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

to support 10 CFR 61 (NRC 1992) radioactive waste disposal regulations. The<br />

WRAP 2A performance specification of a minimum leach index of 6.0 for all<br />

waste forms is the same as the NRC requirements.<br />

Leachate characteristics will also be analyzed and compared with the<br />

design basis for performance modeling-of the mixed waste disposal facility to<br />

ensure that the performance of the liner leachate collection system will not<br />

be compromised. Leachate aggressiveness shall be less than that used for<br />

EPA 9090 performance testing of the W-025 disposal trench liner system.<br />

2.3.3 Biodegradation<br />

The long-term durability of waste forms can be adversely affected if they<br />

are susceptible to microbial degradation. Therefore, the waste form specimens<br />

are tested for resistance to fungal growth ( ASTM G21)-and bacterial growth<br />

(ASTM G22). -The-'tests provide ideal conditions for microbial growth, such as<br />

proper moisture, temperature, and nutrients. After 21 days of incubation, the<br />

specimen is inspected for growth and tested for compressive strength. The<br />

.., WRAP 2A performance specification is for ng observable microbial growth and a<br />

minimum-compressive strength of 5J00 ibf/in following the test.<br />

2.3.4 Thermal Cycling<br />

Thermal cycle testing is used to determine the durability of the waste<br />

form when exposed to extremes of temperature that may be experienced during<br />

storage, transportation, or disposal. The standard method for thermal cycling<br />

is ASTM B-553, which involves exposing the test specimen to temperature<br />

extremes of -40 °C to +60 °C (-40 OF to 140 °F) for a total of 30 five-hour<br />

periods. After cyiling, the compressive strength must continue to meet the<br />

minimum 500 lbf/in performance specification requirement.<br />

2.3.5 Radiation Stability<br />

Exposure of waste matrices to radiation can cause chemical changes in the<br />

molecuiar structure, such as-radiolysis or crosslinking, which can in turn<br />

affect the physical properties of the material. Therefore, 10 CFR 61<br />

(NRC 1992) regulations-require that the waste form be tested to determine the<br />

effects that long-term exposure to radiation may have on the Vaste form. The<br />

t!RAP 2A-perfor„^aner syeci^icati-n cr is for<br />

strength after exposure to a total gamma<br />

NRC regulations.<br />

a minimum *06 ibfjin` compressive<br />

dose of 10 radiation, as required by<br />

2.3.6 Water Immersion<br />

Waste forms in the shallow land disposal environment will inevitably be<br />

exposed to moisture. Depending on the type of waste and the immobilization<br />

matrix, exposure to moisture can cause swelling, cracking, and other adverse<br />

__--_---changes in__tha -waste formr- To e.n.sure adequ ate performance under these<br />

conditions, the waste form specimens are immersed in water for 90 days, after<br />

2-4<br />

x<br />

^

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