The DOI matches its Crossref record; 57 of the 57 references it cites were found in a registry or an index.
Rate-limited mass transfer and transport of organic solutes in porous media that contain immobile immiscible organic liquid
Abstract
A general model is presented that simulates the effect of an immobile immiscible organic liquid, as well as rate‐limited solid phase sorption, on the transport of dissolved organic contaminants in heterogeneous porous media. Specific models are developed for four cases (1) immobile immiscible liquid that resides in nonadvective domains of a heterogeneous porous medium; (2) immobile immiscible liquid that resides in the advective domain; (3) homogeneous porous media wherein mass transfer within the immiscible liquid, as well as across the liquid‐water interface, is rate limited; (4) homogeneous porous media with a single resistance to liquid‐liquid mass transfer. The performance of the homogeneous‐based, single‐resistance model was evaluated by attempting to predict a break‐through curve reported in the literature. Based on the successful prediction of the data, where values for all parameters were obtained independent of the data being simulated, it appears that the conceptual basis of the model is valid. Through a series of simulations, the effect of the immiscible liquid on retention was shown to be great, even at relatively low levels of saturation. Release of solute from residual saturation located within regions of relatively low hydraulic conductivity can be significantly rate limited, even when mass transfer between immiscible liquid and water is rapid. This has ramifications concerning the efficacy of remediation systems based on imposed hydraulic gradients (e.g., pump‐and‐treat). The model should prove useful in further investigations of the effect of immobile immiscible organic liquids on the retention and transport of organic solutes in porous media.
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“For example, simulations showed that the retardation factor for a TCE-like solute increased from 2 for the case of only solid-phase adsorption to 17 for a case including partitioning to NAPL, with a NAPL saturation of 1%. The R increased to 152 when NAPL saturation was increased to 10%.”
From Assessing the potential contributions of additional retention processes to PFAS retardation in the subsurface (2018) · cites this paper as Brusseau (1992)
In the citing paper
“Brusseau (1992) developed a model that accounted explicitly for NAPL partitioning and solid-phase adsorption, and demonstrated that the transport of organic contaminants can be greatly influenced by NAPL partitioning.”
From Assessing the potential contributions of additional retention processes to PFAS retardation in the subsurface (2018) · cites this paper as Brusseau (1992)
Citations
Cites
Diffusion, mass transfer in fluid systems
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Partition coefficients and their uses
Leo, A., Hansch, C., & Elkins, D. (1971) · Chemical Reviews · doi:10.1021/cr60274a001 · Cited by 4,540
Sorption of hydrophobic pollutants on natural sediments
KARICKHOFF, S., BROWN, D., & SCOTT, T. (1979) · Water Research · doi:10.1016/0043-1354(79)90201-x · Cited by 2,647
Diffusion. Mass Transfer in Fluid Systems
Koryta, J. (1985) · Journal of Electroanalytical Chemistry · doi:10.1016/0022-0728(85)87018-2 · Cited by 1,656
Mass Transfer Studies in Sorbing Porous Media I. Analytical Solutions
van Genuchten, M. T., & Wierenga, P. J. (1976) · Soil Science Society of America Journal · doi:10.2136/sssaj1976.03615995004000040011x · Cited by 1,569
Dead-End Pore Volume and Dispersion in Porous Media
Coats, K. H., & Smith, B. D. (1964) · Society of Petroleum Engineers Journal · doi:10.2118/647-pa · Cited by 1,126
Partition equilibriums of nonionic organic compounds between soil organic matter and water
Chiou, C. T., Porter, P. E., & Schmedding, D. W. (1983) · Environmental Science & Technology · doi:10.1021/es00110a009 · Cited by 969
Dissolution of Trapped Nonaqueous Phase Liquids: Mass Transfer Characteristics
Miller, C. T., Poirier‐McNeil, M. M., & Mayer, A. S. (1990) · Water Resources Research · doi:10.1029/wr026i011p02783 · Cited by 581
Sorption nonideality during organic contaminant transport in porous media
Brusseau, M. L., Rao, P. S. C., & Gillham, R. W. (1989) · Critical Reviews in Environmental Control · doi:10.1080/10643388909388358 · Cited by 579
Self-citationValocchi, A. J. (1985) · Water Resources Research · doi:10.1029/wr021i006p00808 · Cited by 575
Research works printed but not linked: 4
- Bouchard D. C., 1989, Reactions and Movement of Organic Chemicals in Soils, SSSA Spec. Publ., 349
- Pellett G. L., 1966, Longitudinal dispersion, intraparticle diffusion, and liquid‐phase mass transfer during flow through multiparticle systems, Tappi, 49, 75
- Schwille F., 1988, Dense Chlorinated Solvents in Porous and Fractured Media
- Wilson J. L. S. H.Conrad Is physical displacement of residual hydrocarbons a realistic possibility in aquifer restoration?conference on Petroleum Hydrocarbons and Organic Chemicals in Ground WaterNatl. Water Well Assoc.Houston Tex.Nov. 5–7 1984.
Cited by
Brusseau, M. L. (2018) · Science of The Total Environment · doi:10.1016/j.scitotenv.2017.09.065 · Cited by 306
Self-citationSilva, J. A. K., Martin, W. A., Johnson, J. L., & McCray, J. E. (2019) · Journal of Contaminant Hydrology · doi:10.1016/j.jconhyd.2019.03.004 · Cited by 108
Partitioning tracer tests for evaluating remediation performance
Cain, R. B., Johnson, G. R., McCray, J. E., Blanford, W. J., & Brusseau, M. L. (2000) · Groundwater · doi:10.1111/j.1745-6584.2000.tb02711.x · Cited by 38
Self-citation
Metadata
- Authors
- Brusseau, M. L.
- Venue
- Water Resources Research
- Publisher
- American Geophysical Union (AGU)
- Published
- 1992-01
- Volume
- 28
- Issue
- 1
- Pages
- 33-45
- ISSN
- 0043-1397
- 1944-7973
- Cited by
- 87
- References
- 57
- Language
- en
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Contains information from the Semantic Scholar Academic Graph Datasets, made available under the ODC Attribution License (ODC-BY 1.0).
Semantic Scholar’s data is described in: Kinney, R., et al. (2023). The Semantic Scholar Open Data Platform. arXiv:2301.10140.