2007 GSA Denver Annual Meeting (28–31 October 2007)

Paper No. 2
Presentation Time: 1:50 PM

REACTIVE TRANSPORT OF 14C THROUGH A CARBONATE AQUIFER: IMPLICATIONS FOR CONTAMINANT MIGRATION


DECKER, David L.1, EARMAN, Sam1, HERSHEY, Ronald L.1, RYU, Ji-Hun1, GARCIA, Elmer2 and REIMUS, Paul W.2, (1)Desert Research Institute, 2215 Raggio Pkwy, Reno, NV 89512-1095, (2)Los Alamos National Laboratory, P.O. Box 1663, Mail Stop J534, Los Alamos, NM 87545, decker@dri.edu

In many contaminant transport models, 14C is treated conservatively, and is assumed to move at the same velocity as groundwater.  However, this work and previous studies show that 14C moving through a carbonate aquifer can experience significant retardation. In this study, batch experiments were conducted to help understand the mechanisms that control 14C retardation, and improve reactive transport models.

Groundwater 14C is typically present as part of the bicarbonate anion, which tends not to sorb at naturally occurring groundwater pHs.  Even in the absence of sorption, there are several processes that may retard 14C.  These include matrix diffusion, precipitation/dissolution, and isotopic exchange with aquifer carbonate minerals. Batch experiments using 14C, high purity calcite, and dolomite were conducted to evaluate these processes. Minerals used in the experiments were analyzed via BET and SEM.  The experimental variables included mineral saturation state, particle age, and particle size, all of which affected 14C uptake.  Experiments suggest that 14C is very reactive with carbonate minerals, and that 14C activity is lost via a non-equilibrium uptake process that cannot be described by an isotherm.

A conceptual model of 14C uptake that captures the non-equilibrium retardation behavior was developed, incorporating exchange/sorption, exchange/recrystallization, and solid-phase diffusion reactions.  Carbon-14 uptake was modeled numerically using a continuous distribution of mass-transfer rate coefficients.  The numerical model describes a process where the sorbent mineral surface is divided into compartments, and a unique reaction rate is applied to each, rather than treating the mineral surface as a homogeneous, single reaction rate mass sink.  The set of reaction rates is calculated with a continuous gamma probability density function.  Mass-transfer rates varied from relatively fast (10-2 h-1) to very slow (10-15 h-1), depending on the experimental variables.