﻿WEBVTT

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[This tape was transfered from a 16mm film original by Colorlab

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for the National Library of Medicine, April 2006,

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NLM call number HF 1245]

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[Music]

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[The U.S. Department of Health, Education, and Welfare, Public Health Service, Presents]

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[Radioactive Waste Disposal]

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[Produced by the Communicable Disease Center for National Institutes of Health, Plant Safety Branch]

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[Narrator:] As the use of radioactive materials increases,

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the problems associated with the disposal

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of the waste become ever more important.

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Of all known toxic materials,

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radioactive nuclides alone cannot be detoxified

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or rendered harmless by any known chemical or physical processing.

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Safe disposal of these materials requires that they be so segregated

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that any return to man is in such a low concentration

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as to be certainly harmless.

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All manner of possible return paths must be considered

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in choosing a processing and disposal method.

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Disposal by burial on land requires the utmost care

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to ensure that there is a negligible contact between

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the waste product and water sources

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through which the isotopes might return to man,

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either directly or through food chains.

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When intermediate products such as edible plants, animals,

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and fish are involved,

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the effects of biological concentrations of particular nuclides

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in these intermediates must be carefully appraised.

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[Intermediate Waste]

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The most common radioactive waste problems concern the relatively

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small user of isotopes obtained primarily from nuclear reactors.

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[High Level Waste]

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The high level waste originating from reactor operation itself,

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and the associated chemical processing,

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require special handling at the installations where the wastes originate.

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The National Institutes of Health is an organization

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devoted to research in clinical medicine

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and the associated basic sciences.

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Some 500 members of the scientific staff use about 100 curies

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of radioactive isotopes each year.

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Because of the biological emphasis of the research program,

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carbon-14 and hydrogen-3, or tritium,

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are the most commonly used nuclides.

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Waste disposal methods must take into account

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the particular properties of these isotopes.

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At the National Institutes of Health,

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the Radiation Safety Office is the organization

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responsible for all radiation safety operations.

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These operations include the processing

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and disposal of radioactive wastes.

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Safety office functions center around the isotope laboratory,

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located apart from other laboratories and service buildings.

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The disposal methods to be shown are the result

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of over ten years of development

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in cooperation with the United States Coast Guard.

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The deep sea was chosen as the most desirable ultimate depository.

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Burial at sea must be carried out so there will be no interference

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with either commercial or sport fishing.

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No significant concentrations of any isotope deposited must appear

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at the surface of the sea or on any beach.

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The waste disposal area, approximately 90 miles due east of Norfolk,

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is over 1,000 fathoms in depth.

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[Waste Disposal Area, Atlantic Ocean, 90 Miles, Depth Over 1,000 Fathoms]

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Radioactive waste processing and packaging is carried out

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in a restricted area near the isotope laboratory.

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This area is surrounded by a custodial fence to separate it

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from the activities and traffic of the Institutes.

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Radioactive wastes must be classified into several different types,

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and the disposal governed accordingly.

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Here a chemical experiment is originating wastes of varying levels of activity.

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Samples are being pipetted out for measuring preparatory to initiating the proper disposal procedures.

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These liquid wastes will be assorted

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depending upon the level of activity

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as measured with the portable survey meter.

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Carefully measured samples are placed in the counting

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planchets to obtain the standardized volume

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for checking with the scintillation counter.

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All of these manipulations take place inside a hood

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with absorbing paper underneath materials

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so that spills can be readily discarded.

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The waste of low activity will be disposed of directly

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into the regular sewer system,

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with water flushing the sample down the drain at the disposal time.

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This other waste, which was found to contain somewhat greater activity,

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will be put into a special sewer system.

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This leads to a large underground retention tank

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where the waste will be held for an appreciable length of time

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before being released to the municipal sewer system.

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Both of these wastes are short half-life,

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or else disposal by either of these means would not be allowable.

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Waste containing carbon-14 or tritium cannot be classified

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by the crude assay method previously shown.

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With these weak beta emitters, carefully prepared samples are counted in a liquid scintillator.

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The scintillating solution,

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and the photo multiplier tubes picking up the tiny flashes of light,

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are kept at a very low temperature

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in a deep freeze to reduce the effect of extraneous disturbances

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on the electric circuits.

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Carbon-14 and tritium wastes that are too concentrated

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for direct disposal will be kept for burial at sea.

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Each of these nuclides have a half-life that is too long

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for appreciable decay to occur during any practical storage period.

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Patient treatment areas generate large quantities

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of contaminated articles, with bed linens an outstanding example.

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Wherever possible, patients receiving radioisotopes

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handle their own urine collections in the treatment areas.

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Urines containing gamma emitters are kept

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in heavily shielded containers and are collected at frequent intervals.

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Another source of active waste material

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comes from animal experiments.

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This animal has been injected

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with a long-lived radioactive material.

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Note that the experimenters are wearing rubber gloves

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to avoid contamination of hands.

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Blood samples are withdrawn,

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placed into counting planchets

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for drying and subsequent assay.

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Marking tape is used

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whenever radioactive material is involved.

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It is most important that all packages be so marked,

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and an approximate value given of the amount

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of the isotope present, and the isotope identified.

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Animal carcasses are stored at low temperature

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until ready for disposal by approved methods.

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Since licenses for radioactive materials are given

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by possession limits,

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it is necessary to keep a careful account of the isotopes that are thrown away.

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Each package must be marked with the amount of the isotope which it contains.

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Throughout all waste disposal operations and processing,

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accurate records are kept of radiation exposure

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of all personnel involved.

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Film badge monitoring devices are loaded

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and prepared for issue throughout the institutes.

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A most important part of the monitoring consists of keeping records.

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Most of these records will be needed perhaps

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five to ten years after they have been entered,

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so neatness, accuracy and legibility

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are most important items in the record keeping.

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Records must be kept of all radioactive waste materials

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that are disposed of by whatever means.

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This represents about one-half of a day's collection

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from the laboratories and clinical areas at the Institutes.

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Delivery of radioactive materials to the radiation safety office

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is made so easy that there will be little or no temptation

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to dispose of these materials by other methods.

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Otherwise, these radioactive materials might be found in the regular trash containers,

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or dumped indiscriminately into the municipal sewer system.

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The polyethylene bags are the liners of the waste containers

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which are handed out to all users of active materials.

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Wastes are classified and records kept of each package,

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its location, and the method of final disposal.

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Here, materials of short half-life are being kept for decay

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and for later incineration.

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Materials which have too long a half-life to allow decay to take place

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will be put into children-sized concrete burial vaults

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for ultimate disposal at sea.

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Liquids, solids, and activities of many different levels

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are some of the diverse materials which are collected.

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Vaults are standard commercially available containers of convenient size.

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They are made of steel-reinforced concrete and have lifting eyes cast into the bottom.

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Short lengths of steel cable are attached to these eyes for handling.

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The vaults are packed as carefully as possible

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to include a maximum amount of material.

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This cuts down the number of containers required and aids

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in obtaining the density required to ensure sinking in the ocean.

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Special waste products require special methods of handling.

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Here are the steps that lead to the ultimate disposal of some cobalt pellets.

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They have already been packaged in lead and welded into a steel pipe.

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Spacing rings encircle the cobalt container so that the pipe

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will be centered into the steel disposal drum.

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The drum will then be filled with concrete.

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Although there is some gamma ray activity

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at the surface of the steel container,

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the handling is done without intervening shields because of the relatively short time involved.

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Observe how the centering devices help as the pipe is lowered into the drum.

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Note the marking of the drum to indicate that it now contains radioactive materials,

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the amount and isotope being marked on the label.

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A wet concrete mortar is now poured

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around the steel container containing the cobalt pellets.

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The concrete in this particular case fills the drum readily

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without any tamping,

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and a solid mass will result without any agitation.

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The concrete can be mixed to any desired consistency.

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The steel pipe is suspended from the top of the drum

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to prevent it sinking through the soft mass before the concrete hardens.

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An immediate check is made of the surface gamma activity of the container.

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This is to make sure that it will comply

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with all of the interstate commerce regulations

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governing the shipment of radioactive materials over state highways.

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The markings on the drums are made in accordance with requirements of AEC licensing.

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They cover the amount and the isotope contained therein,

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also identifying marks, so that if there is any future recovery,

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the origin of the drum can be identified.

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Waste materials are packed in the concrete burial vaults

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and mixed intimately with a thin concrete mortar.

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All of the polyethylene containers are broken

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to ensure an intimate mix with the concrete

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and also to obtain a maximum density

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to ensure sinking in the ocean.

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The vaults are shallow enough to permit

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good mixing of the contents with thin concrete.

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The safety office personnel working directly

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over the vaults wear respirators to prevent the inhalation

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of airborne radioactive materials.

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This is not considered necessary for the cement workers

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who have a casual contact and are not working directly over the vault

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during the active breaking of the polyethylene containers.

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The vaults are actively agitated

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during the entire filling operation to eliminate voids

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and obtain as intimate mixing as possible.

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Actual tests show that the finished containers remain intact

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under the hydrostatic pressures at depths of at least 6,000 feet.

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Vacuum pumps used on a radon plant are contaminated

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to an extent where decontamination would be more expensive than replacement,

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so they are disposed of along with other types of waste.

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This is a sample of the wastes collected at an institution

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such as the National Institutes of Health.

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The vaults are finally sealed with a few inches of richer cement mix

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than is used in the body of the filling.

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These vaults shown here represent about one day's processing

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and contain approximately six months' waste supply from the Institutes.

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Upon completion they are checked for gross gamma activity

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with the gamma-sensitive meter.

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Each vault must be marked with identifying symbols

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to show the isotope contained therein, the approximate amount,

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the authorization permits under which shipment is made,

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and marks and dates for NIH identification purposes.

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The radioactive materials contained in these vaults

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are considered to be class D poisons.

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And therefore require the use of

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Interstate Commerce Commission labels,

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as well as direct identification as radioactive materials.

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The new concrete surfaces are painted to reduce moisture absorption

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while awaiting final disposition.

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The finished vaults are now checked to be sure there is no surface contamination.

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This is done by making a series of wipes

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across the surface of the finished concrete.

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These wipes are then counted in a gas-flow counter.

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This is required because of the possible presence

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of either carbon-14 or tritium, both of which are beta emitters.

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An automatic counter is used, each wipe being counted

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for a preset number of counts,

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with the time required being recorded on a paper tape.

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If the counts are within prescribed limits, essentially zero,

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the vaults can then be handled without gloves from here on.

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If positive contamination is found on the surface,

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it will be removed by scrubbing

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or by covering the contaminant with a heavy coat of paint

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or some other covering material.

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Upon completion of the counts, the counting rate is carefully noted

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and becomes a part of the record of each finished container.

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As the vaults are made ready for loading into trucks

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for transportation to the port of embarkation,

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a final gamma check is made on each individual vault

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to be sure that it fulfills the requirements for transportation over public roads.

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Each truck is loaded so that very low activity vaults,

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or those containing only nonpenetrating beta emitters,

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are placed next to the driver.

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This provides additional shielding between him and any vaults

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which show an appreciable gamma activity at the surface.

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This precaution is perhaps unnecessary but is carried out simply

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because any radioactive exposure should be avoided whenever possible.

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Each convoy is accompanied by a trained monitor in a separate vehicle

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carrying monitoring instruments capable of making measurements

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at any radioactive emergency which may arise during the shipment.

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A truck convoy leaving for the port of embarkation

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must comply with a variety of regulations.

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Weight and vehicle spacings while underway are prescribed by state law.

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The trucks, pulling into an official state weighing station,

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have red lights flashing, merely to indicate a turn off the main highway.

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The lights are not a part of the procedures associated

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with the shipment of the radioactive materials.

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Truck loadings are made with due regard for the loads allowed by state regulations.

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Each finished vault weighs about 1,500 pounds in air.

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Each shipment will have a total weight of 20 to 30 tons.

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After weights are checked the convoy proceeds,

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at all times following the regulations required for convoys.

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Proper spacing between vehicles is maintained

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so that overtaking vehicles need not pass the convoy as a unit,

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but can pull in between the trucks if necessary.

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In general, the convoying sedan follows behind the last truck

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to take care of any stragglers who may have mechanical difficulties.

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The convoy ends at the Coast Guard base at Norfolk, Virginia

00:20:20.290 --> 00:20:21.590
where the waste containers are loaded

00:20:21.590 --> 00:20:24.840
onto the fantail of the Coast Guard cutter.

00:20:24.840 --> 00:20:27.510
This vessel is equipped with steel trays which prevent

00:20:27.510 --> 00:20:30.710
contact of the waste container with the wooden deck,

00:20:30.710 --> 00:20:33.070
and in addition raise the shipment to a level

00:20:33.070 --> 00:20:34.640
that will clear the rail of the ship

00:20:34.640 --> 00:20:37.150
during the dumping procedure.

00:20:37.150 --> 00:20:39.510
One of the larger trays shown here

00:20:39.510 --> 00:20:42.180
is equipped with sections of roller conveyors to facilitate

00:20:42.180 --> 00:20:44.610
the off-loading of the concrete vaults

00:20:44.610 --> 00:20:46.990
at the designated dumping site.

00:20:46.990 --> 00:20:55.020
The steel platform is for handling the steel drums.

00:20:55.020 --> 00:20:57.500
Each set of concrete vaults is locked in position

00:20:57.500 --> 00:21:00.700
by a special locking device which can be tripped at sea

00:21:00.700 --> 00:21:08.170
for the safe release of the containers.

00:21:08.170 --> 00:21:10.070
As in the case of loading the trucks,

00:21:10.070 --> 00:21:11.610
preference is given to those vaults

00:21:11.610 --> 00:21:13.930
showing some gamma activity at the surface

00:21:13.930 --> 00:21:16.430
by placing them outboard and away from the positions

00:21:16.430 --> 00:21:18.370
which will be occupied by the crew

00:21:18.370 --> 00:21:23.980
during the normal working of the vessel.

00:21:23.980 --> 00:21:25.720
It will be noted that here the crew members

00:21:25.720 --> 00:21:28.470
are handling the vaults without protective gloves,

00:21:28.470 --> 00:21:30.990
because of the previous checks which have shown the surfaces

00:21:30.990 --> 00:21:41.700
to be completely free of radioactive contamination.

00:21:41.700 --> 00:21:44.970
Before the trucks are released to return to the Institutes,

00:21:44.970 --> 00:21:47.870
a final check is made with a thin window counter to be sure

00:21:47.870 --> 00:21:51.570
that no contamination has been left in the truck bodies.

00:21:51.570 --> 00:21:54.690
When this has been so demonstrated, the signs are removed,

00:21:54.690 --> 00:22:04.010
and the trucks are available for regular duties without restrictions.

00:22:04.010 --> 00:22:07.520
Aboard ship, steel drums are lashed down to prevent movement

00:22:07.520 --> 00:22:13.810
during the voyage out to the dumping ground.

00:22:13.810 --> 00:22:15.780
The hands and feet of the crew members are checked

00:22:15.780 --> 00:22:18.300
to be sure that no contamination has been received

00:22:18.300 --> 00:22:21.640
by any of them in loading the vaults and drums.

00:22:21.640 --> 00:22:23.770
These surveys are conducted with a Geiger counter

00:22:23.770 --> 00:22:27.790
which will respond to carbon-14 and more energetic emitters,

00:22:27.790 --> 00:22:30.290
but which will not detect tritium.

00:22:30.290 --> 00:22:31.850
With a thorough mixing of the wastes,

00:22:31.850 --> 00:22:35.550
it is hard to imagine a contamination of tritium alone.

00:22:35.550 --> 00:22:55.030
And so an absence of activity is assumed to indicate an absence of tritium also.

00:22:55.030 --> 00:22:57.330
Tripping a dog releases four vaults

00:22:57.330 --> 00:23:00.180
which go overside almost simultaneously

00:23:00.180 --> 00:23:02.210
but without any damaging collisions.

00:23:02.210 --> 00:23:03.690
This is done at the dumping ground

00:23:03.690 --> 00:23:06.220
prescribed in the waste disposal license

00:23:06.220 --> 00:23:21.160
granted by the Atomic Energy Commission.

00:23:21.160 --> 00:23:25.610
Experiments conducted at depths of 1,000 fathoms or 6,000 feet

00:23:25.610 --> 00:23:28.340
suggest that about 15 to 20 minutes is required

00:23:28.340 --> 00:23:30.940
for containers to reach the bottom.

00:23:30.940 --> 00:23:35.420
All materials are disposed of at a depth of not less than 1,000 fathoms,

00:23:35.420 --> 00:23:40.730
which in the Norfolk area means approximately 80 to 90 miles due east,

00:23:40.730 --> 00:23:42.620
to carry the ship beyond the continental shelf.

00:23:42.620 --> 00:23:48.470
[80 miles, 90 miles, 1000 fathoms]

00:23:48.470 --> 00:23:52.260
Here the fathometer reading for one particular trip indicates

00:23:52.260 --> 00:23:57.290
that disposal is made at a depth of 1,000 fathoms.

00:23:57.290 --> 00:24:00.170
[Music]

00:24:00.170 --> 00:24:07.750
[Directed by...Wilmer H. Kimberly, Technical Advisor...Dr. Howard L. Andrews]

00:24:07.750 --> 00:26:59.558
[The End, CDC M-443]