Xue Jinkai, Zhang Yanyan, Liu Yang, Gamal El-Din Mohamed
Department of Civil and Environmental Engineering, University of Alberta, Edmonton, AB, T6G 1H9, Canada.
Biodegradation. 2016 Nov;27(4-6):247-264. doi: 10.1007/s10532-016-9770-9. Epub 2016 Aug 24.
Batch experiments were performed to evaluate biodegradation of raw and ozonated oil sands process-affected water (OSPW) under denitrifying anoxic and nitrifying aerobic conditions for 33 days. The results showed both the anoxic and aerobic conditions are effective in degrading OSPW classical and oxidized naphthenic acids (NAs) with the aerobic conditions demonstrating higher removal efficiency. The reactors under nitrifying aerobic condition reduced the total classical NAs of raw OSPW by 69.1 %, with better efficiency for species of higher hydrophobicity. Compared with conventional aerobic reactor, nitrifying aerobic condition substantially shortened the NA degradation half-life to 16 days. The mild-dose ozonation remarkably accelerated the subsequent aerobic biodegradation of classical NAs within the first 14 days, especially for those with long carbon chains. Moreover, the ozone pretreatment enhanced the biological removal of OSPW classical NAs by leaving a considerably lower final residual concentration of 10.4 mg/L under anoxic conditions, and 5.7 mg/L under aerobic conditions. The combination of ozonation and nitrifying aerobic biodegradation removed total classical NAs by 76.5 % and total oxy-NAs (O3-O6) by 23.6 %. 454 Pyrosequencing revealed that microbial species capable of degrading recalcitrant hydrocarbons were dominant in all reactors. The most abundant genus in the raw and ozonated anoxic reactors was Thauera (56 % in the raw OSPW anoxic reactor, and ~65 % in the ozonated OSPW anoxic reactor); whereas Rhodanobacter (40 %) and Pseudomonas (~40 %) dominated the raw and ozonated aerobic reactors, respectively. Therefore, the combination of mild-dose ozone pretreatment and subsequent biological process could be a competent choice for OSPW treatment.
进行了批次实验,以评估在反硝化缺氧和硝化好氧条件下,原油砂工艺影响水(OSPW)和臭氧化油砂工艺影响水的生物降解情况,实验持续33天。结果表明,缺氧和好氧条件均能有效降解OSPW中的经典环烷酸和氧化环烷酸(NAs),其中好氧条件下的去除效率更高。硝化好氧条件下的反应器使原OSPW中经典NAs的总量降低了69.1%,对疏水性更强的种类去除效率更高。与传统好氧反应器相比,硝化好氧条件显著缩短了NA降解半衰期至16天。轻度剂量的臭氧化显著加速了前14天内经典NAs的后续好氧生物降解,尤其是对于那些具有长碳链的NAs。此外,臭氧预处理提高了OSPW中经典NAs的生物去除率,在缺氧条件下最终残留浓度低至10.4mg/L,在好氧条件下为5.7mg/L。臭氧化与硝化好氧生物降解相结合,去除了76.5%的总经典NAs和23.6%的总氧化NAs(O3 - O6)。454焦磷酸测序显示,所有反应器中能够降解难降解烃类的微生物种类占主导地位。原缺氧反应器和臭氧化缺氧反应器中最丰富的属是陶厄氏菌属(原OSPW缺氧反应器中约占56%,臭氧化OSPW缺氧反应器中约占65%);而红杆菌属(约40%)和假单胞菌属(约40%)分别在原好氧反应器和臭氧化好氧反应器中占主导地位。因此,轻度剂量臭氧预处理与后续生物处理相结合可能是处理OSPW的有效选择。