Arsenic determination was carried out on hair, urine, and blood samples taken from groups of 10-year-old boys, each numbering 20 to 25 individuals, residing in a region polluted by arsenic. In all the examined materials considerably elevated concentrations of arsenic were found. The relation of the observed levels of arsenic to the distance of the place of residence up to a distance of more than 30 km from the source of the emissions was studied. On the basis of the results obtained, the most advantageous material for estimation of nonoccupational exposure to arsenic seems to be hair, in spite of some problems with the decontamination procedure involved. Considerable variability among individual arsenic values in the hair makes group examination a necessity. Hearing changes were analyzed in a group of 56 10-year old children residing near a power plant burning local coal of high arsenic content. The results of both audiometric and clinical examination were compared with those of control group numbering 51 children of the same age living outside the polluted area. The highly standardized audiometric and clinical examination were completed with a questionnaire analysis concerning the personal medical histories of the children. The obtained data were elaborated statistically by means of the x2-test.In the case of air conduction, important hearing losses were found at frequencies of 125, 250 and 8000 Hz, especially at the lowest frequency range. Significant degrees of hearing loss were found in bone conduction as well as in the corresponding ranges of frequencies. The high statistical significance of the hearing impairments found points to very low probability of their being only an "accidental" finding. The possibility of toxic damage to the ear cannot yet be excluded.The air pollution caused by fly ash and sulfur oxides released from coal burning is complicated in some places by the presence of excessive quantities of toxic elements in the emissions of power plants. We have studied the hygienic-toxicologic problems of environmental pollution by arsenic in the vicinity of a power plant which burns local coal with an arsenic content of 900 to 1500 g/ton of dry substance in the form of sulfides. Despite the use of electrostatic eliminators, about half a ton of arsenic is emitted daily in the smoke, according to rather conservation calculations. Most of the arsenic is in the form of arsenic trioxide contained in the solid phase of the emissions. The first indication of arsenic pollution was the mass extinction or severe depletion of colonies of bees at the distance of 30 km from the power plant in the direction of prevailing winds. Several epidemiological studies have been per-