Department of Laboratory Medicine and Pathology, Division of Analytical and Environmental Toxicology, University of Alberta, Edmonton, Alberta, Canada.
Environ Sci Technol. 2011 Sep 1;45(17):7431-7. doi: 10.1021/es201575h. Epub 2011 Aug 2.
Large volumes of oil sands process-affected water (OSPW) are produced in northern Alberta by the surface mining oil sands industry. Naphthenic acids (NAs) are a complex mixture of persistent organic acids that are believed to contribute to the toxicity of OSPW. In situ microbial biodegradation strategies are slow and not effective at eliminating chronic aquatic toxicity, thus there is a need to examine alternative remediation techniques. NAs with multiple rings and alkyl branching are most recalcitrant to microbial biodegradation, but here we hypothesized that these same structural features may lead to preferential degradation in the ozonation process. Total NA degradation increased with increasing pH for commercial NA solutions, suggesting a hydroxyl radical mechanism and that naturally alkaline OSPW would unlikely require pH adjustment prior to treatment. For commercial NAs and OSPW, NAs with more rings and more carbon (and more H atoms) were depleted most rapidly in the process. Relative rate measurements with binary mixtures of model NA compounds not only confirmed this structure reactivity but also indicated that alkyl branching patterns were an additional factor determining NA reactivity. The results demonstrate that ozonation is complementary to microbial biodegradation, and the process remains a promising water reclamation strategy for the oil sands industry.
在加拿大北部,露天开采油砂矿产业产生了大量油砂加工影响水(OSPW)。环烷酸(NAs)是一种复杂的持久性有机酸混合物,据信是 OSPW 毒性的主要原因。原位微生物生物降解策略缓慢,无法有效消除慢性水生毒性,因此需要研究替代修复技术。具有多个环和烷基支链的 NAs 最难被微生物生物降解,但在这里我们假设这些相同的结构特征可能导致臭氧化过程中的优先降解。对于商业 NA 溶液,总 NA 降解随 pH 值的增加而增加,这表明存在羟基自由基机制,且天然碱性 OSPW 在处理前可能不需要调节 pH 值。对于商业 NAs 和 OSPW,具有更多环和更多碳原子(和更多 H 原子)的 NAs 在该过程中被最快耗尽。使用模型 NA 化合物的二元混合物进行的相对速率测量不仅证实了这种结构反应性,还表明烷基支化模式是决定 NA 反应性的另一个因素。结果表明,臭氧化是微生物生物降解的补充,该过程仍然是油砂工业的一种有前途的水回收策略。