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40 C, J. WOOD<br />

not removed, these residues seem to contribute to rapid recontamlnatlon on return to<br />

service. Several alternatives to permanganate are under development, including ozone,<br />

parmanganlc acid, as in the KWU CORD process, potassium ferrate, and chromous LOMI<br />

reagents. None of these reagents have been plant tested in the USA as yet, but some appear<br />

to offer significant potential advantages compared to permanganate.<br />

3. LWR DECONTAMINATION APPLICATION TECHNIQUES<br />

3.1 BWR reactor water recelculation system (RWR) applications<br />

The majority of RWR systems In U.S. BWRs consist of two piping loops, each containing a<br />

high flow centrifugal pump complete wlth suction and discharge isolation valves and<br />

interconnecting piping. The piping on the suction side of the pump runs vertically from<br />

the reactor vessel near the bottom of the annulus. On the discharge slde, the piping<br />

connects to a header above the pump from which five discharge risers extend vertically<br />

upward to where they penetrate the reactor vessel and rise approximately another ten<br />

feet. Once inside the vessel their designation changes and they are called Jet pump risers<br />

and are considered part of the Jet pump assembly rather than the RWR system. Despite the<br />

designation change, each riser is a continuous pipe which is used to contain<br />

decontamination fluid during the application.<br />

Some RWR systems contain a cross-tie line which interconnects the two loops at the<br />

discharge headers. This llne normally contains two isolation valves.<br />

Two different techniques have been employed to decontaminate this system--one and two<br />

phase applications. Due to the design of the RWR system it is not possible for the reagent<br />

to wet all of its various parts in a single step and maintain circulation (as opposed to<br />

fill, soak, drain techniques), unless some form of modification is performed. Thus, single<br />

phase applications are normally performed at plants that are planning a piping replacement<br />

and are prepared to modify the system in order to improve reagent access. Two phase<br />

applications are normally performed on an unmodified RWR system. These techniques are<br />

described in more detail in Sections 3.1.1 and 3.1.2.<br />

The decontamination equipment is common to both types of applications. In each case,<br />

the temporary equipment used has performed all of the process functions required to<br />

complete the decontamination. This consists of circulating and heating up the fluid,<br />

injecting chemicals, reversing flow directions, sampling, monitoring process parameters,<br />

controlling fluid levels and removing the dissolved activity and chemicals on Ion exchange<br />

resins. Only minor variations In the equipment have been required to accommodate the<br />

differences from one chemical decontamination process to another.<br />

Flexible, high pressure, reinforced rubber hoses are used to connect the equipment to<br />

the system or component to be decontaminated. Occasionally the entire system has been<br />

hard-plped, but experience with the rubber hoses has been excellent, and this is now the<br />

preferred option. Hoses typically in the range of 2" to 4" diameter are typically used.<br />

3.1.1 Two Phase RWR Decontaminations. This is the most common approach to RWR<br />

decontamination. It is most effective when extensive inspection or maintenance work,<br />

rather than modifications, are scheduled for the system. The decontamination is performed<br />

In two phases, a discharge side phase and a suction side phase. It can be used whether or<br />

not the RWR system contains a cross-tle llne connecting the discharge headers of each loop,<br />

and whether or not the lower portion of the annulus is to be included in the flowpath.<br />

As shown in Fig. 2, the temporary decontamination equipment is connected to the RWR<br />

system at the suction of each RWR pump. Flanged connections are available for Just such<br />

work on virtually all U.S. BWRs. The equipment is normally located Just outside the<br />

drywell in the vicinity of the equipment access hatch. It is placed and shielded to<br />

minimize radiation exposure to both contractor and plant staff during the application.<br />

To commence the discharge side decontamination, the pump isolation valves on the suction<br />

side are closed, those on the discharge side and on the cross-tie header are opened, and<br />

the discharge piping is filled to a predetermined level of fluid (Just about half way up<br />

each of the ten discharge risers). Flow is established through the discharge half of the<br />

system from the temporary equipment into one loop via the decon flange, through the RWR<br />

pump bowl, and up the discharge piping into the header. The fluid passes into the second<br />

loop via the cross-tie llne and back down the discharge piping, through the pump and back<br />

to the temporary equipment. By adjusting the valve lineup on the decon equipment the<br />

direction of flow can be reversed through the discharge loops.

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