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This paper examines the effect of pH on the solubility of hydrogen sulfide in water. It is shown that in acidic solutions (low pH), the solubility is only slightly different from pure water. In alkaline solutions (high pH), the solubility is dramatically increased.
The solubility of hydrogen sulfide in water is important in industrial practice, especially in these environmentally aware times. The fate of such an unfriendly component such as hydrogen sulfide is important to track. Hydrogen sulfide is highly toxic, has a noxious odor, and can form harmful reaction products (such as SOx).
Since aqueous hydrogen sulfide is acidic, the effect of pH is also very important. The purpose of this paper is to discuss this effect.
Several simplifying assumptions are made in the development presented in this paper. Therefore, the numerical results should be considered approximate.
The solubility of hydrogen sulfide in "pure" water at low pressure has been studied thoroughly and was recently reviewed by Carroll and Mather (1989) (also see Carroll, 1990).
At low pressure (less than 200 kPa or so), the solubility of the molecular H2S in water is given by the strict Henry's law (Carroll, 1991). Molality (moles of solute per kg of solvent) is a convenient unit for this analysis, and thus Henry's Law is given by:
mH2S H = yH2S P
where yH2S is the mole fraction of hydrogen sulfide in the vapor, P is the total pressure, mH2S is the molality of the molecular form of the hydrogen sulfide in the water (moles per kilogram of water), and H is the Henry's constant. The product of the vapor phase mole fraction and the total pressure gives the partial pressure of the given species.
Once dissolved in water, H2S is involved in a series of chemical reactions. The chemical reactions are: (1) the dissociation of the molecular H2S to form the bisulfide ion, (2) the dissociation of the bisulfide ion to the sulfide ion, and (3) the self ionization of water. The reactions are given below:
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Each of these reactions has an associated equilibrium relation, the so-called "mass action" relations. These are given below:
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In the final form of these equations (the expressions on the right), it has been assumed that the activity coefficients are unity. This may be a good assumption for dilute solutions, but it is not the case in general. One must resort to one of the ionic activity coefficient models to account for this effect. The assumption of unit activity coefficients will be used throughout this paper, even though it is known to be in error. It does not, however, detract from the general conclusions of this paper. For a detailed discussion of ionic activity coefficients, the reader is referred to the monograph by Zematis et al. (1986).
In addition the equilibrium constants for these three reactions have been studied over a wide range of temperature. The K's, as a function of the temperature, are available in the literature (see Roberts and Tremaine, 1985, for example).
We are usually interested in the total hydrogen sulfide in the aqueous solution. To obtain this value, we merely sum the concentrations of the various sulfide species:
tH2S = mH2S + mHS- + mS=
Another relation required is that of electroneutrality. The solution cannot have a net charge. Mathematically, this is given by:
mH+ = mHS- + 2 mS= + mOH-
When dealing with an acid or a base, the additional ions must also be accounted for in this relation. For example, in a sodium hydroxide solution, the sodium ion must be included in the left hand side of this equation. And in hydrochloric acid, the chloride ion must be included in the right hand side.
Finally, we require the definition of the pH:
pH = -log(aH+) ~ -log(mH+)
These are the common logarithms (base 10). Again, the activity coefficient is usually neglected.
At first, it seems to be a logical assumption that the presence of an acid would drive the hydrogen sulfide out of solution. However, experimental evidence (and a thorough analysis) demonstrates that this is not the case.
Measurements by Kendall and Andrews (1921) and others (and analyzed by Carroll, 1991) show that the presence of hydrochloric acid can be modeled in a fashion similar to the effect of a neutral ionic solute (such as sodium chloride). It is an interesting observation that the measured solubility, as a function of HCl concentration, exhibits a maximum. At low acid concentrations, the HCl salts-out the hydrogen sulfide (i.e., reduces the solubility). As the acid concentration increases, the solubility increases and if the HCl concentration is large enough the solubility is actually greater than in pure water. However, for the purposes of this discussion, we can neglect any "salt" effects.
Furthermore, Douabul and Riley (1979) found that the solubility of H2S in 5 molar sulfuric acid was essentially the same as in "pure" water.
What dictates the amount of the molecular form of hydrogen sulfide in the aqueous solution is its partial pressure. The ionization reactions are shifted to the left, but this has little effect on the amount of molecular hydrogen sulfide. Since these reactions do not proceed very far to begin with, then this should have a small effect on the total solubility. Thus to a reasonable approximation, the solubility of H2S in an acidic solution is equal to that in pure water.
It is also worth noting that different acids will have different salting-in effects. Thus it is a bit of a misnomer to talk about the solubility of H2S at low pH without discussing which acid is present.
The treatment for the solubility in strong bases is the same as that in acids, but the effect is dramatically different. As with the case of strong acids, the amount of the molecular species is dictated by the partial pressure. However, in this case the reactions are shifted to the right producing more of the ionic sulfide species and thus dramatically increasing the total hydrogen sulfide concentration, tH2S (per the equation given earlier).
Just as with the acid, there is a salting-out effect due to the presence of the ionic species. Different bases will have different salting-out effects. Thus it is insufficient just to discuss the solubility as a function of pH without further including the effect of the particular base under investigation.
We will only consider the case of 25ĒC and a total pressure of 101.325 kPa (1 atm). At these conditions the partial pressure of H2S is 98.15 kPa and we have the following:
H = 991 kPa/molal
K1 = 1.039 E-07
K2 = 6.43 E-16
Kw = 1.019 E-14
The equilibrium constants were taken from Roberts and Tremaine (1985) and the Henry's constant is from Carroll (1990).
First, solving Henry's Law for the concentration of the molecular species gives:
mH2S = 0.099 molal
And from the expressions for the chemical equilibrium, we obtain the following:
mHS-= 1.01 E-04 molal
mS= = 6.4 E-16 molal
mH+ = 1.01 E-04 molal
mOH- = 1.01 E-10 molal
Therefore, in pure water, the hydrogen sulfide solution has a pH of about 4. It is worth repeating that this pH arises without the addition of any acid or base.
Fig. 1 shows the effect of pH on the solubility of hydrogen sulfide. Note, the concentration of the S= ion is not plotted because in every case it would be off scale (i.e., less than 1E-8 molal). In addition, the plot only goes to a pH of 8 because beyond this point the concentration of the ionic species become so large that neglecting the activity coefficients results in significant error. Even at a concentration of 1 molal, the activity coefficients have a very large effect.
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Fig. 1 The Approximate Solubility of Hydrogen Sulfide as a Function of the pH
The model predicts that the molecular form of the hydrogen sulfide has a concentration independent of the pH. This was an assumption that was built into the model. As discussed earlier, a salt effect would have to be included to accurately predict the solubility of the molecular H2S.
At low pH (acidic solutions), the predominant form of the sulfide species is the molecular H2S. This continues to be the case until a pH of about 6 when significant amounts of the bisulfide ion are present. Further increases in the pH results in the formation of more bisulfide. By a pH of slightly less than 7, there are equal amounts of the molecular and bisulfide forms.
At a pH of 8, the concentration of the bisulfide ion is about ten times that of the molecular H2S. The bisulfide ion is the dominant hydrogen sulfide species for pH greater than this value.
The behavior of the solubility of carbon dioxide is very similar to that of hydrogen sulfide in many respects. Carbon dioxide also forms a weak diprotic acid when dissolved in water. And at low pressure the solubility can be estimated using the strict Henry's law. Thus many of the observations about H2S can be directly translated to the behavior of CO2. Of course the numerical results will be different for the two gases, but the qualitative phenomena are the same.
Aqueous solutions of alkanolamines are commonly used in industrial practice to remove hydrgen sulfide and carbon dioxide from gas streams. Commonly employed amines include monoethanolamine (MEA), diethanolaime (DEA), and methyldiethanolamine (MDEA).
These compounds are effective as solvents because they form weak bases when dissolved in water, similar to ammonia. As was just demonstrated, the solubility of hydrogen sulfide increases dramtically in a solution with a high pH. However, the reaction with a weak base can be reversed with a reduction in pressure and by the application of heat. Thus the solvent can be regenerated. With a strong base, such a sodium hydroxide, the reaction is irreversible.
Details of the alkanolamine process can be found in Kohl and Nielsen (1997)
It was the purpose of this paper to briefly discuss the effect of pH on the solubility of hydrogen sulfide and to provide the tools for a more detailed analysis.
It was shown in this work that for low pH (acidic solutions), the presence of the acid has only a small effect on the solubility. This effect is essentially a "salt" effect, similar to that observed for a neutral salt such as sodium chloride.
On the other hand, as expected, the presence of a base (an alkali) greatly increases the solubility because of the formation of ionic species (notably the bisulfide ion).
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Carroll, Alberta, CANADA.