessment, Chinese Research Academy of Environmental Sciences, Beijing, 100012, People's Republic of China.
Environ Sci Pollut Res Int. 2016 Apr;23(8):7962-74. doi: 10.1007/s11356-015-5941-1. Epub 2016 Jan 15.
Benzophenone-3 (BP-3) is a popular ultraviolet absorbing chemical and has an adverse impact on aquatic ecosystems and human health. We determined the reaction kinetic constants of BP-3 and its de-proton pattern reacting with the molecular ozone or hydroxyl radical (·OH) for the first time. The obtained constant of the molecular ozone reacting with BP-3 or BP-3(-) was 1.03(±0.21) × 10(2) or 1.85(±0.098) × 10(5) M(-1) s(-1), respectively. And, the constant for BP-3 reacting with ·OH was 9.74(±0.21) × 10(9) or 10.13(±0.25) × 10(9) M(-1) s(-1) as using 4-chlorobenzoic acid and benzotriazole as reference compounds, respectively. The intermediates generated in the molecular ozone (12 kinds) or ·OH oxidation (18 kinds) were identified by LC-MS/MS. The removal efficiency of BP-3 in ozonation was dependent on the initial concentration of ozone, BP-3, and matrix water quality. The detoxification of BP-3 ozonation was depended on initial ozone dose using Chlorella vulgaris as the probe. Higher ozone dose increased the toxicity of the solution for more BP-3 being degraded and more intermediates formed, suggesting that the sole ozonation is not an effect approach for the degradation of BP-3 and some other energy should be combined.
二苯甲酮 - 3(BP - 3)是一种常用的紫外线吸收剂,对水生生态系统和人类健康具有不利影响。我们首次测定了BP - 3及其去质子化形式与分子态臭氧或羟基自由基(·OH)反应的动力学常数。所得到的分子态臭氧与BP - 3或BP - 3(-)反应的常数分别为1.03(±0.21)×10(2)或1.85(±0.098)×10(5) M(-1) s(-1)。并且,分别以4 - 氯苯甲酸和苯并三唑作为参考化合物时,BP - 3与·OH反应的常数为9.74(±0.21)×10(9)或10.13(±0.25)×10(9) M(-1) s(-1)。通过液相色谱 - 串联质谱(LC - MS/MS)鉴定了分子态臭氧氧化(12种)或·OH氧化(18种)过程中产生的中间体。BP - 3在臭氧化过程中的去除效率取决于臭氧、BP - 3的初始浓度以及基质水质。以小球藻为探针,BP - 3臭氧化的解毒作用取决于初始臭氧剂量。较高的臭氧剂量会增加溶液的毒性,因为更多的BP - 3被降解且形成了更多的中间体,这表明单纯的臭氧化不是降解BP - 3的有效方法,应该结合其他能量。