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National Priorities List (NPL) sites and 26 of the 38 NRC Site Decommissioning Site Plan<br />

(SDMP) sites.<br />

5.11.3 Aqueous Speciation<br />

Because of its importance in nuclear chemistry and technology, a great deal is known about the<br />

aqueous chemistry of uranium [reviewed by Baes and Mesmer (1976), Langmuir (1978), and<br />

Wanner and Forest (1992)]. Uranium can exist in the +3, +4, +5, and +6, oxidation states in<br />

aqueous environments. Dissolved U(III) easily oxidizes to U(IV) under most reducing conditions<br />

+ 1<br />

) readily disproportionates to U(IV) and U(VI).<br />

found in nature. The U(V) aqueous species (UO 2<br />

Consequently, U(IV) and U(VI) are the most common oxidation states of uranium in nature.<br />

Uranium will exist in the +6 and +4 oxidation states, respectively, in oxidizing and more reducing<br />

environments.<br />

2+ 4+ 4+<br />

Both uranium species, UO2 and U , hydrolyze readily. The U ion is more readily hydrolyzed<br />

2+<br />

than UO2 , as would be expected from its higher ionic charge. Langmuir (1978) calculated U(IV)<br />

speciation in a system containing typical natural water concentrations of chloride (10 mg/l),<br />

2+<br />

fluoride (0.2 mg/l), phosphate (0.1 mg/l), and sulfate (100 mg/l). Below pH 3, UF2 was the<br />

dominant uranium species. The speciation of dissolved U(IV) at pH values greater than 3 is<br />

+ N<br />

dominated by hydrolytic species such as U(OH) 3 and U(OH)4(aq).<br />

Complexes with chloride,<br />

fluoride, phosphate, and sulfate were not important above pH 3. The total U(IV) concentration in<br />

solution is generally quite low, between 3 and 30 µg/l, because of the low solubility of U(IV) solid<br />

phases (Bruno et al., 1988; Bruno et al., 1991). Precipitation is discussed further in the next<br />

section.<br />

Dissolved U(VI) hydrolyses to form a number of aqueous complexes. The distribution of U(VI)<br />

species is presented in Figures 5.6a-b and 5.7. The distribution of uranyl hydrolytic species<br />

(Figures 5.6a-b) was calculated as a function of pH using the M<strong>IN</strong>TEQA2 code. The U(VI)<br />

aqueous species included in the speciation calculations are listed in Table 5.16. The<br />

thermodynamic data for these aqueous species were taken primarily from Wanner and Forest<br />

(1992). Because dissolved uranyl ions can be present as polynuclear 2 hydroxyl complexes, the<br />

hydrolysis of uranyl ions under oxic conditions is therefore dependent on the concentration of<br />

total dissolved uranium. To demonstrate this aspect of uranium chemistry, 2 concentrations of<br />

total dissolved uranium, 0.1 and 1,000 µg/l, were used in these calculations. Hem (1985, p. 148)<br />

1 Disproportionation is defined in the glossary at the end of this letter report. This particular<br />

disproportionation reaction can be described as:<br />

+<br />

2UO2 + 4H3O + 2+ 4+<br />

= UO2 + U .<br />

2 -<br />

A polynuclear species contains more than 1 central cation moiety, e.g., (UO2) 2CO3(OH) 3 and<br />

4+ Pb4(OH) 4 .<br />

5.67

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