L - KTH
L - KTH
L - KTH
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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)