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1 <br /> considering alveolar air concentration as a dependent age and environmental air concentration. Geometric i <br /> variable, environmental level and age as covariates, mean values within each group are reported in Figure <br /> and intensity of the sport activity as a factor. The total 4. <br /> explained variance by this statistical model was 73.05% <br /> (F - 107.09, p < .001): 58.35% accounted for chloro- Discussion <br /> form in environmental air (F - 342.14, p < .001), <br /> whereas 13.13"'/n accounted for the age of the subjects Previous studies have evaluated chloroform in water <br /> and 5.1114. for the intensity of the sport activity (F = and air of indoor swimming pools and concentration in <br /> 711.20, p < .(H)1; F e 14.98, p < .001, respectively). blood samples from people attending these environ- <br /> t Analysis of variance and the Student-Neuman Keuls ments. In the present paper, chloroform in alveolar <br /> test showed a significant difference between competi- air was investigated to evaluate the feasibility of this <br /> live swimmers versus visitors (F - 10.91, p < .001). In analysis to assess exposure in indoor swimming pools <br /> Figure 3 are shown geometric means of alveolar air lev- since blood sampling is not always well accepted by <br /> els. The differences among the mean levels of chloro- healthy people. All samples of alveolar air collected af- <br /> form in each group were also confirmed when the val- ter exposure showed chloroform at different levels, <br /> Lies were adjusted for age and environmental air con- whereas it appeared in 53% of samples from nonex- <br /> centration. posed subjects and only in traces. Because exposure <br /> The competitive group was considered separately, via drinking water was excluded, chloroform levels in <br /> according to the kind of swimming but without taking alveolar air samples from exposed subjects were con- <br /> the degree of physical effort into account. The swim- sidered as resulting from indoor exposure in the swim- <br /> mers were classified into the following four groups: (1) ming pool environment where chloroform was always <br /> level I swimmers, using all styles with training suitable present at measurable levels in water and environmen- <br /> for children; (2) level If swimmers, using all styles with tal air. <br /> training suitable for teenagers; (3) finswimmers; and (4) Chloroform in alveolar air depends on the concentra- <br /> water-polo players. The main difference between levels tion in environmental air, the age of the subject, the in- <br /> I and 11 is the amount of lime spent swimming in each tensity of the sport activity, and the type of swimming. <br /> style. Analysis of covariance was performed consider- No correlation was found between alveolar air levels <br /> ing alveolar air concentration as a dependent variable, and concentration in water, although recent data in lit- <br /> environmental levels and age as covariates, and type of erature have suggested a kinetic model of dermal ab- <br /> swimming as a factor. The total explained variance was sorption in which the quantity of volatile organic con- <br /> 78.08% IF - x10.49, p < .001): 70.06% accounted for taminants that can be absorbed from immersion in <br /> chloroform in environmental air (F e 361.11, p < water is considerable, especially in younger subjects.'' <br /> .001), whereas 7.24% accounted for age (F - 37.32, p As the intensity of physical activity increases, pulmo- <br /> < .001), and 4.58"/n (F = 7.87, p < .001) for the kind of nary ventilation rate and cardiac output also increase.17 <br /> swimming. Analysis of variance and Student-Neuman Sport activity, the level of chloroform in environmental <br /> Keuls test showed significant differences between air, and the age of the subject must be accounted for <br /> Group 1 and Groups 2, 3, and 4, and between Group 3 when determining chloroform intake in indoor swim- <br /> and Group 2 (F = 15.608, p < .001). The differences ming pools. <br /> among the mean levels of chloroform in each group The analyses of samples collected only from competi- <br /> am were also confirmed when file values were adjusted for live swimmers showed differences among different pat- <br /> 900 <br /> Alveolar air(nmol/m3) Alveolar air (nmol/rO <br /> _.. _ 1400 <br /> 1200- <br /> 600 -— --------- - --- —- -- <br /> �, - -- 1000 - <br /> \ — \ 900 <br /> 400 — — — <br /> eoo <br /> 200 — - 400 <br /> 200 <br /> law :\ --- -- \ \ <br /> 0 -- o -- <br /> Visitors Beginners Competitive 1 level swim Il level swim Finswimmers Water-polo <br /> Raw gaom.mean ®Adjusted geom.mean Raw gsom.mean 11M Adjusted paom,mean <br /> rr ---- <br /> Fig. 3. Geometric mean values (raw and adiusted values) of chloro- Fig. 4. Geomelric mean values(raw and adjusted values)of chloro- <br /> a- form in alveolar air samples according to physical aclivily. form in alveolar air samples according to the kind of swimming. <br /> July/August 1993(Vol.40(No.4)) 253 <br />