Meshref Mohamed N A, Klamerth Nikolaus, Islam Md Shahinoor, McPhedran Kerry N, Gamal El-Din Mohamed
Department of Civil and Environmental Engineering, University of Alberta, Edmonton, Alberta, T6G 1H9, Canada.
Department of Civil and Environmental Engineering, University of Alberta, Edmonton, Alberta, T6G 1H9, Canada; Department of Hydrogeology, Freiberg University of Mining and Technology, Freiberg, Saxony, Germany.
Chemosphere. 2017 Aug;180:149-159. doi: 10.1016/j.chemosphere.2017.03.113. Epub 2017 Mar 30.
Ozonation at high doses is a costly treatment for oil sands process-affected water (OSPW) naphthenic acids (NAs) degradation. To decrease costs and limit doses, different peroxone (hydrogen peroxide/ozone; HO:O) processes using mild-ozone doses of 30 and 50 mg/L were investigated. The degradation efficiency of O-NAs (classical (O-NAs) + oxidized NAs) improved from 58% at 30 mg/L ozone to 59%, 63% and 76% at peroxone (1:1), 50 mg/L ozone, and peroxone (1:2), respectively. Suppressing the hydroxyl radical (•OH) pathway by adding tert-butyl alcohol did significantly reduce the degradation in all treatments, while molecular ozone contribution was around 50% and 34% for O-NAs and O-NAs, respectively. Structure reactivity toward degradation was observed with degradation increase for both O-NAs and O-NAs with increase of both carbon (n) and hydrogen deficiency/or |-Z| numbers in all treatments. However, the combined effect of n and Z showed specific insights and differences between ozone and peroxone treatments. The degradation pathway for |-Z|≥10 isomers in ozone treatments through molecular ozone was significant compared to •OH. Though peroxone (1:2) highly reduced the fluorophore organics and toxicity to Vibrio fischeri, the best oxidant utilization in the degradation of O-NAs (mg/L) per ozone dose (mg/L) was observed in the peroxone (1:1) (0.91) and 30 mg/L ozone treatments (0.92). At n = 9-11, peroxone (1:1) had similar or enhanced effect on the O-NAs degradation compared to 50 mg/L ozone. Enhancing •OH pathway through peroxone versus ozone may be an effective OSPW treatment that will allow its safe release into receiving environments with marginal cost addition.
高剂量臭氧氧化是一种成本高昂的处理油砂工艺影响水(OSPW)中环烷酸(NAs)降解的方法。为了降低成本并限制剂量,研究了使用30和50mg/L低剂量臭氧的不同过氧单硫酸盐(过氧化氢/臭氧;HO:O)工艺。O-NAs(经典(O-NAs)+氧化NAs)的降解效率从30mg/L臭氧时的58%分别提高到过氧单硫酸盐(1:1)时的59%、50mg/L臭氧时的63%和过氧单硫酸盐(1:2)时的76%。通过添加叔丁醇抑制羟基自由基(•OH)途径确实显著降低了所有处理中的降解,而分子臭氧对O-NAs和O-NAs的贡献分别约为50%和34%。在所有处理中,随着碳(n)和氢缺陷数或|-Z|数的增加,O-NAs和O-NAs的降解均增加,观察到结构对降解的反应性。然而,n和Z的综合效应显示了臭氧和过氧单硫酸盐处理之间的特定见解和差异。与•OH相比,臭氧处理中|-Z|≥10异构体通过分子臭氧的降解途径更为显著。尽管过氧单硫酸盐(1:2)极大地降低了荧光团有机物和对费氏弧菌的毒性,但在过氧单硫酸盐(1:1)(0.91)和30mg/L臭氧处理(0.92)中观察到每臭氧剂量(mg/L)降解O-NAs(mg/L)时最佳的氧化剂利用率。在n = 9 -
11时,与50mg/L臭氧相比,过氧单硫酸盐(1:1)对O-NAs降解具有相似或增强的效果。通过过氧单硫酸盐相对于臭氧增强•OH途径可能是一种有效的OSPW处理方法,只需增加少量成本就能使其安全排放到接收环境中。