Online: http://dust.ess.uci.edu/facts Updated: Sun 25th Jun, 2006, 13:06
Natural Aerosols in the Climate System
by Charlie Zender
University of California at Irvine
Department of Earth System Science zender@uci.edu
University of California Voice:
(949) 824-2987
Irvine, CA 92697-3100 Fax:
(949) 824-3256
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We gratefully acknowledge The Annotated Grateful Dead Lyrics site by David Dodd.
Lyric to Box of Rain (p. 169), © Ice Nine Publishing Company. Used with permission.
This monograph describes mathematical, physical, chemical, and computational considerations pertinent to understanding and simulating the distribution and effects of natural aerosols in Earths atmosphere. Much of the content applies generically to any aerosol, but the majority of the aerosol-specific sections focus on mineral dust. There are also minor sections on sea salt mobilization and gaseous uptake on sulfate particles.
This monograph benefits from my discussions with many scientists. Their names appear in citations whenever possible. However, many of the their ideas, presented at meetings or in private conversations, are recapitulated here without acknowledgement. These people include Drs. Stephane Alfaro (Université Paris), Richard Arimoto (New Mexico State University), Vicki Grassian (University of Iowa), Zev Levin (Tel Aviv University), Natalie Mahowald (National Center for Atmospheric Research), Bill Nickling (Guelph University), Greg Okin (University of Virgina), Kevin Perry (University of Utah), Yaping Shao (University of New South Wales), and Richard Washington (Oxford University).
Heintzenberg (1989) reviewed the state of knowledge of tropospheric aerosol composition gleaned mainly from boundary layer observations. Gomes et al. (1990) report the observed size distributions and elemental compositions of mineral aerosols measured by a cascade impactor in the Sahara. Alfaro et al. (1997) describe results of wind-tunnel experiments to deduce the dependence of the emitted dust size distribution on the saltation intensity and u*. Prigent et al. (1999) and Lacaze et al. (1999) show how multi-angle and microwave satellite sensors can adequately retrieve land surface properties such as LAI and roughness length, key to determining dust mobilization. Sokolik et al. (1998) show the important role of infrared absorption by mineral dust. Sokolik and Toon (1999) analyze the effects of mineral composition on dust optical properties. Chiapello et al. (1999) compared the in situ observations of mineral dust with TOMS satellite retrievals. Lohmann et al. (1999) counted mineral dust particles smaller than 2 μm as cloud droplet condensation nuclei. Reader et al. (1999a) and Reader et al. (1999b) analyzed changes between mineral dust climatologies during the Last Glacial Maximum and the present. Gillette (1999) describes the factors contributing to the recurrence of dust emission hot spots as seen from TOMS. Hamonou et al. (1999) characterize the vertical structure of Saharan dust exported to the Mediterranean basin. Claquin et al. (1999) combined the FAO soil map of the world with surface mineralogy of specific samples to create predictive relationships linking soil type to surface mineralogy on a global scale. Li et al. (1999) showed is it possible to identify specific soil types from as few as six narrow-band infrared measurements. Batt and Peabody II (1999) measured threshold friction velocities for beds of pebbles 550 mm in diameter. Ichoku et al. (1999) describe an intensive field campaign in which radiative, microphysical, and chemical properties of various aerosols in the Negev desert were measured and inter-correlated. King et al. (1999) present an overview of the potential of current and future space-borne platforms to measure tropospheric aerosols including dust. Rillig et al. (1999) discovered that the proportion of soil aggregates larger than 250 μm increases linearly with CO2 concentration in certain grasslands due to biological effects. Wang et al. (2000) describe a Kosa (yellow dust) deflation model and evaluations its fidelity over East Asia. Alfaro and Gomes (2001) describe how to estimate the size distribution of the emitted dust by accounting for the size-dependent binding energy of the saltating particles. Arimoto (2001) present a broad overview of the climate factors influencing the abundance of atmospheric dust, as well as the radiative properties controlling the climate impact of dust. Myhre and Stordal (2001) performed sensitivity tests of the global radiative forcing of anthropogenic mineral dust. Grini et al. (2002b) discuss the stability, accuracy, and behavior of sandblasting fluxes determined by the Alfaro and Gomes (2001) model. Lunt and Valdes (2002) develop the Hadley Centre dust model and evaluate it against the standard suite of observations available on Earth. Léon and Legrand (2003) combined visible and infrared satellite measurements to identify dust sources and track dust plumes near the north Indian Ocean. VanCuren (2003) directly measure chemical composition of aerosol, including mineral dust, from Asia which dominates the mass concentration of remote, high altitude sites as far east as the western United States. van Donk et al. (2003) examine anthropogenic erosion on military bases in the Mojave Desert. Kurosaki and Mikami (2003) discovered that increased frequency of strong winds explains much of the observed increased in Dust Storm Frequency (DSF) in East Asia from 20002002 relative to the previous decade. Cakmur et al. (2004) show how sub-gridscale gustiness, driven largely dry convection, explains dust emissions in regions where mean winds are otherwise too weak to generate observed emissions. Kurosaki and Mikami (2004) derive an empirical Snow Cover Factor (SCF) that accounts for the influence of snow on the threshold wind velocity for dust mobilization. Grini and Zender (2004) apply show that accounting for saltation, sandblasting, and wind-speed PDFs improves the simulated size distribution of long range transported dust in a global model. Menut et al. (2005) further discuss the problems with determining sandblasting fluxes highlighted by Grini et al. (2002b), and present a new numerically stable scheme for their evaluation. Brooks et al. (2005) describe the interaction between climate and society in the Sahara. Arimoto et al. (2006) summarize dust measurements and modeling during ACE Asia. Many studies examine the possible role of dust as a vector for disease organisms affecting humans (Zender and Talamantes, 2006) and downwind ecosystems such as coral reefs (Shinn et al., 2000; Prospero et al., 2005). Yang et al. (2006) quantify the sensitivity of global dust mobilization, loading, and deposition to assumed size distribution. S. et al. (2006) characterize the effects of iron oxides on dust optical properties.
Many researchers have investigated the Martian dust cycle. In fact, until the 1990s, probably more dust research was performed by researchers more concerned with Mars than Earth. Recent global dust simulations on Mars are described in Pankine and Ingersoll (2002), Newman et al. (2002), and Basu et al. (2004).
Surfaces dissipate the momentum of the wind blowing over them. This dissipation is the result of
tangential shear stress between the wind and the surface elements. The rate of change of atmospheric
momentum Ma
defines a stress force
and the magnitude of this stress force τ = (
⋅
)1∕2 expresses the
total momentum the surface extracts from the wind per unit surface area per unit time. Hence the surface
wind stress is also called the surface momentum flux. Some fraction of this wind stress τ does work on the
surface in the form of moving the surface elements, e.g., moving leaves, or causing waves. Over
bare or nearly bare ground much of the wind stress must go into aeolian abrasion (over stony
surfaces) or soil movement since there is little else to absorb the force. The remainder of the
wind stress may be converted to frictional heating of the surface, or small scale atmospheric
turbulence.
We define the horizontal wind stress τ by appealing to basic principles of fluid dynamics. A fluid of
density ρ moving at speed U exerts a pressure p (force per unit area) of
ρU2 on a stationary
object transverse to the flow. The wind stress τ tangential to the surface takes a similar form,
The total stress to the surface
is the vector sum of individual components representing stress
dissipated by the plant canopy, stress dissipated by airborne (saltating and suspended) particles, and,
finally, wind stress dissipated by the solid surface itself. This stress partition or drag partition has
important implications for dust studies.
Using (2.5) to express the wind stress τ (2.1) solely in terms of u* we obtain
We now consider the wind speed profile U(z) between the free atmosphere and the surface. The planetary surface is the interface between the fluid atmosphere and the solid surface (soil, ocean, etc). A solid land surface requires a no slip boundary condition, i.e., the wind speed is zero exactly at the surface. To a good approximation, the ocean may also be treated with the no slip boundary condition since the atmospheric wind speed Ua is usually much larger than the surface current in the ocean uo, i.e., Ua ≫ uo. Let us assume that we know the measured or predicted wind speed Ua at a height z above the surface.
Knowing the wind with speed U at height z exerts a stress τ on the surface,
u* is called the friction velocity, drag velocity, or, more appropriately, the friction speed.Substituting (2.1) into (2.4) we see that
The friction velocity u* is the fundamental quantity determining the flux of dust into the atmosphere. Nevertheless, it is difficult to attach a simple physical interpretation to the friction velocity. However we now demonstrate two important physical properties of u*. First, the mean horizontal wind speed at the top of the laminar layer is u*. Thus immediately after uplift, a particle is embedded in a horizontal wind of speed u*. In §3.3 we use this property of u* to explain the observed cubic dependence of the horizontal mass flux of saltating particles on the wind speed.
Secondly, u* is proportional to the mean velocity gradient
near the surface.
There are many other useful relations which can be established between U, u*, rm, Cm, and τ. These relations are simple, but tedious, to derive. Table 2.1 lists many of the relations between frequently occurring boundary layer parameters.
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The thermodynamic properties of the boundary layer determine the vertical gradient of fluxes within the boundary layer. In neutral conditions the wind speed varies logarithmically with height according to
where k is the Von Karman constant. The n superscript indicates neutral conditions. Strictly speaking, a logarithmic wind profile refers to a wind profile which obeys (2.6). Loosely used, the term refers to any wind profile in the lowest hundred meters or so of the atmosphere. The neutral exchange coefficient for momentum, also called the neutral drag coefficient, is thenFinally, it is sometimes useful to invert (2.7) in order to obtain z0,m in terms of Cn m
The surface fluxes for momentum, heat, and vapor transfer are coupled by micrometeorological exchanges between the surface and the atmosphere in the surface (constant flux) layer. Determination of these fluxes from observation is possible via eddy flux correlation techniques. From a modeling perspective, the fluxes may determined by solving coupled non-linear differential equations in the surface layer. This technique is employed in Large Eddy Simulation (LES) models. LES solution resolve, as exactly as practical, the complex, turbulent eddies which determine the thermodynamic behavior of the boundary layer. However, large scale atmospheric models cannot afford to solve the continuous equations of motions throughout the boundary layer. Instead, a class of bi-level solutions for boundary layer fluxes has been developed based on Monin-Obukhov similarity theory.
Monin-Obukhov similarity theory is usually applied in terms of resistance r and conductance C ≡ r-1 which describe the transfer of scalar quantities between two levels within the boundary layer. For simplicity, one of these levels is taken as zatm the midpoint height of the lowest atmospheric layer in the large scale atmospheric model. A host model provides the potential temperature θatm, pressure patm, specific humidity qatm, and meridional and zonal winds vatm and uatm. The subscript atm indicates the quantities are defined at the height zatm. The momentum fluxes τx and τy [kg m-1 s-2], sensible heat flux H [W m-2], and moisture flux E [kg m-2 s-1] are defined by the vertical gradient of the appropriate thermodynamic quantity between z = zatm and z = zs, where zs is the surface height (defined below). The fluxes are expressed as
The similarity of these expressions to one another arises from the definitions of the resistances rm, rh, and rv. These resistances depend implicitly on the fluxes τ, H, and E, through Monin-Obukhov similarity theory. Thus (2.9)(2.12) must be solved iteratively.Solutions to (2.9)(2.12) must balance the surface energy budget. In other words, power absorbed by the surface must be dissipated by surface heating/cooling, and energy divergence to the atmosphere or soil in the form of latent, sensible, and radiative heating or cooling.
The turbulent surface fluxes, also called Reynolds fluxes, are the fluxes of heat, moisture, and momentum between the surface and the atmosphere. These fluxes arise as the atmosphere and the surface attempt to reach equilibrium states with the prevailing conditions. Because they are usually unresolved, the turbulent fluxes are usually determined by the application of Monin-Obukhov theory to the prevailing mean conditions. One simple and popular method, the bulk aerodynamic approximation, is of particular utility to large scale atmospheric models. We shall describe the essential physics for determining the turbulent surface fluxes, and related parameters, using the bulk aerodynamic approximation and more complex approximations.
There are three turbulent fluxes of interest: the momentum flux (also called the surface stress or wind
stress) τ [kg m-1 s-2], and the sensible and latent heat fluxes H and L, respectively, both measured in
W m-2. These fluxes are defined in terms of the eddy fluxes of the appropriate fields. Any scalar field
x(t) may be decomposed into time-mean and fluctuating components,
and x′, respectively
![]() | = ![]() | (2.14a) |
| x′(t) | = 0 | (2.14b) |
Eddy fluxes arise from the fluctuating components of state variables. Consider the vertical fluxes of the scalar quantity x (2.13). For concreteness, imagine that x represents horizontal wind speed U, temperature T , or specific humidity q. Using (2.13) we see that the instantaneous vertical flux of x is
The time-mean surface flux of x is obtained by applying the time-average operator to (2.16) where we have used the time-mean properties of
and x′ (2.14) and the further property that the vertical
wind vanishes at the surface
(z = 0) ≡ 0.
The eddy fluxes are multiplied by a pre-factor to obtain the conventional units
| τ | = -ρw′U′ | (2.17a) |
| H | = cpρw′T′ | (2.17b) |
| L | = lρw′q′ | (2.17c) |
The bulk aerodynamic approximation for turbulent fluxes defines the eddy fluxes in terms of the time-mean state variables. The eddy correlations are assumed to be proportional to the product of the horizontal wind speed U and change of the appropriate state variable (U, θ, or q) between the surface and the height of interest.
| -w′U′ | = C mUΔU = CmU2 | (2.18a) |
| w′T′ | = C hUΔθ | (2.18b) |
| w′q′ | = C vUΔq | (2.18c) |
Combining (2.17) with (2.18) we obtain
![]() | (2.19) |
Each of the variables in (2.19) is height dependent. However, it is very common to evaluate the exchange coefficients at a particular height known as the reference height zr. The reference height is usually taken to be 10 m. Shifting the exchange coefficients between zr an arbitrary height z is useful for putting measurements from a variety of heights into a common framework for analysis.
Table 2.2 describes the defining relations of many of the related quantities which prove useful in boundary layer meteorology.
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Garratt (1977) reviews drag coefficient terminology, relationships, measurements, and constraints.
We assume aerosol has the same flux properties in the boundary layer as momentum. The roughness length for momentum transfer z0,m is a property of the surface characteristics only, i.e., z0,m is independent of wind speed when the following conditions are met:
Rougher surfaces tend to absorb more wind stress into non-erodible elements. Thus saltation decreases as z0,m increases, and visa versa. The frequency of saltation events follows the same pattern, since smooth surface initiate saltation more readily.
Raupach (1994) derived simple analytic relations for the roughness length z0,m and the zero-plane displacement D of vegetated surfaces as functions of vegetation height h and area index Λ. Microwave radar data may be inverted to obtain high resolution roughness length (and soil moisture) data of bare ground globally (e.g., Prigent et al., 1999; Lacaze et al., 1999; Zribi and Dechambre, 2003).
There are two roughness lengths pertinent to wind erosion over bare ground. The first is the aerodynamic roughness length of the bare ground including the non-erodible elements such as pebbles, rocks, and vegetation. This is what is traditionally known as the roughness length for momentum transfer, z0,m. The second roughness length is the so-called smooth roughness length, zs 0,m (Marticorena and Bergametti, 1995). zs 0,m is the roughness length of a bed of potentially erodible particles without any non-erodible elements. The roughness length most easily measured in laboratory wind tunnel experiments is zs 0,m. Wind tunnel experiments over uniform beds comprised of known particle sizes show that
However, uniform beds of purely erodible particles are rare in Nature.It is useful to distinguish between the susceptibility of soil to erosion, called erodibility, from the power of the wind (or some other force) to cause erosion, called erosivity. Erodibility depends on the microphysical, chemical, and mechanical properties of the the soil, vegetation, and topography (DOdorico et al., 2001). Erosivity depends on the wind speed, intermittency, shear, and turbulence.
Discounting erodible particles which are sheltered by non-erodible elements, the roughness length felt by the atmosphere over erodible particles is zs 0,m. Moreover, our theoretical understanding of threshold wind velocities is based on zs 0,m, while most large scale atmospheric models are concerned with total momentum flux, and thus tend to compute z0,m. Thus a theory is necessary to connect the zs 0,m to z0,m. This is the theory of drag partition. The increase fd in threshold friction velocity for saltation u*t due to drag partition is (Marticorena and Bergametti, 1995)
The inverse of fd is the fraction of momentum transferred that is available for inducing saltation, called the wind friction efficiency, fe = fd-1. The roughness lengths z 0,m and zs 0,m are properties of the surface characteristics only, i.e., they are independent of wind speed so long as the surface is not in motion. Gillette et al. (1998) present corrections to this assumption for saltating surfaces.Strong saltation can modify z0,m because the saltators provide a sink for momentum distinct from the surface. Consider a saltator ejected from the surface with an initial speed proportional to u*. It is common assumption that, after launching, a saltating particle experiences no vertical acceleration except gravity. Such trajectories are called ballistic. In a ballistic trajectory, the vertical velocity decreases linearly with time, and the initial upwards velocity equals the final downwards velocity. It is easy to show the height reached by a ballistic saltator is proportional to u*2∕g. Strong saltation causes an effective thickening of the roughness length also in proportion to u*2∕g. For strongly saltating surfaces with u * ≫ u*t, Chamberlain (1983) suggests
For moderate wind friction speeds u* ~ u*t, such effects may be neglected (Leys and Raupach, 1991).Table 2.3 shows typical roughness lengths of non-vegetated surface types.
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The roughness length of fluids depends on the surface wind shear. The shear stress deforms the fluid and generate ripples or waves at higher wind speeds. These waves, in turn, modify the surface roughness length. Chamberlain (1983) pointed out that, in certain circumstances, wind drag entrains very similar amounts of surface mass into the atmosphere over many different surface types. He assembled a variety of observational data which showed that saltation of sand and snow was analogous to entrainment of sea-spray over the ocean. This agreement could be explained by assuming z0,m was proportional to u*2∕g over each of the surfaces. Over oceans, we adopt the dependence of z0,m on U proposed by Large and Pond (1982)
The reference height zr is the height at which the neutral exchange coefficient Cn m is determined. In theory this could be any height but in practice Cn m is measured and parameterized as a function of the wind speed at 10 m (e.g., Large and Pond, 1981; NCAR Oceanography Section, 1997; Bryan et al., 1997). Thus we use U10 instead of Ur. The constraint that U10 > 1 m s-1 prevents surface exchanges from vanishing at small wind speeds.Note that Cn m (2.28) is the not the drag coefficient but is the neutral drag coefficient. Stability-based corrections must be applied to Cn m in order to obtain Cm. Large and Pond (1981) summarize the procedure used to convert Cn m to a (non-neutral) drag coefficient, shifted to any height z:
When z = zr, then Cm is the drag coefficient at the reference height.Exchange coefficients such as the drag coefficient Cm (2.29) are positive-definite by definition, e.g., (2.1). Some care must be taken to ensure numerical procedures do not erroneously predict negative-valued exchange coefficients. For example, (2.29) predicts Cm(z) < 0 when . . . fxm
As mentioned above, the vertical profile of momentum in the boundary layer is, to a first approximation, logarithmic with height (2.6). However, the stability properties of the atmosphere introduce a correction
![[ ( ) ( ) ( )]
U (z ) - U(z ) = u*- ln z2 --D- - ψ z2---D- + ψ z1 --D- (2.30 )
2 1 k z1 - D m L m L](aer46x.png)
The stability parameter ζ is the ratio of the height z to the Monin-Obukhov length L [m] (defined below).
The stability parameter is the non-dimensionalized height in the surface turbulence equations.In the surface layer, the stability parameter equals the flux Richardson number, ζ = Rf. The flux Richardson number is the ratio of the production (or loss) of turbulent kinetic energy (TKE) by buoyancy to the production of turbulent kinetic energy by shear stresses. When Rf = 1, turbulence is consumed by buoyancy as fast as it is produced by shear stress. This is why the similarity functions defined below have discontinuous first derivatives at ζ = 1. This behavior is well-documented in nature.
It is convenient to define separate stability parameters for the processes of momentum, vapor, and heat transfer in the boundary layer:
The correction factor ψm is defined in terms of the similarity function φ via
Correction factors ψv and ψh for vapor and heat transfer are defined analogously to (2.33).
Monin-Obukhov similarity theory is a more physically accurate description of surface turbulent fluxes than the bulk aerodynamic formulation (2.19). We may re-write in terms of the mean gradients of the scalar properties and their respective transfer resistances.
| τ | = ρ(Ur - Us)∕rm | (2.34a) |
| H | = -cpρ(Tr - Ts)∕rh | (2.34b) |
| L | = -lρ(qr - qs)∕rv | (2.34c) |
The Monin-Obukhov similarity theory relates surface turbulent flux to the mean gradients of the scalar quantities in the surface (constant flux) layer.
| τ | = ρ![]() ![]() | (2.35a) |
| H | = -cpρ![]() ![]() | (2.35b) |
| L | = -lρ![]() ![]() | (2.35c) |
Many studies have constructed empirical similarity functions from boundary layer experiments. We adopt forms for the similarity functions summarized by (Brutsaert, 1982, p. 71) and Zeng et al. (1998):
| φm(ζ) = φh(ζ) = φv(ζ) | = 1 + 5ζ ζ ≥ 0 | (2.36a) |
| φm(ζ) | = (1 - 16ζ)-1∕4 ζ < 0 | (2.36b) |
| φh(ζ) = φv(ζ) | = (1 - 16ζ)-1∕2 ζ < 0 | (2.36c) |
Zeng et al. (1998) find that the similarity functions for very stable (ζ > 1) and very unstable (ζm < -1.574, ζh < -0.465) conditions approach different limits than (2.36). For completeness, we present the Zeng et al. (1998) recommendations for the entire range of ζ for momentum
and for heat (and vapor) The locations of the functional interfaces in (2.37) and (2.38) were, to some degree, chosen to ensure the stability functions evenly match eachother.
The Monin-Obukhov length L [m] characterizes the stability of a fluid. There are many equivalent definitions of L, such as
where θv [K] is the virtual potential temperature and θv* [K] is the scaling parameter for temperature. The Monin-Obukhov length is the height above the ground at which the production of turbulence by mechanical (shear) and thermal (buoyancy) forces are equal. L increases with friction velocity (shear turbulence), and decreases with buoyancy flux (convective turbulence). Positive and negative L indicate stable and unstable atmospheres, respectively. When the magnitude of L is very large, e.g., ∣L∣ > 105, the atmosphere is neutrally stable.The procedure for estimating the surface turbulent fluxes often begins with an initial estimate of the Monin-Obukhov length L. The following method is based on Zeng et al. (1998) and is used in CLM (Dai et al., 2003). We assume use five quantities to estimate L: First, the wind speed at reference height Ur. Second and third, the virtual potential temperatures at reference height θvr and at surface θvs [K] (or, equivalently, their difference Δθv ≡ θvr - θvs). Fourth, the reference height zr [m]. Fifth and finally, the roughness length for momentum z0,m [m]. These five quantities may be measured or, in a model, their values from the previous timestep may be used.
Given these quantities, we first estimate a flux wind speed Uf [m s-1] which depends on stability. We define the term flux wind speed operationally as the wind speed used to compute surface fluxes. In stable conditions, the flux wind speed is simply the vector magnitude of the mean zonal and meridional components, u and v.
The minimal value of 0.1 m s-1 avoids singularities and represents the small eddies present even in a becalmed, stable atmosphere. In unstable conditions, Uf includes the convective velocity scale w* as well. The inclusion of w* (2.40) helps Uf account for the contributions of large eddies in the convective boundary to the surface fluxes (Zeng et al., 1998).After the flux wind speed is estimated (2.40), we obtain the bulk gradient Richardson number Ri
where Δz ≡ zr - D is the difference between the reference height zr and the zero plane displacement height D. The gradient Richardson number characterizes the turbulence intensity. Formally, Ri is the ratio of convectively available potential energy (CAPE) to the magnitude of low-level shear. Hence (2.41) is simply a first estimate for Ri.We use Ri to form an initial guess for ζm (2.32)
However, these guesses allow ζm outside the range of measured values. Hence we contrain the results of (2.42) as follows:Finally, we estimate L from ζm (2.42) and z0,m using (2.32)
This initial estimate for L (2.42) is refined in subsequent iterations.
The single most important parameter determining surface erosion is the wind speed. In practice we predict or measure the wind speed U at a certain height above the ground and wish to relate U to an observed or predicted dust flux. It is convenient to define a reference height zr so that U and Q may be intercompared at disparate locations. By convention zr is set to 10 m, which is a standard height both for field observations and for numerical model output. As discussed below, it is actually the wind friction speed which is directly linked to dust mobilization.
This section describes the wind driven processes which determine the flux of long-lived mineral dust into the atmosphere. The atmospheric dust burden is the end result of a chain of processes which begins with saltation. Saltation is the wind-initiated movement of large soil particles in the downstream direction. Particles large enough to be entrained into motion directly by wind are called sand. Sand ranges in texture (size) from very fine to coarse, 1∕16 < D < 2 mm (62 < D < 2000 μm) respectively. Smaller particles of crustal material, those susceptible to long term suspension and transport in the atmosphere, are collectively referred to as dust. When the drag on the particles is large enough to overcome the inertial and cohesive forces attaching the particle to the soil bed, the particle suddenly lifts from the bed in a nearly vertical trajectory. Blown from behind and unable to resist gravitational settling for very long, the particle arcs back to the surface along a shallower trajectory. The energy dissipated by the impact of the saltating particles on the surface, may, in turn, break adhesive bonds and liberate much smaller dust particles known as dust from the surface. Although the distinction is somewhat arbitrary, dust particles are smaller than the population of saltators which liberate them.
The size of dust particles is generally taken to be D < 50 μm. Since the time a particle requires to settle out of the atmosphere under the influence of gravitation alone is proportional to the square of the particle diameter (see §5 below), dust particles have significantly longer atmospheric residence times than sand.
Two books are devoted to physical mechanisms of wind erosion, Bagnold (1941) and Shao (2000). Raupach and Lu (2004) provide an excellent review of all aspects of dust mobilization and dry deposition.
The conditions necessary to initiate or maintain the movement of particles depend on many properties, including wind speed, particle size, surface roughness, stability, sheltering effects, surface moisture, and interparticle forces. Laboratory experiments have been performed over a wide range of ambient pressures and particle densities to isolate and define these dependencies (Iversen and White, 1982; Shao et al., 1996). We now characterize the aerodynamic forces on particles which initiate and maintain particle motion which in turn causes saltation, dust mobilization and wind erosion.
Bagnold (1941) first derived the size dependence of the threshold wind velocity by considering the balance of forces on a particle. His lucid derivation, though lacking in completeness, nevertheless provides the starting point for more complete theory of mobilization. Consider a particle of density ρp resting atop a bed of similar particles in a fluid of density ρ traveling above and around the particles with speed u*. Define the packing angle α as the angle from the vertical subtended by the downstream point of contact P of the particle with the bed it lies atop. If the particles are all spherical and regularly packed, then α is the angle from the center of the upper sphere to the center of one of the lower spheres.
The forces considered by Bagnold (1941) are drag and gravity. Bagnold assumes particle movement initiates when the aerodynamic drag exerted by the wind on the particle overcomes the component of the particles weight directed opposite to the wind stream. A more complete physical statement of the balance of forces leading to saltating is that particle motion commences when the sum of the forces acting on the particle result in a net moment of zero at the downstream point of contact P . We shall use this more general principle to include the cohesive and lift forces later; for now, we retrace Bagnolds original derivation.
The mass of the particle is πD3ρ p∕6 and its net weight relative to the surrounding fluid is πgD3(ρ p -ρ)∕6. The contact point P is the pivot, or axis of support, about which gravity attempts to pull the particle downwards and backwards. The gravitational torque acts through the center of mass of the particle to create a moment of force. The gravitational moment MW is the product of the gravitational force and the distance between the axis through which gravity acts (i.e., the center of mass) and the point P . This distance is (D sin α)∕2, and thus
The horizontal drag force MD exerted on the particle by the fluid is proportional to the exposed cross sectional area of the particle normal to the fluid flow, MD ∝ D2. The drag per unit particle surface area is proportional to ρu*2. Assuming the net drag force is directed through the center of mass of the particle, then the distance from the axis of drag force to P is (D cos α)∕2, and thus the drag moment is
where C2 = C1∕2 is a constant of proportionality which depends upon the exact grain geometry, micrometeorology, and grain packing.At the threshold velocity u*t, the gravitational moment equals the drag moment on the particle so that any small perturbation in wind speed may initiate particle motion, i.e., saltation. Equating MW (3.1) and MD (3.2)
where A2 ≡ (
) tan α. For particles in air, ρp ≫ ρ and so (3.3) becomes
![]() | (3.4) |
The preceding discussion applies to the initiation of particle motion in a bed of grains initially at rest. Thus u*t defined by (3.3) is called the fluid threshold friction velocity or aerodynamic threshold friction velocity. Once particle motion begins, the threshold velocity actually decreases since some of the momentum needed to initiate further particle motion is supplied by particles already in motion. The friction velocity in an environment of particles already in motion is known as the impact threshold friction velocity u*ti. For large sand grains, Bagnold (1941) found that u*ti ~ 0.8u*t The effect of particle motion on the surface wind speed and its feedbacks to further particle motion will be discussed further in §3.3 below.
Subsequent developers of this theory have continued to use the parameter A as it appears in (3.3) and in (3.4), i.e., as the proportionality factor between u*t and the factor containing the square root of the particle diameter.
![]() | (3.5) |
A is called the dimensionless threshold friction speed, or simply the threshold parameter (Iversen and White, 1982). Theoretical approximations and empirical parameterizations of A will be discussed in §3.2.3 below.
Bagnold (1941) developed (3.3) for particles large enough to appear as isolated elements to the fluid flow. In particular, experiments confirm the predictions of (3.3) only for particle sizes larger than about 200 μm. A ~ 0.1 for large particles in air and A ~ 0.2 for particles in water (Bagnold, 1941, p. 88). In this size range u*t increases linearly with D1∕2. For smaller particles, however, it is found that cohesive and lift forces may not be neglected, and that these forces combine to produce an optimum size for particle saltation, i.e., a minimum in u*t(D) not suggested by (3.3).
In order to develop a more complete theory of saltation and dust emissions, let us first examine the physics
of airflow around a single particle. The balance of these forces determine when particle motion is initiated
by airflow. Consider an isolated particle of size D at rest in a Newtonian fluid of density ρ moving with
velocity
. For simplicity, we consider the component of motion in the x direction. As shown in
§18.14, the equation of continuity (conservation of mass) for an incompressible fluid (18.80)
requires
![]() | (3.6) |
and momentum conservation in the x direction (18.90) requires (18.92)
![]() | (3.7) |
We can gain insight into the relevant physical processes by non-dimensionalizing the equations. We do this by changing to a non-dimensional coordinate space which is scaled by the relevant physical dimensions of the fluid flow. For fluid flow around an isolated particle at rest, the relevant velocity is the upstream velocity v∞ far from the particle. The relevant length scale is D.
![]() | (3.8) |
The dimensionless time and pressure variables are
![]() | (3.9) |
Thus, by definition, none of the transformed coordinates has any physical dimensions. Substituting the non-dimensional coordinate definitions into (3.6) we obtain
where the constant factor v∞∕D results from the coordinate transformation. Thus the incompressible continuity equation does not change in the transformed coordinate system. Substituting the non-dimensional coordinate definitions into (3.7), and using ν ≡ μ∕ρ (18.6), Factoring the physical scales from each side we obtain
![]() |
Multiplying each side by D∕v∞2 we find
![]() | (3.12) |
Note that all physical scales in the problem appear in a group which multiplies the diffusion term. This single dimensionless factor must determine the behavior of the entire system. The Reynolds number Re is defined as the inverse of this factor
![]() | (3.13) |
The Reynolds number expresses the ratio of inertial to viscous forces. The nature of the solutions to (3.12) is strongly sensitive to whether Re < 1 or Re > 1. When Re ≪ 1, viscous forces dominate and the LHS of (3.12) is small relative to the RHS (because Re-1 ≫ 1) and may be neglected. The steady state behavior of (3.12) then approaches
![]() | (3.14) |
The solution to (3.14) for a sphere at rest in a fluid is one of the central results of fluid mechanics.
The Reynolds number of an arbitrary flow is defined as
![]() | (3.15) |
so that Re varies with position. The gravitational settling speed vg of particles smaller than 10 μm is less than 10-2 m s-1. This implies Re < 10-2 for D < 10 μm (3.15). Thus inertial effects may be neglected for most aerosols falling at terminal velocity. However, vg increases as the square of the particle diameter so that Re > 1 for D > 50 μm. When Re ≫ 1, then inertia plays a large in the motion. In this case, the flows described by (3.12) become highly turbulent.
The relative velocity between strong winds and an undisturbed sand grain at the surface, however, easily exceeds vg. The relevant wind speed for entraining particles from the surface is not the atmospheric wind speed, but the friction velocity u*. Section 2 defines and describes the friction velocity as the characteristic wind velocity dissipated by shear stress and small scale turbulent interactions between the surface and the atmosphere. In complete analogy with (3.15) we define the friction Reynolds number as
![]() | (3.16) |
Windy conditions in the free atmosphere, e.g., wind speeds of 510 m s-1, typically correspond to u * between 1050 cm s-1 over barren surfaces. In such conditions, Re > 1 for particles larger than about 20 μm, and inertial forces should not be neglected.
The friction Reynolds number at the threshold friction velocity is called the threshold friction Reynolds number
![]() | (3.17) |
The literature of particle mobilization quite often uses B instead of Re*t. The symbols are equivalent, and the following sections shall use both notations.
Our presentation follows the detailed summary of Greeley and Iversen (1985), which remains the state-of-the-art in theoretical modeling of particle mobilization in planetary atmospheres. Most of the empirical elements were presented in a unified theory in Iversen and White (1982). We begin by reconsidering a loose particle at rest atop a bed of similar particles. We shall account for the effects of five moments acting on this particle. The forces creating these moments are drag FD, gravity FW, lift FL, interparticle cohesion FC, and rotational inertia. Drag and gravity were explicitly considered by Bagnold (1941) and were discussed in §3.2.1.
The lift force is due to the extremely large velocity gradient above the particle. For Re smaller than about 5, the particle resides in a thin (110 mm) quasi-laminar sublayer where the velocity profile is
![]() | (3.18) |
Thus the velocity shear is constant in the quasi-laminar sublayer
![]() | (3.19) |
In typical dust-prone conditions on Earth, u* = 0.25 m s-1 and ν = 1.3 × 10-5 m2 s-1, so that the velocity shear (3.19) is nearly 5 × 103 m s-1 m-1. The strong velocity shear is an indication that the pressure distribution along the top of the particle generates a lift force akin to an airfoil. The lift force acts through the center of mass of the particle in the vertical direction, i.e., opposite to the gravitational force.
Once the particle is lifted out of the quasi-laminar sublayer the lift force is expected to decrease significantly. Some particles receive their initial vertical momentum from the impact of being struck by other saltating particles. However, the vertical momentum of particles not released due to ballistic impact is thought to be due to the lift force. Experiments (Chepil, 1958; Einstein and El-Samni, 1949, MFC) show that lift and drag forces on hemispheres are of the same order of magnitude. Experiments show qualitatively similar behavior in the lift force occurs in fully turbulent boundary layers (Re* > 5).
Originally, it was thought that the observed optimal size for initiation of particle saltation was due to aerodynamic effects. The observations suggested the existence of forces which act in opposition to the drag on small particles (3.2). Iversen and White (1982) demonstrated that interparticle cohesive forces are important for small particles. Interparticle cohesive forces include a number of processes including moisture, suction, electric charge, and chemical reactions. Many of these forces may be conceived as acting along the line connecting the centers of adjacent particles. The sum of all interparticle cohesive forces is denoted FC.
The angle of repose of a soil is the maximum inclination at which the soil does not undergo spontaneous slippage. Thus the angle of repose is a qualitative estimate of the importance of interparticle cohesion. The greater the tilt, the more important interparticle cohesion is in preventing slippage. The angle between the leeward face of a sand dune and the horizontal is an excellent proxy for the angle of repose. For ordinary dune sand, the angle is 34∘ but, for very small particles, the angle can approach the vertical (Iversen and White, 1982). Bagnold (1941) conjectured that the packing angle α (§3.2.1) is, on average, close to the angle of repose.
The forces described above act on the particle along axes at varying distances from the downstream point of contact P . The distance between the axis of force and P is called the moment arm. From the figure we see that the moment arm for drag is a, for gravity and lift is b, and for interparticle cohesion is c. Thus the moments associated with each force are
At the threshold velocity, these moments are assumed to sum to zero so that any small perturbation in wind speed may initiate particle motion, i.e., saltation. The balance at threshold is where the RHS contains the moments which tend to dislodge the particles and the LHS contains the moments which stabilize the particles. Note the moment of rotational inertia I has been introduced on the LHS. The rotational inertia is not a force per se, rather, it measures of resistance of an object to angular acceleration about a specified axis. The rotational inertia I of an object is defined as ∫ r2 dM, where r is the distance of the element of mass dM from the origin of coordinates. A solid sphere has a rotational inertia I = 2Mr2∕5 = MD2∕10 about its center. Assuming the particle is spherical, we apply the parallel axis theorem to obtain the rotational inertia of the particle about P where we have expressed the particle mass in terms of its diameter in the last step.It is possible to measure the relative strength of lift, drag, and rotational inertia by non-dimensionalizing the forces in (3.20) and (3.22). Following Greeley and Iversen (1985), the small particle shear flow force coefficients KD, KL, KI, for drag, lift, and rotational inertia, respectively, are defined as
Greeley and Iversen (1985) summarize the agreement between the measured and theoretical values of KD, KL, and KI. Relatively good agreement is found for measured and theoretical values of the drag parameter, with all values falling in the range 4.65 < KD < 9.82 for Re = 0.95. Wind tunnel inferences of KL are much larger (factor of 40) than theoretical values (Saffman, 1965, 1968, MFC). All three moment arms in (3.20) are proportional to D, and so may be defined as a =
D, b =
D, and
c =
D. The non-dimensional moment arms
,
, and
may be obtained for a specified packing
geometry. Coleman (1967, MFC) showed that, for closely packed spheres of identical size,
Empirical constraints on KD, KL, and KI were inferred by Iversen and White (1982) using data from the Mars Surface Wind Tunnel, MARSWIT. Wind tunnels allow direct measurement of T , p, D, ρp, U(z), and, most importantly, Ut(z). From these, one uses theory to infer z0,m, ρ, ν, u*, u*t, and Re*t. f(Re*t). Iversen and White (1982) performed wind tunnel observations with MARSWIT over wide ranges of ρ, U, and D. The data were expressed in terms of A, the non-dimensional threshold friction speed from (3.3).
Substituting (3.20), (3.23) and (3.24) into (3.21) we obtain
With the atmospheric approximation ρp ≫ ρ, A2 ≈ u *t2ρ∕(gρ pD) (3.4). Thus we manipulate (3.26) to solve for A2Substituting (3.24) into (3.27) we obtain
The final term term on the RHS represents the effects of cohesion. The D-3 dependence of the cohesion term suggest that A2 may approach an asymptotic value for large D as long as K L is not strongly dependent on D.Iversen and White (1982) defined the cohesionless threshold coefficient A1 by setting the cohesion force FC = 0 in (3.28)
Note that A1 does not depend on D, and thus, in principle, may be inferred from measurements of A2 when the influence of cohesion on (3.28) is known.Greeley et al. (1980, MFC) and Iversen and White (1982) used experiments with MARSWIT to infer KD, KL, and KI (3.23). They removed the effects of cohesion from the data and performed a least squares fit to find
for 0.03 < Re*t < 0.3. Note that the lift parameter KL was found to explicitly depend on Re*t. This dependence on Re*t suggests that the form of KL chosen to non-dimensionalize FL in (3.23) could be improved.If the measured values in (3.30) are used in (3.29), we find
![]() | (3.31) |
Equation (3.31) predicts A1 > 0.66. As previously mentioned, many observations suggest A ≈ 0.2 for large particles (e.g., Bagnold, 1941, p. 88) where cohesive force are presumably small. Thus the assumptions leading to (3.31) have rendered the theory a qualitative, rather than an exact, description of saltation initiation.
In order to reconcile theory with observations, Iversen, Greeley, and colleagues set forth to isolate each functional dependence in (3.28) which could be independently measured. They assumed A could be expressed as the product of three factors: the cohesionless threshold A1 (3.29), a function f(Re*t) (3.17), and a function g(D) which accounts for all interparticle cohesive forces (Iversen et al., 1976a,b, MFC)
![]() | (3.32) |
The absence of interparticle cohesion corresponds to g = 1.
Based on the theoretical influence of FC on A (3.28), g is assumed to have a square-root relationship with A and to be a function of particle size to an unknown power n
![]() | (3.33) |
where n and I are to be determined empirically. Clearly g(D) is a generalized version of the final term in
(3.28): the factor 6
FC∕(π
) is combined into I, and n allows cohesion to depend on a non-integer power
of D. The latter assumption is intuitively appealing because cohesive forces depend on surface
properties (e.g., van der Waals forces, capillarity) as well as volume properties (e.g., electrostatic
charge).
In order to determine I and n, Iversen and White (1982) grouped together many observations of A2(D) for a fixed value of Re *t. Each such curve showed A was strongly dependent on particle size for D < 80 μm, but confirmed that A approaches an asymptotic value of about 0.02 for D > 150 μm. Iversen and White (1982) found that these data were best fit by I = 6 × 10-7 kg m1∕2 sec-2 and n = 2.5
![]() | (3.34) |
where all quantities are expressed in MKS units. Taken together with (3.28), the observed of best fit value
n = 2.5 implies the FC ∝
. The quality of the fit in (3.34) adds confidence to the form of
parameterization chosen for A (3.32).
Once g(D) was known from (3.34), Iversen and White (1982) were able to infer the product A1f(Re*t) from A (3.32). The data were found to obey different functional relations depending on the value of Re*t,
where, following many of the source references, we have used B instead of Re*t. Note that A approaches a limiting value near 0.120 for for B > 10.Using (3.32), (3.34), and (3.35) to compute u*t(D,B) (3.4),
Since Re*t is defined in terms of u*t (3.17), (3.36) is an implicit definition of u*t which must be solved numerically. Note that the semi-empirical u*t defined by (3.36) is a fluid threshold friction velocity, as opposed to an impact threshold friction velocity (cf. §3.3). A computationally efficient form of (3.36) is given in (17.1).Rather than solving (3.36) iteratively, Marticorena and Bergametti (1995) parameterized Re*t(D) using ρ and ν typical of dust source regions
The RHS of (3.37) is usually known. Thus Re*t(D) may be evaluated without iteration, a considerable advantage. However, we are unable to reproduce the accuracy of (3.37) demonstrated in their Figure 1.The numerical solution of (3.36) shows that u*t(D) has a fairly shallow minima at u*t0 which defines the optimal particle diameter for saltation, D0. For a steady friction velocity u* > u*t0 over dry, bare ground, we expect saltation to initiate with particles of size D0. For typical arid regions of Earth, D0 ~ 75 μm (Iversen and White, 1982; Pye, 1987; Shao et al., 1996; Marticorena et al., 1997). The minima is not symmetric in D or u*, however, due to the rapid increase of cohesive forces with decreasing size. Broadly speaking, particles in the range 40 < D < 200 μm are susceptible to saltation.
Predictions of (3.36) agree remarkably well with wind tunnel observations. Iversen and White (1982) tested (3.36) over a wide range of Re*t for particles as small as D = 12 μm. Agreement was within 5% for particles larger than D = 40 μm. Uncertainties in both the model and the measurements become significant for D < 40 μm, which is outside the saltation range. Thus, these uncertainties need not be worrisome. As previously mentioned (3.36) agrees with Bagnolds formulation for particles larger than 200 μm.
For particles smaller than D0, u*t increases very quickly. In fact, for particles D < μm, (3.36) predicts u*t > 1 m s-1, i.e., the threshold speed exceeds values plausible for terrestrial conditions.
Shao and Lu (2000) derive an alternative theory for u*t that fits the wind tunnel data of Iversen and White (1982) but which also has the virtue of resulting in simpler expressions than (3.36).
To summarize, Bagnolds formulation (3.4) predicts that u*t decreases with D so that very small particles should be most efficiently mobilized. Noting, however, that all observations show that u*t(D) decreases with D until a critical particle size D = D0, Iversen and colleagues developed a semi-empirical formulation for u*t (3.36) which accounts for lift and cohesive forces. Their formulation agrees well with wind tunnel measurements for 12 < D < 1000 μm.
Until now we have concentrated on the determination of the threshold friction velocity u*t required to initiate motion of particles of diameter D initially at rest. A useful theory of dust mobilization also requires specification of the horizontal mass flux of all particle sizes and at all heights, since this quantity can be measured in a wind tunnel.
![]() | (3.38) |
where n is the number distribution of particles, M their mass, and v their horizontal velocity. The units of q are kg m-2 s-1. In addition to u *t(D), a useful theory of dust mobilization requires specification of the vertically integrated horizontal mass flux due to saltation
![]() | (3.39) |
where zs is the height of the saltation layer,
The units of Q are kg m-1 s-1 rather than kg m-2 s-1 since a vertical integration of the streamwise mass flux has been performed. The integration over D ensures Q includes all sizes of saltating particles, while the integration over z ensures Q includes particles (including suspended dust) at all levels. Thus Q is the mass crossing orthoganally through an infinitely tall column per unit width of the column. Q is often called the streamwise mass flux since it measures the movement of crustal material in the direction of the prevailing winds.
The total streamwise movement of surface material Q is the result of three intertwined processes, saltation, suspension, and surface creep. Saltation includes the movement of all airborne particles which are too large to become suspended. Suspension, on the other hand, includes the movement of all particles The prevailing aerodynamic conditions play a role in determining what particles are susceptible to long term suspension and transport, so there is no single size below which particles are always suspended and above which never suspended. However, as a rule of thumb we call particles larger than 60 μm in diameter sand, other particles are collectively referred to as dust.
Surface creep accounts for the movement of particles which are pushed along the surface. The creep may be caused by the wind directly or by nudges from saltator impacts. The important distinction is that saltating particles remove momentum from the near surface wind which decreases the friction velocity felt by the surface. Creeping particles, on the other hand, do not directly remove any momentum from the near surface wind, and thus do not lessen the surface friction velocity.
With the above discussion in mind, we may also write Q (3.39) as the sum of the individual streamwise fluxes due to saltation Qs, surface creep Qc, and suspended dust Qd thusly
According to Bagnold (1941), Qc ~
Qs in typical conditions. Observations by Shao et al. (1993)
indicate that Qd ~ < Qs. As described in §3.3.4, Qd∕Qs is called the bombardment efficiency.
A primary goal of mineral dust studies is the prediction of the lifecycle of dust particles which begins with Qd. As shown above, wind tunnel studies (e.g., Iversen and White, 1982) show that the threshold velocity u*t (3.36) increases rapidly (due to cohesive forces) for particles smaller than about 60 μm, and exceeds terrestrial conditions for D < 10 μm. Thus most long-lived dust particles are thought to be initially lofted by impacts from more massive saltators rather than directly lofted by the wind. Hence particles in suspension are said to be secondary particles. For this reason Qd depends intimately on Qs. Thus we concentrate on Qs before turning our attention to the link between Qs and Qd in §3.4.
Many expressions have been proposed which express Q in terms of u* and u*t. Greeley and Iversen (1985) summarize these expressions in their Table 3.5. These expressions are based on theories or observations of particle saltation. The theories must predict the concentration and motion of particles set into motion by u*, as well as particles released by the impact of saltating particles. Complicating these theories is the interaction between particles of different sizes.
Theoretical and empirical evidence strongly suggests the horizontal flux of saltating particles Q varies with the cube of the wind friction velocity during saltation u*,s Owen (1964); Shao et al. (1993)
For now C is a dimensional constant which is a function of aerodynamic, surface, and soil properties to be defined below. Note that (3.41) is equivalent to (41) of Owen (1964).Since the wind speed is related to the wind friction speed by U = Cm1∕2u *, we may rewrite (3.41) as
Leys and Raupach (1991) used a portable wind erosion tunnel to measure u*t(D) and total streamwise mass flux Q in field conditions in Australia. The observed Q was well described by (3.39). They also predicted u*t with four competing methods, including Equation (3.36). Unfortunately, no method, including (3.36), adequately predicted the observed u*t.
We now show the development of many theories for Q, including those of Bagnold, Kawamura, Owen, and the Australian school. Unfortunately, authors in this field have often inadvertently incorporated typographical errors into their papers (and models) (Namikas and Sherman, 1997). Baas (2005) covers this subject with more up-to-date examples, and intercompares some of these theories. Papers with known typographical errors include Blumberg (1993, equation 3.2), Lancaster (1995, equation 2.12), White (1979) (equation 22), Greeley et al. (1996, table 2, equation 4), Pye and Tsoar (1990, equation 4.48), Pankine and Ingersoll (2002), and Zender et al. (2003a) (equation 10). Researchers are urged to verify the correctness of their saltation formulations by comparison to the original formulations.
Bagnold (1941) developed the original theory relating Q to wind speed based on the energetics of an idealized, steady state, linear, saltation zone. A few qualitative observations motivate the strategy of Bagnolds theory of saltation. The first, alluded to in §3.2.1, is that once saltation has initiated by winds exceeding the fluid threshold (u* > u*t), the downstream surface wind speed drops because some fraction of the drag is now exerted on suspended particles rather than directly on the surface. Downstream saltation continues as long as the surface wind speed exceeds the impact threshold, i.e., u* > u*ti.
Once saltation initiates, moreover, the ambient wind speed U may reach any strength but the surface wind speed is relatively constant. In other words the velocity gradient near the surface can grow without bound, but the surface wind speed at about 3 mm height is insensitive to this gradient. These qualitative observations strongly suggest that drag in excess of that necessary to maintain saltation is dissipated in the atmosphere by the saltating grains. Note that this observation is the basis of the second hypothesis of Owen (1964) (cf. §3.3.2).
These observations underpin Bagnolds simple energetic explanation of the cubic dependence of Q on u*. Consider the following idealized scenario: A bed of particles of identical size D and mass Ms saltates in a steady state wind with friction velocity u*. The wind (rather than impacts by other particles) is responsible for lifting each particle into the atmosphere with an initial horizontal velocity u0. The wind transports each particle a mean horizontal distance L before the particle fall to the surface. During this transport, the wind accelerates the particle to a final horizontal velocity u1 which is completely dissipated in the impact.
We now impose energy conservation constraints on this system. The initial and final momenta of the particle are Msu0 and Msu1, respectively. The difference between these momenta, Ms(u1 - u0), is extracted from the atmosphere over the distance L. Therefore the rate of loss of atmospheric momentum per unit area due to a total horizontal mass flux of saltating particles Qs must be
![]() | (3.43) |
Newtons second law (18.81) tells us that the rate of change of momentum is equivalent to the applied force. In this case, the applied force is the surface wind stress due to particle the drag of the particles on the wind τp.
We note that τp < τ since some of the total wind stress τ (2.1) goes directly into the surface rather than into increasing the momentum of airborne particles. Subsequent theories of Qs, presented below, explicitly account for the distinction between τ and τp. Inserting (2.3) into (3.44) To progress further, Bagnold (1941) made use of two qualitative observations. First, the initial trajectory of a particle uplifted by wind is nearly vertical, but the trajectory at impact in nearly horizontal which implies u1 ≫ u0 so that Second, Bagnold observed that u1∕L ≈ g∕w0, where w0 is the mean initial vertical velocity of a saltating particle. This observation is consistent with the approximation that sand particles undergo ballistic trajectories. The atmospheric residence time Δt of a sand particle ejected into the atmosphere at speed w0 is Δt = 2w0∕g. If the mean horizontal velocity of the particle is
then the total streamwise distance
traversed is Inserting (3.47) in (3.46) and assuming
~ u1 leads to where we have dropped the factor of 2 in (3.47) for consistency with Bagnolds original formulation.
To proceed further than (3.48), is necessary to discover or formulate a relationship between w0 and u*. Bagnold argued that, on average, w0 = C1u* where C1 is called the impact coefficient. In a perfectly elastic reflection, or ricochet, C1 = 1. An elastic collision may also eject multiple saltators as products, in which case C1 < 1 for each product. However, it is quite possible to have C1 > 1 when large particles eject smaller particles. Bagnold reasoned that particles are ejected with a velocity proportional to the incident velocity of the impacting particle which, he argued, ought to be u* on average. This reasoning is somewhat difficult to defend, but the assumption turns out to be correct. A better justification for this assumption is that fxm. This leads to our first derivation of the well known phenomena that the horizontal mass flux due to saltation is proportional to the cube of the friction velocity
Bagnolds observations fit (3.49) best with C1 ~ 0.8.Based on careful analysis, Bagnold empirically modified (3.49) to include a factor of (D)1∕2. With this correction, and subsuming C1 into a new empirical constant cs
where all parameters are specified in MKS.Expressing (3.50) in terms of U rather than u*, Bagnold found
where (3.51) yields (3.52) for typical conditions in natural dunes.
Owen (1964) developed a physical theory describing the saltation of uniform particles in air. His theory continues to serve as the best mathematical definition and description of saltation, as well as being a valuable exposition of mathematical physics in its own right.
Owens two hypotheses are:
|
I. The saltation layer behaves, so far as the flow outside it is concerned, as an aerodynamic roughness whose height is proportional to the thickness of the layer. II. The concentration of particles within the saltation layer is governed by the condition that the shearing stress borne by the fluid falls, as the surface is approached, to a value just sufficient to ensure that the surface grains are in a mobile state. |
Kawamuras work on sand transport in the late 1940s and early 1950s is not widely known. During this time Kawamura developed a rather complete theory for the streamwise saltation flux (1951) which appeared in translated form in 1964. White based his formulation for the streamwise saltation flux (White et al., 1976; White, 1979) squarely on Kawamuras work. Thus, White appears to be the first to recognize the efficacy of Kawamuras work for modern dust models. Unfortunately (but understandably), many references inadvertently attribute Kawamuras formulation of streamwise mass transport to White (1979). In recognition of Whites association, we sometimes refer to this as the Kawamura/White formulation.
Rather uniquely, White and colleagues performed numerical simulations of the saltation jumps of individual particles based on first principles, i.e., the equations of motion. These simulations, in aggregate, later serve to validate simplifying assumptions he makes in his bulk theory. The equations of motion for a particle saltation take the form

,
) and (
,
) are the x and y components of the particles velocity and acceleration, respectively,
FL and FD are the lift and drag forces on the particle, u is the streamwise wind speed, and ur is the relative
speed of the particle to the wind. By definition the mean vertical wind speed is zero in the saltation layer
so that 
The lift and drag forces on the particle are expressed in terms of the lift and drag coefficients CL and CD as

The drag force on a particle is usually expressed in terms of the density of the medium, the projected area of the particle, and the square of the particles velocity.
where A is the cross-sectional area of the particle. This form of relationship between CD and FD has been chosen for several reasons. First, the solution to the problem of flow over a sphere tells that FD ∝ v∞ when Re ≪ 1. However, we also know that the pressure, or force per unit area, should vary as ρv∞2 (from Bernoullis theorem?) as Re → 1, F D. For spherical particles, (3.58) implies As presented in §2.1.1, the total stress to the surface τ is the sum of a particle drag and an aerodynamic
drag. The particle drag on the surface, τp, is caused by the horizontal deceleration of the impactors
by the surface. The aerodynamic drag on the surface, τa, is the drag directly due to gas flow
over the surface (2.2). We know τ (2.3) and can obtain τa using Owens second hypothesis
(§3.3.2)

Equation (3.61) defines τp as a residual between the total surface stress and the aerodynamic stress. We may also define τp directly from kinematic considerations as the rate of deposition of streamwise momentum to the surface by the saltating particles. If Fs is the downward mass flux of saltating particles per unit area per unit time, then the total streamwise momentum deposited to the bed by the particles is
where u0 and u1 are the mean initial and final streamwise velocities during a saltator jump. Conceptually, we may view u1 - u0 as the velocity change of the same saltator as it repeatedly skips of the surface, depositing some momentum with each impact. Then the particulate mass flux Fs times the mean change in particle velocity is the momentum flux. Note that the initial saltator velocity u0 contributes to particle momentum rather than surface stress, so it is subtracted from τp.Let us denote the mean initial vertical velocity of saltating particles as w0. Then the mean initial vertical momentum of saltating particles is w0Fs. Clearly the initial vertical momentum of saltating particles varies with the intensity of saltation. One possibility is that w0Fs obeys a functional relationship with the surface saltation stress τp. For example, one might hypothesize that τp is converted into vertical momentum with some non-unity efficiency. More specifically, we shall assume that w0Fs is linearly proportional to τp. Then (3.61) and (3.62) imply
Note that (3.63) assumes If the initial vertical momentum of a saltating particle is proportional to the kinetic energy released by surface bombardment then (or is this assuming the vertical momentum flux of ejected particles must vary as the horizontal momentum flux deposited by bombarding particles)The relationship in (3.63) assumes that the kinetic energy of bombardment converts to vertical momentum of the product saltators with an imperfect, but constant, efficiency. In other words the bombardment process is inelastic. The disposition of the unaccounted-for energy is not specified. The theory of Shao et al. (1993), presented below, extends this treatment of energy conversion in developing a theory for the vertical flux of small dust particles.
The crucial advance of Kawamuras theory is made possible by the assumption of a relation between Fs and the friction speeds. MARSWIT data and the saltation model of White (1979) (described above) both support the following empirical relationship
Combining (3.64) with (3.63) we obtain White (1979) noted that the values of w0 and L predicted by (3.65)(3.66) agreed with direct numerical integration of the equations of motions for saltating particles.The total streamwise saltation flux is simply the product of Fs and L. Using (3.64) and (3.66),
where, as before, cs is the dimensionless constant of proportionality between saltation mass flux and the factors proportional to the cube of the friction speed. Factoring out the u*3 factor in the final step brings the form of (3.67) into closer agreement with Bagnold (3.50) and Owens. Note that (3.67) was derived and tested for monodisperse soil distributions.Namikas and Sherman (1997) and Baas (2005) document that Equation (19) in White (1979), which corresponds to Equation (3.67) has a typographical error which propagated into some dust emission models apparently including Pankine and Ingersoll (2002). If adopted, this error would cause models to overpredict dust emissions. In practice, however, the erroneous equation performs no worse than other (correct) mobilization implementations. By coincidence, Zender et al. (2003a) also contains a typo in its version of Equation (3.67)1 .
White (1979) used MARSWIT to replicate a variety of Earth and Martian saltation conditions in order to determine cs. With small glass beads (D = 0.208 mm) as saltators, they found cs = 2.61 under a wide range of conditions. This differed by only 6% from Kawamuras original estimate of cs = 2.78 (Namikas and Sherman, 1997; Baas, 2005). From this we may infer that (3.67) contains all the relevant physics of saltation for both the Earth and Mars simulations. Of course, such complicating factors as moisture, heterogeneous soil sizes, and vegetation were not considered in the tests. Nevertheless, the consistency of the experiments of White (1979) with (3.67) are very encouraging as a point from which to begin to include the effects of more complicating factors.
Researchers in Australia published theories for saltation and sandblasting beginning in the 1990s. This research involved many groups, though Michael Raupach and Yaping Shao appear to be most consistently behind it. I refer to their approach as the Australian School, since it is nicely synthesized and originally evaluated with Australian models. Shao et al. (1993) present a theory for the streamwise saltation flux which differs slightly from the Kawamura/White formulation (§3.3.3). Lu and Shao (1999) and Shao (2001) summarize the full development of this theory. Raupach and Lu (2004) includes these theories in the context of more general treatments of mobilization and dry deposition.
The Australians approach considers uniform particles of mass Ms in steady state saltation. In steady state, the mean rates of saltator bombardment and ejection per unit surface area are equal, and denoted by N↑ s which has units of m-2 s-1. With these assumptions the vertically integrated streamwise saltation flux defined in (3.39) may be rewritten as
where, as before, L is the downstream projection of the mean particle jump.As in the Kawamura/White formulation (§3.3.3), we assume τ and τa are given by (3.60). Combining Bagnolds expression for τp (3.44) with (3.68) we obtain
Finally we obtain a relation for N↑ s by substituting values from (3.60) and (3.69) into each term in (2.2) Following Bagnold, Shao et al. (1993) note that L =
Δt where
is the mean streamwise velocity
during the jump. For ballistic trajectories, Δt = 2w0∕g so L = 2w0
∕g. Thus, using the ballistic
assumption for L and (3.70) for N↑
s in (3.68) where cs is a dimensionless coefficient which incorporates the last two factors on the RHS of (3.71). Following
reasoning similar to that presented in the development of (3.47) and (3.49), Shao et al. (1993) assert
~ u1
and w0 ~ u*2 .
If both factors comprising cs are of order unity, then cs is 𝒪(1) as well.
The parameter cs (3.72) appears in most theories of Qs (e.g., Greeley and Iversen, 1985, p. 100). As presented in §3.3.1, Bagnold (1941) estimated cs ~ 0.8. Equation (47) of Owen (1964) estimates cs empirically to be
where vg (5.25) is the terminal fall speed of the particle. For D ~ 150 μm and u* ~ 0.8 m s-1, (3.73) predicts cs ~ 0.8, which agrees with Bagnolds estimate.Note that N↑ s (3.70) can be expressed in terms of Qs using (3.68) and the ballistic approximation for L
If a saltating particle undergoes constant streamwise acceleration while airborne then its mean horizontal
velocity is
= (u0 + u1)∕2. Constant acceleration is a plausible assumption for some particles (fxm:
which???). The total streamwise distance traversed is then
Until now we have concentrated on predicting the wind-initiated motion of saltating particles but we have put aside consideration of the mass flux of the smaller, suspended particles known as dust. Bombardment by saltating particles, or sandblasting, is thought to be the ultimate source of most fine dust emissions. The theory of sandblasting has been extensively developed by Alfaro, Gomes and coworkers (Gomes et al., 1990; Alfaro and Gomes, 1995; Alfaro et al., 1997, 1998; Alfaro and Gomes, 2001). Applications of these theories in regional scale models is infrequent (Shao et al., 1996; Shao and Leslie, 1997; Gong et al., 2003). Saltation-sandblasting is beginning to appear in global scale models (Grini and Zender, 2004; Grini et al., 2005). The small size and long atmospheric residence time of dust particles causes them to exert significant influences over climate.
Saltation is summarized by the streamwise saltation flux Qs. Likewise, the streamwise mass flux of dust is denoted Qd. The vertical mass flux of dust particles through a horizontal plane is
![]() | (3.77) |
When z > zs, then (3.77) includes only dust mass so that F = Fd. The units of F are kg m-2 s-1. To distinguish dust particles from saltating particles, we shall use Md and Ms, respectively. Dust, by definition, is suspended in the atmosphere and does not immediately settle back to the surface. Thus F is somewhat insensitive to z once z > zs. Many large scale atmospheric models assume turbulence uniformly mixes all dust emissions into the lowest atmospheric layer, so that the net dust source term is taken to be F(z = zs). Note that the mean streamwise distance from ejection to impact L, which proved useful in defining Qs (3.68), does not appear in (3.77).
Prediction of Fd is the crux of mineral dust aerosol models. To date, all theories are based on establishing a relation between Q (3.41) and Fd (3.77). There is good observational evidence to support this link (Shao et al., 1993; Gillette et al., 1997, e.g.,), but the lack of theoretical support is somewhat discomfiting.
The most successful theories are based on the energetics of the impact-ejection mechanism. Each ballistic impact a saltating particle with the surface results in a transfer and conversion of momentum and kinetic energy from the saltating particle to the surface. We have seen that some horizontal momentum is transferred into soil creep. The vertical momentum may be reflected into the next bounce of the saltator, or it may initiate the ejection of another saltator. When the product of an impact is the ejection of dust, however, it is likely that some energy has been used to break the cohesive bonds binding the dust particle to the surface. Thus some fraction of the energy from particle bombardment is responsible for the injection of dust into the atmosphere. The theory of Shao et al. (1993) explains many, but not all, of the observed features of the Fd-Qs relationship.
Shao et al. (1993) developed a theoretical framework for the rupture of the interparticle bonds between dust particles and the surface. They allow for a mean interparticle binding energy of ψ. ψ is the depth of the energy potential well which must be surmounted in order to free the dust grain from the surface. Thus ψ accounts for the forces of cohesion FC and gravity FW discussed in §3.2.3. ψ is also related to the modulus of surface rupture discussed by Gillette and Passi (1988).
They consider a scenario where a saltator impacts the surface and ruptures the bonds of, on average, Π dust grains which are then ejected from the surface along with zero or more saltators. We call this the impact-rupture-ejection scenario. Let the kinetic energy of the impacting saltator be E1 and the total kinetic energy of the product saltators (which include the original when reflection occurs) be E2. Thus the energy available for freeing dust bonds is ΔE = E1 - E2. Let us define cε as the mean fraction of ΔE which is channeled to rupturing dust bonds. Energy conservation requires cε < 1 since, in addition to other sinks, some of E1 is converted into the kinetic energy of the ejected dust particles. Then the energy balance of each saltator impact is
By definition, dust is suspended once it is emitted, so there is no downward flux of dust particles in the saltation layer. Therefore the net vertical dust flux is simply the dust emission flux, which is the product of the areal rate of saltator impacts N↑ s and the dust production efficiency per impact Π. With these assumptions the areal rate of emission of dust mass from the surface defined in (3.77) may be rewritten as
Substituting Π from (3.78) into (3.80) we obtain We use (3.70) for N↑ s to rewrite the RHS of (3.81) in terms of Qs Let us now examine the ΔE term. If u1 and w1 are the mean streamwise and vertical components of a
saltators velocity at impact, then its kinetic energy is E1 =
Ms(u12 + w
12). Shao et al. (1993) assume
that u1 ≫ w1 so that E1 ~
Msu12. Then, they assume each bombardment ejects only one saltator. We
call this conservative bombardment since, on average, it is equivalent to an inelastic saltator reflection at
each impact-rupture-ejection event. In conservative bombardment every sand grain is the sole product of
one bombardment, i.e., E2 = E0. Clearly this assumption is only plausible for steady state saltation. In
these conditions
If the conditions for conservative bombardment are met, then we may substitute (3.83) for ΔE so that
where α, which has dimensions of m-1, is the ratio of the dust vertical mass flux F d to the streamwise saltation flux Qs. α is called the flux ratio3 . As described below, it is possible to infer α from measurements of Qd and Qs (Shao et al., 1993). Thus we shall compare the α defined by (3.85) to the α predicted using alternate theories.Inserting (3.72) back into (3.84), Shao et al. (1993) defined a new parameter α1
where α1, whose units are kg s2 m-5, subsumes the final two factors on the RHS of the preceding equation. Note that the RHS of (3.84) and (3.86) is a function of the size of the saltating particles Ds. Since surface soils comprise a continuous size distribution of saltators, (3.84)(3.86) should be discretized into bins which each represent the dust emissions produced by a given Ds. An example of this discretization in a global mineral dust model is described in §17.The factors defining α (3.85) and α1 (3.86) are similar and bear further examination. Consider first the dimensionless speed factor γ = (u1 + u0)∕(2u*). Equations (19) and (20) of Owen (1964) are formulae for u0 and u1 in terms of u* and D. Shao et al. (1996) evaluated these expressions numerically and found that γ ≈ 2.5 for most conditions. Hence the proportionality parameters from (3.85) and (3.86) are, respectively,
where γ ≈ 2.5. Knowing all the terms in (3.88) would allow us to predict vertical dust emissions at all scales. The two terms which remain ill-defined are the mean kinetic energy transfer efficiency, cε, and the mean energy binding dust particles to the surface, ψ (3.78). Estimating cε and ψ from first principles is currently one of the most pressing challenges in theoretical studies of aeolian erosion.Shao et al. (1996) introduced a semi-empirical method for obtaining cε and ψ. First, they assumed that ψ is the product of a length scale determined by the dust particle size and the mean drag force due to the friction wind
where cψ is the dimensionless length scale and is 𝒪(1). Substituting (3.89) into (3.88) where we have defined the bombardment parameter β ≡ cε∕(cscψ) in the last step. The bombardment parameter contains most of the uncertainties in the problem.We may invert (3.90) to solve for β
In a wind tunnel experiment, all quantities on the RHS of (3.91) are inputs known a priori (ρ,ρp,g,Dd,U), are determined by theory and/or measurements (u*t,γ), or are directly measured after the experiment (Qs,Fd). The best empirical fit to the wind tunnel dataset gathered by Shao et al. (1993) is where Dd,Ds are in mm and β > 0.Shao and Li (1999) further developed these theories and applied them in a Large Eddy Simulation.
Marticorena and Bergametti (1995) have synthesized many theories and observations into a comprehensive global mineral dust emission model. Many components of their model are described in the sections above. We focus now on the components which are native to their model.
Marticorena and Bergametti (1995) begin by adapting the streamwise saltation results of White (1979) for Qs (3.67) to account for more realistic soil conditions. First, they accounted for the fraction of surface that actually consists of erodible soils. This fraction, E, includes only bare ground or sparsely vegetated surfaces susceptible to saltation. For example, E excludes bare stone surfaces, swamps, and lakes. However, E does not exclude surfaces which require only large friction speeds to initiate saltation, e.g., wetted soils. Clearly Qs is linearly proportional to E. Defining R as the ratio of threshold friction speed to friction speed, (3.67) may be rewritten as
where the functional dependence of Qs on D indicates that (3.93) applies only to a monodisperse distribution of particles of size D.In order to apply (3.93) to a continuous size distribution n(D) in the source soil, some simplifying assumptions are required. First, Marticorena and Bergametti (1995) assume that the value cs = 2.61, empirically derived from monodisperse saltation experiments in MARSWIT (White, 1979), is size-independent and applies equally to heterogeneous, polydisperse size distributions. Second, they assume that the mass flux Qs(D) arises only from motions of particle sizes between D and D + ΔD. In other words they assume that interactions between particles of different sizes do not contribute significant errors to (3.93), which is based on monodisperse assumptions. This approximation breaks down in the limit of dust production by ballistic impacts, since the impact of one large particle is assumed to eject many small dust particles. Shao et al. (1996) contains a more thorough discussion of the validity of these approximations. Nevertheless, with these two assumptions,
where p(D) is the PDF which defines the normalized, fractional contribution of each size D to the total mass flux. These assumptions imply that cs = 2.61 defines Qs through (3.93), regardless of the underlying size distribution of the parent soil. The only remaining difficulty is in determining p(D).Marticorena and Bergametti (1995) assume that p(D) is best represented by the fractional cross-sectional area distribution of the soil. This appears to be a reasonable assumption because, in the absence of information to the contrary, the fractional surface area covered by grains of a given size should vary linearly with the cross-sectional area of the grains. Moreover, the exposure of saltation grains to wind also is proportional to the cross-sectional area of the grains. Another plausible assumption is made by Shao et al. (1996), who, as described below, set p(D) to the fractional mass distribution of the soil.
The discretization of (3.94) proceeds as follows. Continuous soil size distributions are most often
approximated as multi-modal log-normal distributions, i.e., The three parameters required to define each
mode. The parameters usually available from soil sieving techniques are the mass median diameter
v,
the geometric standard deviation σg, and the mass fraction M. Thus it will be convenient to express p(D)
in terms of M(D). To do so, we first put down the geometric relations between the cross-sectional area,
mass, and volume of spherical particles
![]() | (3.95) |
We now take the limit of (3.95) to define the differential changes of area and mass in terms of eachother
![]() | (3.96) |
We may normalize the increments of area and of mass by dividing (3.96) by A and M, respectively
![]() | (3.97) |
By definition, ∫ dA = 1 and ∫ dM = 1. Thus A and M are properly normalized PDFs and either may take the place of p(D) in (3.94).
Using (3.97), we may discretize (3.94)
To convert this to a vertical dust flux Fd, Marticorena and Bergametti (1995) assume the relation
Subject to the approximations discussed in §3.4.1, (3.99) was proved by Shao et al. (1993) (3.85). Instead of attempting to evaluate α from first principles, they take an empirical approach.Gillette (1979, 1981) describes a dataset comprised of measurements of Fd and Qs at numerous (anywhere from two to ten) friction velocities for each of nine distinct soils. These data are reproduced in Table 3.1.
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All soils except soil 9 (a clay) are very dry, with volumetric water contents θ < 0.013 (θ is defined in §3.7.1). These data show that more finely textured soils (i.e., with higher clay content) produce more dust per unit Qs than coarser soils (i.e., with higher sand content).
Marticorena and Bergametti (1995) showed that, in this dataset, the percentage of clay particles (D < 2 μm) in the source soil explains more than 90% of the covariation of Fd with Qs. Their best linear fit is
where M% clay is the mass fraction (in percent) of clay particles in the parent soil. Thus α is extremely sensitive to Mclay, increasing by nearly three orders of magnitude as Mclay the soil texture changes from Mclay = 0.0 (sand) to 0.20 (sandy loam). In SI units, (3.100) becomes Thus, α is observed to increase exponentially with Mclay for Mclay < 0.20. For clayier soils the few available observations suggest α eventually begins to decrease with Mclay. This reduced deflation efficiency for soils very rich in clay is consistent with interparticle cohesive forces increasing the mobilization inhibition as clay particles begin to dominate the soil (Gillette, 1979, 1981; Marticorena and Bergametti, 1995). The physical arguments for mobilization inhibition due to interparticle cohesive forces is discussed more quantitatively in §3.7 below. Unfortunately the soils in Gillettes dataset with Mclay > 0.20 had significantly higher soil water content than did the soils with Mclay < 0.20. Thus it is difficult to use these data to form conclusions regarding the behavior of α for dry soils when Mclay > 0.20.In their regional dust model, Marticorena et al. (1997) used a blended average approach rather than using (3.100) directly. First they defined four distinct characteristic populations of coarse particles found in arid and semiarid regions based on Chatenet et al. (1996). The mineralogical and geometric features of these populations are described in Table 3.2.
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The value of α assigned to each population was arrived at by blending the observed α from the datasest of Gillette (1979, 1981). The first soil type, Aluminosilicated Silt, refers to many compounds such as Al2O3, SiO2, . . . The second soil type, Fine sand, includes . . . The third soil type, Coarse sand, includes . . . The fourth soil type, Salts, includes . . . fxm
Alfaro and co-workers find that soil texture and composition affect soil crusting and aggregation in wind-tunnel experiments on soils of widely varying composition and texture. In particular, CaCO3 affects aggregation. Interestingly, they found no detectable influence of texture and composition on sandblasting efficiency per se. Thus, composition and texture may influence the threshold velocity of saltation, but have no direct affect on sandblasting. This surprising result de-couples composition from sandblasting and helps to simplify models.
Shao represents the size distribution of saltators in air, ns m(D) as a weighted combination of the size distribution of the source soil in a natural (undisturbed) state, nn m(D), and in a fully disturbed state, nf m(D).
where a is fractional area of the fully disturbed soil. The relationship between nn m and nf m must be determined empirically.Aeolian soils are those formed with significant contributions from upwind dust sources. These soils are often called loess, although the specific definition of loess is context-sensitive (fxm: add note loess commission in INQUA). Soils accumulate and form downwind of dust sources when bioclimatic constraints such as vegetation and incisions trap near-surface clay and silt particles. Muhs (1983) shows that regional winds called Santa Anas deposit silty loam soils on the Channel Islands in California. Sweeney et al. (2005) and Stroeve et al. (2005) describe the evidence for loess-production in the the Eureka Flat flat region of the Palouse in the northwest U.S.A.
The composition of many of the most common minerals comprising dust is given in Table 3.3.
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Quartz (SiO2) is most commonly associated with sand. Opal (SiO2(H2O)n) content is often measured in oceanographic cores (e.g., Adkins).
For lack of other information, many studies assume mineral dust comprises the same elemental distribution as is found, on average, in Earths mantle. Table 3.3 list the elemental composition of Earths crust according according to Lide and Frederikse (1995).
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Marticorena et al. (1997) found that the Western Sahara desert could be adequately described by eight different soil types. Each of the eight possible soil types is a predefined blend of the four soil populations described in Table 3.2. Table 3.5 defines the populations composing each of the eight soil types.
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The characteristics of the complete soil size distribution of a given soil type are a weighted average of the chacteristics of each of the soil sub-populations. Thus the mean flux ratio for a given soil type with N distinct soil subpopulations, shown in the last column of Table 3.5, is computed as
where Mi, given in Table 3.5, is the relative mass fraction of the ith subpopulation. Each soil type is comprised of up to three log-normal size distributions in the saltation range 125 ≤
n ≤ 690 μm.
The dynamical model of Marticorena et al. (1997) has 1∘× 1∘ horizontal resolution. Using a GIS database of surface features, they subdivided each of these dynamical gridpoints in the Western Sahara into at most five subgrid soil types. The total dust emission flux into each dynamical gridpoint was then composed of the areal weighted fraction of its constituent soil types.
One of the aspects of wind tunnel observations which has not been explained by (3.84) is the apparent increase in bombardment efficiency, as measured by Qd∕Qs (c.f. Shao et al., 1993, Figure 5).
Relaxing the conservative bombardment assumption so that more than one saltator ejection per impact is allowed results in
where ui is the initial streamwise velocity of the ith product saltator.
Equation (3.39) is valid only in an instantaneous or equilibrium sense. Prediction of wind erosion in large scale atmospheric models is complicated by the non-linearity of (3.39). To obtain the total horizontal flux in a given period of time we must include the effects of spatial and temporal wind speed variation.
Consider a time-series of wind speeds U(t) with time mean wind speed
. In practice
is known
either from observations or model predictions, and represents the mean of the actual wind speed
U(x,y,t) over given region and period of time. In a typical large scale atmospheric model
may be a
1030 minute average wind speed over an area of 104 km2. The non-linear, cubic relation between Q and
U causes Q(
) to differ significantly from Q(U) on such scales. To more accurately estimate of
we
must make assumptions about the temporal and spatial distributions of the wind whose mean value is
.
The importance of the sub-gridscale wind PDF cannot be overstated. Both Aeolian and fluvial shear stress experiments show that the tail-end of the fluid velocity distribution causes much, if not most, of the entrainment. Since wind variability is related to the mean wind speed (Justus et al., 1978) and saltation is driven by high wind speeds, it follows that dust events are characterized by highly variable winds. In turbulence studies, these are called burst and sweep cycles. A burst is a high-intensity shear event which creates a micro-low pressure zone. The sweep occurs as the fluid fills in this low, often excavating (eroding) the surface at the same time. These events may remove the quasi-laminar layer (Section 5.5) (Sehmel and Hodgson, 1978a).
We assume that an analytic probability distribution function (PDF) governs the spatial and temporal distribution of surface wind speeds. The PDF differential p(U) dU is the probability that the wind speed at a given time or location is between U and U + dU. This is equivalent to the relative fraction of time or space4 occupied by wind speeds between U and U + dU. Since the probability of having a finite wind speed is exactly one, the PDF must be normalized such that ∫ 0∞p(U) dU = 1. A suitable PDF thus acts as a weighting function to the instantaneous horizontal flux. The temporal and spatial average horizontal flux is found by convolving p(U) with (3.42)
![]() | (3.108) |
Justus et al. (1978) showed that an analytic form well suited for describing the probability density function of the surface wind field is the Weibull distribution. More recent studies have justified the use of the Weibull distribution for dust emissions in particular (e.g., Gillette and Passi, 1988; Shao et al., 1996; Cakmur et al., 2004). We define and derive the analytic properties of the Weibull distribution of wind speeds pW (U) (18.20) in §18.10 below. In a Weibull distribution the frequency of occurrence of winds exceeding Ut decreases exponentially with Ut, i.e., pW (U > Ut) = exp(-Ut∕c)k where c and k are, respectively, the scale parameter and shape parameter of the Weibull distribution (18.29). Employing pW (U) in (3.108) we obtain
![]() | (3.109) |
As shown in §18.10, integrals of the form Unp W (U) may be expressed analytically in terms of the incomplete gamma function. Applying (18.26) to (3.109) we obtain
![]() | (3.110) |
Gillette and Sinclair (1990) estimated that the injection of mineral dust into the atmosphere over the United States by dust devils is comparable to that injected by large scale dust mobilization. Renno (fxm: find this reference) also suspect dust devils are important.
Golitsyn et al. (2003) investigated weak dust emission processes, i.e., processes important in weak wind conditions when saltation is minimal and dust fluxes are small. They found emissions in the Aral Sea region are consistent with a dust devils and, possibly, with electrophoresis. Yablokov and Andronova (2004) explain the conditions under which electrostatic effects may be import for dust liftoff. Koch and Renno (2005) develop a theory for dust entrainment by dry convective plumes and vortices, and estimate such dust devils are responsible for about one-third of total dust mobilization on Earth.
In a series of papers Raupach and colleagues have developed a theory of the drag partition between erodible and non-erodible surfaces (Raupach, 1991, 1992; Raupach et al., 1993; Raupach, 1994). Part of this theory recognizes that saltation alters the roughness characteristics of the boundary layer. In neutral conditions the relation between wind speed U and wind friction speed u* is a logarithmic profile (2.6). The relationship depends on height z above the surface and the roughness length. In a non-saltating environment, (2.6) may be re-expressed as
In (3.111), the symbol z0,0 is the non-saltating roughness length. The Owen effect is the name given to the positive feedback of saltation on wind erosion via roughness length increases. Owen (1964) showed that the saltation layer which develops during wind erosion events acts as an additional sink of atmospheric momentum, causing an increase in momentum deposition to the surface and thus an increase in roughness length. Saltating particles mediate this effect by removing momentum from the atmosphere and transferring it to the surface during each (non-ballistic) impact.Raupach (1991) showed that the Owen effect entails an implicit relationship between the saltating roughness length z0,s in terms of the non-saltating roughness length z0,0
where A is a constant of order unity, g is the acceleration of gravity, and R is the ratio of u*t to u* (3.93). Equation (3.112) must be solved iteratively because the friction speed u* itself depends upon z0,s (cf. §2.2.2). Studies have verified that roughening of the surface due to the Owen effect could be quite dramatic (Gillette et al., 1998), although difficult to predict using (3.112).Gillette et al. (1998) tested Raupachs theory (Raupach, 1991) of the Owen effect (Owen, 1964) against data from Owens Lake, California. Using measurements of saltation events taken at three stations over the course of a year, Gillette et al. not only verified (3.112), but parameterized it into a form easier to evaluate. First, they defined the saltating friction velocity u*,s as the friction velocity measured during fully developed saltation, when the roughness length z0,m ≡ z0,s, the saltating roughness length. Under neutral conditions, and with reference to (3.111), the relation between Un, u *,s, and z0,s is
Gillette et al. (1998) reasoned that the saltating friction speed u*,s is composed of two parts, the non-salting friction speed u* and the contribution due to the Owen effect. Defining the difference between the saltating and non-saltating friction speeds as
they used the Owens Lake data to parameterize Δu* in terms of the 10 m wind speed U10 and the 10 m threshold wind speed U10,t. According to (3.116), the saltating friction speed u*,s increases quadratically with windspeed in excess of the the friction speed5 Since u*,s determines the saltation mass flux [e.g., (3.41), (3.50), (3.51), (3.67)] neglecting the Owen effect (3.115) would cause significant underprediction of saltation6 . Rearranging (3.114) and using (3.115), the saltating friction speed isThe proliferation of terminology regarding friction speeds can lead to confusion. With saltating and non-saltating friction speeds, smooth and non-erodible roughness lengths, drag partition and wind friction efficiency, it may be difficult to understand how to predict wind erosion given output of a large scale atmospheric model. It is important to remember that the wind friction speed u* predicted in such models is generally not the relevant friction speed to employ in dust emissions schemes. First, large scale models use a roughness length z0,m typifying momentum exchange on a scale of order 100 km to predict u*.
The wind friction speed u* and roughness length z0,m measured in wind tunnels changes qualitatively once saltation develops.The ideas behind drag partitioning are quite general. Sullivan (2002) applied the drag partitioning theory of Raupach (1992) and Raupach et al. (1993) to Mars. Sullivan estimates that Martian threshhold friction velocity and surface wind speed (at 1.6 m height) must be near u*t ≈ 4.5 m s-1 and U ≈ 45 m s-1 near the Pathfinder landing site. MacKinnon et al. (2004) generalize Rauchpachs drag partition theory to apply to an arbitrary number of roughness surfaces. They applied this generalization to measured and modeled surfaces in the Mojave Desert.
As the preceding section shows, the susceptibility of soils to wind erosion is highly sensitive to particle size. In nature, soils are composed not of a discrete, monodisperse size of particles, but of a continuous distribution of particles and compositions which define the soil texture.
As is clear from many experiments, interparticle cohesive forces rapidly begins to dominate the moment balance on dust particles as the size of the particles falls beneath about 40 μm White (1979); Iversen and White (1982); Greeley and Iversen (1985). Most of the aforementioned experiments, however, were performed upon dry soil beds. Thus these experiments suit completely dry environments such as Mars, but idealize field conditions in partially wet environments such as the semi-arid regions of Earth. The notion that a wet soil bed will not detrain any dust particles agrees with experience, and the quantification of this phenomena for the entire soil spectrum from dry to saturated is the topic of this section. These effects are especially important when considering the persistance of soil moisture perturbations or soil moisture memory (e.g., Koster and Suarez, 2001).
See the discussion in Pye (1987), p. 31.
In this section we summarize the traditional measures of soil-water interaction. The following sections will build upon these definitions to present parameterization of the influence of soil moisture on u*t.
The fundamental determinant of soil-water interactions is the amount of water contained in the soil. The most easily (and frequently) measured descriptor of soil water content is the gravimetric water content w on a dry-mass basis
where MH2O is the mass of liquid water and Ms,d is the mass of dry soil. The dryest condition attained by a soil in nature is called air dry. The dryest condition to which a soil can be brought in the laboratory is called oven dry. By convention, Ms,d is defined as the mass of soil in equilibrium with an oven at a temperature of 105∘C (Hillel, 1982). Even at this temperature, clay soils may retain appreciable moisture, i.e., up to a few percent.The wettest possible condition of soil, in which all pores are filled with water, is called saturated soil. We shall affix the subscript s to quantities to indicate the saturation condition, e.g., ws is the gravimetric water content at saturation. The value of ws, depends on the soil type, but typically 0.25 < ws < 0.60. Soils rich in organic matter, e.g., peat, may have ws > 1. Occasionally in the literature the gravimetric water content is expressed on a wet-mass basis, which is simply defined by replacing Ms,d with Ms,w, the mass of moist soil, in (3.118). In this text we shall only use w defined on a dry-mass basis, as in (3.118).
The other frequently used measure of soil moisture is the volumetric water content θ
VH2O, Vp, and Va are the volumes of water, (moist) soil particles, and interparticle gases (i.e., air) in the sample. The total volume or bulk volume Vb of the soil sample is defined as Vp measures only the volume of the soil particles themselves, whereas Vb includes volume occupied by porous interparticle spaces and by water. Thus θ is the fractional volume of liquid water relative to the bulk volume (water plus soil plus air) of the soil. Typically it is assumed that VH2O ≪ Vp and Va ≪ Vp so that (3.120) may be approximated as This approximation, which appears to be standard in the literature, may be inappropriate for loose, wet soils. As discussed above, θs will denote the volumetric water content at saturation.A further distinction may be made between the volume of ambient soil particles Vp and the volume of the dry soil particles Vp,d. The two quantities are related by the swelling of the soil under moist conditions which depend on the amount of swelling. We define the dimensionless soil swelling function S to depend on gravimetric water content and on soil mineralogy χ as follows
For minerals which do not absorb water, e.g., quartz, S(w,χ) = 1, while S(w,χ) > 1 for minerals which swell with water, e.g., smectites (Table 3.3). Note that θ (3.120) is defined relative to the bulk soil volume Vb while w (3.118) is defined relative to the dry soil mass Ms,d. This can lead to confusion since ambient soil volume Vp depends on water content for some soils (3.122). Although measurement of w is more straightforward than θ, the literature appears to favor use of θ hydrologic theory.
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Converting between θ and w simply requires knowledge of the densities of water ρH2O and of dry soil particles ρp,d. If we assume Vb = Vb,d

If we do not assume Vb = Vb,d, then
where the approximation (3.121) has been made in the final step. Alternatively, we can define θ in terms of w as where the last step has used an approximation, analogous to (3.121) that Like (3.121), approximation (3.127) is only valid if MH2O ≪ Ms,d and so breaks down for very wet soils. Conversely, approximations (3.121) and (3.127) are both well-suited for use determining moisture inhibition of dust deflation in arid soils. As described in §3.7.43.7.6, moisture inhibition of deflation is virtually assured for w ~ > 0.2 kg kg-1.By convention, both w and θ are reported as percentages (i.e., multiplied by 100) rather than as fractions. When a soil moisture or mass value is to be expressed in percent, we superscript it with the % symbol, i.e., θ% ≡ 100θ and w% ≡ 100w. Otherwise the value is assumed to be a fraction.
The energy of a water parcel in soil determines its hydraulic behavior. The total potential energy of a parcel of soil water, Φ, is the sum of the forces acting on the water which cause it to differ from a surface of pure, bulk water. These forces include gravitation, pressure, and osmotic properties, respectively:
Both the gravitational potential Φg and the pressure potential Φp may be converted to mechanical (kinetic) energy of flow in open soils. Φg and Φp are discussed in more detail below. The osmotic potential Φo is due to the presence of salts in the water, and will not be discussed further. Darcys law states that the mass flux of water flowing through a surface is proportional to the gradient of Φ across the surface. Of course water tends to flow downgradient, i.e., from high to low Φ.The gravitational potential of a parcel of soil water is defined in exact analogy to the potential energy of an air parcel. Thus the gravitational potential Φg of a mass M at a height z is
where zr is the height of the reference level. In soil energy studies it is common to define the reference level as the level of the soil surface, i.e., zr = 0. For the remainder of this work we take zr = 0 and assume that g(z) equals the mean acceleration of gravity at the Earths surface, g. Then (3.129) reduces to where ρl is the density of liquid water and V is its volume. Thus Φg < 0 for water beneath the soil surface.The pressure potential of a water parcel is due to the displacement of the parcel relative to a free surface of water. In other words, a water parcel at the surface of a free body of water feels no pressure potential. A parcel residing at a depth d beneath the free surface of water feels a total pressure pt which is the sum of the atmospheric pressure p and the hydrostatic pressure pl due to the column of liquid water above it
If the volume of the parcel is V , then the pressure potential energy of the parcel is Thus the pressure potential per unit volume is
∕V = pl.
In soil energy studies it is very common to normalize the total potential energy of the water by the
amount of water. When applied to (3.131), this results in the gravitational potential energy of the water per
unit mass, Φg, and per unit volume,
. Dividing (3.131) by M and by V , respectively, we obtain
≈ 1000Φg.
Work by Clapp and Hornberger (1978) and Cosby et al. (1984) provided widely used approximate empirical relationships between the soil matric potential, water content, and soil texture. First, the saturated volumetric water content θs depends weakly on the mass fraction of sand in the soil
Knowledge of θs is important since, under a simplifying assumption, be used to obtained the bulk density of the soil. If the process of soil saturation is assumed is due to filling of pores (rather than soil swelling), then θs equals the volume concentration of air pores which have been displaced. Assuming soils reach saturation once all air pores have been displaced then where LHS and RHS are evaluated at complete saturation and at oven-dry conditions, respectively. For values of Msand in [0.0, 1.0] (3.136) predicts Va(θ = 0) ∈ [0.489, 0.363].For soils with a swelling function S equal to unity (3.122), the volumetric water content at saturation and the (poreless) volume Vp occupied by soil particles are simply related
The dry bulk density or dry density of the soil ρp,d is this poreless soil volume Vp times the mean mass density ρp of individual soil particles The contribution of air has been neglected in (3.139) since ρ ≪ ρp. It follows from (3.136) that (3.139) is also an approximation which is best suited to sandy soils. In particular, (3.136) and (3.139) together imply that soil bulk density have no dependence on clay or silt content.Since ρp measures the mass density of the particle solids only, it does not depend on the structure or texture of the soil. Therefore ρp does not depend on water content (except for swelling soils), but is sensitive to particle coatings and aggregates, such as organics. Soil Organic Matter (SOM) is less dense than most minerals, so soils high in organic matter (such as those near the surface), are less dense than mineral-dominated soils of the same texture. Values of ρp for important mineral types are presented in Table 3.3. A standard value of ρp = 2.65 g cm-3 (valid for pure quartz) is often employed when the specific soil mineralogy is unknown. This value is especially appropriate in mineral dust source regions, which are typically very low in SOM and high in quartz, feldspars, and colloidal silicates. Dust from volcanic and meteoric ash is less dense, closer to ρp = 2.65 g cm-3.
The relative saturation of the soil s is somewhat analogous to relative humidity:
Thus s expresses the degree of saturation on a normalized scale 0 ≤ s ≤ 1.The soil matric potential at saturation, ψs, is, to a first approximation, a function only of the mass fraction of the soil that is sand, Msand
where ψs is in mm H2O.Finally, Clapp and Hornberger (1978) and Cosby et al. (1984) showed that the measured soil matric potential fits a power law dependence on the relative saturation
where the dimensions of ψ are mm H2O. Thus b depends upon both the sand mass fraction through s(3.140) and the clay mass fraction through b. Clearly the omission of any dependence on the silt mass fraction in (3.142) is an approximation.
The influence of moisture on the threshold friction velocity arises from two forces caused by the presence of liquid water between grains of soil. The first force is the capillary force, which arises from the surface tension of water and the size and geometry of grains and pores. As described in §18.3, capillary forces cause a pressure differential to develop between the curved miniscus of a liquid phase water wedge and the air with which it is in equilbrium. The second force is the adsorptive force, which arises from the attraction of polarized water molecules to charged surfaces of soil grains. Adsorptive forces cause liquid water (and water vapor) to coat the surfaces of soil grains.
The combined forces of capillarity and adsorption are called the matric suction or matric potential. The soil matric potential ψ is usually expressed as the potential energy per unit volume of soil in J kg-1. However, the dimensions and definition of ψ are somewhat confusing. For example, (3.142) below is an expression for ψ in mm H2O. Thus we describe how to convert between various descriptions and units of the energy levels of soil water.
Based on the above discussion, it is clear that the friction threshold of a soil is sensitive to the water content of the soil, i.e., u*t = u*t(w). Generally, the influence of moisture on u*t is described by the threshold inhibition function fw, defined as the ratio between the wet and dry friction thresholds, u*tw and u*td, respectively
Thus fw > 1. In practice, the functional dependence on θ may be replaced by any other measure of water content, e.g., w. In addition to water content, fw can depend on soil texture (i.e., size), salt content, and time since precipitation. For the time being we neglect these dependencies and refer the interested reader to the discussions in Pye (1987) and Gillette (1988).A number of investigators have created simple parameterizations which account for the increase of u*t with θ (Belly, 1964; Pye, 1987; Gillette, 1988; Selah and Fryrear, 1995; Shao et al., 1996; Fécan et al., 1999). Belly (1964) measured u*t for various soil moisture contents. His results fit the logarithmic parameterization
where θ% is the percent volumetric water content Unlike most authors, Belly (1964) measured the threshold friction velocity required to develop a sustained saltation, rather than the fluid threshold friction velocity. As a result, (3.145) tends to predict higher values of u*t than other parameterizations (Shao et al., 1996; Fécan et al., 1999).The wind tunnel experiments of Shao et al. (1996) fitted the exponential relationship
In practice (3.146) predicts that fw becomes so large for θ > 0.04 m3 m-3 that dust mobilization effectively ceases.The differences between (3.145) and (3.146) are significant. The logarithmic form of (3.145) curves concave downwards starting from fw(0.01) = 1.2. The exponential form of (3.146) curves concave upwards starting from fw(0) = 1.
Gillette (1988) studied the dependence of u*t on soil type and condition. He characterized the modulus of rupture of the soil.
Selah and Fryrear (1995) studied the behavior of erosive thresholds on soil moisture in carefully controlled wind tunnel experiments. Two soil moisture reading were made for each of five different soil textures considered. The first is the water holding content, ws, which is simply the gravimetric water content at saturation. Selah and Fryrear (1995) found that ws is tightly correlated with soil clay fraction Mclay
This relationship (3.147) is in contrast to previous studies which found θs depends most on sand fraction Msand (3.136) (Clapp and Hornberger, 1978; Cosby et al., 1984; Bonan, 1996). Second is the maximum gravimetric water content which permits erosion wT , i.e., wind erosion ceases for w > wT .7 The experimental design allowed separate retrieval of wT in both abrading and non-abrading environments where the difference was the presence or absence, respectively, of upstream saltation (which assists triggering local saltation). Regressions of their measurement results showed high-correlation when defined in terms the non-dimensional equivalent threshold moisture
t
Clearly
t < 1 for standard soils.
It may be helpful to recap the various moisture thresholds related to wind erosion. The soil water content w falls into four possible ranges described in Table 3.7.
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The following relations between u*t, and
t were obtained:
t in both
cases.
McKenna-Neuman and Nickling (1989) developed a theoretical expression for the increase of u*t due to soil moisture valid for sandy soils. Adsorptive forces are thought to be insignificant in soils containing only coarse sand particles (D > 100 μm) (Hillel, 1982). This is because the molecular forces which lead to adsorption are largely caused by clay sized particles.
McKenna-Neuman and Nickling (1989) assume that the only remaining force able to cause significant interparticle cohesion in sandy texture soils is the capillary force Fc. Assuming a disymmetrical conical geometry represented the grain-pore relationship, they found that Fc could be expressed solely in terms of the surface tension of liquid water σ, a factor G determined by the grain-pore geometry, and the pressure deficit P as
The pressure deficit P is the only factor in (3.150) which directly depends on the moisture content. Note that ss P → 0, Fc becomes ill-defined. Thus (3.150) is not valid for planar water surfaces where the capillary forces become very weak. The work of McKenna-Neuman and Nickling (1989) showed that, for coarse sandy soils, fw depended
on the square root of the capillary force. Two geometrically distinct arrangements of particles and pores
were analyzed. The first, corresponding to a particle resting angle of β = 30∘, is called an open packed
system. The second, corresponding to a particle resting angle of β = 45∘, is called an close
packed system. For each of these systems, they found fw ∝
. As indicated in (3.150), Fc
depends on the grain geometry through both G and P . The resulting expressions for fw are
Wind tunnel data for three sizes of sand (D = 190, 270, and 510 μm) fit (3.151) reasonably well over the experimental range of moisture contents tested, 0 < θ < 0.02. The predictive skill of this theory in the absence of any treatment of adsorptive forces substantiates the hypothesis that adsorptive forces are insignificant at increasing u*t for large particles.
The dominance of capillary over adhesive forces in coarse sand soil supports a hypothesis about the partitioning of water between capillary pores and surface coatings. If the interparticle forces due to adsorption are negligible for coarse sandy soil, then it is reasonable to assume that the fraction of liquid water which is adsorbed to surfaces is negligible compared to the fraction bound into capillary wedges. Thus McKenna-Neuman and Nickling (1989) assume that virtually all of the soil water in coarse soils is found in capillary wedges and pores, and very little is found in surface coatings. Since the interparticle cohesive forces for coarse sandy soils are dominated by Fc (3.150), the soil matric potential, which is the sum of the gravitational and pressure potentials (3.128), and must be closely related to Fc as well. In fact, McKenna-Neuman and Nickling (1989) assumed that the soil matric potential is equivalent to the capillary potential, i.e.,
For clayey soils a significant fraction of the water is bound into adsorptive coatings, so that a simple relationship between ψ and Fc (3.152) is not justified. However, a similar relationship may by posited and its results tested against experiments, as is done by Fécan et al. (1999).
Fécan et al. (1999) developed a semi-empirical parameterization for fw(w) suitable for use in large scale atmospheric models. Their parameterization extends the theory of McKenna-Neuman and Nickling (1989) for coarse sandy soils to realistic soils containing arbitrary amounts of clay and silt. The major limitation of McKenna-Neuman and Nickling (1989) is its neglect of these smaller particles. As already discussed, the stronger electrostatic surface forces of clays, together with their higher surface area to volume ratio, causes adsorptive forces to become significant in the presence of clays. As noted by Hillel (1982), the adsorptive and capillary forces are difficult to disentangle when small particles are present because the distinction between the coatings and wedges at the contact points is ill-defined. In fact, the adsorptive coatings and capillary wedges are essentially distinct thermodynamic phases of water whose equilibrium is very difficult to predict for an arbitrary geometry.
Thus, in the absence of a theoretical description of the simultaneous effects of both capillary and adsorptive forces, Fécan et al. (1999) chose to to fit an assumed functional form to experimental data. First they noted that the combined cohesive forces due to water (capillary and absortive) are what determines the soil matric potential of soil with arbitrary clay and silt content
Unlike (3.152), (3.153) applies to any soil type, include clayey soils. According to the work of Clapp and Hornberger (1978) and Cosby et al. (1984) presented earlier (3.136)(3.143), ψ may be empirically expressed in terms of coefficients which explicitly depend only on the soil sand and clay contents.The total water content of an arbitrary soil may be considered as the sum of two components, water at contact points which contributes to capillary forces, θc, and water in surface coatings which contributes to adhesive forces, θa,
As noted earlier, fw is proportional to the square root of the capillary force (3.151) for coarse sand-textured soils.
Fécan et al. (1999) parameterized fw in terms of gravimetric water content w rather then volumetric water content θ because most of the field measurements were reported in terms of w. Fécan et al. (1999) posit that fw(w) is unity for water contents less than the threshold gravimetric water content wt. For w < wt, the water is mostly distributed in adsorptive coatings which do not affect u*t. When w = wt, the adsorptive capacity of the soil has been reached and additional water increases the capillary forces in the soil, which do increase u*t. Thus, for soils wetter than wt, inhibition of particle deflation through increasing u*t is to be expected. Fécan et al. (1999) show that most variation in wt is an explicit function of the soil clay content. Using multiple datasets (Belly, 1964; McKenna-Neuman and Nickling, 1989, , and others) spanning the domain 0.0 < Mclay < 0.5, they found
Note that all gravimetric water contents and soil textures in Fécan et al. (1999) are assumed to be in percent. According to (3.155), as Mclay increases from 0.0 to 1.0, wt increases quadratically from 0.0 to 0.31 kg kg-1. Typical Saharan desert clay contents of 0.1 < M clay < 0.2 lead to 0.018 < wt < 0.04 kg kg-1.Fécan et al. (1999) parameterized the observed relationship between fw, w, and wt from multiple datasets.
By construction, moisture does not affect u*t until w > wt, after which increased w quickly quenches dust production by increasing u*t. Note that (3.156) maintains the quadratic dependence of fw on θ explained by McKenna-Neuman and Nickling (1989) (3.151), but also allows for the influence of clay on soil. These results may be expressed in terms of θ by employing (3.125).
Schaaf et al. (2002) Tsvetsinskaya et al. (2002) Tegen et al. (2002) Zender et al. (2003b) Gillette et al. (2001) describe three phases of saltation activity related to crusting on the saline playa of Owens Lake. Gill (1996) reviews evidence for anthropogenic and dessication-induced dust emission from playas and dry lakes worldwide. Evans et al. (2004) describe the provenance of dust from the Bodélé Depression.
Prospero et al. (2002) characterize dust source regions on the basis of satellite retrieved indices from the Total Ozone Mapping Spectrometer (TOMS). Washington et al. (2003) use TOMS and in situ observations to characterize source regions. Sun et al. (2001) use in situ dust storm reports to analyze the climatology and distribution of dust sources in the Gobi Desert, Takla Makan Desert, and other regions of China. Table 3.8 characterizes the most important dust source regions. Koren and Kaufman (2004) use satellite measurements to show funneling effects of topography appear to significantly enhance wind speed in the Bodélé Depression relative to surrounding regions. Zender and Kwon (2005) analyze TOMS aerosol and satellite-derived climate timeseries to infer the dominant erodibility mechanisms in source regions. in Semiarid Soils Using Airborne Hyperspectral Technology (2004) and Goldshleger et al. (2004) characterize soil crusting and rainfall infiltration in terms of near infrared soil spectral reflectance.
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While dust emissions often peak in playas and dried lake-beds, they are strongly-structured, not uniformly distributed, throughout these sources. Emissions seem to peak at the windward edge of playas.
The Bodele Depression is presently Earths strongest dust source. Half of its emissions cross 15∘W and enter the Subtropical Atlantic Region, where they contribute to the trans-Atlantic dust plume seen clearly in satellite measurements (Husar et al., 1997; Herman et al., 1997; Prospero et al., 2002). Conversely, much of the Bodélé dust remains over North Africa, where it contributes to the background dust resevoir. Indirect evidence for this reservoir is seen in the insensitivity of trans-Atlantic dust events to the timing of wind events in African source regions (Colarco et al., 2003).
One research group which visited the region found that white diatomite from Paleolake Megachad covers a large fraction of the region (Giles, 2005). Diatomite is the ultimate source of much of the Bodélés dust. The dust appears to form by splintering and erosion of large diatomite particles saltating in sand dunes, rather than by lofting of fine diatomite powders seen in other regions of the Sahara.
Washington et al. (2006) summarize the physical, meteorological, geomorphological, and anthropogenic reasons why the Bodélé Depression emits dust so efficiently. The depression is situated between two mountain ranges, the Tibesti and the Ennedi. These topographic features funnel a low-level easterly jet over the depression.
The Takla Makan Desert in the Tarim Basin is the most active dust source in Asia (Husar et al., 1997; Herman et al., 1997; Prospero et al., 2002).
The Lake Eyre Basin is the most important dust source in Australia. It is an inland-drainage basin and vestigial wetland.
Sea salt and desert dust mix more often than their names imply. [Levin, Zev]Zev Levin finds that about 60% of all coarse particles 500 m over the Mediterranean are internal mixtures of dust and sea salt.
Monahan (1971) has a very concise title. Monahan et al. (1982) used closed tanks experiments to empirically determine the spectral mass flux of sea salt generated by bubble-bursting. Monahan et al. (1986) presented the first model with distinct parameterizations for the direct and indirect formation mechanisms. Testing of this model showed it overpredicted direct droplet production at high wind speeds, a deficiency which has been addressed by more recent studies. Smith et al. (1993) developed a generation function based on two-lognormal modes. Gong et al. (1997a) and Gong et al. (1997b) present a global model of the generation and distribution of sea salt aerosol. Andreas et al. (1995) reviewed and summarized extent production mechanisms. Andreas (1998) contrasted various spume productions parameterizations with theory and modified the best of these into an improved parameterization. Vignati et al. (2001) present a tri-modal lognormal generation function based on open ocean, ship-borne observations.
Sea salt aerosol is generated by two fundamentally distinct mechanisms (e.g., Monahan et al., 1986). Wind drag in rough seas detaches droplets directly from the surface. Surface tension prevents wind from directly separating droplets smaller than Dp ~ 40 μm from waves. These relatively large droplets are called spume and the generation of spume by wind drag is known as the direct mechanism of sea salt generation. Spume generation occurs most readily at the crests of breaking waves where internal forces binding liquid together are overcome by the wind drag acting on the cross-sectional area of the crest water. Thus the direct mechanism is a source exactly at the ocean-atmosphere interface that occurs only during strong wind events, say U ~ > 10 m s-1.
The indirect mechanism of sea salt generation is mediated by air bubbles. Whitecaps form when ocean surface waves break and generate small scale turbulent motions in the surface ocean. The white appearance is caused by air trapped in small bubbles on the surface called foam or by bubbles entirely within the near surface water. When bubbles buoyantly reach the ocean surface and burst their liquid shells explode into film drops. Film drops are typically 0.1 < D < 5 μm with a modal size of about 12 μm. During the subsequent collapse of the bubble, a plume of about 110 tiny drops known as jet drops may be released into the atmosphere. The surface tension of the bubble contributes to the generation of the jet. Jet drops range in size from 3 < Dp < 100 μm with a modal size of about 10 μm.
A sea salt generation function which represents the indirect mechanism must estimate the fraction of ocean surface which is foam-covered under specified conditions. Whitecap coverage depends on wind speed, stability, temperature, salinity, wind duration, fetch, and surfactant amount.
Monahan et al. (1982) performed tank experiments to deduce the spectral mass flux of sea salt by the indirect mechanism (bubble-bursting). Based on these experiments, Monahan et al. (1986) reported the expression for N↑ ss the vertical number flux of sea salt particles entering the atmosphere as a function of 10 m wind speed Ur
[# m-2 s-1 μm-1] | = 1.373U r3.41R p-3(1 + 0.057R p1.05)101.19e-B2 | (4.1a) |
[# m-2 s-1 m-1] | = 1.373U r3.41. . . | (4.1b) |
Monahan et al. (1986) also parameterized the size-dependent vertical number flux of sea salt aerosol due to the direct mechanism Fss
[# m-2 s-1 μm-1] | = 8.60 × 10-6e2.08UrR p-2 | (4.2a) |
[# m-2 s-1 μm-1] | = 6.45 × 10-4e2.08UrR p-3e-D2 | (4.2b) |
Smith et al. (1993) developed a more accurate (and complicated) parameterization of sea salt formation based on measurements taken on the coast of South Uist Island in the Outer Hebrides, about 100 km in the North Sea northwest of the Scottish mainland. The measurements comprehensively sampled aerosols in wind speeds of U ∈ [0.0, 34.0] m s-1 at a It was found that the number fluxes at a height of about 14 m over the surface were comprised of two log-normal distributions whose mean and geometric standard deviation were insensitive to wind speed. The measurements were made in a range of environmental conditions and the parameterization (4.3) was normalized to predict fluxes of particles whose radii are in equilibrium with a relative humidity of 80%, r80.
where the empirically determined parameters f1, f2, r1, and r2 are 3.1, 3.3, 2.1 μm, and 9.2 μm, respectively. The f1 and ri parameters do not depend on wind speed. These field measurements could not distinguish between differing production mechanisms, so (4.3) implicitly accounts for film, jet, and spume mechanisms.The relative contribution of the two modes, represented by the Ai parameters, strongly depends on wind speed.
| A1 | = exp(0.0676U14 + 2.43) | (4.4a) |
| A2 | = exp(0.959 - 1.476) | (4.4b) |
![( )
u*- 14-
U14 = U10 + k ln 10
[ ∘ ---- ( )]
--Cnm- 14-
= U10 1 + k ln 10 (4.5 )](aer259x.png)
Andreas (1998) presents a thorough comparison of existing spume production parameterizations (Monahan et al., 1986; Smith et al., 1993) and contrasts these to theoretical models. He identifies important characteristics which accurate parameterizations should contain, and then modifies the spume generation parameterization of Smith et al. (1993) (4.3) to reflect this.
Andreas (1998) argues convincingly that (4.3) underestimates the number of both film drops and spume drops for two reasons. The measurements resulting in (4.3) were probably biased by a number of factors (Andreas, 1998). First, the measurements were taken from a 10 m tower located on the high-water mark of a gently sloping beach. During high tide the water reached the foot of the tower, but during low tide the water was approximately 300 m away. While the distance from the instruments to the water isolated the measurements from the immediate surf zone, it also meant that particles were subject to several seconds of atmospheric transport before reaching the tower. During this transport, evaporation and gravitational sedimentation remove particles from the marine air and this, argues Andreas, causes (4.3) to underestimate number fluxes by a factor of about 3.5, an argument not disputed by Smith et al..
Therefore Andreas (1998) recommend using (4.3) for r80 ∈ [1, 10] μm(r0 ∈ [2, 21] μm), but multiplying it by 3.5. Presented in terms of radius at point of droplet formation r0, the spectral vertical number flux of the modified Smith et al. generation function is
The first term on the RHS is evaluated using Smith et al. (1993) (4.3) for r80 ∈ [1, 10], and using simple power laws described below (4.9) for large spume. The relation between sea spray droplet size at formation, r0, and the droplet size at relative humidity of 80%, r80, is determined by the hygroscopic growth properties of sea salt. Smith et al. (1993) adopted an equilibrium relative humidity RH = 98.3% for the near surface ocean. This is close to the RH = 98% used in Large and Pond (1981). Assuming r0 is in equilibrium with RH = 98.3%, Andreas (1998) suggest| r80 | = 0.518r00.976 | (4.7a) |
| r0 | = 1.963r801.0246 | (4.7b) |
![]() | = 0.506r0-0.024 | (4.8a) |
![]() | = 2.011r800.0246 | (4.8b) |
For larger spume droplets, Andreas (1998) parameterizes droplet concentration data measured within 20 cm of the ocean surface. The parameterization simply scales the number flux with a power of the droplet radius, and there are three different regimes
The parameters C1C3 depend only on wind speed. They are evaluated by requiring the modified Smith et al. distribution (4.6) be continuous with (4.9) at r80 = 10 μm.It may be more convenient to forecast N↑ ss(r0) directly rather than N↑ ss(r80). Substituting (4.7) and (4.8) into (4.9) we obtain N↑ ss in terms of r0, and remove the RH = 80% assumption
For studies which work in terms of particle diameter D0 rather than radius, we may simplify (4.3) and
(4.10). Using dr0 =
dD0, and rewriting r0x as 2-xD
0x we obtain
According to Grini et al. (2002a), the experiments of (4.1) were also conducted at 80% relative humidity. The particle size in these parameterizations is, therefore, the ambient size of deliquescent sea salt aerosol in equilibrium with RH = 80% environment. Consequently the mass flux associated with (4.1) should represent particles whose density is the correct average of the salts and the water.
Vignati et al. (2001) present a tri-modal lognormal generation function based on open ocean,
ship-borne observations. These observations show that a fine particle mode (
n = 0.4 μm) is present in
the surf zone. Table 4.1 shows the parameters of the tri-modal log-normal number distribution generation
function which gives the best fit to the observations.
|
|
For the three modes the median radii
i
n μm at 80% relative humidity are [0.2, 2.0, 12.0] and the
geometric standard deviations σg,i are [1.9, 2.0, 3.0]. The total number flux N↑
ss # m-2 s-1 μm-1 of the
tri-modal distribution is
The processes by which aerosols are removed from the atmosphere in the absence of precipitation are collectively termed dry deposition. The dry deposition processes which remove aerosols from the atmosphere to the surface (or canopy) include gravitational sedimentation, inertial impaction, and Brownian diffusion. Dry deposition processes determine the atmospheric residence time of large aerosols. Dry deposition processes are analogous to electrical resistances in that each process is like a path to ground, and the efficiency of each path may be construed as a resistance and included in parallel or series with all other possible routes by which an aerosol may reach the surface.
Slinn et al. (1978) is a review paper on all aspects of air-sea transfer, including wet and dry deposition. Sehmel (1980, 1984) form a comprehensive review of particle and gaseous dry deposition. Wesely (1989) presents a regional scale dry deposition parameterization for gases. Slinn and Slinn (1980) introduced a widely-used two layer model of particulate deposition to water surfaces. Williams (1982) presents a deposition model for water surfaces that explicitly accounts for atmospheric stability and for hygroscopic particle growth in the deposition (quasi-laminar) layer. Rojas and Grieken (1993) perform an inter-model comparison of Slinn and Slinn (1980), Williams (1982), and their own model, a generalization of Slinn and Slinn (1980) that accounts for arbitrary reference heights and stability. Peters and Eiden (1992) derive from first principles a complex model of particle depostion to vegetated surfaces. Zhang et al. (2001) present a size-segregated particle dry deposition scheme with partially addresses underestimates of sum-micron aerosol deposition velocities prevalent in models. Landing et al. (1995) examined dust deposition and mineralogy in Florida from 19921994. Raupach et al. (2001b) and Raupach et al. (2001a) derive and present a detailed dry deposition model for particles and apply it to pesticide spray. The articles are notable for their clear statement of physical and mathematical assumptions.
We make the steady state assumption that the net flux Fd of a species from a reference height zr to a given surface is related to the concentration of the species N(zr) by a parameter having units of velocity,
where vd (m s-1) is known as the deposition velocity of the species.The physics of dry deposition are entirely contained in vd, the rate of removal of the species due to all dry deposition processes. Note that vd is positive when the net flux is Fd is from the atmosphere to the surface. In the following we assume that there is no upward flux of particles due to dry deposition. This is equivalent to stating that the sticking efficiency (6.13) is zero so that particles which strike the surface remain there. Since the upward or resuspension flux is zero, F m d is both the net particle flux and the downward particle flux. For gas phase species, N may be expressed as either a number concentration in # m-3 or a mass concentration in kg m-3. The deposition flux Fd is then either a number flux or a mass flux of molucules in # m-2 s-1 or kg m-2 s-1, respectively.
For aerosol, the deposition velocity is a function of particle diameter so that vd = vd(D). The fundamental assumption which defines deposition velocities for aerosols is that turbulent and diffusive processes maintain a constant proportion between the flux of particles of a given size to the surface and the concentration of these particles at a reference height above the surface. The fluxes of interest are the spectral deposition number flux F n d (D) (# m-2 s-1 m-1) and the spectral deposition mass flux F m d (D) (kg m-2 s-1 m-1).
The deposition velocity is the same for both types of spectral fluxes. Note the similarity between these definitions and the definition of precipitation fluxes in (6.16)(6.18). Integrating (5.2) over particle size we obtain expression which defines the number mean deposition velocity
d,N
The same integration procedure applied to (5.3) leads to The explicit definitions for the number mean and mass mean deposition velocities in (5.4) and (5.5) are
Two experimental methods to determine vd(D) are wind tunnel and field experiments. Wind tunnel
experiments can select particle sizes and thus control nn(D)ΔD (or nm(D)ΔD). Usually F n
d (D)ΔD (or
F m
d (D)ΔD) are measured in steady state conditions and vd(D) is then inferred from a discretized version
of (5.7). In field experiments it is often impossible to control particle size so independent
measurements of the integrated quantities F n
d or F m
d (D) and N0 or M0 are made instead. From such
measurements only
d,N or
d,M may be inferred. Additional assumptions or separate measurements of
nn(D) or nm(D) are required to obtain information about the size dependence vd(D) from
(5.7).
It is reasonable to assume the particle number flux F n d (D) is the result of diffusive and gravitational processes acting in parallel. The diffusive transport may be further decomposed into the sum of downgradient turbulent transport and Brownian diffusion. Let the turbulent transport be characterized by an eddy diffusion coefficient ε. According to Ficks first law (11.35), the Brownian diffusion is characterized by 𝒟B (5.39). The spectral number flux (defined to be positive downwards) may then be written as the sum of the diffusive and gravitational components as
One may define the non-dimensional length
Since the units of ν are m2 s-1 and the dimensions of u
* are m s-1,
is dimensionless. Non-dimensionalizing
(5.8) by (5.10) we obtain Integrating over the particle concentration from the reference height z down to the height of zero particle
concentration 
Sehmel and Hodgson (1978a,b) performed wind tunnel experiments over a range of particle sizes 0.03 < D < 29 μm, surface types (grass, gravel, and water) friction velocities 11144 cm s-1, and roughness lengths 0.001 < z0,m < 0.6 cm. The results were used to parameterize the quasi-laminar layer resistance to particle deposition
where
r is the dimensionless relaxation timescale For particles D ~ < 0.01 μm, (5.13) results in surface resistances that are too large, and Sehmel and
Hodgson (1978a) recommend using pure Brownian diffusion in the quasi-laminar layer.
The three most significant barriers to aerosol dry deposition are aerosol mass, boundary layer stability, and quasi-laminar layer resistance.
There is debate whether the transfer coefficient for aerosol deposition through the turbulent layer follows the aerodynamic resistance to heat transfer or to momentum transfer. Williams (1982) use ra = rh. Sehmel and Hodgson (1978a), Slinn and Slinn (1980) and derivatives use ra = rm.Settling by aerosol due to gravity occurs independently of turbulent mechanisms of dry deposition. Thus vg is added in parallel to deposition velocity due to turbulent mix-out.
Figure 5.1 shows the simulated dry deposition velocity as a function of aerosol size and surface roughness length.
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|
Sehmel and Hodgson (1978a) and Sehmel (1980) predict a stronger dependence of vd on z0,m than is shown in Figure 5.1. The reason for the discrepancy is not yet understood.
Dry deposition of gaseous species requires consideration of an additional term accounting for the so-called canopy resistance rc. The canopy resistance accounts for the process of gases becoming irreversibly absorbed by plant stomata.
Gravity provides a direct force for moving particles through the turbulent boundary layer, through small scale eddies near the surface, and through the quasi-laminar layer immediately adjacent to the surface. However, gravity is an inefficient removal mechanism for particles smaller than 1 μm. Our treatment of gravitational settling follows the method of Seinfeld and Pandis (1997).
First, we assume particles are always falling at the their steady state gravitational settling velocity vg. This is the speed at which aerodynamic drag balances gravitational acceleration so that net acceleration is zero. For this reason vg is called the terminal velocity.
The Stokes settling velocity uSt is the terminal fall speed of particles satisfying two aerodynamic criteria first identified by Stokes. First, the Reynolds number associated with the particle must be less than 0.1. Second, the particle must be large enough so that its slip correction factor (defined below) is near unity. Under these conditions
As a rule of thumb, uSt = vg for particles in the size range 0.01 < D < 1 μm.Very small particles undergo fewer collisions than large particles, and are susceptible to non-continuum or kinetic effects of fluids. These properties combine to define the slip correction factor
![]() | (5.19) |
where λ is the mean free path of air, defined in §11.1.1. Corrections to (5.18) due to Cc exceed 10% for mineral particles smaller than about 1.5 μm.
The drag coefficient CD of particles is usually expressed in terms of the Reynolds number Re of the particle motion relative to the medium. Analytic solutions for drag coefficients exist for spherical particles for low Re. For high Re, and for most aspherical shapes, CD are determined from computer simulations of the unsteady flow fields past the particle (Wang, 2002). For example, Wang (2002) define CD for cylinders of diameter D as
where α is one-half of the cross-sectional area of the particle normal to the flow direction, and
is the
velocity field.
Exact relationships exist for the Stokes regime where Re < 0.1. For Re > 0.1, theory and experiment provide parameterizations which match the available data, but do not always agree with one another. To begin with, Seinfeld and Pandis (1997), p. 463, suggest
It can be seen that there are three regimes of Re beyond Stokes flow. In the transition regime, 0.1 < Re ~ < 5, the method of asymptotic expansions provides experimentally confirmed values. In the Turbulent regime, 5 ~ < Re ~ < 500, a pure parameterization is used. In the Limiting regime, Re ~ > 500, CD approaches a limiting value of 0.44.In reality, objects encounter a turbulence transition in the limiting regime that causes CD to decrease with increasing Re. Based on http://aerodyn.org/Drag/speed-drag.html, we changed the limiting regime cutoff from Re = 2 × 105 (5.21) to 1 × 105. Moreover, we splice a new turbulence transition regime onto (5.21) where CD decreases linearly with the logarithmic increase in Re according to
There are two problems with (5.21). First, the expressions are not smoothly matched at the boundaries. This causes finite CD jumps between continuously varying particle sizes. For example, when ρp ~ 2.65 g cm-3 (mineral dust), a jump occurs near D = 80 μm because the motion Re suddenly changes from Re < 2 to Re > 2. This jump nearly doubles sedimentation speed and is very unrealistic. We attempt to solve this problem by blending solutions over limited ranges of Re. The second problem is the accuracy of the expressions in the transition regime. Asymptotic expansions in this regime (Proudman and Pearson, 1957; Chester and Breach, 1969; Pruppacher and Klett, 1978, 1998) show that
where γ = 0.577215664 is Eulers constant. The final term in the Seinfeld and Pandis (1997) expression in the transition regime (5.21) is ln(2Re) rather than ln(Re∕2) as in (5.23). This appears to be a misprint in Seinfeld and Pandis and the (5.23) form is preferred, regardless of whether the final two terms in (5.23) are employed. Despite its apparent complexity, the fourth term in (5.23) has been verified independently (Pruppacher and Klett, 1998).The complete solution of the equation of motion for a falling particle does not neglect the non-linear dependence of the drag coefficient on Re. The vertical equation of motion applicable to particles of any size falling in still air is
![]() | (5.24) |
The particle reaches its terminal velocity when the LHS of (5.24) is zero, i.e., when the acceleration vanishes. Solving for vg in this case yields
![]() | (5.25) |
We use (5.25) to characterize the size range of particles which are susceptible to long term atmospheric suspension and transport, and the size range of saltators which fall too fast to become suspended.
Note that CD (5.25) is a function of vg through (3.15) and (5.21). Thus (5.25) is an implicit equation for vg. An iterative solution to (5.25) is straightforward but too time consuming for large scale atmospheric models. A reasonable approximation is to define the Stokes correction factor CSt as
![]() | (5.26) |
The CSt correction to (5.18) exceeds 10% for mineral particles larger than about 45 μm.
In the case where the particles are very large, such as falling raindrops, (5.25) simplifies considerably. For D > 1 mm we have Re > 500 and thus CD = 0.44 (5.21) and Cc ≈ 1. Inserting these values in (5.25) we obtain
![]() | (5.27) |
for very large particles and raindrops. Finally, we may re-express the Reynolds number (3.13), (3.15) of flow around a falling particle explicitly in terms of its terminal velocity as
![]() | (5.28) |
Most mineral particles are not perfect spheres (Ginoux, 2003). Aspherical particles require modifications to the preceding formulation of kinematic properties, such as the settling speed. First, asphericity alters the drag coefficient which must be known over same range of Re as for spherical particles (5.21) in order to determine fall speeds. Theoretical treatments of the drag coefficient for aspherical particles are few (Abraham, 1970; Boothroyd, 1971; Mitchell, 1996; Ginoux, 2003). The microphysical treatise by Wang (2002) describes the types of analyses brought to bear on these problems with ice crystals. Many of these analyses hold for mineral dust particles as well. Ivanova et al. (2001) present a method for removing number and mass of aspherical ice crystals of various shapes that should be applicable to dust as well. VanCuren and Cahill (2002) describe the trajectory of Asian dust events which reach North America.
Wang (2002) performed ab initio simulations of flow past finite cylinders with aspect ratios satisfying the relations of Auer and Veal (1970). His results show that differences between the infinite and finite cylinder approximations are small for Re > 100. The following parameterization fits his data within a few percent
Unfortunately, (5.30) was constructed from simulations of cylinders with prescribed aspect ratios typical of ice crystals (Wang, 2002, p. 53). It is desirable to find an analogue to (5.30) which is a function of aspect ratio.Pitter et al. (1973) computed the drag coefficient of flow past very thin oblate spheroids for low and intermediate Reynolds numbers. Wang (2002) computed the drag coefficient of flow past hexagonal plates and broad-branched crystals and fit his results to the same functional form as Pitter et al.. For hexagonal plates, the results are
For broad branch crystals, the results are
Kalashnikova and Sokolik (2004) present a comprehensive analysis of the radiative properties of aspherical mineral dust using a Composition-Shape-Size (CSS) approach based on the Discrete Dipole Approximation (DDA). Kalashnikova et al. (2005) apply these modeling techniques to dust aerosol retrievals from MISR. of Multi-Angle Remote Sensing Observations to Identify et al. (2005) document MISR dust retrievals in optically thick dust plumes. of Multi-Angle Remote Sensing Observations to Identify and data analysis (2005) show their CSS approach allows MISR retrievals to distinguish natural dust particle shapes and composition.
A number of recent papers are devoted to the effects of mineral dusts (and other aerosols) in determining surface reflectance in deserts and snowpack. Motoyoshi et al. (2005) demonstrate the presence of soot in fresh snow by minimizing model fits to measured reflectances. Kokhanovsky et al. (2005) compare aspherical snow grain models to measured reflectances at high spectral resolution, and demonstrate the feasibility of retrieving snow grain size from such measurements. Aoki et al. (2005b) report high resolution spectral surface albedos over multiple desert surface types in western China including dunes and crusted soils. Aoki et al. (2005a) simulated the aerosol radiative forcing of multi-component dust aerosol over many surface types, and explored the sensitivity of the results to a number of assumptions such as underlying surface albedo, presence of other aerosols, and snowpack. Aoki et al. (2006)
Exact radiative treatments of particle asphericity are often hampered by the large number of computations required (e.g., DDA) the incomplete range of size parameters χ applicable (e.g., Geometric Optics for large χ, and Finite-Difference-Time-Domain (FDTD) for small χ), or the absence of crucial information such as the phase function (ADT).
Equal volume-to-surface area (V/S) (sometimes called volume-to-area or V/A) techniques simulate aspherical optical properties using a collection of spheres which preserve desired properties of the aspherical particles (Grenfell and Warren, 1999; Neshyba et al., 2003). Grenfell and Warren (1999) note that
The use of equivalent spheres to represent the scattering and absorption properties of nonspherical particles has been unsatisfactory in the past because the sphere of equal volume has too little surface area and thus too little scattering, whereas the sphere of equal area has too much volume giving too much absorption.
They suggest representing aspherical particles by distributions of spheres with the same volume-to-surface-area (V∕S) ratio as the aspherical particle. They suggest the V/S technique works best for highly complex shapes, such as natural dust particles and ice crystals. The V/S technique requires as many, but no more, computations than the standard Mie theory.
The V/S ratio of a sphere is
Based on (5.33), the sphere with the same volume-to-surface ratio as an arbitrarily shaped aspherical particle with volume and surface area S [m2] and V [m3], respectively, must have radius r V∕S [m] whereThe final ingredient necessary to implement the V/S technique is the number NV∕S [# m-3] of V/S-spheres with the same volume (or area) as the aspherical particles. We establish NV∕S by imposing the condition that NV∕S spheres with equal V/S ratios as the aspherical particles have the same total volume as N aspherical particles.
We could have have imposed the condition of conserving the aspherical surface area instead of volume in (5.34). By construction V/S-spheres will have the correct area because V/S-spheres have, by definition, the correct V/S ratio. Once NV∕S∕N is known (5.36), we can construct a model population of spheres with the same total volume and surface area as the aspherical particles. What differs beteween the model population of spheres and the actual population of aspherical particles is the number concentration.The special cases of rV∕S and NV∕S for hexagonal prisms are given in Section 18.11.3 in Equations (18.50) and (18.51), respectively.
Neshyba et al. (2003) evaluate the V/S approximation for hexagonal prisms over the range of densities from thin cirrus clouds to thick snowpack. One difficulty in applying the V/S approximation in both clouds and snowpacks is determining the correct V/S ratio. Knowledge of particle shape (e.g., hexagonal crystals) and aspect ratio for all particle sizes is necessary to apply the V/S approximation. While this is helpful in theory, in practice this shape and aspect ratio information is unavailable and difficult to measure.
One alternative is to estimate the bulk V/S ratio (e.g., of the entire cloud or snowpack) rather than the size-specific ratios and work backwards from there. For example, bulk snow mass concentration M0 [kg m-3] (i.e., density) may be available from model or observations. This may be combined with theoretical or empirical estimates of specific snow surface area S ≡ S0∕M0 [m2 kg-1] to yield the snow surface area concentration S0 = SM0 [mSxmC]. Legagneux et al. (2004) describe a theory for the time evolution of S, and Cabanes et al. (2003) give examples of this function for particular snowpacks.
Betzer et al. (1988) present evidence for particles as large as 75 μm reaching Hawaii from Asia. Ginoux (2003) studied the processes contributing to large particle transport.
Large particles less able to change direction with a boundary layer flow that must veer sharply to avoid obstructions such as roughness elements (plants, trees) and the surface. Instead, the particles inertia carries it through the quasi-laminar layer, allowing the particle to be deposited on the surface. This dry depositional process is called inertial impaction. The Stokes number St determines the particle susceptibility to inertial impaction. The Stokes number relevant to boundary layer flow depends on the particle size D, particle density ρ, slip correction factor Cc, fluid velocity v∞, viscosity μ, and characteristic length scale L.
![]() | (5.37) |
St is the ratio of the particle stopping distance to the characteristic length of the flow.
It is difficult to apply (5.37) directly in the boundary layer since L and v∞ have not been characterized yet. Instead, we make the assumptions that . . . Then St may be computed as
![]() | (5.38) |
Note that (5.38) employs vg (5.25) rather than uSt (5.18).
Transport through the quasi-laminar layer also depends on the Brownian diffusivity 𝒟B of the particles. Brownian diffusivity measures the efficiency of particle displacements due to random motion between collisions. This thermally driven motion is isotropic and depends on the temperature of the fluid and the mass of the particle.
![]() | (5.39) |
Without the slip correction factor (5.39) is known as the Stokes-Einstein relation. The displacement of a particle due to Brownian motion may carry the particle across the quasi-laminar layer and deposit it to the surface. It is instructive to compare the diffusivity of aerosols (5.39) to the diffusivity of gases (11.16).
The Schmidt number Sc is the ratio of the kinematic viscosity of the fluid to the Brownian diffusivity of the particle
![]() | (5.40) |
Thus Sc is the ratio of two diffusions: the diffusivity of momentum and vorticity ν to the Brownian diffusivity of the particle 𝒟B (Slinn, 1982).
The two most important processes (besides gravity) for aerosol transport through the quasi-laminar layer are inertial impaction (5.38) and Brownian diffusion (5.40). The total resistance of the quasi-laminar layer to aerosol dry deposition may be approximated as the resistance to these processes acting in parallel
The Schmidt number term in the denominator accounts for Brownian diffusion and is dominant for D ~ < 0.7 μm. The Stokes number term accounts for inertial impaction and becomes important for D ~ > 5 μm. There is some confusion concerning the dependence of rb on Sc. The resistance to particle or gaseous diffusion across the quasi-laminar layer to a solid surface is proportional to Sc-2∕3 (Slinn et al., 1978). This result can be derived by considering viscous flow at high Reynolds number over a fixed, smooth surface. A free surface such as liquid water, however, will tend to slip in the direction of the mean wind so that the characteristic air velocity in the diffusion layer is somewhat larger. According to Slinn and Slinn (1980), the resulting transfer coefficient for particles across the quasi-laminar layer to a free surface (e.g., ocean) is proportional to Sc-1∕2.Equation (5.41) neglects the following processes which may contribute to aerosol transport across the quasi-laminar layer: thermophoresis, electrophoresis, and diffusiophoresis1 (phoresis means force) (e.g., Slinn et al., 1978; Seinfeld and Pandis, 1997).
This section describes the sink processes which occur in the presence of clouds and precipitation. Due to the problem of unresolved scales and uncertain collision and collection coefficients, representation of wet deposition in large scale atmospheric models is as much art as science. Wet depositional processes have accumulated much redundant terminology. For our purposes, wet deposition refers to (the sum of) all depositional processes by which aerosol are removed from the atmosphere due to physical uptake (collection, precipitation) by cloud or precipitation particles.
The efficacy of various aerosol wet deposition schemes has been tested for the case of 210 Pb deposition. 222Rn is continuously emitted from the Earths continental surfaces at a rate which is fairly well known on large scales, 0.721.2,atom cm-2 s-1 (Guelle et al., 1998). 222Rn has a half-life of 3.8 days and decays to 210Pb with a half-life of 22 years. The 210Pb gas attaches rapidly to ambient aerosol in the accumulation mode.
Removal of accumulation mode 210Pb by dry deposition is inefficient so that removal of atmospheric 210 Pb is due to wet deposition to first approximation. Giorgi and Chameides (1986) introduced a first-order loss rate method. Balkanski et al. (1993) apply the method of Giorgi and Chameides (1986) to 210Pb. Guelle et al. (1998) generalize Balkanski et al. (1993) to include size-dependence and evaluate the scheme with 210Pb. Lawrence and Crutzen (1998) show that the gravitational settling of smaller non-precipitating cloud particles may cause a significant downward redistribution of soluble trace gases. Collision or coalescence scavenging mechanisms are thought to be responsible for the incorporation of the dust particles into raindrops. Levin et al. (1990) reported pH as high as 8.2 in raindrops containing mineral dust.
Slinn (1982, 1984) reviews the measurements and theory of wet and dry deposition and presents a summary of the various dimensionless fluid mechanical quantities which define particle flow. The Peclet number Pe is the ratio of the transport velocity of particles (i.e., vg for gravitational sedimentation) to their diffusion velocity (𝒟B∕r).
Inserting (5.40) into (6.1) we obtain Although we shall not, many authors use Pe in place of the product of the ReSc in aerosol kinematics such as (6.4) below.Dana and Hales (1976) synthesized then available parameterizations of diffusion, impaction, and interception into a numerically tractable definition of the scavenging coefficient. Nieto et al. (1994) performed a sensitivity study of the scavenging coefficient to the formulation of the particle and droplet size distribution and showed that a lognormal distribution of raindrop sizes produce negligible bias compared to other size distributions.
? use SO2 concentration as a proxy for chemical aging and hygroscopicity of mineral aerosol. Such aging exacerbates nucleation scavenging of dust downwind of polluted regions, and may help explain model underprediction of dust deposition in the northwest Pacific relative to the tropical North Atlantic.
The collision efficiency between collector particles (i.e., raindrops) of size DP and collected particles (i.e., aerosols) of size Dp1 is denoted E(DP,Dp). If aerodynamic interactions between the particles did not occur then E(DP,Dp) would be unity. Thus E(DP,Dp) corrects geometric collection volumes for the effects of streamline deformation due to particle-fluid interactions. In practice the processes accounted for by E(DP,Dp) include Brownian diffusion, interception, and inertial impaction and so we assume
![]() | (6.3) |
where EBD, EMPC, and ENTC are the individual collision efficiencies for the processes of Brownian diffusion, interception, and inertial impaction. Processes not typically accounted for include thermophoresis and electrophoresis. We next consider the physical forms of the individual processes.
The collision efficiency due to Brownian Diffusion, EBD, accounts for particles random walking across streamlines due to thermal motion. Brownian diffusion is primarily important for very small particles, thus EBD dominates E(DP,Dp) for Dp < 0.2 μm (cf. Figure 6.1, below). According to Slinn (1984),
The first two terms inside the brackets constitute the particle Sherwood number. The 0.4 coefficient was determined experimentally. Note that Re and Sc in (6.4) refer to different particles: Re is the Reynolds number of the raindrop, but Sc is the Schmidt number of the aerosol.
The collision efficiency due to interception, ENTC, accounts for particles which follow the streamlines of fluid flow around an approaching raindrop, but whose radius is greater than the distance of the streamline to the raindrop. Thus interception is strictly due to particle size, not mass, and is primarily important for large particles. According to Slinn (1984),
where
≡ Dp∕DP is the ratio of the collectee to collector sizes. As in (6.4), the Re refers to the raindrop,
not to the aerosol. The viscosity ratio, ω ≡ μa∕μH2O, is the ratio of the dynamic viscosity of the
atmosphere to the dynamic viscosity of the fluid in the collector (i.e., liquid water in the case of
raindrops). Slinn (1982) uses f, the ratio of the maximum internal circulation speed within the
raindrop to the to raindrop fall speed, in place of ω in (6.5). Section 10.3.1 of Pruppacher and
Klett (1998) contains an extensive discussion of both of these quantities. They suggest an appropriate
viscosity ratio for falling raindrops of ω ≈ 1∕55, and an appropriate velocity ratio f ≈ 1∕25.
Interception ENTC dominates E(DP,Dp) for 1 < Dp < 3 μm (Nieto et al., 1994) (cf. Figure 6.1,
below).
The collision efficiency due to impaction, EMPC, accounts for particles whose inertia prevents them from following the streamlines of fluid flow around an approaching raindrop. Due to their large size (and Stokes number) and the sharpness of the streamlines, inertia prevents these particles from being pushed out of the trajectory falling raindrops so collisions occur. A more apt description of this process is inertial impaction. Impaction is primarily important for very large particles.
The derivation of EMPC depends on the fluid mechanical concept of potential flow. The relative flow between a raindrop and an aerosol is characterized by the difference in fall velocities, Vg -vg. The Stokes number of the aerosol in this relative flow is
where τr is the characteristic relaxation timescale of the aerosol Since ρpu*2∕μ a has units of s-1,
r is indeed dimensionless. The relaxation timescale is the e-folding time
for a particle to approach its terminal velocity starting from a motionless state. τr is purely a function of
the aerosol particle and the environment. The raindrop properties enter the definition of St by determining
the speed of the relative flow, and by determining the characteristic length of the flow. This characteristic
length, DP, which appears in the denominator of (6.6), is the distance the aerosol must be displaced in
order to avoid impaction.
A critical Stokes number St* for this relative flow may be derived for particles directly in the path of the upstream stagnation point of the approaching sphere (raindrop). St* is the maximum Stokes number of the relative flow a particle can have and not be impacted when it is directly in the path of the approaching sphere. Particles with St < St* are even less likely to impact in slower, more viscous flows (Slinn, 1982). A combination of numerical simulation and analytic expansion yields
As before, Re (3.13) refers to the raindrop, not the aerosol.The critical Stokes numbers for flow near the stagnation point past a sphere, circular cylinder, and disk have been derived analytically as 1∕12, 1∕8, and π∕16, respectively (Slinn, 1982). Thus (6.9) asymptotes to the correct St* for large Re past a sphere.
According to Slinn (1982), EMPC may be expressed solely in terms of St and St* as
The threshold in (6.10) results in a discontinuous transition from a regime of no impaction for Dp ~ < 3 μm to impaction-dominated for Dp ~ > 3 μm. EMPC dominates E(DP,Dp) for Dp ~ > 3 μm (cf. Figure 6.1, below). Particle density ρp plays a role in the impaction efficiency as EMPC ∝ ρp-1∕2 (6.10). Raindrop density ρ P plays two roles in the impaction efficiency. First, EMPC ∝
. Second, the Reynolds number deterimines St* (6.9) and Re ∝ V
g ∝
(5.25).
Summing contributions from these three processes, Brownian diffussion, interception, and impaction, (6.3) becomes
where H(x) is the Heaviside step function, ρP is the density of the precipitation, and ρp is the aerosol density. Slinn (1982) cautions that although the processes discussed so far in (6.11) may be reasonably well known (i.e., within a factor of two), other processes (particle growth, thermophoresis and electrophoresis) may cause the actual E(DP,Dp) to differ from (6.11) by orders of magnitude.Figure 6.1 shows the simulated collision efficiency E(DP,Dp) between monodisperse raindrops and an aerosol population.
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The transition between diffusion and interception regimes occurs near Dp = 0.6 μm, and the transition between interception and impaction regimes occurs near Dp = 5.0 μm. Dana and Hales (1976) present simpler, analytically integrable forms of E(DP,Dp).
The collision efficiency (6.11) embodies an impressive amount of theoretical and empirical physical studies. We shall note some interesting features of the solution. Particle density ρp appears directly only in the impaction term. Diffusion and interception are functions of aerosol size (not mass), and of environmental and raindrop properties. Thus aerosols of different compositions are expected to have similar collision efficiencies except in the inertial impaction regime where E(DP,Dp) ∝ (ρP∕ρp)1∕2.
The preceding discussion covers only the geometric and fluid dynamical aspects of particle
motion that contribute to particle collision. To compute the actual mass removal rate we must
know how often collisions result in collection or retention of the the aerosol. Thus we are
interested in the sticking efficiency or retention efficiency of interparticle collisions. Sticking
efficiency is defined as the fraction of collisions that result in immediate accretion of the collected
particle, as opposed to collisions where the particle simply bounces off the collector. The
collection efficiency
(DP,Dp) is defined as the sticking efficiency times the collision efficiency
may depend on many factors besides size, such as composition, charge, and relative
humidity.
Submicron particles have surface areas very large relative to their volume (mass). In these conditions molecular forces such as dipole-dipole interactions and van der Waals forces are strong enough that ξ = 1 is well-justified particles are always retained after collisions (Slinn, 1982). There are no data suggesting the sticking (retention) efficiency ξ is other than unity for D ~ < 20 μm Larger particles are less susceptible to Van der Waals forces, and there is evidence that ξ < 1 (Slinn, 1982, p. 330), although ξ is still highly species-dependent. Lacking any comprehensive data we shall assume ξ = 1 unless otherwise noted.
Having discussed the aerodynamic properties of particle-particle interactions we are now ready to formulate the problem of scavenging of aerosols by raindrops in a form suitable for numerical models. The problem is do determine the rate of removal of aerosols of a given size distribution by a precipitation rate of a given intensity and size distribution. We shall adopt the convention that uppercase symbols refer to the collector species (called raindrops) and lowercase symbols refer to the collected species (called aerosols).
It will prove useful to derive expressions for the precipitation fluxes in terms of the raindrop size distribution. The rainfall rate P may be expressed in terms of the microphysical distribution of raindrops of size DP and their fallspeeds, Vg. The spectral precipitation intensity Pz(DP) (m3 m-2 s-1 m-1 or m s-1 m-1) is the convolution of the raindrop volume distribution with the terminal velocity of the raindrops
The physical dimensions precipitation intensity can be confusing and require clarification. The spectral volume flux Pz(DP) (m3 m-2 s-1 m-1) is the volume of rain (m3) falling per unit horizontal area (m-2) per unit time (s-1) per unit raindrop size (m-1). Cancelling spatial dimensions in numerator and denominator leaves the dimensions s-1, which lack any physically intuitive meaning. Canceling like dimensions less assiduously results in m s-1 m-1, which is more easily interpreted as the rate of change of depth of water per unit surface area per unit raindrop size.Usually P is measured or quoted as a precipitation intensity or precipitation volume flux Pz (m s-1) which is the total rate of increase of liquid water depth in a unit area due to precipitation of all sizes. The total precipitation intensity Pz (m3 m-2 s-1 or m s-1) is obtained by P z(DP) integrating over all raindrop sizes
To obtain Pz in the more commonly used units of mm hr-1, multiply P z by 1000 × 3600 = 3,600,000. For comparison, typical values of precipitation intensity Pz during drizzle and heavy rain are 0.5 and 25 mm hr-1, respectively.Precipitation intensity may also be be expressed as a mass flux. The spectral precipitation mass flux PM(DP) (kg m-2 s-1 m-1) and precipitation mass flux P M are defined analogously to (6.14) and (6.15), respectively, but with raindrop volume replaced by raindrop mass
Here we have assumed that the precipitation is liquid water so that the density of the collectors ρP = ρl. In environments where precipitation composed of ice, snow, or other chemical constituents, ρl should be replace by the appropriate density in the definition of PM(DP). For the simple case of rain, however, PM ≈ 1000Pz. Thus to convert PM to Pz in mm hr-1, multiply P M by 3600. Although P is relatively easy to measure at the surface, its vertical distribution is not.Precipitation scavenging of aerosol takes place in the atmosphere below clouds when falling raindrops collide with and collect aerosols. Consider the physics of precipitation scavenging from the point of view of a single rain droplet of diameter DP falling with speed Vg. During its descent this raindrop sweeps out a volume of πDP2V g∕4 per unit time. Any aerosol partially located in this volume will also be collected, so the geometric collection volume of the raindrop is actually π(DP + Dp)2V g∕4 per unit time. Finally, the motion of the aerosol reduces the collection volume Vc (m3 s-1) of a raindrop to a cylinder expanding at the speed of the relative motion,
The number of aerosols of size between Dp and Dp + dDp in a given volume of space is, by definition, nn(Dp) dDp. The number of aerosol particles a raindrop of size DP encounters per unit time in its geometric path,
g, is
![]() | (6.20) |
Assuming a perfect sticking efficiency ξ = 1,
g is the rate of aerosol collection (# m-3 s-1) in the
geometric limit. The rate of mass collection (kg m-3 s-1) in the geometric limit would be obtained by
simply replacing nn with nm in (6.20).
The great complication to the geometric formulation of aerosol number and mass scavenging is due to
the aerodynamic interaction of the raindrop and aerosol described above. These interactions were
combined into an aerodynamic correction factor called the collision efficiency, E(DP,Dp). We may
now understand E(DP,Dp) to be the fraction of particles of size Dp contained within the
geometric collision volume of raindrops of size DP (6.20) that are actually encountered. With this
aerodynamic correction, the definition of the actual rate of collection of aerosol by a raindrop,
, is
completed
![]() | (6.21) |
Note that in the following we use E(DP,Dp) rather than
(DP,Dp) in conformance with convention.
However, if the sticking efficiency ξ
1 then E must be replaced with
(6.13).
(DP,Dp) applies to a single raindrop and aerosol size. The total rate of collection of aerosol
particles of size Dp is obtained by integrating (6.21) over the number distribution of the raindrops
Nn(DP),
![]() | (6.22) |
Fortunately the complexity of (6.22) can be reduced for typical atmospheric atmospheric conditions. The fall speed of rain (DP > 100 μm) greatly exceeds the fall speed of any long-lived aerosol (Dp < 20 μm), so Vg ≫ vg (5.25) and (DP + Dp)2 ≈ D P2. These approximations are not necessarily valid for drizzle.
Using these approximations, in conditions of steady precipitation the rates of number and mass removal of aerosol particles of size Dp due to below cloud precipitation scavenging are
With the great uncertainties presented above firmly in mind, we are ready to define the scavenging
coefficient, Λ as the first order removal rate of aerosol mass and number concentration. Noting that
= dnn∕dt and
= dnm∕dt, (6.23) may be rewritten as first order loss equations in nn(Dp) and
nm(Dp), respectively
All the information about the raindrop size and rainfall intensity in Λ(Dp) is contained in Vg and Nn(DP) (6.17). It is useful to recast Λ(Dp) explicitly in terms of P , which is often measured (or predicted).
Suitable approximations for may considerably simplify the problem of parameterizing Λ(Dp) in large scale models. Using the approximation for raindrop fall speed Vg (5.27), yields
Assuming analytically integrable distributions (e.g., lognormal) for Nn(DP), the principal difficulty in applying (6.29) is the complicated form of E(DP,Dp) (6.11).Solving (6.24)(6.25) for the time dependent number or mass concentration yields
The e-folding timescale for wet scavenging of particle number and mass is [Λ(Dp)]-1. Figure 6.2 shows the simulated Λ(Dp) for monodisperse raindrops (DP = 400 μm) collecting aerosol during a mild precipitation event with intensity Pz = 1.0 mm hr-1.|
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The discontinuity between the interception and impaction regimes is located at about Dp = 2 μm. On either side of this discontinuity removal timescales change from about 1 hr to a few days.
To determine the total removal of aerosol number and size by raindrops, we must integrate the scavenging rate of each aerosol size (6.24)(6.25) over the aerosol size distribution nn(Dp)
Inserting nm(Dp) =
Dp3ρ
pnn(Dp) into (6.32) we obtain
The number mean scavenging coefficient ΛN (s-1) is defined by an analogous procedure. Beginning with (6.32) we have
where where we have followed Seinfeld and Pandis (1997) in changing the order of integration to introduce Pz (6.15) into the final expression. This order change is only legal when raindrops are monodisperse because DP is present in E(DP,Dp), see, e.g., (6.5). The solution of (6.36) for time dependent aerosol mass concentration is The timescale for number depletion of the entire aerosol distribution by wet scavenging is thus ΛN-1.The scavenging efficiency η(Dp) (dimensionless) is the fractional change in aerosol number or mass concentration during a time increment Δt. Applying this definition to either time-dependent concentration (6.30) or (6.31) yields the same result,
Thus η(Dp) depends explicitly only on particle size. The sign convention used in (6.40) ensures that η(Dp) is negative definite.The mass mean scavenging efficiency ηM applies to the entire mass distribution. The derivation of ηM is analogous to (6.40), but begins with the time-dependent solution to total aerosol mass concentration (6.35),
The derivation of the number mean scavenging efficiency ηN proceeds analogously from (6.39) and yieldsAssuming precipitation falls at a uniform rate P during a time period Δt, we may redefine the scavenging efficiency in terms of rainfall depth rather than elapsed time. Let ΔPz (m) be the depth of precipitation accumulated in time Δt, i.e.,
To complement ΔPz we define precipitation-volume-normalized scavenging coefficients whose dimensions are m-1: and precipitation-mass-normalized scavenging coefficients whose dimensions are m2 kg-1: Note that
expressed in mm-1 (6.46) is numerically equal to
expressed in m2 kg-1 (6.49) as long as
the hydrometeor density is taken to be 1000 kg m-3, which is accurate for rainwater.
Figure 6.3 shows the simulated
(Dp) for various lognormal size distributions of raindrops. The
number median raindrop size and geometric standard deviation of lognormal raindrop distributions used
to simulate convective and stratiform rain events are
P,n = 1000 μm, σg,P = 1.86 and
P,n = 400 μm,
σg,P = 1.86, respectively (Nieto et al., 1994).
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These normalized scavenging coefficients can be scaled to any precipitation flux simply by multiplying by PM (6.49). Polydisperse raindrops do not greatly reduce the scavenging discontinuity between interception and impaction regimes seen in monodisperse simulations (cf. Figure 6.1). As discussed in §6.3, aerosol density does not play a role in the scavenging efficiency except in the impaction process. Thus Figure 6.3 is virtually identical for all aerosol compositions (i.e., sulfate, dust, carbon, and sea salt) for sizes Dp ~ < 2 μm.
Figure 6.3 also shows that great care must be taken in discretizing the continuous equations of aerosol evolution. If any part of a size bin contains Particles susceptible to inertial impaction (Dp ~ > 2 μm) should not be placed in the same bin as smaller particles. For instance, if a binning approach is taken and a bin contains any Given the uncertainties involved in predicting or measuring the raindrop size distribution Nn(DP), Slinn (1984) recommends using the mass-weighted mean raindrop size DP,v to determine the scavenging rates. Mason (1971) found that the fourth power of DP,v varied linearly with the precipitation intensity:
where all equations except for the first are in SI units. According to (6.50), DP,v = 700 μm when Pz = 1 mm hr-1.The microphysics of precipitation are simultaneously one of the most important and least understood aspects of the climate system. Precipitation prediction (and, eventually, modification) is the holy grail of weather forecasting. Aerosols interact with precipitation formation by serving as additional nucleation sites, and thus adjusting the overall competition for water vapor in the cloud. Hygroscopic dust may serve as CCN, and even hygrophobic dust with appropriate crystal structure may serve as IN. Relatively coarse-sized dust (D ~ > 5 μm) which nucleate immediately create large cloud droplets. These nuclei are called giant cloud condensation nuclei, or GCCN. [Levin, Zev]Zev Levin finds that about 30 GCCN cm-3 are enough to double integrated precipitation in warm clouds. This holds unless IN are present. [Möhler, O.]O. Möhler found that deposition freezing on Saharan dust commences at 1.1 ~ < RHi ~ < 1.2. This is far lower than the RHi required for deposition freezing on carbonaceous or liquid aerosol. DeMott et al. (2003) found in that dust aerosols act as Ice Nuclei more efficiently than any other particles above homogeneous freezing temperatures. They found IN concentrations exceeded 1 cm-3 in aerosol layers containing sub-micron dust particles. Sassen et al. (2003) show that dust particles glaciated a supercooled (-8.8 < T < -5.2∘C) altocumulus cloud during CRYSTAL-FACE. This causes an indirect effect on climate through cloud structure. Yamagata et al. (2004) found mineral dust aerosol was included in more than 50% of droplets artificially formed in a mineshaft. Dunion and Velden (2004) show that the Saharan Air Layer (SAL), and the dust it often carries, sometimes plays an important role in suppression tropical cyclone activity in the North Atlantic.
Hygroscopic growth of aerosol must be considered in the formulation of precipitation scavenging.
Swelling and coating of aerosol can increase the number median diameter
n of an aerosol
distribution by a factor of two or more. This increase in size will change the mean scavenging
properties of the aerosol distribution ΛM. If the aerosol mass is largely contained within the
accumulation mode then hygroscopic growth will increase ΛM. If the aerosol mass is largely
contained in sizes smaller than the accumulation mode then hygroscopic growth could decrease
ΛM.
Adams and Faure (1995) and Crowley (1995) present vegetation reconstructions of the LGM climate. Peltier and Marshall (1995) present an energy-balance/ice-sheet model which accounts for dust triggered ice-albedo feedbacks that may play a role in deglaciations. Overpeck et al. (1996) use a modeled dust distribution to show that the longwave radiative effects of dust may have induced significant regional warming during the LGM. Crowley and Baum (1997) study the effects of vegetation on LGM climate (without aerosols). Ram et al. (1997) describe the eleven year cycle of dust found in the Greenland GISP2 ice core. Harrison et al. (2001) review the role of dust in present day and LGM climate changes. Using extensive records (Kohfeld and Harrison, 2001) together with models, they predict the impact of dust on future climate. Robertson et al. (2001) assembled hypothesized aerosol and solar forcing time series, including mineral dust, from 1500present. Archer et al. (2000) Bopp et al. (2003) use a global coupled climate ocean biogeochemistry model constrained by DIRTMAP data to estimate the glacial-interglacial effect of dust-supplied Fe on atmospheric pCO2 is less than 30 ppm. An et al. (2005) summarize oceanic and terrestrial sediment records which demonstrate Global Iron Connections (GICs) on multiple timescales over the last 130 kya. The evidence they summarize is consistent with the Iron Hypotheses in all ocean basins except the South Pacific. Using a simple technique they estimate Asian dust is responsible for ΔpCO2 ~ 49 ppm, or one-tenth to one-third of the total dust effect estimated by Bopp et al. (2003). E. W. Wolff and Gaspari (2006) show 750,000m,yr timeseries of natural aerosols from the EPICA ice core of Dome C in Antarctica.
The kinetic theory of temperature links relates the macroscopic temperature to statistical properties of the molecular ensemble comprising the parcel. Statistical mechanics (e.g., Tsonis, 2002, p. 8) tells us that the mean kinetic energy of molecules with three spatial degrees of freedom is
where k is Boltzmanns constant. Inverting this definition for temperature yields
∞(T) is given in Table 14.3. The Ideal Gas Law (IGL) has many forms. For purposes of illustration, we
take the fundamental IGL form to be in terms of pressure p [Pa], volume V [m3], mole number n [mol],
temperature T [K], and universal gas constant R* [J mol-1 K-1]:
Introducing the specific volume v [m3 kg-1] of gas
leads to Since the density ρ [kg m-3] is v-1 The explicit presence of density in the equation of hydrostatic equilibrium (??) makes Equation (8.10) a particularly useful form of the IGL.
Applying (8.4) to water vapor leads to
Thus ρv,s, like
, is a function of T only. The rate of change of saturated properties (vapor
pressure, density, mixing ratio) with respect to temperature often appears in cloud and aerosol
microphysics. Measurements of d
∕dT are available in a similar form to
(Table 14.3). These
independent measurements result in a parameterization that is slightly different from a direct
algebraic derivative of Table 14.3. Most commonly gradients of other saturated properties are
expressed in terms of
and d
∕dT . Differentiating the Ideal Gas Law for vapor (8.12) shows that
George (2001) modeled radiative forcing by dust in the Arabian Sea region and evaluated the predictions against pre-INDOEX measurements. Myhre et al. (2003), Highwood et al. (2003), and Haywood et al. (2003) modeled radiative forcing by North African mineral dust during the Saharan Dust Experiment (SHADE) campaign (Tanré et al., 2003). Christopher et al. (2003) PRIDE fxm. Miller et al. (2003) examine the surface radiative forcing by dust and its influence on the hydrologic cycle. Clarke et al. (2004) measured the size distribution and analyzed the optical properties of soot-dust mixtures in Asian outflow. Roush (2005) presents the optical constants of montmorillonite, an important constituent of mineral dust. Roush et al. (1991) measure optical constants of kaolinite and montmorillonite. Querry et al. (1978) measure optical constants of limestone, aka amorphous calcite from 0.232.8 μm. Egan and Hilgeman (1979) report optical optical constants of many minerals including montmorillonite, illite, kaolinite, mica, and feldspar. Long et al. (1993) measure optical constants of crystalline and powdered calcite and gypsum from 2.5300 μm.
The interaction of radiation with matter is characterized by the index of refraction of the material at a give wavelength, n(λ). For non-absorbing media, such as air, the index of refraction is real-valued and represents the ratio of the speed of light through a vacuum to the speed of light through the material. For instance, the index of refraction of water is approximately 1.33, thus light propogates through a vacuum about one-third more quickly than through the ocean. In cloud and aerosol physics, however, absorption may not be neglected and the refractive index is best represented by a complex number, where the real part represents scattering and the imaginary part absorption. The nomenclature of refractive indices is quite intricate, since many related properties are also represented by complex numbers and this is not always made clear. Our discussion of refractive indices adopts the notation of Bohren and Huffman (1983), whose notation is concise yet is not ambiguous.
Refractive indices describe the absorbing and scattering properties of the medium. As such, the refractive index is connected to the dielectric properties of the medium. Plane electromagnetic waves of the form
satisfy Maxwells equations under certain conditions. Here Ec and Hc are complex representation of the electric and magnetic fields, respectively. The actual electric and magnetic fields are the real components of the complex representations, i.e., E = Re(Ec) and H = Re(Hc), respectively. The wavenumber vector k (m-1) and the angular frequency ω (s-1) define the spatial and temporal scales of the waves. The constant vectors E0 and H0 determine the amplitude and direction of the field.When the medium is absorbing, the wavenumber vector is complex
where k′ and k′′ are positive, real vectors. The wave vector of a homogeneous wave may be simplified as When (9.2) is substituted into the constituitive relations (e.g., Bohren and Huffman, 1983), we obtain where n is the index of refraction. The real and imaginary components of n, nr and ni, are positive definite due to the sign conventions chosen in (9.1) and (9.4).For example, the irradiance of a plane wave passing through an electromagnetic medium is attenuated with the distance z within the medium that the wave has traversed. For a wave of initial irradiance F0
where α is the absorption coefficient and is related to the index of refractionComplex refractive indices (9.4) are not the only quantities which concisely describe the optical properties of a material. The permittivity ɛ is usually expressed in terms of the relative permittivity ε and the vacuum permittivity ɛ0, also called the permittivity of free space.
![ɛ ≡ εɛ0 (9.7 )
ɛ ≡ -1---≈ 8.8541878176 × 10-12 [F m -1] (9.8 )
0 c2μ0](aer402x.png)
Refractive indices may be measured by many techniques, including Kramers-Kronig1 analysis and dispersive analysis. The dispersive analysis measures the zenith (normal) spectral reflectance of the material, and fits this to a series of independent damped oscillator resonances known as Lorentz lines (Querry et al., 1978; Long et al., 1993)
where the three parameters for each Lorentz line are the line strength Si, the resonance position
0,i, and
the damping constant γi [cm-1]. We write (9.10) in terms of wavenumber rather than frequency for
consistency with Querry et al. (1978) and Long et al. (1993) who report line parameters in
cm-1 units.
Long et al. (1993) tabulate a modified line strength A defined by
The modified line strengths A are smaller than S and this increases the convergence speed of data-fitting to (9.10).Querry et al. (1978) report resonance parameters from a dispersive analysis which constructs the dielectric constant as
where A′ i is a line strength and γ′ i is a (dimensionless) damping constant. It is straightforward to verify that (9.12) is equivalent to (9.10) when the following equivalence between the line strength and damping parameter definitions of Querry et al. (1978) and Long et al. (1993)| S | = A 02 = 4πA′
02 | (9.13a) |
| A′ | = S∕(4π
02) = A∕(4π) | (9.13b) |
| γ | = 0γ′ | (9.13c) |
| γ′ | = γ∕
0 | (9.13d) |
Fresnels equation determines the normal spectral reflectance ℛ in terms of the refractive index n
Heterogeneous aerosols are very common in nature. Analytic solutions exist for certain geometries of mixtures, such as concentric spheres (Bohren and Huffman, 1983). One way to treat the optics of these complex particles is to determine an effective refractive index which implicitly accounts for the fraction and optical properties of each individual component. The search for the best effective refractive index has fostered a variety of approximations known as effective medium approximations (EMAs). The web site Effective Medium Theories is devoted to EMAs, and is remarkably useful. EMAs include volume-weighting, the Maxwell Garnett approximation (Garnett, 1904), the Bruggeman approximation (Bruggeman, 1935), the Hollow Sphere Equivalent (Bohren and Huffman, 1983), and the extended effective medium approximation (Videen and Chýlek, 1998). Effective medium approximations all have the virtue of not requiring exact knowledge of the geometries of the multi-component aerosols.
The use of inclusion mass fraction M and inclusion volume fraction V in effective medium approximations varies. If the density of the medium and the inclusion are equal, then M and V may be interchanged in (9.23) and (9.23). In general, V is more appropriate because it is a spatial measure and effective medium approximations are based on approximations to the spatial distribution of radiation. Most authors use V (e.g., Videen and Chýlek, 1998). However, some authors (e.g., Bohren and Huffman, 1983) use M. We consistently use V in favor of M.
A two component aerosol is the simplest example of a multi-component aerosol (MCA). An idealized geometry would be a spherical matrix containing a spherical inclusion. The mass Mm, and volume Vm of the matrix component do not depend on the inclusion, though the matrix radius rm does. The inclusion radius rn, mass Mn, and volume Vn are completely independent of the matrix. Relations among the radius fraction rn∕m, mass fraction Mn∕m, and volume fraction Vn∕m of the inclusion relative to the matrix are
Note that (9.19) applies to the ratios of inclusion to matrix properties (analogous to dry mixing ratios), not inclusions to total properties (analogous to moist mixing ratios).
The Hollow Sphere Equivalent approximation (Bohren and Huffman, 1983, p. 149) defines. . .
The simplest estimate for the multi-component index of refraction is to weight the optical properties of each component by the volume occupied by that component.
Volume-weighting the refractive indices n (9.20) rather than the electric permittivity ɛ (9.21) leads to different answers since
=
2 (9.4). Whether (9.20) or (9.21) makes more physical sense or performs
better should be investigated.
The volume-weighted approximation is often made for liquid mixtures. However, Section 9.6.1 describes a more accurate treatment, the theory of partial molar refraction.
The Maxwell Garnett approximation2
(Garnett, 1904) defines an effective dielectric function
for a medium formed of a background
matrix containing random sizes, shapes, orientations, and positions of inclusions of different
compositions. The approximation takes a relatively simple form for homogeneous spherical inclusions
of any size and position and with the same composition embedded in a matrix of a distinct
composition. Let the (complex) dielectric constants of the inclusions and the matrix be ɛ and
ɛm, respectively, and let the total volume fraction of the inclusions be V. Then the Maxwell
Garnett approximation for the effective dielectric constant of the two component mixture is
We use (9.9) to rewrite the Maxwell Garnett approximation (9.23) in terms of refractive indices
where V is the volume fraction of the inclusion, and nm and n are the matrix (medium) and inclusion (particle) refractive indices, respectively (Videen and Chýlek, 1998). Equation (9.23) is suitable for evaluation when refractive indices, rather than electrical permittivity, is the independent variable of choice. Equivalently, This form may yield greater insight into the relative roles of the the matrix and inclusion in the optical properties, at the expense of a few more complex arithmetic operations.Although (9.23) has the correct limit as ɛm → ɛ, it is not symmetric under the exchange of the matrix and the inclusion. This is problematic when it is difficult to determine which component is the matrix and which is the inclusion. Nonetheless, no approximation has been more successful or widely used than (9.23).
The Maxwell Garnett approximation extends to N-component aerosol mixtures where N > 2 (Bohren
and Huffman, 1983, p. 216). One of the N components must be identified as the matrix; the remaining
N - 1 components are considered inclusions. Inclusions contribute to the effective permittivity
according to their volume, permittivity, and geometry:
The geometric factor β reduces to a simple analytic expression for idealized spherical inclusions
Substitution of (9.27) into (9.25) with N = 2 leads directly to (9.23).The Bruggeman approximation (Bruggeman, 1935) for the mean dielectric function of a two component mixture is (Bohren and Huffman, 1983)
Certain limits of (9.28) must be carefully treated numerically First, (9.28) is indeterminate in the limit as ɛm → ɛ. In this case, set
= ɛ = ɛm. Second, the limit as V → 0 may cause difficulty with the quadratic
equation numerical solution presented below (cf. (9.29)). In this case, direct substitution of V = 0 into
(9.28) yields the correct result that
→ ɛm.
A prime advantage of (9.28) is its symmetry:
is invariant under exchange of ɛ and ɛm. The
terminology of matrix and inclusion is therefore ill-suited for the Bruggeman approximation, since
conceptually, a matrix occupies more volume than an inclusion and therefore has a preferred status. It is
more consistent to simply label components by numerical subscripts (e.g., n1,n2) in the Bruggeman
approximation. However, the very symmetry of the components allows us to continue to use our old
terminology with the Bruggeman approximation without fear of applying the matrix or inclusion
properties in the wrong slot (since their identities are irrelevant).
This component symmetry of the Bruggeman approximation (9.28) has conceptual advantages over other effective medium approxiations (e.g., (9.23)) whenever it is difficult to assign one component the role of the matrix and the other the role of inclusion. However, (9.28) has not been quite as successful at predicting experimental results as the Maxwell Garnett approximation (Bohren and Huffman, 1983, p. 217).
Application of the Bruggeman approximation is more difficult than the Maxwell Garnett theory
because of the implicit definition of
in (9.28). Fortunately, straightforward algebraic manipulation
reduces the definition to a quadratic polynomial in
. Multiplying (9.28) by ɛ + 2
and then by ɛm + 2
we
obtain
. In deciding which of the roots is physical, one must
discard roots which make (9.28) indeterminate, i.e.,
- ɛ∕2 and
- ɛm∕2. Finally, the
square root of
with the positive imaginary component, if any, must be taken to conform with
the sign conventions (9.1) and (9.4). In practice, root finding methods (e.g., bracketing) may
be preferable when a large number of smoothly varying spectral properties must be solved
for.
In terms of refractive indices, the Bruggeman approximation (9.28) is equivalent to
where V is the volume fraction of the inclusion, and n and nm are the inclusion and matrix refractive indices, respectively. Recall that the Bruggeman approximation is symmetric under interchange of the components, so either component may be labeled the matrix and the other the inclusion. The solution to (9.30) is obtained by substituting (9.9) into (9.29): which is a quadratic equation in
2. The preceding discussions on physically realistic solutions to (9.29)
apply equally to (9.31).
The Bruggeman approximation extends to N-component aerosol mixtures where N > 2.
The extended effective medium approximation (EEMA) (Videen and Chýlek, 1998) relaxes the
assumption (implicit in other effective medium approximations) that the grain sizes are small compared to
the wavelength of light. The resulting extended effective refractive index
is obtained by iterative
solution to
is the effective refractive index, nm is the matrix (medium) refractive index, n is the inclusion
refractive index, k denotes the iteration, V is the volume fraction of the inclusion, Ak and Bk are given by
| Ak | = -![]() | (9.33a) |
| Bk | = ∑
n(2n + 1)[an(r,nm∕ k) + bn(r,nm∕ k)] | (9.33b) |
The most general definition of the size parameter χ is is the ratio of particle circumference times real refractive index of the surrounding medium to wavelength
For particles in air, nr ≈ 1 so χ ≈ 2πr∕λ. The size parameter χp of inclusions in cloud droplets is approximately nr ≈ 1.33 times the size parameter χ of the same inclusion in air or in vacuum. Videen and Chýlek (1998) show that the extended effective medium approximation is more accurate thatn Maxwell Garnett and Bruggeman appoximations for inclusion size parameters χp > 0.5.
Laboratory and field measurements of dust refractive properties are reported in Patterson et al. (1977); Volz (1973); Patterson (1981); Bohren and Huffman (1983); Tanré et al. (1988); Sokolik et al. (1993); Hess et al. (1998). Refractive properties of salts (e.g., NaCl, (NH4)2SO4, NH4NO3) are in Volz (1973); Tang and Munkelwitz (1994); Tang (1997), Refractive properties of pure water are reported in Ray (1972); Segelstein (1981); Wieliczka et al. (1989); Pope and Fry (1997) (liquid phase) and Ray (1972); Warren (1984); Perovich and Govoni (1991) (ice phase). Sophisticated models may be used in conjunction with field measurements to constrain optical properties. Multiple studies have used this technique to estimate ni for dust (Dubovik, 2001; Dubovik et al., 2002; Colarco et al., 2002; Sinyuk et al., 2003; Torres, 2003). Uncertainty in dust optical properties straddles the boundary between dust causing net cooling and net heating of the climate system. This boundary occurs at a single scattering albedo ϖ ~ 0.91 (Liao and Seinfeld, 1998b). At 0.64 μm, Kaufman et al. (2001) found ϖ = 0.97 ± 0.02 from a combination of satellite measurements and in situ remote sensing from AERONET. This is in contrast to ϖ = 0.87 ± 0.04 typical of earlier studies (Sokolik and Toon, 1996). Colarco et al. (2002) determined the UV imaginary index of refraction ni of Saharan dust particles from TOMS data using a three-dimensional model of dust transport. At Sal and Tenerife, ni = 0.0048(0.00240.0060) and ni = 0.004(0.0020.005) at λ = 331 and 360 nm, respectively. At Dakar, ni = 0.006(0.00240.0207) and ni = 0.005(0.00200.0175) at λ = 331 and 360 nm, respectively. After integrating over the measured size distributions, they obtained single scattering albedos at λ = 331 nm of ϖ = 0.81(0.650.90), 0.84(0.820.91), and 0.86(0.830.89) at Dakar, Sal, and Tenerife, respectively.
The problem of determining the optical properties of a coated sphere (or cylinder) has been solved analytically. Naturally, the solutions bear a strong resemblance to Mie theory. Additional features are caused by interference patterns between the reflections of the core and the mantle.
The partial molar refraction approximation assumes that all components are homogeneously mixed in the aerosol. Thus the approach is best-suited to liquid aerosols. The parameterization technique, described and evaluated by Stelson (1990), depends on the observed additivity of a quantity known as the molar refraction R [m3 mol-1] of condensed phase species. The molar refraction may be simply defined in terms of the molar volume and the refractive index n as
where the molar volume Ṽ [m3 mol-1] is the physical volume occupied by the solution per mole of solution.If the ratio of the two quadratic functions of n in (9.35) appears non-intuitive, it is worthwhile to trace its origins because it appears in many optical approximations. The factor (n2 - 1)∕(n2 + 2) appears in the a1 coefficient of Mie theory. The a coefficients are defined in terms of spherical Bessel functions, and when the Bessel functions are expanded into power series (e.g., Bohren and Huffman, 1983, p. 131), the dominant term in the a1 coefficient contains the quadratic factor.
The mean molecular weight of a solution
[kg mol-1] is the sum of the dimensionless volume
mixing ratio (i.e., molar fraction) χi of each species times its mean molecular weight ℳi.
by the density of the bulk solution ρ we obtain the bulk molar volume Ṽ in m3 mol-1
The molar refraction R (9.35) of a solution is the sum of the partial molar refractions of all the constituent species Ri, weighted by the respective volume mixing ratios χi
To illustrate the usefulness of the partial molar refraction approximation we consider a two component solution. For concreteness, imagine that the first component is liquid water and the second component is NaCl, so that the solution is similar to deliquescent sea salt aerosol (which would also include MgSO4). The physical properties of the components and of the bulk solution are labeled with and without subscripts, respectively, (e.g., Ṽ1, Ṽ2, and Ṽ). Using (9.39) and then (9.35) we see that
If we consider the properties of the first component (e.g., pure water) as known, and the properties of the solution are measured, then the molar refraction of the second component (e.g., NaCl) may be inferred as Since all the quantities on the RHS are known, R2 is determined. Stelson (1990) show that the R2 determined from (9.40) is generally independent of ionic strength.In modeling studies, often the mass fractions of the various species are known (or predicted) and it is the mean refractive index of the bulk solution that is of interest. Inverting (9.35) to obtain n in terms of R and Ṽ we obtain
Thus the quantity R∕Ṽ is seen to determine the optical properties of the bulk solution. We may rewrite R∕Ṽ in terms of the physical volume V [kg m-3] of the bulk solution, and the mass fraction Mi and density ρi of each component. Combining (9.38) and (9.39) we obtain
According to (Kiehl et al., 2000)
For H2SO4 with
n = 0.1 μm and ln σg = 0.7, Kiehl et al. (2000) showed
[c1,…,c5] = [11.24,-0.304,-1.088,-177.6, 15.37].
Due to human influence the fraction of Earths aerosol composed of absorbing substances, especially carbon, is constantly increasing. It is therefore of interest to quantify the aerosol-induced heating. In highly absorptive atmospheric conditions, it may be possible to use sophisticated instruements to determine aerosol properties such as the single scattering albedo from the measured temperature change resulting from radiant heating.
Net particle heating qp is the result of latent, sensible, and radiant heating, each a complex microphysical process. Condensation and deposition of vapor to the surface of a particle cause latent heating. Evaporation and sublimation of vapor from the surface of a particle cause latent cooling. Thus latent heating, denoted ql, requires mass transfer to or from the particle surface. Thermal conductance, that is, the transfer of heat to or from the surface of the particle by molecular diffusion, is called sensible heating and denoted by qh. Absorption and emission of radiant energy by a particle is called radiant heating, denoted qr.
We now briefly digress to discuss the physical units employed in this section. To understand aerosol heating it is convenient to work in terms of power, or energy per unit time. Thus we shall express qp, ql, qh, and qr in J s-1 or Watts. It is technically correct to say that these q x measure a heating rate, i.e., the rate at which heat, in any of its forms, is transferred. However, in the literature the terminology heating rate is generally used for quantities measured in temperature change per unit time, e.g., K s-1 or K day-1.
Meteorological models often predict heating rates related, but not identical to qx. Most often it is the heatings per unit volume, qv x, J m-3 s-1 = W m-3, that are available. qv is the integral of the particle heating weighted by the particle distribution in a unit volume,

The heat budget (9.44) of wetted particles is driven by the latent heating which occurs as particles constantly adjust to changing humidity in their environment by seeking a thermodynamically stable size. During the continual processes of condensation and evaporation any net change of mass changes the latent heat stored by the particle so that
The rate of diffusional growth of a particle depends on Δρv, the difference between the vapor density at the surface of the particle, ρv,r and the vapor density far from the surface, in the surrounding medium, ρv,∞. The solution to the vapor diffusion equation (see §11.4.2) for a spherical particle yields where fm is the mass ventilation coefficient. The mass ventilation coefficient fm is of order unity and accounts for the alteration of vapor convection and diffusion to the particle due to particle motion. It can be shown that the limiting behavior of fm is characterized by the dimensionless product Scv1∕3Re1∕2, where Re is the particle Reynolds number (3.13) and Sc v is the Schmidt number of vapor in air. Empirical parameterizations (see Pruppacher and Klett, 1998, p. 541) show Thus whether the dependence on Scv1∕3Re1∕2 is quadratic or linear depends on Sc v1∕3Re1∕2 itself.By analogy to (5.40) we have
where ν is the kinematic viscosity of air and DH2O, the diffusivity of vapor in air, is given by (11.17).Combining (9.48) with (9.46) yields
When curvature effects are negligible and the particle is (at least coated with) liquid water, the surface vapor pressure is the saturated vapor pressure over planar surfaces, ρv,r = ρv,s(Tp). The Ideal Gas Law (8.12) states that ρv,s(Tp) =
∕(RvTp) so that ql depends on Tp directly, and
implicitly through
S (14.6). The temperature dependence can be factored out of (9.51) by expressing the
vapor density gradient in terms of ΔT
It is important to bear in mind that diffusional growth (9.48) is only one of several limiting growth processes, others being surface- and volume-dependent chemical reactions (Seinfeld and Pandis, 1997, p. 685). However, we shall neglect the effects of chemistry on particle mass and on particle temperature, Tp.
Heat diffusion and mass diffusion (§9.8.1) from a particle are exact mathematical analogues of eachother. Thus Ficks First Law (11.35) suggests that the rate of sensible heat transfer is proportional to the the difference between the surface temperature of the particle, Tp, and the temperature of the surrounding medium, T∞.
The sign convention for ΔT is arbitrary and we chose (9.54) to follow Pruppacher and Klett (1998). Heat flows to the particle when ΔT > 0, from the particle when ΔT < 0. In complete analogy to (9.48), the solution to the heat diffusion equation for a spherical particle is where ka (W m-1 K-1) is the thermal conductivity of dry air (Pruppacher and Klett, 1998, p. 508) Related to ka is the thermal diffusivity of air κa (m2 s-1) (Pruppacher and Klett, 1998, p. 507)The sign convention in (9.55) ensures that particles get warmer (qh > 0) when T∞ > Tp and heat is conducted to the particle. Thus qh (9.55) and ql (9.53) both depend linearly on ΔT .
The thermal ventilation coefficient ft is a factor of order unity which accounts for the effects of particle motion on heat conduction. Since heat diffusion and mass diffusion are mathematically analogous, ft is usually expressed in terms of fm. To obtain ft from (9.49), we simply replace the mechanical diffusivity DH2O by the thermal diffusivity of air κa (9.57) in (9.50) to obtain a Schmidt number for thermal diffusion Sct
Using Sct in place of Scv (9.49), we obtainRadiant heating qr is generally of secondary importance for Ta, because qr ≪ ql. When this is the case, the net particle heating is a balance of latent and sensible heat transfer. A growing cloud droplet, for example, condenses more water vapor than it evaporates. The excess latent heat of condensation is ultimate conducted to the atmosphere by thermal diffusion, i.e., sensible heat transfer. The balance of latent and sensible heating is described in many texts (Pruppacher and Klett, 1978, p. 447),(Pruppacher and Klett, 1998, p. 542),(Rogers and Yau, 1994, p. 103).
Radiant heating qr may be very important in the heat balance of dry particles since ql ≈ 0, and, as shown below, for particles not in thermal equilibrium. An experimental apparatus may employ powerful radiant heating techniques such as lasers to probe aerosols.
There are many approaches to the problem of determining qr. Under the assumptions of the
Mie approximation, qr depends on the mean intensity
ν or actinic flux intercepted by the
particle and on the surface temperature of the particle Tp but not on the orientation of the
particle in space. A particle with equivalent-sphere radius rs will radiate isotropically and
absorb incident radiation as a perfect blackbody modulated by its absorption efficiency Qa
λ(λ)
into the sum of a collimated light source of strength F(λ) (e.g., the sun) and a mean intensity from the
diffuse field (which does not include the collimated source) of strength
D
λ . Then we have
Thus qr is itself the net result of radiant heating, caused by F and
D
λ , compensated by radiant cooling,
caused by Bλ. Neglecting F for the time being, (9.62) makes clear that the largest radiative contributions
to qr occur where the radiation field is out of thermal equilibrium, i.e., where
D
λ
Bλ. At cloud top, for
instance,
D
λ ≈
Bλ (Barkstrom, 1978).
We may further simplify (9.62) by considering the case of a spectrally uniform, collimated source,
e.g., a laser. In this case F(λ) = F(λ0) ≡ F0. We shall assume that the diffuse radiation field is in thermal
equilibrium at all wavelengths. Finally we shall drop rs in favor of r for simplicity, with the
understanding rs should be used in practice, where appropriate. With
λ = Bλ, (9.62) reduces to
Substituting (9.51), (9.55), and (9.60) into (9.44) we obtain
The heat gained or lost by the particle when qp
0 (9.44) causes Tp to change. The heating will thus
cause ΔT to change at a rate proportional the particle mass M and the specific heat at constant pressure cp
of the particle
Setting (9.64) equal to (9.65) we obtain
The RHS of (9.66) implicitly depends on ΔT both through Δρv (9.52) and through qr (9.60). To solve (9.66) analytically, we introduce the approximation for Δρv (9.52) into (9.66)For dry particles, which cannot participate in latent heating, all factors containing l are zero and we obtain the much simpler relation
The two terms on the RHS represent sensible and radiative heat transfer, respectively.For the time being we shall neglect the dependence of qr on ΔT and treat (9.67) as a linear, first order differential equation for ΔT
The A term and the B term are independent, but B - A is positive when the particle is losing mass, and negative when the particle is gaining mass.The solution to (9.70) may be obtained by multiplying each side by the integrating factor eAt. Then the LHS side becomes is the perfect differential of eAtΔT and the RHS may be integrated by standard techniques. The constant of integration is identified by imposing the temperature gradient initial condition ΔT(t = 0) = T∞ - Tp(t = 0) ≡ Δ0T . The result is
It is instructive to examine the limiting cases of (9.70). As t →∞, ΔT → B∕A. Thus the particle asymptotes to a steady state temperature difference with the environment given by B∕A.Inserting (9.70) into (9.70) yields
The relaxation (e-folding) time for the particle-environment heating gradient to reach steady state in this (simplified) scenario is τh = A-1.
τh is also called the adaptation timescale. In the absence of latent heating processes, ΔT and τh depend only on conduction and radiant heating. Thus the heating balance for dry particles (9.72) reduces to
Mineral dust aerosol affects atmospheric chemistry through both heterogeneous and photochemical processes. Heterogeneous chemistry includes reactions occurring on the surface of mineral aerosol. Mineral dust affects atmospheric photochemistry by scattering and absorbing sunlight and thus altering the actinic flux field. Through these mechanisms, mineral dust may significantly alter tropospheric concentrations of S(IV), NOy, O3, and OH.
Brimblecombe (1996) is a good introductory treatment of air composition and chemistry. Calvert et al. (1985) examined mechanisms of HNO3 and H2O2 formation in the troposphere. Chameides and Davis (1982) examined the effect of free radicals on the composition of cloud water and rain. Chameides and Stelson (1992) showed that the atmospheric cycles of sulfur and sea salt aerosol are coupled. Graedel et al. (1986) showed that transition metals can alter cloud droplet chemical compositions. Graedel and Goldberg (1983) present a detailed model or raindrop chemistry. Hedin and Likens (1996) discussed the role of atmospheric dust in the acid rain problem. The absorption cross sections and quantum yields of the most important photochemical paths in atmospheric chemistry are summarized every few years in DeMore et al. (1997). Klippel and Warneck (1980) discuss the formaldehyde content of atmospheric aerosol. Leighton et al. (1996) develop and validate a three dimensional cloud chemistry model. Chemistry in a rainband has been simulated by Barth et al. (1992); Barth (1994); Leighton et al. (1990) Pandis et al. (1995) present a thorough overview of the dynamics of tropospheric aerosols. Pilinis and Li (1998) discuss the effects of particle shape and internal inhomogeneity on radiative forcing. Solomon et al. (1996) examined the role of natural aerosol variations in anthropogenic ozone depletion. Müller and Brasseur (1995) describe the development and validation of the global chemical transport model IMAGES. Brasseur et al. (1998) describe the development and validation of the global chemical transport model MOZART. Column, in situ, and episodic aerosol radiative forcing has been studied by many authors (e.g., Jayaraman et al., 1998; Liao and Seinfeld, 1998b; Pan et al., 1998; Stenchikov et al., 1998). Aerosol forcing of climate has been studied by many authors (e.g., Kiehl and Briegleb, 1993; Koloutsou-Vakakis and Rood, 1998; Tegen et al., 1996; Miller and Tegen, 1998a,b; Shay-El et al., 1998; Alpert et al., 1998; Boucher, 1995; Charlson and Wigley, 1994; dAlmeida et al., 1991; Haywood and Ramaswamy, 1998; Liao and Seinfeld, 1998a; Schult et al., 1997; Tegen et al., 1997; Wong et al., 1998). Global sulfur aerosol distributions have been studied by many authors (e.g., Rasch et al., 2000; Barth et al., 2000; dAlmeida et al., 1991; Tegen et al., 1997).
The oxidation state of an atom measures its valence, and thus its reactivity, in a substance. The oxidation state of an atom in a pure element is zero (e.g., Ar). An ion is a compound whose net charge is not zero. In a monatomic ion the charge and the oxidation state are the same For example, both the oxidation state and charge of H+ are +1. For homonuclear compounds formed by covalent bonds (e.g., N2, O2), the electrons are split evenly between the atoms. For heteronuclear compounds formed by covalent bonds, the electrons are captured by the elements with the stronger attraction. For example, oxygen has a greater attraction for electrons than hydrogen, and strips the electrons from the hydrogen. In H2O therefore, the oxidation state of hydrogen is +1 and that of the oxygen is -2 (each hydrogen lost its electron to the oxygen). In non-metallic covalent compounds, hydrogen always loses its electrons to other atoms and is assigned an oxidation state of +1.
Oxygen is nearly always assigned an oxidation state of -2 in covalent compounds, e.g., SO2, NO2, CO2. One exception is for peroxides, e.g., H2O2, where oxygen has an oxidation state of -1. The total number of electrons is conserved so that, for an electrically neutral structure, the sum of the oxidation states equals zero. For example, HNO3 has oxidation states of hydrogen, nitrogen, and oxygen of +1, +5, and -2, respectively. The sum of the oxidation states is 1 × (1) + 1 × (5) + 3 × (-2) = 0. For an ion, the sum of the oxidation states equals the total charge of the ion. For example, the sulfate ion SO2- 4 has oxidation states of sulfur and oxygen of +6 and -2, respectively. The sum of the oxidation states is 1 × (+6) + 4 × (-2) = -2.
In the atmospheric literature, oxidation states are usually expressed as Roman numerals. Thus the oxidation states of sulfur and oxygen in SO2- 4 are written as +VI and -II, respectively. Often, the oxidation state of a compound determines its reactivity, and thus is a good predictor of its atmospheric residence time. For example, most anthropogenic sulfur is emitted to the atmosphere as SO2, which is an S(IV) compound. Through various oxidation reactions, S(IV) is usually transformed transformed to S(VI), which is highly stable. For sulfur, the solubility of the compound increases with oxidation, so that S(VI) compounds are highly soluble. As a result, much of the S(VI) in the atmosphere is in the form of particles or droplets and its residence time is determined by dry and wet deposition processes.
Table 10.1 lists the members of important families of atmospheric chemicals.
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Table 10.2 lists the oxidation states of important atmospheric sulfur compounds.
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Table 10.3 lists the oxidation states of important atmospheric nitrogen compounds.
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Ozone is a very important molecule.

The Chapman mechanism is a useful too for demonstrating many of the concepts of atmospheric chemical cycles, including photochemistry, second-order reactions, rate limiting steps, diurnal cycles, and chemical families.
By the 1960s it became clear that the Chapman mechanism alone overpredicts the abundance of ozone in the stratosphere. Additional ozone destruction mechanisms are necessary to bring observations into agreement with the predictions of (R1)-(R4). In the 1970s a number of catalytic mechanisms for ozone destruction were proposed

The anthropogenic contribution to the total sulfur burden of the atmosphere is greater than XXX%. Sulfur is important because . . . .
Benkovitz et al. (1996) provides a global data of sulfur emissions.
Gas phase oxidation of SO2 occurs in the presence of the OH radical and water vapor

Approximately 80% of Earths atmosphere by weight is nitrogen in the form of N2. Nitrogen is crucial source of energy to the biosphere, but most organisms cannot utilize N2 directly. Instead, these biochemical processes require nitrogen that has been fixed, or converted to a chemically useful state. The next most abundant compounds of nitrogen in the atmosphere are nitrous oxide (NO2) and ammonia (NH3).
Benkovitz et al. (1996) provides a global data of nitrogen emissions.
In the troposphere, the photochemistry of nitrogen oxides provides the main source of atomic oxygen. Since atomic oxygen is the rate limiting constituent in ozone formation, nitrogen photochemistry is crucial to determining ozone levels in the troposphere.
Reactions on aerosol surfaces were recognized as fundamental to the Earth system only in the recent past. The annual springtime catalytic destruction of Antarctic stratospheric ozone, i.e., the ozone hole, was attributed to surface heterogeneous chemistry only in 1986 (Solomon et al., 1986; McElroy et al., 1986). Since then, a multitude of studies have examined the role of surface heterogeneous chemistry on volcanic aerosols, polar stratospheric clouds (PSCs), and cirrus clouds.
Heterogeneous chemistry requires additional parameters not necessary in pure gas phase chemistry. The most significant single parameter required, of course, is knowledge of the abundances of species on the surface. For concreteness, we shall assume that the solid surface facilitating reactions is an aerosol, such as mineral dust. Such surfaces are often composed of reactive compounds. For example, mineral dust particles are approximately five percent calcium carbonate (CaCO3) by weight (Pye, 1987). Thus neutralizing reactions between the surface and acids adsorbed from the gas phase are possible.
The loss rate of an atmospheric species to an aerosol surface may be expressed as a pseudo first order reaction rate, K, which is a function of aerosol radius and ambient conditions. The gas-phase diffusion limited surface uptake rate k is
The total pseudo-first-order rate coefficient K is where K is in s-1 and k is in m3 s-1.
Chapman-Enskog theory Hirschfelder et al (1954)
This expression is very unwieldy. However, it contains useful insights into limiting cases for λAB. If the molecules are considered as hard spheres then the collision integral ΩAB(1,1) = 1 and (11.8) reduces to Taking the limits of (11.9) we find Thus for all cases of interest in the atmosphere, we may say that λAB is of order DAB∕
A. A number of
simple expressions for λAB in terms of DAB have been derived from the kinetic theory of gases. These
include the expression of Fuchs and Sutugin (1971, MFC) The expression used by Loyalka (1973) and an expression derived from applying the kinetic gas theory to Ficks First Law (11.35)
The four alternative definitions of λAB, (11.9), (11.11), (11.12), and (11.13), differ from one another by
constants of order unity. These definitions are employed to determine mass transfer coefficients in §11.4.4.
Which expression to use may be determined by which theory of mass transfer is employed. The ambiguity
in λAB reflects a corresponding ambiguity in DAB. Thus the validity of the expression chosen for λAB or
DAB may depend on the application.
Consider the binary diffusivity of a trace gas A in an atmosphere of gas B. For concreteness, imagine B is dry air. The diffusivities of the various species are computed as in Seinfeld and Pandis (1997).
Thus values for B in this procedure should be weighted averages of the properties of N2 and O2. When the diffusivity appears with only a single subscript, e.g., DA, it implies the diffusivity of A in air. The least well-known of the parameters required in (11.15)(11.16) is σA. Table 11.1 gives σ for some important atmospheric gases.