Sources of cadmium exposure in an Italian population: a cross-sectional study
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(3) P-1 _ SOURCES OF CADMIUM EXPOSURE IN AN ITALIAN POPULATION: A CROSSSECTIONAL STUDY Filippini Tommaso1, Cherubini Andrea2, Greco Salvatore2, Maffeis Giuseppe2, Malagoli Carlotta1, Bottecchi Ilaria1, Malavolti Marcella1, Sieri Sabina3, Krogh Vittorio3, Vescovi Luciano4, Modenesi Marina4, Castiglia Paolo5, Michalke Bernard6, Vinceti Marco1 1Environmental,. Genetic and Nutritional Epidemiology Research Center (CREAGEN), Department of Diagnostic, Clinical and Public Health Medicine, University of Modena and Reggio Emilia, Reggio Emilia, Italy 2Italy TerrAria srl, Milan, Italy 3Epidemiology and Prevention Unit, Fondazione IRCCS Istituto Nazionale dei Tumori Milan, Italy 4IREN, Reggio Emilia and Piacenza, Italy 5Department of Biomedical Sciences, Hygiene and Preventive Medicine Unit, University of Sassari – AOU Sassari, Sassari, Italy 6Research Unit Analytical BioGeoChemistry, Helmholtz Zentrum München – German Research Center for Environmental Health GmbH, Munich, Germany. Main sources of Cadmium (Cd) exposure in the. sources of exposure. We used both crude and. human are food and cigarette smoking as, but. multivariate. also outdoor and indoor air pollution can be. determine the influence of outdoor PM10. important, mainly from industrial emissions,. levels, smoking and dietary Cd intake on serum. fossil. waste. Cd. Median values (25th–75th) for serum and. incineration. The aim of this study was to. dietary Cd were 40.85 ng/l (30.05-53.50) and. assess the influence of outdoor air pollution on. 13.36. serum Cd levels in fifty residents randomly. coefficients were 0.617 (95% CI -0.194–1.428,. selected from the municipal population of. P=0.133), 0.026 (-0.827–0.829, P=0.952) and. Modena, Northern Italy. We geocoded the. 6.962 (-0.022–13.945, P=0.051) for PM10, diet. current residence of these subjects and. and. modeled. air. adjusted values were 0.463 (-0.365–1.292,.
(4) . P=0.266), -0.036 (-0.866–0.793, P=0.930) and. (PM10), with the CAlifornia LINE Source. 6.057 (-1.175–13.289, P=0.099), respectively.. Dispersion Model version 4 (CALINE-4), as a. In our population, the most important factor. proxy of environmental air Cd. Information on. influencing Cd serum content thus appears to. smoking habits and Cd. be cigarette smoking, followed by outdoor air. fuel. combustion. their. and. outdoor. solid. ambient. dietary intake were. also collected, to assess these two additional. linear. μg/die. smoking,. regression. (10.45-. respectively.. models. . to. -. Corresponding. pollution and lastly by diet.. 46.
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