『Abstract
In order to explore the reasons for the apparent discrepancy
between laboratory and field weathering rates and to determine
the extent to which weathering rates are controlled by the approach
to thermodynamic equilibrium, secondary mineral precipitation,
and flow rates, a multicomponent reactive transport model (CrunchFlow)
was used to interpret soil profile development and mineral precipitation
and dissolution rates at the 226 ka Marine Terrace Chronosequence
near Santa Cruz, CA. Aqueous compositions, fluid chemistry, transport,
and mineral abundances are well characterized [White A.F., Schulz
M.S., Vivit D.V., Blum A., Stonestrom D.A. and Anderson S.P. (2008)
Chemical weathering of a Marine Terrace Chronosequence, Santa
Cruz, California. I: interpreting the long-term controls on chemical
weathering based on spatial and temporal element and mineral distributions.
Geochim. Cosmochim. Acta 72(1), 36-68] and were used to constrain
the reaction rates for the weathering and precipitating minerals
in the reactive transport modeling. When primary mineral weathering
rates are calculated with either of two experimentally determined
rate constants, the nonlinear, parallel rate law formulation of
Hellmann and Tisserand [Hellmann R. and Tisserand D. (2006) Dissolution
kinetics as a function of the Gibbs free energy of reaction: An
experimental study based on albite feldspar. Geochim. Cosmochim.
Acta 70(2), 364-383] or the aluminum inhibition model proposed
by Oelkers et al. [Oelkers E.H., Schott J. and Devidal J.L. (1994)
The effect of aluminum, pH, and chemical affinity on the rates
of aluminosilicate dissolution reactions. Geochim. Cosmochim.
Acta 58(9), 2011-2024], modeling results are consistent with field-scale
observations when independently constrained clay precipitation
rates are accounted for. Experimental and field rates, therefore,
can be reconciled at the Santa Cruz site.
Additionally, observed maximum clay abundances in the argillic
horizons occur at the depth and time where the reaction fronts
of the primary minerals overlap. The modeling indicates that the
argillic horizon at Santa Cruz can be explained almost entirely
by weathering of primary minerals and in situ clay precipitation
accompanied by undersaturation of kaolinite at the top of the
profile. The rate constant for kaolinite precipitation was also
determined based on model simulations of mineral abundances and
dissolved Al, SiO2(aq) and pH in pore waters.
Changes in the rate of kaolinite precipitation or the flow rate
do not affect the gradient of the primary mineral weathering profiles,
but instead control the rate of propagation of the primary mineral
weathering fronts and thus total mass removed from the weathering
profile. Our analysis suggests that secondary clay precipitation
is as important as aqueous transport in governing the amount of
dissolution that occurs within a profile because clay minerals
exert a strong control over the reaction affinity of the dissolving
primary minerals. The modeling also indicates that the weathering
advance rate and the total mass of mineral dissolved is controlled
by the thermodynamic saturation of the primary dissolving phases
plagioclase and K-feldspar, as is evident from the difference
in propagation rates of the reaction fronts for the two minerals
despite their very similar kinetic rate laws.』
1. Introduction
2. Site description
3. Model formulation and model constraints
3.1. Primary and secondary minerals
3.2. Mineral surface areas
3.3. Aqueous transport
3.4. Aqueous chemistry
3.5. Cation exchange
3.6. Alternative rate law formulations
3.7. Model conditions and parameters
4. Results
4.1. Base case model
4.1.1. Profile evolution for end-member compositions
4.1.2. Primary mineral stoichiometry and solubility
4.1.3. Solute profiles and mineral saturation states
4.1.4. Cation exchange and the evolution of clay abundances
4.2. Results using alternative rate law formulations
4.3. Comparison to previous weathering rate estimates at the
Santa Cruz, CA chronosequences
5. Discussion
5.1. Solid state profile development and reaction front geometry
5.1.1. Primary mineral dissolution
5.1.2. Secondary mineral precipitation and the development of
an argillic horizon
5.2. Effect of flow rates on weathering rates and weathering
profiles
5.3. Secondary mineral precipitation as a control on primary
mineral weathering
5.4. Exporting experimental rate constants to natural systems
5.5. Positive feedback behavior in weathering profiles
6. Conclusion
Acknowledgments
Appendix A. model sensitivities and limitations
A.1. Effect of mass loss or mass gain via eolian deposition
or erosion on observed profiles and reaction rates
A.2. Effect of variations in soil pCO2
A.3. Effect of kaolinite solubility and initial protolith abundance
on kaolinite rates
A.4. Parameter sensitivity and covariance
Appendix B. Model limitations and assumptions
References