MOE Key Laboratory of Pollution Processes and Environmental Criteria, Nankai University, Tianjin, China.
Chemosphere. 2013 Jan;90(2):203-9. doi: 10.1016/j.chemosphere.2012.06.035. Epub 2012 Jul 26.
The 6:2 FTOH [F(CF(2))(6)CH(2)CH(2)OH] is a major raw material being used to replace 8:2 FTOH [F(CF(2))(8)CH(2)CH(2)OH] to make FTOH-based products for industrial and consumer applications. A novel aerobic sediment experimental system containing 20 g wet sediment and 30 mL aqueous solution was developed to study 6:2 FTOH biotransformation in river sediment. 6:2 FTOH was dosed into the sediment to follow its biotransformation and to analyze transformation products over 100 d. The primary 6:2 FTOH biotransformation in the aerobic sediment system was rapid (T(1/2)<2d). 5:3 acid [F(CF(2))(5)CH(2)CH(2)COOH] was observed as the predominant polyfluorinated acid on day 100 (22.4 mol%), higher than the sum of perfluoropentanoic acid (10.4 mol%), perfluorohexanoic acid (8.4 mol%), and perfluorobutanoic acid (1.5 mol%). Perfluoroheptanoic acid was not observed during 6:2 FTOH biotransformation. The 5:3 acid can be further degraded to 4:3 acid [F(CF(2))(4)CH(2)CH(2)COOH, 2.7 mol%]. This suggests that microbes in the river sediment selectively degraded 6:2 FTOH more toward 5:3 and 4:3 acids compared with soil. Most of the observed 5:3 acid formed bound residues with sediment organic components and can only be quantitatively recovered by post-treatment with NaOH and ENVI-Carb™ carbon. The 6:2 FTCA [F(CF(2))(6)CH(2)COOH], 6:2 FTUCA [F(CF(2))(5)CF=CHCOOH], 5:2 ketone [F(CF(2))(5)C(O)CH(3)], and 5:2 sFTOH [F(CF(2))(5)CH(OH)CH(3)] were major transient intermediates during 6:2 FTOH biotransformation in the sediment system. These results suggest that if 6:2 FTOH or 6:2 FTOH-based materials were released to the river or marine sediment, poly- and per-fluorinated carboxylates could be produced.
6:2 FTOH[F(CF2)(6)CH2CH2OH]是一种主要的原料,用于替代 8:2 FTOH[F(CF2)(8)CH2CH2OH],以制造用于工业和消费应用的 FTOH 基产品。开发了一种新型的好氧沉积物实验系统,该系统含有 20g 湿沉积物和 30mL 水溶液,用于研究河流沉积物中 6:2 FTOH 的生物转化。将 6:2 FTOH 加入沉积物中,以跟踪其生物转化并在 100 天内分析转化产物。好氧沉积物系统中 6:2 FTOH 的主要生物转化非常迅速(T1/2<2d)。在第 100 天观察到 5:3 酸[F(CF2)(5)CH2CH2COOH]是主要的多氟羧酸(22.4mol%),高于全氟戊酸(10.4mol%)、全氟己酸(8.4mol%)和全氟丁酸(1.5mol%)的总和。在 6:2 FTOH 生物转化过程中未观察到全氟庚酸。5:3 酸可以进一步降解为 4:3 酸[F(CF2)(4)CH2CH2COOH,2.7mol%]。这表明与土壤相比,河流沉积物中的微生物更有选择性地将 6:2 FTOH 降解为 5:3 和 4:3 酸。形成的大部分 5:3 酸与沉积物有机成分结合形成结合残留,只能通过用 NaOH 和 ENVI-Carb™碳进行后处理才能定量回收。6:2 FTCA[F(CF2)(6)CH2COOH]、6:2 FTUCA[F(CF2)(5)CF=CHCOOH]、5:2 酮[F(CF2)(5)C(O)CH3]和 5:2 sFTOH[F(CF2)(5)CH(OH)CH3]是 6:2 FTOH 在沉积物系统中生物转化过程中的主要瞬态中间产物。这些结果表明,如果 6:2 FTOH 或基于 6:2 FTOH 的材料释放到河流或海洋沉积物中,可能会产生多氟和全氟羧酸酯。