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DOE-STD-1128-98
Guide of Good Practices for Occupational Radiological Protection in Plutonium Facilities
determines that the waste will be a mixed waste. In these cases, minimizing the volume is
most important. For example, if a plutonium-contaminated surface has been painted with a
lead-based paint, the decontamination waste will be mixed waste unless it is further treated
to ensure that the lead is not in a leachable form. In this example, removing the paint by dry
ice blasting, high-pressure water blasting, heat, or a similar method would be preferable to
sand blasting in which the sand would be added to form an additional mixed waste that
could require storage for many years.
Laundry wastes are a special problem because radioactive contamination, body oils, and
odors must be removed from protective clothing. For a time, dry cleaning was extremely
popular, because the solvents were easily redistilled and recycled. However, because the
solvents were usually chloroflorocarbons and because the small volume of waste generated
was mixed waste, this method is now rarely used. Incineration of disposable protective
clothing is an outstanding choice if an incinerator of sufficient capacity is available, but this
is rarely the case. Water washing is often the method of choice. In a few cases, plutonium
in the waste stream is removed adequately by filtration and the effluent can be disposed to a
sanitary sewer or to the environment under a National Pollutant Discharge Elimination
System (NPDES) permit. It is important to select a detergent for water washing that does
not foul or plug the filter and that has a minimal impact on ion exchange resins if they must
be used. Many household laundry detergents have fillers such as wood fiber to give them
greater bulk. These should never be used because the fiber has no beneficial use and will
end up as solid waste. As a general rule, extensive testing on clean material should be done
to optimize disposal of laundry waste.
Floor-drain wastes are much more of a problem in some facilities than in others. In some
facilities, there is a culture that says, "if you don't know what to do with it, pour it down the
floor drain." Such practices can lead to a mixture of water, detergent, oil, antifreeze, and
other substances that clog filters and foul ion exchange resins. In the worst cases,
solidification with Portland cement is the only alternative, and this increases an already large
volume. The use of catch basins under chemical and lubricating systems and extensive
training of personnel minimize the probability of such occurrences. Oil skimmers on floor-
drain collection tanks are sometimes advisable, as well.
8.4.2 Operational Controls
Once the facility is properly designed, training of personnel is the primary operational
control against generating excessive volumes of waste or against generating waste with
contaminants that interfere with treatment or change the classification.
Some facilities have used color codes to prevent materials from entering an area where they
will adversely affect waste management. For example, certain electronic contact cleaners
8-15


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