See more from this Division: General Discipline Sessions
See more from this Session: Hydrogeology III - Uranium, Metals, and Other Contaminants in Groundwater
Thursday, 9 October 2008: 10:15 AM
George R. Brown Convention Center, 342BE
Abstract:
Because of the dramatic difference between water flow velocities in fractures and rock matrix, matrix diffusion (mass transfer between fractures and the rock matrix through molecular diffusion) can significantly retard solute transport processes in fractured rock, and therefore is important for analyzing a variety of problems, including geological disposal of nuclear waste. Matrix-diffusion-coefficient values measured from small rock samples in the laboratory are generally used for modeling field-scale solute transport in fractured rock. However, by compiling results from a number of field tracer tests corresponding to different geological settings (including the unsaturated zone of Yucca Mountain, Nevada), this study demonstrates that the effective matrix-diffusion coefficient at field scale is generally larger than that at lab scale and tends to increase with testing scale. We also find that this interesting scale dependence may be related to rock matrix heterogeneity in fractured rock and the existence of fractures at different scales.
See more from this Division: General Discipline Sessions
See more from this Session: Hydrogeology III - Uranium, Metals, and Other Contaminants in Groundwater