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WHC-SD-W100-TI-003 Rev. 0<br />

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Waste immobilization matrices fall into several general categories. Inorganic<br />

--- binders, thermoplastics, organic polymers, ceramics, and glasses are the<br />

matrices that have been widely used for radioactive waste immobilization.<br />

Inora anic Binders<br />

Inorganic binders are commonly used materials for waste stabilization and<br />

immobilization. They are inexpensive, readily available, and well established<br />

in the radioactive waste management field.<br />

Portland cement<br />

Portland cement is the most common immobilization matrix. It is the same<br />

material used in construction of concrete structures. Portland cement<br />

consists mostly of hydrated calcium silicates, with some aluminates and<br />

magnesium content. The calcium hydroxide content causes portland cement to<br />

exhibit a high pH. The three predominant types are described below.<br />

Type I (ordinary)<br />

Ordinary portland cement ( OPC) is widely used for construction purposes. It<br />

requires about one month to cure to full strength.<br />

Type II ( sulfate-resistant)<br />

Type II cement is resistant to sulfate ions. This gives increased durability<br />

in saline environments.<br />

Type III ( high-early-strength)<br />

Type III cement is ground more finely thus increasing its reactivity. High<br />

early strength creates higher curing exotherms.<br />

Pozzolanic cement additives<br />

Pozzolanic additives are used to modify the reactivity, curing time, and<br />

ultimate strength of cement grout. Two commonly used additives are ground<br />

blast furnace slag, and pulverized coal fly ash.<br />

Blast furnace slag<br />

Blast furnace slag his a higher silica content that cement. This decreases<br />

the reactivity and eliminates the high curing exotherm. It also increases the<br />

curing time required to attain full strength.<br />

Pulverized fly ash<br />

G-3

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