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在中性pH条件下使用零价铁(Fe0)对阿特拉津进行脱氯处理。

Dechlorination of atrazine using zero-valent iron (Fe0) under neutral pH conditions.

作者信息

Kim Geonha, Jeong Woohyeok, Choe Seunghee

机构信息

Department of Civil and Environmental Engineering, Hannam University, Ojungdong, Daejon 306-791, Republic of Korea.

出版信息

J Hazard Mater. 2008 Jul 15;155(3):502-6. doi: 10.1016/j.jhazmat.2007.11.092. Epub 2007 Nov 29.

DOI:10.1016/j.jhazmat.2007.11.092
PMID:18329167
Abstract

Zero-valent iron (Fe0) is frequently used for the dechlorination of pesticides, because it is economical, easily acquired and stable. The kinetics of dechlorination by Fe0 are improved at low pH, but this requires additional acid addition, while dechlorination hardly occurs under basic conditions. Due to the buffer capacity of geological materials such as clay and sediment, however, the addition of acid to obtain a low pH may not be effective. In this research, the dechlorination constants of atrazine by Fe0 were measured with the addition of buffer solution to simulate the buffer capacity of sediment. In the presence of the buffer solution, the pH values remained neutral, while dechlorination occurred more slowly than that observed under acid additions but faster than that without any buffer. When the initial concentrations of atrazine were 10mg/L, 30 mg/L, and 50mg/L, its dechlorination was explained using pseudo-first order reaction kinetics. The pseudo-first order constants were 3.01 x 10(-2)d(-1) at 10 mg/L, 3.23 x 10(-2)d(-1) at 30 mg/L and 3.38 x 10(-2)d(-1) at 50mg/L. In addition, the half-lives of atrazine were 8.91 d at 10mg/L, 9.32 d at 30 mg/L, and 10.00 d at 50mg/L. Acid addition may not be omitted to obtain acidic pH conditions when dechlorination is necessary in geologic materials.

摘要

零价铁(Fe0)因其经济、易获取且稳定,常被用于农药的脱氯处理。Fe0脱氯的动力学在低pH值时有所改善,但这需要额外添加酸,而在碱性条件下脱氯几乎不会发生。然而,由于粘土和沉积物等地质材料的缓冲能力,添加酸以获得低pH值可能并不有效。在本研究中,通过添加缓冲溶液来模拟沉积物的缓冲能力,测定了Fe0对阿特拉津的脱氯常数。在缓冲溶液存在的情况下,pH值保持中性,虽然脱氯比在添加酸的情况下发生得更慢,但比不添加任何缓冲剂时更快。当阿特拉津的初始浓度分别为10mg/L、30mg/L和50mg/L时,其脱氯过程用准一级反应动力学来解释。准一级常数在10mg/L时为3.01×10(-2)d(-1),在30mg/L时为3.23×10(-2)d(-1),在50mg/L时为3.38×10(-2)d(-1)。此外,阿特拉津在10mg/L时的半衰期为8.91天,在30mg/L时为9.32天,在50mg/L时为10.00天。在地质材料中进行脱氯处理时,如果有必要获得酸性pH条件,酸的添加可能无法省略。

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