Bromate, chlorite, chlorate, haloacetic acids, and trihalomethanes occurrence in indoor swimming pool waters in Italy

Subjects attending indoor swimming pools are exposed to disinfection by-products (DBPs) by inhalation, dermal contact and/or ingestion, as a consequence of water disinfection treatments with chlorine and related compounds. The occurrence of trihalomethanes (THMs) in poolwaters has been well documented, while information about other DBPs, including bromate, chlorite, chlorate and haloacetic acids (HAAs), is very limited even though someof these substances are potentially dangerous for human health. The aimof this studywas to investigate the occurrence of bromate, chlorite, chlorate, HAAs and THMs both in pool and in source water of 24 public indoor swimming pools in Emilia Romagna Region, Northern Italy. THMs were evaluated with a standardized method involving the head-space gas-chromatographic technique, while HAAs, bromate, chlorite, and chlorate were detected by Ion Chromatography with Mass Spectrometry. THMs were measured in all the pool water samples (mean value: 36.9 \ub1 28.2 \u3bcg/l), while they were detectable in less than 50% of source waters and always at very low levels (mean value: 2.0 \ub1 4.1 \u3bcg/l), as a consequence of drinking water disinfection with chlorine dioxide, a widespread disinfection method in Italy. Bromate was always absent in source water samples, and it was detected in 3 samples of poolwater only (range: 10\u201348 \u3bcg/l). HAAs were scarcely detected in sourcewaters (3 positive samples, maximum level observed: 21 \u3bcg/l), while in pool water theywere always present at detectable levels and showed high concentrations (range: 11\u2013403 \u3bcg/l, mean value of 164 \ub1 108 \u3bcg/l). Chlorite was present in 22 water supply samples (mean value: 149 \ub1 122 \u3bcg/l) but only in one pool water. Chlorate, on the contrary, resulted as the most prevalent DBP both in source (range: 2\u2013499 \u3bcg/l) and in pool waters, where it showed the highest levels, with a mean value of 3661 \u3bcg/l and a maximum value of 19537 \u3bcg/l. Such environmental levels could result in an important human exposure, mainly by ingestion and/or dermal contact, to non volatile DBPs different than THMs. Exposure to those DBPs, therefore, needs to be further investigated and strategies aimed at minimizing it should be identified and undertaken. Attention should be paid, above all, to chlorate: this substance appears reallywidespread in swimming pool water and, according to themost recent toxicological studies, its potential human health effects could be relevant