L - KTH
L - KTH
L - KTH
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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.