Geochemistry. William M. White

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is useful only for very dilute solutions, less than 10−5 mol/kg, which is more dilute than essentially all solutions of geologic interest. We will consider several methods of estimating activities in higher ionic strength solutions in Chapter 4.

Schematic illustration of the ionic strength of natural electrolyte solutions and the applicability of the Debye–Hückel and Davies equations.

      Given the composition for the average river water in column A in the table below, calculate the activity of the Ca2+ ion at 25° C using the Debye–Hückel equation.

      Answer: Our first step is to convert these concentrations to molality by dividing by the respective molecular weights. We obtain the molal concentrations in column B. We also need to compute z2 (column C), and the product z2m (column D). Using equation 3.75, we calculate the ionic strength to be 0.00202 m. (Note, one must use the ionic strength in molal or molar, and not millimolar, units in the Debye–Hückel Equation.

A B C D
Ion g/kg mol/kg × 103 z2 mz2 × 103
Cl 0.0078 0.2201 1 0.2201
images 0.0112 0.1167 4 0.4667
HCO images 0.0583 0.9557 1 0.9557
Mg 2+ 0.0041 0.1687 4 0.6746
Ca 2+ 0.015 0.3742 4 1.4970
K + 0.0023 0.0588 1 0.0588
Na+ 0.0041 0.1782 1 0.1782

      We substitute this value for I, then find å = 6, A = 0.5092, and B = 0.3283 in Table 3.1, and obtain a value for the activity coefficient of 0.8237, and an activity of 0.308 ×10−3 m. If we did the calculation for other temperatures, we would see that for a dilute solution such as this, the activity coefficient is only a weak function of temperature, decreasing to 0.625 at 300° C.

      Solid solutions differ from those of gases and liquids in several respects. First, solution in the solid state inevitably involves substitution. While we can increase the concentration of HCl in water simply by adding HCl gas, we can only increase the concentration of Fe in biotite solid solution if we simultaneously remove Mg. Second, solid solutions involve substitution at crystallographically distinct sites. Thus, in biotite a solid solution between phlogopite (KMg3AlSi3O10(OH)2) and annite (KFe3AlSi3O10(OH)2) occurs as Fe2+ replaces Mg2+ in the octahedral site; the tetrahedral Si site and the anion (O) sites remain unaffected by this substitution. Third, substitution is often coupled. For example, the solid solution between anorthite (CaAl2Si2O8) and albite (NaAlSi3O8) in plagioclase feldspar involves not only the substitution of Na+ for Ca2+, but also the substitution of Al3+ for Si4+. The anorthite–albite solution problem is clearly simplified if we choose anorthite and albite as our components rather than Na+, Ca2+, Al3+ and Si4+. Such components are known as phase components. Choosing pure phase end members as components is not always satisfactory either because substitution on more than one site is possible, leading to an unreasonably large number of components, or because the pure phase does not exist and hence its thermodynamic properties cannot be measured.

      However we choose our components, we need a method of calculating activities that takes account of the ordered nature of the crystalline state. Here we will discuss two ideal solution models of crystalline solids. We tackle the problem of nonideal solid solutions in Chapter 4.

      3.8.1 Mixing-on-site model

      Many crystalline solids can be successfully treated as ideal solutions. Where this is possible, the thermodynamic treatment and assessment of equilibrium are greatly simplified. A simple and often successful model that assumes ideality but takes account of the ordered nature of the crystalline state is the mixing-on-site model, which considers the substitution of species in sites individually. In this model, the activity of an individual species is calculated as:

      (3.78)equation

      where X is the mole fraction of the ith atom and ν is the number of sites per formula unit on which mixing takes place. For example, ν

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