Wrong site for Japanese labs.
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The current regulations of the U.S. Nuclear Regulatory Commission (NRC) normally require limitation of radiation exposure in any part of unrestricted occupied areas to 2 mrem in any one hour and to 100 mrem in 7 days. To meet these limits when patients are treated therapeutically with radioactive materials, it is advisable to designate specific rooms in a hospital and often necessary to incorporate substantial costly shielding into one or more walls and the room door. Plans have been formulated for shielding existing hospital rooms housing brachytherapy patients receiving 192Ir and 137Cs therapy in order to meet the above NRC requirements for adjacent corridors and rooms. Typical shielding thicknesses required are 4-6 in. of concrete for certain walls and 1/4 in. of lead in the doors. Shielding costs are approx. $6000 per room for one shielded wall and a shielded door. Applying recent estimates of the cancer risk from low-level gamma radiation, the cost of shielding per cancer fatality averted has been estimated to range from $1.8 million to $10.9 million. Cost/benefit comparisons with many other life-saving activities suggest that these costs and the application of the 2 mrem/hr limit which necessitated them are not justified.
Numerical calculations were done of the indoor exposure rate due to the cosmic rays. Only muons were considered, and the calculations were done within a two-dimensional framework under the non-scattering approximation. The effects of various structural parameters on the level and the distribution of the exposure rate were studied by a case control method. It was shown that a building's dimensions and the floor thickness were important in all cases. However, the effect of partition walls would become significant only when the partition number is large. The effect of neighboring buildings would be especially important in the lower floors of tall buildings. In such a case, attention is necessary not only to the buildings' internal structures but also to the relationship between that particular building and its neighborhood. The maximum amplitude of the possible variation of the exposure rate due to the change of any single structural parameter would be 30% in ordinary Japanese housing conditions.
Children are particularly vulnerable to injury and death in two types of 20th century conflicts; terrorist attack and civil war. This account describes some first-hand experiences of the aftermath of the Rwandan Civil War of 1994. Events leading to the conflict are described, eye witness accounts of child trauma during the war are recorded and the medical problems (currently ongoing) affecting children are described. Over a period of 3 months from April to June 1994, between half and one million Rwandese, a significant proportion of them women and children, were murdered in brutal hand-to-hand killing, dying from close-quarter gunshot and machete slaughter. Nearly half of the population became refugees in neighbouring countries or displaced persons in their own land. UNAMIR II, the United Nations Emergency Humanitarian Response, grew to some 7000 persons by May 1995. Medical aid was provided by emergency medical contingents from the United Kingdom, Canada and Australia, the latter through its Australian Medical Support Force, providing the definitive emergency medical infrastructure from August 1994. In the consequent post-war civil and social disruption, children suffered from burns, cholera and from motor vehicle trauma. Ongoing landmine blasts continue to affect children and adolescents especially. A new International humanitarian code to build a time-expiry device into landmines and other similar ordinance is urgently required as the post-conflict ongoing disasters in Rwanda, Afghanistan and Cambodia illustrate. Current problems affecting children include an increasing risk of HIV infection, trauma and the special humanitarian needs of thousands of orphans.
The WTC disaster provided an opportunity to look for ways to prevent morbidity among occupants of high-rise buildings during fires. This paper first describes the overall morbidity resulting from the explosion and fire, and second, presents the results of a case-control study carried out to identify risk factors for smoke-related morbidity. The main ones include: increased age, presence of a pre-existing cardio-pulmonary condition, entrapment in a lift and prolonged evacuation time. Study results point to the importance of the following safety systems during high-rise building fires: smoke-control systems with separate emergency power sources; lift-cars, lift-car position-monitoring systems, and lift-car communication systems with separate emergency power sources; two-way emergency communication systems on all floors and in stairwells; stairwells with emergency lighting and designed for the rapid egress of crowds; evacuation systems/equipment to assist in the evacuation of vulnerable people (elderly, infirm). Also important are evacuation plans that include regularly scheduled safety training and evacuation drills.
This paper gives an overview of the global pattern of casualties in earthquakes which occurred during the 30-month period from 1 September 1993 to 29 February 1996. It also describes some of the behavioural and logistical regularities associated with mortality and morbidity in these events. Of 83 earthquakes studied, there were casualties in 49. Lethal earthquakes occurred in rapid succession in Indonesia, China, Colombia and Iran. In the events studied, a disproportionate number of deaths and injuries occurred during the first six hours of the day and in earthquakes with magnitudes between 6.5 and 7.4. Ratios of death to injury varied markedly (though with some averages close to 1:3), as did the nature and causes of mortality and morbidity and the proportion of serious to slight injuries. As expected on the basis of previous knowledge, few problems were caused by post-earthquake illness and disease. Also, as expected, building collapse was the principal source of casualties: tsunamis, landslides, debris flows and bridge collapses were the main secondary causes. In addition, new findings are presented on the temporal sequence of casualty estimates after seismic disaster. In synthesis, though mortality in earthquakes may have been low in relation to long-term averages, the interval of time studied was probably typical of other periods in which seismic catastrophes were relatively limited in scope.
Accidental events such as fires, explosions, and leaks often result in large-scale contaminations of buildings with toxic chemicals. After decontamination, the certification for original use requires testing for residual contamination. The two basic kinds of sampling plans in use up to recently both fall short of the required performance. Their deficiencies are analyzed in terms of the scientific questions implicit in both the sampling plan and the subsequent statistical evaluation. A sampling strategy of a new kind is proposed and discussed in the same context. It is motivated by concern for the long-term safety of the building's occupants and is, therefore, based on factors important in risk assessment. Three different sampling plans are derived in the framework of this methodology, two of which have already been used in actual certification proceedings.
The two major noise sources that cause environmental problems for the U. S. Army are helicopters and large weapons such as artillery, tanks, and demolition. These large weapons produce blast sounds that contain little energy above 200 Hz and that are particularly troublesome to deal with because they excite rattles in structures. The purpose of this study was to systematically test subjective response to the presence or absence of rattles in otherwise similar blast sound environments. A second purpose of the study was to test if there were structural changes that could reduce annoyance within the indoor blast sound environment. This study was done using a specially constructed test house and highly repeatable shake table to generate the blast sounds. The data clearly show that no commonly used environmental noise measure adequately describes the indoor environment when the blast excites rattles. Although the indoor blast ASEL changes by only about a decibel or so (and the indoor blast CSEL changes by even less), the subjective response changes by up to 13 dB. At low blast levels, the increase in human annoyance response is largest, and this annoyance response offset decreases to about 6 dB when the outside, flat-weighted peak sound-pressure level of the blast increases from 112 to 122 dB.
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