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Updated: 13-Feb-2001 NATO Information

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CISAM CENTRO INTERFORZE STUDI APPLICAZIONI MILITARI ISTITUTO AUTORIZZATO

VERBALE DI INTERVENTO
SFOR - Brigata Multinazionale
Area Contingente Italiano in Bosnia


INDEX

1.Introduction
1.1 Foreword
1.2 Aims of inspection
1.3 Directions to personnel


2. Basic informations


3. Areas subjected to radiological evaluation


4. Measurement procedures
4.1 Measurement instrumentation
4.2 Formalities for the drawing of environmental samples
4.3 Measurements


5. Radiological evaluations


6. Recommended precaution measures


7. Conclusive remarks



1. Introduction

1.1 Foreword
Following war events in Bosnia, CISAM's specialized personnel was formally tasked, by disposition n. COI/J4L/28801 of 21 December 2000, to deploy preliminarily to Bosnia, joining the Italian Forces operating in that area in order to identify the radioprotection situation as related to the military personnel operating in the theatre since December 1995 and to the troups that are now committed in the same area. The preliminary inspection in Bosnia has been carried out by Rear Admiral Francesco Andreuccetti, who has acted in cooperation with Manager Dr. Vittorio Sabbatini, certified expert, registered with n.5 on the list of the experts holding 3rd level certification. Radiological checks have been carried out on 23 December 2000 at Sarajevo and in the area surrounding the city with the cooperation of the Italian military personnel led by LTC Buschettari and with the participation of NBC specialized personnel.

1.2 Aims of inspection
The mission, whose objective was to give a preliminary evaluation of the radiological conditions consequential to the utilization of DU ammunition by the NATO forces in the Sarajevo area, pursues the following goals:

a) to evaluate eventuel residues of the above mentioned amunition in the areas occupied by Italian troups since 1995 and in those which are now being used.
b) to provide SMD and COI with immediate input on the inspected sites, on the basis of the first measurements performed.
c) to draw environmental samples from the mentioned areas which are to be submitted to lab tests in order to determine the concentration of DU necessary to evaluate the doses affecting personnel.
d) indicate protective measures to be adopted.
e) prepare for a successive, more complete radioprotection investigative campaign.

All radiological checks have been carried out in compliance with the norms in force.

1.3 Directions to personnel
During the inspections, when the situation called for it, the personnel has been duly informed on the identified, specific risks and instructed on the protective measures to be adopted.

2. Basic Information

Knowledge by the NATO forces of 10.800 shells equipped with 300 gr DU piercing projectiles, but lack of detailed information (coordinates and number of projectiles actually utilized) on the areas and targets affected, and on the weather conditions at the time of the explosions, left us no alternative but that of acting on the basis of input provided by the Italian Military Command represented by Gen. Sanpaolo and Col. Beraldo. We have, thus, proceeded with a preliminary inspection of the sited around Sarajevo, where the Italian military presence has been and still is concrete, and where the signs of ruin and machine-gunning of various types and intensity are quite evident. Environmental samples have been drawn from these areas where deemed appropriate.

3. Areas subjected to radiological evaluation

Areas subjected to radiological evaluation and relative geographic denominations are shown in the following chart:
Chart n. 1
Areas subjected to preliminary radiological evaluation
Areas subjected to preliminary radiological evaluation City: Remarks:
"Tito Barracks", ex Yugoslavian Army Academy, Battle Group HQS. Sarajevo City damaged, tottering, shut down buil-dings, absence of hit tanks.
"Tito Barracks", ex Yugoslavian Army Academy, area assigned to Task Force. Sarajevo City damaged, tottering, shut down buildings, absence of hit tanks.
8th Regiments HQS and Italian Field Hospital from Dec 95 to June 97. Vogosca Area located between tottering buildings, shut down premises, ab-sence of hit tanks.
Helicopter Squadron HQS and ex seat of Yugoslavian Air Force Academy. Railovac Controlled by German and French units, absence of hit tanks.
Brigade Command HQS from 12.95 to 15.3.2000 and ex Sarajevo Pediatric Hospital. Sarajevo, Zetra Damaged, tottering, shut down buildings, absence of hit tanks.
Carabinieri Installation close to Sara-jevo Airport Sarajevo, Butmir New prefab buildings, reclamed land, absence of hit tanks.

4. Measurement procedures

4.1 Measurement instrumentation utilized on site
The following portable monitors have been utilized to assess the cardiological situation in the areassubjected to inspection and listed on chart n.1.

· Air Kerma rateo monitor, Victoreen 290 SI with G.M. beta-gamma 189-4 probe;
· ROTEM DA-3 with beta-gamma GM-10;
· Surface contaminometer, Contamat FHT 111M.

4.2 Formalities for the drawing of environmental samples.
Soil samples have been drawn from the areas subjected to radioprotection tests for lab measurements to be carried out in CISAM's Health Physics and Radioprotection departments of the CISAM Nuclear Office.
The mentioned soil samples have been drawn in significan areas, according to the procedures set by NATO SIRA (Standard Identification of Radiological Agents).
While on site radiometric checks and sample drawings were being carried ou, a search was conducted in the damaged buildings and in the areas close to them for ammunition residues showing radioactivity, particularly shells and projectiles from 30 mm guns along with other residues. Such search has given negative results.

4.3 Measurements
The rateo dose density measurements (Kerma rateo in air) taken from numerous traces left on buildings and roads by projectiles of different types, have shown levels undistinguishable from those found in the natural environment (not superior to 0.5 microGy/h).

Further, on site measurements, taken from the ground surface and from the buildings, have failed to show levels of superficial contamination and dose intensity distinguishable from those present in the natural environment. The drawn samples are expected to undergo lab measurements which, being characterized by higher sensitivity, will allow an evaluation of eventual traces of DU and of other radiosotopes.

5. Radiological evaluations

Depleted Uranium, which by law decree n. 230/95 is classified as lo toxicity, radioactive material, is made of 99.7% uranium 238 (U238), 03% U235 and traces of U234.
Uranium 238 is the founder of the natural uranium family, while Uranium 235 is the founder of the Actinium-Uranium natural family. The two radioisotopes, whose balance is characterized by alpha, beta and gamma emission descendants, have halving times of respectively 4.5 billion and 0.7 billion years. Such isotopes, which are generally known to exist in low concentration, are naturally present in the earth waters and soils.
The use of depleted uranium in perforating projectiles causes the following two problems of radioprotection nature:
a) risk from external irradiation in proximity of DU shells or consistent parts of them.
b) risk of DU incorporation from inhalation or swallowing

As for the first possibility, we must remember that the measurements taken during the Kosovo campaigns from an integral projectile have shown, upon contact, a dose intensity of about 200 microGy/h which has gradually decreased as the distance from it increased, until becoming undistinguishable from the density level present in the natural environment.
For what concerns the second possibility, the experience acquired during the Kosovo environmental campaigns in areas hit by numerous armor piercing projectiles, has shown that the highest risk comes from swallowing, associated with the careless and extended handling of DU shells.
As far as Bosnia and Kosovo, incorporation by direct inhalation of DU fumes produced by the projectile-target impact must be excluded, owing to the time lapsed between the end of the war activities (September 1995) and the arrival of the Italian force in the theatre (20.12.95).
Finally, the risk from inhalation associated with re-suspension, which may be determined by lifting dust from the contaminated soil, must be deemed negligible and technically justifiable, given the physical characteristics of uranium, and on the basis of the results obtained from the specific measurements taken.
The on site measurements taken in the checked areas and those previously taken in areas hit by DU shells in Kosovo, reveal that the external irradiation risk is negligible, while it leads us to conclude that the exposure level affecting the personnel operating in the mentioned areas is below the safety limits expected for the general public.

6. Recommended precaution measures

Precaution and conservative measures recommended for implementation in order to reduce the risks from ionizing radiations generated by the presence of DU are listed below:

a) request from the competent authorities a detailed list of the sites in Bosnia where DU shells have been utilized, along with coordinates and number of exploded shells.

b) demand that NBC personnel conduct preventive inspections of the areas where DU ammunitions are admittedly used, while reducing the permanence of other personnel in the concerned areas to the bare minimum necessary;
c) personnel operating in these areas must be equiped with anti-dust masks and disposable gloves, and must be escorted by NBC personnel carrying revelation instruments;
d) under the supervision of NBC personnel and complying with given instructions, all identified, exploded ammunition, shells and other material must be collected and stored in two distinct metal containers equipped with lids, one for DU projectiles and fragments, the other for contaminated materials. These containers must be stocked in warehouses located in guarded, assigned areas, while no one must be allowed to get closer to them than 5 meters.
e) Personnel must be warned about the areas affected by DU ammunition and informed about the characteristics of the same, while solicited to contact NBC personnel immediately upon identification of such ammunition.
f) Warn the company and platoon Commanders of the importance to ensure that their personnel, acting contrary to the given instructions, have not picked and kept suspicious objects that have not been checked by NBC personnel.

7. Conclusive remarks

The instruments utilized by the CISAM personnel in the areas subjected to radiological checks have revealed absence of DU shelling traces and verified a subsequent absence of risk associated with the presence of DU.
In order to obtain more precise evaluations and more effective protective measures for the operating personnel and the population at large, while at the same time providing a complete picture of the radioprotection situation in Bosnia, more environmental checks must be carried out in the areas where Italian personnel has been and is now engaged. Thanks to the specialistic activities conducted in Kosovo and to the experience gained from them, we are now in a position to evaluate, among the possible risks that may affect (and may have affected) the people involved, that of irradiation from integral projectiles and that of internal contamination resulting from swallowing and caused by the careless handling of exploded DU shells. The same experience leads us to classify as negligible the risks from irradiatin caused by shells on the ground and risks of internal contamination caused by inhalation of re-suspension dust.
The implementation of the protective measures suggested, allows the reduction to negligible levels of the risks for the personnel operating in Bosnia.
The preliminary results of the inspections have been conveyed to the Italian Command in Bosnia. The drawn environmental samples are now being examined in the CISAM's Health-Physics and Radioprotection labs. The lab results will be the subject of a further report.