Applied Environmental Research Laboratories, Department of Chemistry, Vancouver Island University, 900 Fifth Street, Nanaimo, BC V9R 5S5, Canada; Department of Chemistry, University of Victoria, PO Box 3055, Victoria, BC V8P 5C2, Canada.
Natural Resources Canada, CanmetENERGY Devon, 1 Oil Patch Drive, Devon, AB T9G 1A8, Canada.
J Hazard Mater. 2022 Oct 15;440:129798. doi: 10.1016/j.jhazmat.2022.129798. Epub 2022 Aug 18.
With the increasing use of unconventional, heavy crude oils there is growing interest in potential impacts of a diluted bitumen (DB) spill in marine and freshwater environments. DB has the potential to release several toxic, trace organic contaminants to the water column. Here, the aqueous concentrations and compositions of two classes of organic contaminants, naphthenic acids (NAs) and polycyclic aromatic hydrocarbons (PAHs), are followed over 8 weeks after a simulated spill of DB (10 L) into a freshwater mesocosm (1200 L) with river sediment (2.4 kg). These complex samples contain biogenic dissolved organic matter, inorganic ions, petroleum contaminants, suspended sediments, and oil droplets. We report the first use of condensed phase membrane introduction mass spectrometry (CP-MIMS) as a direct sampling platform in a complex multi-phase mesocosm spill tank study to measure trace aqueous phase contaminants with little to no sample preparation (dilution and/or pH adjustment). CP-MIMS provides complementary strengths to conventional analytical approaches (e.g., gas- or liquid chromatography mass spectrometry) by allowing the entire sample series to be screened quickly. Trace NAs are measured as carboxylates ([M-H]) using electrospray ionization and PAHs are detected as radical cations (M) using liquid electron ionization coupled to a triple quadrupole mass spectrometer. The DB-affected mesocosm exhibits NA concentrations from 0.3 to 1.2 mg/L, which rise quickly over the first 2 - 5 days , then decrease slowly over the remainder of the study period. The NA profile (measured as the full scan in negative-electrospray ionization at nominal mass resolution) shifts to lower m/z with weathering, a process followed by principal component analysis of the normalized mass spectra. We couple CP-MIMS with high-resolution mass spectrometry to follow changes in molecular speciation over time, which reveals a concomitant shift from classical 'O' naphthenic acids to more oxidized analogues. Concentrations of PAHs and alkylated analogues (C1 - C4) in the DB-affected water range from 0 to 5 μg/L. Changes in PAH concentrations depend on ring number and degree of alkylation, with small and/or lightly alkylated (C0 - C2) PAH concentrations rising to a maximum in the first 4 - 8 days (100 - 200 h) before slowly decaying over the remainder of the study period. Larger and heavily alkylated (C3 - C4) PAH concentrations generally rise slower, with some species remaining below the detection limit throughout the study period (e.g., CH class including benzo[a]pyrene). In contrast, a control mesocosm (without oil) exhibited NA concentrations below 0.05 mg/L and PAHs were below detection limit. Capitalizing on the rapid analytical workflow of CP-MIMS, we also investigate the impacts of sample filtration at the time of sampling (on NA and PAH data) and sample storage time (on NA data only).
随着非常规重质原油的使用日益增多,人们对在海洋和淡水环境中稀释沥青(DB)泄漏的潜在影响越来越感兴趣。DB 有可能将几种有毒的痕量有机污染物释放到水柱中。在这里,在一个淡水中型生态系统(1200 L)中模拟了 10 L DB 泄漏后,我们跟踪了两类有机污染物(环烷酸(NA)和多环芳烃(PAH))的水相浓度和组成 8 周。这些复杂的样品中含有生物源溶解有机物质、无机离子、石油污染物、悬浮沉积物和油滴。我们报告了首次使用凝聚相膜进样质谱(CP-MIMS)作为一种直接采样平台,在一个复杂的多相中型生态系统泄漏罐研究中,对痕量水相污染物进行测量,几乎不需要进行样品制备(稀释和/或 pH 调整)。CP-MIMS 通过允许整个样品系列快速筛选,为常规分析方法(例如气相或液相色谱质谱)提供了补充优势。痕量的 NA 作为羧酸盐 ([M-H]) 使用电喷雾电离进行测量,而 PAH 则使用液体电子电离和三重四极杆质谱检测为自由基阳离子 (M)。受 DB 影响的中型生态系统的 NA 浓度为 0.3 至 1.2 mg/L,在前 2-5 天迅速上升,然后在研究期间的剩余时间缓慢下降。NA 谱(以在负电喷雾电离下的全扫描在名义质量分辨率下测量)随着风化而向较低的 m/z 转移,这一过程随后通过归一化质谱的主成分分析进行。我们将 CP-MIMS 与高分辨率质谱相结合,以跟踪随时间变化的分子形态变化,这揭示了从经典的'O'环烷酸到更氧化类似物的同时转变。受 DB 影响的水中的 PAH 和烷基化类似物(C1 - C4)浓度范围为 0 至 5 μg/L。PAH 浓度的变化取决于环数和烷基化程度,小的和/或轻度烷基化(C0 - C2)PAH 浓度在前 4-8 天(100-200 h)达到最大值,然后在研究期间的剩余时间缓慢衰减。较大的和重度烷基化(C3 - C4)PAH 浓度上升较慢,有些物种在整个研究期间仍低于检测限(例如,包括苯并[a]芘的 CH 类)。相比之下,一个没有油的对照中型生态系统(NA 浓度低于 0.05 mg/L,PAH 低于检测限)。利用 CP-MIMS 的快速分析工作流程,我们还研究了采样时样品过滤(对 NA 和 PAH 数据)和样品储存时间(仅对 NA 数据)的影响。