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5h C.J. ~V()()O<br />

that solutions containing oxalic acid under some conditions induce fntergranular attack on<br />

sensitized type 304 stainless steel. A cautious period followed, when sufficient corrosion<br />

evaluation was conducted to understand and avoid conditions which could potentially cause a<br />

problem. The LOHI process, which does not contain oxalic acid, was first used on a BWR in<br />

1984, and was selected by most BWR utilities carrying out decontaminations from 1985 on,<br />

Including Monticello and Quad Cities BWRs in 1989. Aside from the encouraging corrosion<br />

data, LOHI offered at least comparable DFs and required short application times. CITROX<br />

has continued to be used at the Brunswick BWR. Meanwhile a new process, CANDEREH, which<br />

does not contain oxalic acid, was developed from CAN-DECON, and is now available and was<br />

recently used on a heat exchanger at Indian Point 2 PWR and on the steam generator channel<br />

heads at Beaver Valley I PWR. CANDEREM and LOMI are given equal prominence at this time in<br />

the development of corrosion data necessary for full system decontamination in PWRs.<br />

2. TECHNICAL BACKGROUND<br />

2.1 Concentrated reagents<br />

The 1984 de contamlnatlon of the complete primary system (with the fuel removed) of the<br />

Dresden-I BWR, using the NS-I process, was the only recent U.S. application of concentrated<br />

chemical reagents. This decontamination was unusual in several respects. Dresden-l, an<br />

early BWR, was shutdown in 1978 and Is unlikely to operate again. The decontamination was<br />

originally scheduled for 1980, but environmental impact and safety issues were mainly<br />

responsible for a delay of four years.<br />

Decontamination factors exceeded 11.3, and over 750 curies of activity was removed. The<br />

total activity removed was extremely close to the 1979 calculation of total activity in the<br />

system, when decay was taken Into account. The use of an organic inhibitor to control<br />

corrosion in concentrated reagents tended to slow down the cleanup process, and the return<br />

of the total organic carbon to reactor water speclffcatlon took considerable tlme.<br />

The detailed report of this project (9) reveals both the strengths and the problems of<br />

concentrated (or "hard") decontamlnatlon--processes. High removal of activity was achieved,<br />

but waste disposal was a major difficulty, and concern about corrosion effects necessitated<br />

a large and expensive materials qualification program. Recently-developed dilute<br />

decontamination reagents ("soft" processes) achieve as much activity removal, with greatly<br />

reduced concerns about corrosion damage and waste disposal. With the current Industry<br />

emphasls on avoiding corrosion and reducing radwaste volumes, it seems unlikely that<br />

concentrated processes will be used on operating plants again, although localized<br />

applications on components such as pumps will continue. This review focuses on system and<br />

subsystem decontamination dilute chemical processes.<br />

2.2 Dilut e reasents - BWR<br />

There are two types of dilute chemical reagents. In the early '80's, the organic acld<br />

reagents based on citric and oxalic acids (e.g., CITROX), using a chelating agent such as<br />

EDTA to retain dissolved corrosion products In solution (e.g., CAN-DECON), were used for<br />

the majority of plant applications. Since 1985, however, the low oxldatlon-state metal ion<br />

(LOMI) process has been the most widely used process In the United States. Table 2-I lists<br />

primary coolant system decontamlnatlons (IO).<br />

The organic acid reagents dissolve oxides by simple acidic dissolution<br />

8H + + Fe304 ~ Fe 2+ + 2Fe 3+ + 4H20 (I)<br />

acid oxide metal ions<br />

in solution<br />

and reductlve dissolution:<br />

8H + + 2e- + Fe304 ÷ 3Fe 2+ + 4H20 (Most likely the major<br />

pathway for oxide<br />

acld reducing oxide metal ions destabillzatlon)<br />

agent in solution<br />

The radioactive Impurities, such as Co-60, Co-58, Fe-59, Mn-54, are released at the same<br />

time. A corrosion inhfbltor may be necessary for some applications, depending on the<br />

materials In the system, the process temperature, duration, and reagent strength. Because<br />

3+<br />

Fe solubility is small, a chelating agent needs to be present at the site of dissolution<br />

in order to retain the iron in solution.<br />

(2)

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