Marchesi J R, Owen S A, White G F, House W A, Russell N J
School of Molecular and Medical Biosciences, Biochemistry Unit, University of Wales, Cardiff, UK.
Microbiology (Reading). 1994 Nov;140 ( Pt 11):2999-3006. doi: 10.1099/13500872-140-11-2999.
A laboratory-scale river microcosm was used to investigate the effect of the anionic surfactant sodium dodecyl sulphate (SDS) on the attachment of five Pseudomonas strains to natural river-sediment surfaces. Three of the Pseudomonas strains were chosen for their known ability to express alkylsulphatase enzymes capable of hydrolysing SDS, and the other two for their lack of such enzymes. One strain from each category was isolated from the indigenous bacterial population present in the river sediment used; other isolates were from soil or sewage. The alkylsulphatase phenotypes were confirmed by gel zymography of cell extracts. Addition of SDS to mixed suspensions of river sediment with any one of the biodegradation-competent strains stimulated the attachment of bacteria to the sediment particles. In contrast, the attachment of biodegradation-incompetent strains was weak and, moreover, was unaffected by SDS. The SDS-stimulated attachment for competent organisms coincided with rapid biodegradation of the surfactant. The primary intermediate of SDS biodegradation, dodecan-1-ol, accumulated transiently, and the numbers of attached bacteria correlated closely with the amount of dodecan-1-ol present. Direct addition of dodecan-1-ol also stimulated attachment but the effect was more immediate compared with SDS, when there was a lag period of approximately 2 h. To account for these observations, a model is proposed in which SDS stimulates the attachment of biodegradation-competent bacteria through its conversion to dodecan-1-ol, and it is hypothesized that the observed reversibility of the attachment is due to the subsequent removal of dodecan-1-ol by further bacterial metabolism.
采用实验室规模的河流微观系统,研究阴离子表面活性剂十二烷基硫酸钠(SDS)对5株假单胞菌附着于天然河流沉积物表面的影响。选择其中3株假单胞菌是因为它们已知能够表达可水解SDS的烷基硫酸酯酶,另外2株则缺乏这种酶。每类菌株中的一株是从所用河流沉积物中的本地细菌群体中分离得到的;其他菌株分离自土壤或污水。通过对细胞提取物进行凝胶酶谱分析来确认烷基硫酸酯酶表型。向含有任何一种具有生物降解能力菌株的河流沉积物混合悬浮液中添加SDS,会刺激细菌附着于沉积物颗粒。相比之下,缺乏生物降解能力的菌株的附着较弱,而且不受SDS影响。SDS刺激具有生物降解能力的生物体附着,这与表面活性剂的快速生物降解同时发生。SDS生物降解的主要中间产物十二烷-1-醇会短暂积累,附着细菌的数量与十二烷-1-醇的含量密切相关。直接添加十二烷-1-醇也会刺激附着,但与SDS相比,其效果更迅速,SDS存在约2小时的滞后期。为了解释这些观察结果,提出了一个模型,其中SDS通过转化为十二烷-1-醇来刺激具有生物降解能力的细菌附着,并推测观察到的附着可逆性是由于随后细菌进一步代谢去除了十二烷-1-醇。