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1 INSTAAR and Dept. of Geography UCB-450
University of Colorado, Boulder, CO
80309, USA
E-mail:
suzanne.anderson{at}colorado.edu
2 Institute of Mineralogy, University of Hannover
Callinstrase 1, 30167
Hannover, Germany
3 U.S. Geological Survey, Menlo Park, CA 94025, USA
| ABSTRACT |
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KEYWORDS: Critical Zone, weathering, erosion, soil, regolith, denudation
| INTRODUCTION |
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Knowledge gained from studying the link between mechanical and chemical weathering contributes to understanding how weathering and erosion affect atmospheric CO2 and climate. Early climate models explored a negative feedback in which chemical weathering rates depend on temperature and temperature depends on CO2 (Walker et al. 1981). A later alternative proposed that uplift and erosion control chemical weathering and hence CO2 and climate (Raymo and Ruddiman 1992). Recent work emphasizes rock type, in addition to temperature and erosion, in controlling chemical weathering rates and climate (Dupré et al. 2003). These global models rely on largely empirical correlations among chemical weathering, climate, and physical process rates. Rarely considered in these assessments of chemical weathering flux—the chemical weathering rate per unit land surface area—are the influences of variations in development of the CZ and the reactive surface area within it.
The balance between mechanical and chemical contributions to weathering determines how the CZ forms. Geomorphologists often consider weathering to be preparation of material for transport, primarily by mechanical breakdown into transportable blocks or possibly by chemical weakening. Transportable material is "regolith." Physical erosion rates are either "transport limited," where regolith is deep, or "weathering limited," where they are controlled by rates of regolith production (Carson and Kirkby 1972). There are two geomorphic models for the rate of regolith production: (1) rate decreases exponentially with overlying regolith thickness, and (2) rate is at its maximum under some thickness of regolith, the so-called "humped" function (Heimsath et al. 1999). Evidence for the humped function comes from observation of the highest rates for chemical and physical processes (frost cracking, biotic disturbance) below the surface (Gilbert 1877; Anderson 1998; Gabet et al. 2003). Wilkinson et al. (2005) suggest that a "shifting mosaic" of vegetation may produce the appearance of exponential dependence of regolith production on thickness. In these models, regolith thickness stands as an indicator for the various physical and chemical mechanisms that break down rock.
The concepts of weathering-limited and transport-limited erosion were embraced by Stallard and Edmond (1983) in their analysis of landscape control of chemical weathering fluxes in the Amazon. They recognized that weathering-limited environments, which have little or no soil, deliver relatively unaltered sediment to streams. These landscapes produce high chemical-weathering fluxes, presumably due to highly weatherable minerals at the surface. Soil-mantled, transport-limited environments are more likely to yield highly weathered sediments and produce low solute fluxes. Geochemical controls on global weathering fluxes and physical controls on erosion are interrelated. Both geochemical and physical processes decay rock, each process feeding back on the other. It is time to move beyond correlations of weathering and erosion or regolith thickness and understand how these processes interact to shape the CZ and fluxes from it.
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| THE CRITICAL ZONE: A FEED-THROUGH REACTOR |
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Solutions produced from percolating rainwater, renewed with each rainstorm, bathe the CZ reactor. These are enriched with organic exudates and charged with dissolved gases (notably CO2 and O2). Water percolates at rates controlled by the precipitation (or infiltration) rate and by the hydraulic conductivity of the soil. Such conductivity can be highly variable depending on the material, its history, and the hydrologic conditions. Mineral dissolution or rock fracturing can increase permeability, while clay formation can reduce it. Unsaturated hydraulic conductivity varies by orders of magnitude with slight changes in water content. Mechanical and biomechanical processes open new avenues for water flow through rock, hence exposing new surfaces to reactive weathering solutions, moving the weathering front down, and bringing new material into the reactor. Thus, the vertical extent of the CZ—the size of the reactor—reflects the relative rates of downward weathering-front advance and erosion from the top.
Where in the Critical Zone Does Chemical Weathering Occur?
From a theoretical perspective, the composition, age, and surface area of
minerals, as well as the temperature, flux, and composition of solutions, are
important controls on intrinsic chemical weathering rates. These parameters
vary with depth. Gradients through the CZ in solution parameters such as pH,
dissolved Al, and H2CO3 influence reaction kinetics,
while gradients in hydraulic conductivity, controlled by porosity, pore size,
and water content, affect transport. A CZ reactor does not generally provide
optimal chemical-weathering conditions. The fluid is likely most reactive and
the matrix most permeable near the top of the reactor, while the minerals most
prone to weathering are usually at the bottom of the reactor. How do these
competing effects play out?
Differing system behaviors are reported in the literature. In the warm, wet, steep terrain of Luquillo Experimental Forest, Puerto Rico, complete weathering of plagioclase occurs at the bedrock-saprolite interface, while more resistant minerals survive farther up into the CZ (White et al. 1998). The silicate weathering flux in Luquillo is the highest recorded. In contrast, in the equally warm and wet Nsimi watershed, south Cameroon, silicate weathering fluxes are very low (Braun et al. 2005). The difference between these granitoid systems appears to be hydrologic. In Luquillo, the water table is below the saprolite, and water flushes rapidly through the profile. In Nsimi, high rainfall and low relief keep the water table above the saprolite, and water flow at the weathering front is sluggish. Another warm, wet, granitoid system occurs in Sri Lanka. Despite steep terrain, chemical weathering fluxes are low (von Blanckenburg et al. 2004), comparable to the swampy Nsimi catchment. In Sri Lanka, weathering appears to be hampered by low physical erosion rates, a consequence of tectonic quiescence.
Access of rock to solutions seems to control weathering fluxes from a headwater catchment near Coos Bay, Oregon Coast Range, USA. There, half of the solute flux is derived from fractured rock, despite a highly porous but hydrologically unsaturated regolith rich in primary minerals (Anderson and Dietrich 2001). Dissolved silica fluxes at Coos Bay are nearly as high as in Luquillo (Anderson et al. 2002), despite lower temperatures and rainfall, illustrating the importance of access of aggressive water to unweathered minerals in controlling weathering fluxes.
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. where Z represents CZ
thickness and
the rock uplift rate (or
equivalently, total denudation rate). Waldbauer and Chamberlain
(2005) termed this the
effective surface age, a name that applies equally well at the mineral-grain
scale as at the landscape scale. Note that this residence time is conveniently
determined from cosmogenic nuclide concentrations at the top of a steadily
eroding profile. Several have argued that a shorter residence time for rock in the CZ, driven by faster erosion rates, produces higher chemical weathering solute yields (Anderson et al. 2002; Riebe et al. 2004; Waldbauer and Chamberlain 2005). The reasoning, similar to that of Stallard and Edmond (1983), is that where rock moves rapidly through the CZ, more weatherable minerals are accessible, mechanical breakdown of rock is faster, and mineral weathering rates are higher (White and Brantley 2003). Waldbauer and Chamberlain (2005) developed a model of chemical weathering flux as a function of rock uplift rate, illustrating direct correlation with mineral weatherability.
Setting the Pace of Chemical Denudation
What controls whether a mineral will weather in the CZ or survive for
physical erosion? Mineral dissolution rates exhibit a dynamic range of about
six orders of magnitude from the highest experimental to the lowest natural
rate (FIG.2). While
some of this range is attributed to rougher mineral surfaces over time, the
bulk of the decrease must be related to other time-dependent factors: (1)
decrease in reactive surface area following diminished compositional and
structural heterogeneities; (2) physical occlusion of surfaces by secondary
precipitates and leached layers; and (3) extrinsic properties, such as the
nature of the solution or its saturation state. For dilute conditions typical
in experiments, reaction rate is limited by the mineral surface area and is
independent of fluid composition and water flow rate. As solute concentrations
approach equilibrium, reaction rate becomes limited by the rate of solute
transport. This transport-limited chemical weathering happens in soil columns,
where reaction rate increases with water percolation rate. Therefore,
weathering under close-to-equilibrium conditions (the case in many field
settings) is transport controlled (White
and Brantley 2003). Water flow rate tends to decrease with depth
in the CZ; this and progressive accumulation of weathering products would
decrease chemical weathering rates at depth, but erosion of weathered material
would tend to dampen this decrease.
One approach to determining the chemical denudation rate is to measure the
total rate in the catchment using cosmogenic nuclides with the chemical
depletion fraction, CDF (Riebe et al.
2004). CDF is the fraction of the total denudation resulting from
chemical weathering, easily determined in a 1-D system from immobile element
concentrations (such as zirconium and titanium) in the rock. A global survey
using this approach in granitic catchments indicates a correlation between
physical erosion and chemical weathering rates
(FIG. 3). Surveys
based on riverine fluxes show a similar relationship
(Gaillardet et al. 1999;
Dupré et al. 2003;
West et al. 2005) over a range
of geological settings. Such compilations also show a relationship between
chemical weathering flux and runoff, and to a lesser extent, temperature (e.g.
Oliva et al. 2003). Silicate
weathering flux is responsible for
10% of the total (physical + chemical)
denudation rate. This confirms that silicate weathering flux is affected by
physical denudation rate, but depends only weakly on climate. The link to
climate is mainly through precipitation-driven groundwater flow.
Advancing the Weathering Front
Perhaps the most crucial physical-chemical interactions occur at the base
of the CZ, where the weathering front advances into fresh rock. The difficulty
in accessing this interface hampers understanding it. Chemical weathering
control is illustrated in granite bedrock at Panola, USA
(White 2005). Alteration of
plagioclase to kaolinite can be seen in weathered rock 7.5 m below the
surface, while adjacent orthoclase feldspar and biotite are untouched
(FIG. 4). Such a
pattern is attributed to small differences in mineral solubilities, despite
similar kinetic reaction rates at far from saturation conditions. Percolating
soil water (water in the soil above the groundwater table) reaches saturation
with respect to K-feldspar but remains unsaturated with respect to
plagioclase. Low permeability in the weathered rock limits water access; the
saturation state of water at the base of the CZ controls the advance of the
weathering front.
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Fletcher et al. (2006) explored complex coupling between chemical and mechanical processes that advance the weathering front through spheroidal weathering of granite. Increased volume from oxidation of iron in biotite exerts stresses, ultimately fracturing the rock, forming multiple, onion-skin layers separated by cracks. Although diffusion of oxygen controls initial chemical weathering, the flow paths created by fractures allow rapid transport of oxygen and water deeper into the unweathered core. The rate of advance of the weathering front is linear with time, rather than a function of the square root of time, as expected for true diffusion. Fluids are supplied and solutes removed through artery-like fractures. Thus, the slow diffusion of water through the rock matrix can operate over the short distances between fractures rather than over the whole thickness of the saprolite.
Fractures are undoubtedly important in advancing the weathering front. Tectonic processes likely control fracture density below the CZ (Molnar et al. 2007), and high fracture density predisposes rock for weathering and erosion. Much of the emphasis in discussions of weathering and climate has been on the effects of mountain building and erosion. Hovius and von Blanckenburg (2007) speculate that it is the rate and geometry of active tectonic faulting that accelerate physical, and therefore also chemical, denudation, whether faulting takes place in mountain belts or in extensional settings. Faulting potentially initiates two processes that advance the weathering front. First, faulting can induce rock fracturing, and second, faulting can trigger landscape readjustment by changing river base level, enhancing erosion.
Hovius and von Blanckenburg (2007) suggest two chains of consequences resulting from faulting:
fall in relative base level
incision of the drainage network
enhancement of soil erosion and
rates of physical denudation and sediment production
fall in relative base level
incision of the drainage network
development of new groundwater flow
paths
stronger dilution and less saturation of soil pore water
enhanced rates of mineral dissolution
higher rates of chemical
weathering and soil production The influence of tectonic control on silicate weathering is illustrated in Sri Lanka, where very low rates of weathering and erosion have been observed, counter to expectations of behavior under conditions of high relief, hot climate, and high precipitation (von Blanckenburg et al. 2004). Sri Lanka, and the similar case of the Guyana Shield (Edmond et al. 1995), must be seen in light of the absence of tectonic forcing. Thick, clay-rich, weathered layers shield the bedrock from corrosive fluids. The absence of recent tectonic forcing, also characteristic of cratons, prevents high rates of weathering and denudation.
The Critical Zone on a Slope
We now consider the third dimension, that is, lateral transfer of material
through the CZ. Lateral transfer affects the disarticulated and disaggregated
material found in regolith and soil, not the deeper parts of the CZ. The
importance of slope processes is recognized in the study of soil catenas, the
distribution of soils on slopes. Transport processes collectively called
creep move soil down slope, usually producing a velocity profile
(averaged over many displacements associated with biotic or mechanical
disturbances) that is fastest at the surface and declines with depth. One
manifestation of creep is its impact on the chemical depletion factor (CDF).
Yoo et al. (2007) show that
this extra source of weathered material (enriched in immobile elements) must
be factored into CDF calculations; otherwise, the CDF can be significantly
overestimated.
Several models now exist that track regolith production, sediment transport, and chemical weathering on a hillslope (Mudd and Furbish 2006; Yoo et al. 2007). In steady state, such models predict that the mean age of the soil column is uniform everywhere on the hillslope, so chemical evolution and soil age should not vary with slope position. These models are not yet sophisticated enough to capture the differences in hydrologic conditions down a slope, thought to be important in soil catenas, and are not field tested. Clearly much remains to be explored with respect to sediment movement and weathering processes.
| CONCLUDING THOUGHTS |
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| ACKNOWLEDGMENTS |
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