线性烷基苯磺酸盐及其与阳离子表面活性剂配合物在河流沉积物上的吸附及其在河流水体中的生物降解

Akiko Utsunomiya, Y. Mori, Kazuo Hasegawa
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引用次数: 10

摘要

为了了解线性烷基苯磺酸盐(LAS)及其配合物(LAS-CS)与阳离子表面活性剂(CS)、烷基三甲基氯化铵(TM)和二烷基二甲基氯化铵(DM)在水生环境中的行为,研究了LAS-CS的形成、在河流沉积物上的吸附以及在河流水中的初级生物降解。LAS-CS的生成在30分钟内达到平衡,pH和反应温度对LAS-CS的生成没有影响。证实了LAS与TM和DM分别以1:1 ~ 6:1和1:1 ~ 2:1的摩尔比形成了LAS- cs。在摩尔比为1:1和2:1时,LAS和LAS- cs与TM或DM的吸附等温线符合Freundlich方程。LAS- cs的吸附量小于LAS。其排列顺序为LAS>LAS- tm >2LAS-TM>LAS- dm >2LAS-DM。LAS、LAS- tm和2LAS-TM的吸附量随LAS的烷基链长度的增加而增加,而LAS- dm和2LAS-DM的吸附量随烷基链长度的增加而变化不大。与TM和DM的摩尔比为1:1和2:1时,LAS- cs的初级生物降解速率比LAS慢。14 d生物降解率依次为LAS (100%)>2LAS-TM (56%)>LAS- tm (36%)>2LAS-DM (31%)>LAS- dm(29%)。LAS和LAS- cs的生物降解也随着LAS烷基链长度的增加而降低。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Adsorption of Linear Alkylbenzenesulfonates and Their Complexes with Cationic Surfactants on River Sediment, and Their Biodegradation in River Water
In order to know the behavior of linear alkylbenznesulfonate (LAS) and their complexes (LAS-CS) with cationic surfactants (CS), alkyltrimethylammonium chloride (TM) and dialkyldimethylammonium chloride (DM), in the aquatic environment, the formation of LAS-CS, their adsorption on the river sediment and primary biodegradation in the river water were studied. The formation of LAS-CS reached to the equilibrium within thirty minutes, and no effects of pH and reaction temperature were observed. It was confirmed that LAS formed LAS-CS with TM and DM at molar ratios from 1 : 1 to 6 : 1 and from 1 : 1 to 2 : 1, respectively. The adsorption isotherms of LAS and LAS-CS with TM or DM at molar ratios of 1 : 1 and 2 : 1 followed to the Freundlich's equations. The adsorption capacities of LAS-CS were smaller than that of LAS. Their order was LAS>LAS-TM>2LAS-TM>LAS-DM>2LAS-DM. The adsorption capacities of LAS, LAS-TM and 2LAS-TM increased with increasing the alkyl chain length of LAS, whereas those of LAS-DM and 2LAS-DM showed little variation among the alkyl chain length homologues. The primary biodegradation rates of LAS-CS with TM or DM at molar ratios of 1 : 1 and 2 : 1 were slower than that of LAS. Their order of biodegradation (% decreased during 14 days) was LAS (100%)>2LAS-TM (56%)>LAS-TM (36%)>2LAS-DM (31%)>LAS-DM (29%). The biodegradation of LAS and LAS-CS also decreased with increasing the alkyl chain length of LAS.
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