Constantin COSMA¹, Alexandra CUCOŞ DINU¹, Botond PAPP¹, Mircea MOLDOVAN¹, Robert BEGY¹, Tiberius DICU¹, Dan C. NIŢĂ¹, Bety D. BURGHELE¹, Dan FULEA¹, Ciprian CÎNDEA¹, Oana DUMITRU RUSU¹, Cristian MALO޹, Liviu SUCIU², Gheorghe BANCIU ² & Carlos SAINZ^1,3
1Faculty of Environmental Science and Engineering, “Babeş-Bolyai” University, Fântânele street, no. 30, 400294, Cluj-Napoca, Romania, E-mail: constantin.cosma@ubbcluj.ro; alexandra.dinu@ubbcluj.ro; papp.botond@ubbcluj.ro; mircea.moldovan@ubbcluj.ro; robert.begy@ubbcluj.ro; tiberius.dicu@ubbcluj.ro; negru_frozen@yahoo.com; burghele.bety@ubbcluj.ro; fulea.dan@gmail.com; cipcin@yahoo.com; oana.rusu@ubbcluj.ro; cristian.malos@ubbcluj.ro; carlos.sainz@unican.es
²I.C.P.E. BISTRITA SA, Parcului street no. 7C, Bistriţa, Romania, E-mail: liviu@icpebn.ro;
gheorghebanciu@yahoo.com
³Department of Medical Physics, Faculty of Medicine, University of Cantabria, c/Herrera Oria s/n., 39011, Santander, Spain, E-mail: carlos.sainz@unican.es

RADON MEASUREMENTS AND RADON REMEDIATION IN BĂIŢA-ŞTEI PRONE AREA

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Băiţa-Ştei was the largest uranium reserve in Romania with estimated reserves of 450,000 tons of high grade metal. It was a large open pit mine in the northwest of Romania (West Carpathian Mountains), situated at 123 km south-east of Oradea, the capital of Bihor County. The transport during the time of sediment by Crişul Băiţa water course increased the uranium and radium content in the river meadow. The

as building material the uranium waste from this mine. Preliminary indoor radon measurement (grab samples) in the villages situated on the route of ore transport (Băiţa Plai - Ştei) shown high adonconcentrations, until 5000 Bq m⁻³. The new result obtained in this work in springer season 252 Bq m⁻³ is comparable with the annual means of 241 Bq m⁻³ and 229 Bq m⁻³ respectively, previously obtained, but more than twice times higher than the average value of 126 Bq m⁻³, computed for Romania. About 3000 of etched CR-39 track detectors were used followed by a selection of 20 houses proposed for remediation where a systematic investigation regarding radon sources was performed. The measured indoor radon concentration in the surveyed buildings ranged from 40 to 4000 Bq m⁻³. For experimental research, a representative pilot house was chosen. This house represents an example of a typical building from this area, with complex and various radon entry pathways which are correlated with the geology of soil. This building was chosen as pilot house due to the fact that it requires different ventilation systems or other remedial measures to be installed.