Headspace solid phase microextraction (HS-SPME) with further quantification by gas chromatography and electron capture detector (GC/ECD) was used to analyze trihalomethanes (THMs) in water and air from indoor swimming pools (ISPs). High correlation coefficients were obtained for the calibration lines in water with detection limits of 0.2 µg/L for trichloromethane (TCM) and bromodichloromethane (BDCM), 0.1 µg/L for dibromochloromethane (DBCM) and 0.5 µg/L for tribromomethane (TBM). Coefficients of variation values were 5-10% for repeatability and 15-25% for reproducibility. In air analysis, high correlation coefficients were also obtained for the calibration lines with detection limits of 2.5 µg/m 3 for TCM and BDCM and 1.25 µg/m 3 for DBCM and TBM. Repeatability and reproducibility coefficients of variation were the same as in water analysis. Analytical results from a survey in four Portuguese ISPs showed that the mean concentration of total trihalomethanes (TTHMs) in water ranged from 22 ± 2 to 577 ± 58 µg/L. In the lack of European specific regulation for THMs in water from ISPs and taking into consideration that ingestion is a form of exposure, TTHMs' values were compared with European drinking water maximum contamination level (100 µg/L, Directive 98/83/CE). From the reported TTHMs mean concentration values in ISPs' water, 40% exceeded that value. TTHMs values determined in the air (T = 30• C) ranged from 98 ± 10 to 1225 ± 123 µg/m 3 and from 51 ± 5 µg/m 3 to 519 ± 52 µg/m 3 at 5 and 150 cm above the water surface, respectively. As expected, swimmers are more exposed to high concentrations of THMs than lifeguards. As there is no European specific regulation for THMs in ISPs' air, the highest TCM values were compared with maximum values reported in the literature for ISPs (1630 µg/m 3 ) and with the inhalation exposure limit (10,000 µg/m 3 ) established for TCM by European occupational legislation (Directive 2000/39/CE).
A solid phase microextraction method was used for the analysis of nine haloacetic acids (HAAs) in water and air (aerosols) from indoor swimming pools (ISPs). The analysis is characterized by derivatization of HAAs to their methyl-esters with dimethyl sulphate, headspace solid phase microextraction (HS-SPME) with a Carboxen-polydimethylsiloxane (CAR-PDMS) fiber and gas chromatography -electron capture detector (GC/ECD). High correlation coefficients were obtained for esters mixture calibration lines and detection limits were found to be at the low ppb level. Repeatability was assessed and coefficients of variation varied from 10 to 20%. Reproducibility was also evaluated and coefficients of variation from 15 to 25% were obtained. Analytical results from four Portuguese ISPs showed that the mean concentration of total HAAs (THAAs) in water ranged from 10 ± 2 to 183 ± 28 µg/L in which 55 ± 20% corresponded to trichloroacetic and dichloroacetic acids (TCAA and DCAA). THAAs highest concentrations were directly related to higher ISPs' water organic matter content. In the lack of European specific regulation for water from ISPs and taking into consideration that ingestion is a form of exposure, THAAs concentration values were compared with drinking water maximum contamination level (MCL) of 60 µg/L proposed by the US EPA for the sum of five HAAs. In 35% of water sampling campaigns the sum of MBAA (monobromoacetic acid), MCAA (monochloroacetic acid), DCAA and TCAA exceeded that MCL value. The concentrations obtained for THAAs in the ISPs' atmosphere ranged from 5 ± 1 to 64 ± 10 µg/m 3 (T = 28 • C at 5 cm above the water surface) and were proportional to the aerosols' quantity, which was deeply related to indoor air ventilation system.
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