Department of Civil and Environmental Engineering, University of Alberta, Edmonton, Canada.
J Environ Sci Health A Tox Hazard Subst Environ Eng. 2012;47(1):1-21. doi: 10.1080/10934529.2012.629574.
Naphthenic acids, NAs (classical formula C(n)H(2n+z)O(2), where n is the carbon numbers, z represents zero or negative even integers), found in oil sands process waters (OSPWs), are toxic to aquatic environments depending upon several factors such as pH, salinity, molecular size and chemical structure of NAs. Among various available methods, biodegradation seems to be generally the most cost-effective method for decreasing concentrations of NAs (n ≤ 21) and reducing their associated toxicity in OSPW, however the mechanism by which the biodegradation of NAs occurs are poorly understood. Ozonation is superior over biodegradation in decreasing higher molecular weight alkyl branched NAs (preferentially, n ≥ 22, -6 ≥ z ≥ -12) as well as enabling accelerated biodegradation and reducing toxicity. Photolysis (UV at 254 nm) is effective in cleaving higher molecular weight NAs into smaller fragments that will be easier for microorganisms to degrade, whereas photocatalysis can metabolize selective NAs (0 ≥ z ≥ -6) efficiently and minimize their associated toxicity. Phytoremediation is applicable for metabolizing specific NAs (O(2), O(3), O(4), and O(5) species) and minimizing their associated toxicities. Petroleum coke (PC) adsorption is effective in reducing the more structurally complex NAs (preferentially 12 ≥ n ≥ 18 and z = -10, -12) and their toxicity in OSPWs, depending upon the PC content, pH and temperature. Several factors have influence on the degradation of NAs in OSPWs and aquatic environments, which include molecular mass and chemical structure of NAs, sediment structure, temperature, pH, dissolved oxygen, nutrients, and bacteria types.
环烷酸( Naphthenic acids,NAs)(经典化学式为 C(n)H(2n+z)O(2),其中 n 为碳原子数,z 代表零或负偶数整数)存在于油砂处理水中(Oil Sands Process Waters,OSPW),其毒性取决于 pH 值、盐度、分子大小和化学结构等多种因素。在各种可用方法中,生物降解似乎是降低 NAs(n ≤ 21)浓度并降低其在 OSPW 中相关毒性的最具成本效益的方法,然而,NAs 生物降解的机制尚不清楚。与生物降解相比,臭氧化在降低高分子量支链烷基 NAs(优先为 n ≥ 22,-6 ≥ z ≥ -12)以及促进生物降解和降低毒性方面更为有效。光解(254nm 处的紫外线)可有效将高分子量 NAs 裂解成更小的片段,这些片段更易于微生物降解,而光催化可有效代谢选择性 NAs(0 ≥ z ≥ -6)并最大程度地降低其相关毒性。植物修复适用于代谢特定的 NAs(O(2)、O(3)、O(4)和 O(5))并最大程度地降低其相关毒性。石油焦(Petroleum coke,PC)吸附可有效降低 OSPW 中结构更为复杂的 NAs(优先为 12 ≥ n ≥ 18 和 z = -10、-12)及其毒性,这取决于 PC 含量、pH 值和温度。有几个因素会影响 OSPW 和水生环境中 NAs 的降解,这些因素包括 NAs 的分子量和化学结构、沉积物结构、温度、pH 值、溶解氧、营养物质和细菌类型。