4.7 Article

Mineralogy controls on reactive transport of Marcellus Shale waters

期刊

SCIENCE OF THE TOTAL ENVIRONMENT
卷 630, 期 -, 页码 1573-1582

出版社

ELSEVIER
DOI: 10.1016/j.scitotenv.2018.02.223

关键词

Natural attenuation; Reactive transport modeling; Mineralogy; Marcellus Shale waters; Metal contamination; Environmental impact

资金

  1. U.S. Department of Energy (DOE) Subsurface Biogeochemistry Research program [DE-SC0007056]
  2. U.S. Department of Energy (DOE) [DE-SC0007056] Funding Source: U.S. Department of Energy (DOE)

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Produced or flowback waters from Marcellus Shale gas extraction (MSWs) typically are highly saline and contain chemicals including trace metals, which pose significant concerns on water quality. The natural attenuation of MSW chemicals in groundwater is poorly understood due to the complex interactions between aquifer minerals and MSWs, limiting our capabilities to monitor and predict. Here we combine flow-through experiments and process-based reactive transport modeling to understand mechanisms and quantify the retention of MSW chemicals in a quartz (Qtz) column, a calcite-rich (Cal) column, and a clay-rich (Vrm, vermiculite) column. These columns were used to represent sand, carbonate, and clay-rich aquifers. Results show that the types and extent of water-rock interactions differ significantly across columns. Although it is generally known that clay-rich media retard chemicals and that quartz mediaminimize water-rock interactions, results here have revealed insights that differ from previous thoughts. We found that the reaction mechanisms are much more complex than merely sorption and mineral precipitation. In clay richmedia, tracemetals participate in both ion exchange and mineral precipitation. In fact, the majority of metals (similar to 50-90%) is retained in the solid via mineral precipitation, which is surprising because we typically expect the dominance of sorption in clay-rich aquifers. In the Cal column, trace metals are retained not only through precipitation but also solid solution partitioning, leading to a total of 75-99% retention. Even in the Qtz column, trace metals are retained at unexpectedly high percentages (similar to 20-70%) due to precipitation. The reactive transport model developed here quantitatively differentiates the relative importance of individual processes, and bridges a limited number of experiments to a wide range of natural conditions. This is particularly useful where relatively limited knowledge and data prevent the prediction of complex rock-contaminant interactions and natural attenuation. (C) 2018 Elsevier B.V. All rights reserved.

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