USEPA, National Exposure Research Laboratory, 960 College Station Road, Athens, GA, 30605, United States.
USEPA, National Exposure Research Laboratory, 944 East Harmon Avenue, Las Vegas, NV, 89119, United States.
J Chromatogr A. 2019 Jan 4;1583:73-79. doi: 10.1016/j.chroma.2018.11.013. Epub 2018 Nov 11.
Analytical data for ultra-high-performance liquid chromatography (UHPLC), nontargeted, high-resolution, mass-spectrometry (HR/MS) molecular features from a wide array of samples are used to calculate CC/C isotopologue ratios. These ratios increase with molecular carbon number roughly following a trend defined by atmospheric carbon. When the effective source reservoir C/C ratio is calculated from the isotopologue ratio (assuming a fractionation factor of unity), features in biotic samples uniformly are tightly grouped, proximate to atmospheric C/C ratio. In contrast, features in soil natural organic matter (NOM), dust NOM and anthropogenic compounds range from proximate to relatively divergent from atmospheric C/C. For the NOM, C/C ratios are consistent with an expected preferential volatilization of C, rendering features in soil NOM C-enriched and some features in dust NOM C-depleted. Anthropogenic compounds tend to diverge most dramatically from atmospheric C/C, generally toward C-depletion, but pesticides we tested tended toward C-enriched. This pattern is robust and evident in: i) anthropogenic vs natural features in dust; ii) perfluorinated compounds in standards and as soil contaminants; and iii) sunscreen compounds in commercial products and wastewater. Considering the observed wide C/C range for anthropogenic compounds, we suggest Rayleigh distillation during synthetic processes commonly favors one isotope over the other, rendering a source reservoir that is progressively depleted as synthesis proceeds and, consequently, generates a wide variation in C/C for man-made products. However, kinetic-isotopic effects and/or synthesis from petroleum/natural gas might contribute to the anthropogenic isotopic signature as well. Regardless of cause, C/C can be used to cull HR/MS molecular features that are more likely to be of anthropogenic or non-biotic origin.
使用来自各种样品的超高效液相色谱 (UHPLC)、非靶向、高分辨率、质谱 (HR/MS) 分子特征的分析数据来计算 CC/C 同位素比值。这些比值随分子碳数的增加而增加,大致遵循大气碳定义的趋势。当从同位素比值计算有效源储层 CC/C 比值(假设分馏因子为 1)时,生物样品中的特征均匀地紧密聚集,接近大气 CC/C 比值。相比之下,土壤天然有机质 (NOM)、尘埃 NOM 和人为化合物中的特征从接近到相对偏离大气 CC/C。对于 NOM,CC/C 比值与 C 的优先挥发一致,使土壤 NOM 中的特征 C 富集,而一些尘埃 NOM 中的特征 C 贫化。人为化合物通常与大气 CC/C 偏离最大,通常向 C 贫化方向偏离,但我们测试的农药倾向于 C 富集。这种模式在以下方面具有稳健性和明显性:i)尘埃中人为与自然特征;ii)标准和土壤污染物中的全氟化合物;以及 iii)商业产品和废水中的防晒霜化合物。考虑到人为化合物观察到的广泛 CC/C 范围,我们建议在合成过程中,瑞利蒸馏通常有利于一种同位素而不是另一种同位素,从而使源储层随着合成的进行而逐渐耗尽,因此,人为制品的 CC/C 变化范围很广。然而,动力学同位素效应和/或源自石油/天然气的合成也可能对人为同位素特征有贡献。无论原因如何,CC/C 都可用于剔除更可能具有人为或非生物来源的 HR/MS 分子特征。