Environmental Safety Department, Procter and Gamble Company, Ivorydale Technical Center, Cincinnati, Ohio 45217, and Department of Biology, University of Dayton, Dayton, Ohio 45469.
Appl Environ Microbiol. 1990 Feb;56(2):333-9. doi: 10.1128/aem.56.2.333-339.1990.
In wetlands and canopied bodies of water, plant detritus is an important source of carbon and energy. Detrital materials possess a large surface area for sorption of dissolved organics and are colonized by a large and diverse microbiota. To examine the biodegradation of surfactants by these microorganisms, submerged oak leaves were obtained from a laundromat wastewater pond, its overflow, and a pristine control pond. Leaves were cut into disks and incubated in sterile water amended with 50 mug of C-labeled linear alkylbenzene sulfonate (LAS), linear alcohol ethoxylate, stearyltrimethyl ammonium chloride, distearyldimethyl ammonium chloride, benzoic acid, or mixed amino acids per liter. Sorption of the test compounds to the detritus and evolution of CO(2) were followed with time. All of the compounds sorbed to the detritus to various degrees, with LAS and stearyltrimethyl ammonium chloride the most sorptive and benzoic acid the least. All compounds were mineralized without a lag. With leaves from the laundromat wastewater pond, half-lives were 12.6 days for LAS, 8.4 days for linear alcohol ethoxylate, 14.2 days for stearyltrimethyl ammonium chloride, 1.0 days for benzoic acid, and 2.7 days for mixed amino acids. Mineralization of LAS and linear alcohol ethoxylate by control pond leaves was slower and exhibited an S-shaped rather than a typical first-order pattern. This study shows that detritus represents a significant site of surfactant removal in detritus-rich systems.
在湿地和树冠水体中,植物碎屑是碳和能量的重要来源。碎屑物质具有很大的表面积,可用于吸附溶解有机物,并被大量多样的微生物区系所定植。为了研究这些微生物对表面活性剂的生物降解作用,从洗衣房废水池塘、其溢流水和原始对照池塘中获取了浸没的橡树叶。将叶子切成圆盘,在无菌水中培养,水中添加 50 微克的 C 标记的直链烷基苯磺酸盐(LAS)、直链醇乙氧基化物、硬脂基三甲基氯化铵、双硬脂基二甲基氯化铵、苯甲酸或混合氨基酸/升。随着时间的推移,追踪测试化合物对碎屑的吸附和 CO2 的演化。所有化合物都不同程度地吸附在碎屑上,其中 LAS 和硬脂基三甲基氯化铵的吸附性最强,苯甲酸的吸附性最弱。所有化合物都没有滞后地被矿化。对于来自洗衣房废水池塘的叶子,LAS 的半衰期为 12.6 天,直链醇乙氧基化物的半衰期为 8.4 天,硬脂基三甲基氯化铵的半衰期为 14.2 天,苯甲酸的半衰期为 1.0 天,混合氨基酸的半衰期为 2.7 天。对照池塘叶子中 LAS 和直链醇乙氧基化物的矿化速度较慢,表现出 S 形而不是典型的一级模式。这项研究表明,在富含碎屑的系统中,碎屑代表了表面活性剂去除的重要场所。