University of British Columbia, Dept. of Earth and Ocean Sciences, 6339 Stores Road, Vancouver, BC, Canada V6T 1Z4.
J Contam Hydrol. 2010 Mar 1;112(1-4):15-29. doi: 10.1016/j.jconhyd.2009.09.002. Epub 2009 Sep 20.
Contaminant attenuation processes in the vadose zone of a crude oil spill site near Bemidji, MN have been simulated with a reactive transport model that includes multicomponent gas transport, solute transport, and the most relevant biogeochemical reactions. Dissolution and volatilization of oil components, their aerobic and anaerobic degradation coupled with sequential electron acceptor consumption, ingress of atmospheric O(2), and the release of CH(4) and CO(2) from the smear zone generated by the floating oil were considered. The focus of the simulations was to assess the dynamics between biodegradation and gas transport processes in the vadose zone, to evaluate the rates and contributions of different electron accepting processes towards vadose zone natural attenuation, and to provide an estimate of the historical mass loss. Concentration distributions of reactive (O(2), CH(4), and CO(2)) and non-reactive (Ar and N(2)) gases served as key constraints for the model calibration. Simulation results confirm that as of 2007, the main degradation pathway can be attributed to methanogenic degradation of organic compounds in the smear zone and the vadose zone resulting in a contaminant plume dominated by high CH(4) concentrations. In accordance with field observations, zones of volatilization and CH(4) generation are correlated to slightly elevated total gas pressures and low partial pressures of N(2) and Ar, while zones of aerobic CH(4) oxidation are characterized by slightly reduced gas pressures and elevated concentrations of N(2) and Ar. Diffusion is the most significant transport mechanism for gases in the vadose zone; however, the simulations also indicate that, despite very small pressure gradients, advection contributes up to 15% towards the net flux of CH(4), and to a more limited extent to O(2) ingress. Model calibration strongly suggests that transfer of biogenically generated gases from the smear zone provides a major control on vadose zone gas distributions and vadose zone carbon balance. Overall, the model was successful in capturing the complex interactions between biogeochemical reactions and multicomponent gas transport processes. However, despite employing a process-based modeling approach, honoring observed parameter ranges, and generally obtaining good agreement between field observations and model simulations, accurate quantification of natural attenuation rates remains difficult. The modeling results are affected by uncertainties regarding gas phase saturations, tortuosities, and the magnitude of CH(4) and CO(2) flux from the smear zone. These findings highlight the need to better delineate gas fluxes at the model boundaries, which will help constrain contaminant degradation rates, and ultimately source zone longevity.
在明尼苏达州贝米吉附近的一个原油泄漏场地的非饱和带中,已经使用包含多组分气体传输、溶质传输和最相关的生物地球化学反应的反应传输模型模拟了污染物衰减过程。考虑了油组分的溶解和挥发、其好氧和厌氧降解以及与连续电子受体消耗、大气 O(2)的进入以及浮油生成的污染带中 CH(4)和 CO(2)的释放有关的反应。模拟的重点是评估非饱和带中生物降解和气体传输过程之间的动态关系,评估不同电子接受过程对非饱和带自然衰减的速率和贡献,并提供历史质量损失的估计。反应性(O(2)、CH(4)和 CO(2))和非反应性(Ar 和 N(2))气体的浓度分布是模型校准的关键约束条件。模拟结果证实,截至 2007 年,主要的降解途径可归因于污染带和非饱和带中有机化合物的产甲烷降解,导致污染物羽流主要由高 CH(4)浓度组成。与现场观测结果一致,挥发和 CH(4)生成区与总气压略高、N(2)和 Ar 分压略低相关,而好氧 CH(4)氧化区的特点是气压略低、N(2)和 Ar 浓度升高。扩散是非饱和带中气体的最重要传输机制;然而,模拟结果还表明,尽管气压梯度非常小,但对流对 CH(4)的净通量的贡献高达 15%,对 O(2)的进入也有更有限的贡献。模型校准强烈表明,从污染带中生物生成的气体的转移对非饱和带气体分布和非饱和带碳平衡起着主要控制作用。总体而言,该模型成功地捕捉到了生物地球化学反应和多组分气体传输过程之间的复杂相互作用。然而,尽管采用了基于过程的建模方法、尊重观察到的参数范围,并且通常在现场观测和模型模拟之间取得良好的一致性,但准确量化自然衰减速率仍然很困难。建模结果受到气体相饱和度、曲折度以及污染带中 CH(4)和 CO(2)通量大小的不确定性的影响。这些发现突出表明需要更好地划定模型边界处的气体通量,这将有助于限制污染物降解速率,并最终限制源区寿命。