Evaluator
A. Vesala Department of Chemistry and Biochemistry, University of TurkuEvaluation
The work of Weil, Dure, and Quentin (1) discusses the determination of extremely small solubilities. Their saturation process was carried out by a chromatographic technique to avoid contamination on glass surfaces and formation of possible colloidal aggregates of the solute. In their procedure, Mg silica gel, overcoated with the solute, was eluted with water. However, the analytical procedure was not reported, a factor which makes it difficult to estimate the precision of the measured values. It is known that certain problems and complications arise in the course of the determination of solubilities of this magnitude. First of all, the effects of a third component (glass or silica gel) may be significant. Also, the purity of the solvent (water) can exert a dominant influence on results in cases of highly diluted, saturated systems. In addition to distillation and deionization, the solvent should also be degassed, a procedure not done for the reported measurements. For such reasons, the values of Weil et al. may involve large absolute errors.
Hollifield (2) applied a nephelometric procedure for the estimation of the solubility of hexachlorobenzene in water. His analytical method involved the preparation of a standard curve by successive dilution of an acetone solution of the test substance with water. The turbidities of the solutions were measured nephelometrically. Extrapolation of this curve to an intensity of the reagent blank gave an estimate of the solubility in water. The solubility value reported for 297 ±2 K was 110 μg (l)/kg. The method evidently gives rough estimates of the solubilities and it has the advantage of being rapid. The lack of precision in the procedure can be appreciated from a review of the reported solubility data which show deviations of several orders of magnitude from reported literature values. Consequently, these solubility values are not considered further in this evaluation.
Sharov (3) has reported the solubility of hexachlorobenzene in water at higher temperatures. Two variables (temperature and pressure) make a comparison with other solubility data difficult. Only the value referred to 353 K was probably measured at normal pressure. Even so, its value of 10 mg (l)/kg (2) cannot be used to support the solubility value of Weil et al.
The following solubility value for hexachloride in water is based upon the value reported by Weil et al. However, for the reasons stated, the value should be considered.
None
| C $T$ ($\pu{K}$) | D $x_{1}$ | D MR1 (g/kg) | D $C_{1}$ (mol/dm3) |
|---|---|---|---|
| 298.15 | 3.2 x 10-10 | 5.0 x 10-6 | 1.8 x 10-8 |
Sources:
3
Sharov, V.; G. B. Sb. Dostizheniy Nauk-Neftekhim-Vam. 1975, 138-41.
1
Weil, L.; Dure, G.; Quentin, K. E.; Wasser Abwasser Forsch. 1974, 7, 169-75
2
Hollifield, H. C.; Bull. Environ. Contam. Toxicol. 1979, 23(4/5) 579-86.