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K.27<br />

TABLE K.3.1. Predominant Solution Species <strong>of</strong> Elements Without Organic Ligands<br />

(Karn-Bransle-Sakerhet 1978)<br />

Little Affected by<br />

Elements Oxidation-Reduction In an Oxidizing Environment In a Reducing Environment<br />

Am Am 3 + , AmSo4 , 2 +<br />

Am(OH)<br />

Sb HSb02 0 , Sb(OH) 3 , SbOF 0 , SbO+<br />

Ce Ce 3+ +<br />

, CeSO4 Cs Cs +<br />

Co Co 2+ , Co(OH)2 +<br />

Cm Cm 3 + , CrmH 2 + , Cm(OH)2 +<br />

Sb(OH) 4<br />

Eu Eu 3+ , EuS04 + 2<br />

, Eu2 P20 7 +<br />

I I, 103- I<br />

Np Np02 + , Np02HP04-, NpOH 3 + 4 +<br />

, Np<br />

Pu<br />

NpO2HCO 3<br />

Pu02+<br />

Pm Pm 3 P 2<br />

Ra<br />

Ra 2+<br />

Ru Ru(OH)2 + , Ru04-, Ru04 2<br />

Sr<br />

Sr 2+<br />

2<br />

Pu0 2 +, PuO 2 (CO3 )(OH) 2 -, PuOH 2 +, Pu 3 +<br />

Tc TcO 4 - TcO 2<br />

Th ThF 3 + , Th(OH) 3 +<br />

3 H H + , 3 H-O-H<br />

SUO" , UO2F+, UO (OH2)o ,<br />

0 3 +<br />

Zr Zr(OH) 4 , Zr(OH)5, ZrF<br />

uo2(co 3 ) -<br />

Ru0 4<br />

2<br />

U02 (C0 3 )<br />

, UOH 3 + , U2<br />

Examples <strong>of</strong> inorganic sorption materials are given in Table K.3.3. Chabazite, erionite<br />

and clinoptilolite are zeolites that occur in large depos-its <strong>of</strong> sedimentary origin (Hay<br />

1966) and montmorillonite is the main clay mineral in bentonites. Thermal and hydrothermal<br />

stabilities generally are acceptable for the intended use. The thermal conductivities <strong>of</strong><br />

both clay minerals and zeolites are comparatively low. The zeolites are quite permeable to<br />

ground-water while sodium-based montmorillonites show low permeabilities (Jacobsson 1977).<br />

Pusch (1978) has suggested that varying amounts <strong>of</strong> quartz sand be added to bentonite<br />

and that it be compacted to improve its load-bearing and thermal conductive characteristics<br />

while retaining some <strong>of</strong> its cation exchange properties. Through the use <strong>of</strong> simple relation-<br />

ships between diffusion or solution flow-controlled migration and equilibrium distribution<br />

coefficients, Neretnieks (1977) determined the retention time in years in 1-m-10%<br />

bentonite/90% quartz and clinoptilolite sorption barriers as shown in Table K.3.4.<br />

The barrier depths (in meters) required to retard various radionuclides for 30 half-<br />

lives are shown in Table K.3.5. Clinoptilolite is a better sorption barrier, but it is more<br />

permeable and.has less bearing strength than the bentonite-quartz mixture. For use within<br />

the canister, the clay minerals and zeolites can be dehydrated at just below their stability<br />

temperatures.

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