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A Review of Criticality Accidents A Review of Criticality Accidents

A Review of Criticality Accidents A Review of Criticality Accidents

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additional reflection afforded by the added poisoned<br />

aqueous solution was apparently insufficient to<br />

compensate for this effect.<br />

After addition <strong>of</strong> the cadmium nitrate solution, a<br />

hose was inserted into the holding vessel through a top<br />

port to siphon out the solution. Surprisingly, at the very<br />

beginning <strong>of</strong> the siphoning, a sixteenth, and final,<br />

excursion occurred. Later, upon consideration <strong>of</strong> the<br />

facts, it was recognized that this last excursion was a<br />

result <strong>of</strong> siphoning from the bottom <strong>of</strong> the vessel. Even<br />

though the draining <strong>of</strong> the cadmium nitrate decreased<br />

reflection, it allowed the organic to assume a more<br />

reactive geometry as it reentered the hemispherical<br />

bottom <strong>of</strong> the vessel.<br />

The siphoning action was continued (in spite <strong>of</strong> the<br />

last excursion) until the vessel was drained. Altogether<br />

about 65 l <strong>of</strong> organic with a uranium concentration <strong>of</strong><br />

33 g U(90)/ l, corresponding to about 2.14 kg <strong>of</strong><br />

U(90), were removed from holding vessel 694.<br />

14. United Nuclear Fuels Recovery Plant, 24 July 1964 23,24<br />

This accident occurred in a chemical processing<br />

plant at Wood River Junction, Rhode Island, which was<br />

designed to recover highly enriched uranium from<br />

scrap material left over from the production <strong>of</strong> fuel<br />

elements. The plant operated three, 8–hour shifts, 5<br />

days a week. The scrap material was shipped to the<br />

plant as uranyl nitrate solution in 55 gallon (208 l)<br />

drums, at concentrations ranging from 1 to 5 g/ l <strong>of</strong><br />

uranium. The uranyl nitrate was then purified and<br />

concentrated by solvent extraction using tributyl<br />

phosphate mixed with kerosene as the organic wash.<br />

After the final acid strip, the purified uranyl nitrate<br />

solution was bubbled through a column containing a<br />

fixed charge <strong>of</strong> 4 to 6 l <strong>of</strong> trichloroethane (TCE). The<br />

TCE removed any organic that remained in the<br />

solution. The original plant design was based on a<br />

predicted life <strong>of</strong> 6 months to 1 year for a single charge<br />

<strong>of</strong> the TCE.<br />

Typical <strong>of</strong> the difficulties that should be expected<br />

with a new operation (the plant had begun operations<br />

on 16 March 1964) a larger amount <strong>of</strong> organic<br />

carryover and a higher retention <strong>of</strong> uranium reduced<br />

the TCE’s useful life to approximately 1 week. In early<br />

April, therefore, a procedure was developed to remove<br />

the uranium from the TCE before discarding it. The<br />

very low concentration <strong>of</strong> uranium in the solution<br />

(400 to 800 ppm) was recovered by washing the TCE<br />

with sodium carbonate solution. Originally, the<br />

During the nearly 16 hours over which the accident<br />

took place, the plant operators and supervisors on shift<br />

at the beginning <strong>of</strong> the excursions remained at the<br />

facility to assist with recovery operations and to<br />

document the events.<br />

The total number <strong>of</strong> fissions, based on 140 La fission<br />

product analysis, was estimated to be about 6 × 10 16 . A<br />

prompt and efficient evacuation was initiated by the<br />

sounding <strong>of</strong> the criticality alarm system. The largest<br />

individual dose received was less than five rem. There<br />

was no damage to the equipment or radioactive<br />

contamination.<br />

The accident occurred (despite the fact that the<br />

vessels were steam cleaned monthly) presumably<br />

because <strong>of</strong> a rather quick and large accumulation <strong>of</strong><br />

both organic and aqueous solutions. Subsequently,<br />

changes were made to the process design and between<br />

January and September 1964, large numbers <strong>of</strong> process<br />

vessels were replaced. At the end <strong>of</strong> this renovation,<br />

nearly all <strong>of</strong> the vessels were <strong>of</strong> favorable geometry.<br />

Uranyl nitrate solution, U(93), in a carbonate reagent makeup vessel; two excursions; one fatality, two significant<br />

exposures.<br />

operation was performed by manually shaking or<br />

rocking the solution within 5 inch (127 mm) diameter,<br />

11 l bottles. This somewhat laborious process was<br />

used until 16 July. On that date, because an unusually<br />

large amount <strong>of</strong> contaminated TCE had accumulated,<br />

an operator was given permission by his supervisor to<br />

use a sodium carbonate makeup vessel to perform this<br />

process as long as the uranium content did not exceed<br />

800 ppm. The vessel was 18 inches (457 mm) in<br />

diameter and 26.375 inches (670 mm) deep and was<br />

located on the third level <strong>of</strong> a tower housing solvent<br />

extraction columns. This new procedure was communicated<br />

to one other operator on a different shift.<br />

Between 16 and 24 July, these two operators washed<br />

10 to 12 bottles each using the carbonate makeup<br />

vessel. It should be noted that the treatment <strong>of</strong> the TCE<br />

by any method was not part <strong>of</strong> the facility license, and<br />

therefore was not approved by the regulating authority.<br />

On the day before the accident, a plant evaporator<br />

had failed to operate properly, making it necessary to<br />

disassemble it for cleaning. During the cleaning, a plug<br />

<strong>of</strong> uranium nitrate crystals was found in a connecting<br />

line. The crystals were dissolved with steam, and the<br />

resulting concentrated solution (256 g U/ l) was<br />

drained into polyethylene bottles identical to those that<br />

normally held the very low concentration TCE<br />

solution. All <strong>of</strong> the bottles containing the high concentration<br />

solution were labeled as such.<br />

33

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