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This dissertation characterizes the influences of water chemistry on the acute toxicity of lead (Pb) to two of the long-standing sentinel test organisms commonly employed by the United States Environmental Protection Agency (USEPA), the fathead minnow (Pimephales promelas) and daphnid (Ceriodaphnia dubia), for parameterization of an acute Pb Biotic Ligand Model (BLM). In addition, a toxicogenomic approach was employed to identify genes that might serve as molecular markers of Pb exposure and long-term effects, as well as provide new insights as to the underlying toxic mechanisms of chronic Pb exposure in P. promelas. The endpoints of growth, reproduction, Pb accumulation, prey capture ability, and swimming performance of P. promelas were examined to assess the influences of water chemistry during chronic Pb exposures and to potentially link microarray-identified genes to outcomes of ecological significance. Importantly, this work revealed that calcium does not protect against acute toxicity to C. dubia or chronic Pb accumulation by P. promelas, indicating that current hardness-based regulations are inappropriate and provide further support for the need for alternative approaches to setting environmental regulations for Pb. The findings reported herein should facilitate the arrival of such an approach in the form of a new acute Pb BLM. However, different responses with respect to the influences of water chemistry on the acute toxicity of Pb were exhibited by these species suggesting that development of separate BLMs for P. promelas and C. dubia should be considered to ensure adequate protection for both species. Furthermore, the influences of water chemistry were found to be inconsistent during acute and chronic Pb exposures to P. promelas and thus caution against inferring chronic effects from acute exposures. A number of Pb-responsive genes were identified that exhibited a strong potential for serving as robust indicators of Pb exposure and accumulation in P. promelas. While these genes also provided insight as to the likely toxic mechanisms of Pb, additional work will be necessary to firmly link these genes to chronic outcomes of ecological relevance in the context of ambient water chemistry.

Disinfection byproducts (DBPs), such as organic chloramines, THMs, HAAs, and nitrosamines, are formed during mandatory disinfection processes in drinking water treatment. Many of these DBPs have been shown to be potentially carcinogenic. Extensive research has been conducted on the occurrence and formation of these DBPs. However, there has been limited research on their relationships with each other, which may be important for the understanding of their formation mechanisms, and the nature of their precursors is still relatively unknown. Ultimately, this information will be key for the development of possible improvements in treatment technologies. Results of this study improve the understanding of DBP formation in swimming pool water. Some BFAs and PCP additives were identified as potential DBP precursors. Influence of BFAs and PCP additives on DBP formation in swimming pool water was also illustrated. Results provided feasible strategies to minimize DBP formation while maintaining the efficiency of disinfection.

Aerobic exercise such as cycling is known to elicit a post-exercise hypotensive (PEH) response. However, it is not known if swim exercise produces a similar effect in normotensive individuals. We tested the hypothesis that an acute bout of swimming would elicit a PEH response that is less compared to an equivalent bout of cycling. 10 trained and 11 untrained normotensive (SBP/DBP < 120/80 mmHg) individuals (23±1 years) underwent 30 min intensity-matched cycling and swimming sessions to assess changes in BP and cardiovascular responses. While PEH was similar between modalities within groups, the magnitude and temporality of change in BP following swimming was significantly different (p < 0.01) between groups, with untrained participants showing a significant PEH response. Attenuation of PEH in trained individuals was reflective of a significant increase in sympathetic outflow and slower vagal reactivation, suggesting training in an aquatic environment leads to alterations in post-exercise BP regulatory mechanisms.

Disinfection byproducts (DBPs), such as organic chloramines, THMs, HAAs, and nitrosamines, are formed during mandatory disinfection processes in drinking water treatment. Many of these DBPs have been shown to be potentially carcinogenic. Extensive research has been conducted on the occurrence and formation of these DBPs. However, there has been limited research on their relationships with each other, which may be important for the understanding of their formation mechanisms, and the nature of their precursors is still relatively unknown. Ultimately, this information will be key for the development of possible improvements in treatment technologies. Results of this study improve the understanding of DBP formation in swimming pool water. Some BFAs and PCP additives were identified as potential DBP precursors. Influence of BFAs and PCP additives on DBP formation in swimming pool water was also illustrated. Results provided feasible strategies to minimize DBP formation while maintaining the efficiency of disinfection.

Aerobic exercise such as cycling is known to elicit a post-exercise hypotensive (PEH) response. However, it is not known if swim exercise produces a similar effect in normotensive individuals. We tested the hypothesis that an acute bout of swimming would elicit a PEH response that is less compared to an equivalent bout of cycling. 10 trained and 11 untrained normotensive (SBP/DBP < 120/80 mmHg) individuals (23±1 years) underwent 30 min intensity-matched cycling and swimming sessions to assess changes in BP and cardiovascular responses. While PEH was similar between modalities within groups, the magnitude and temporality of change in BP following swimming was significantly different (p < 0.01) between groups, with untrained participants showing a significant PEH response. Attenuation of PEH in trained individuals was reflective of a significant increase in sympathetic outflow and slower vagal reactivation, suggesting training in an aquatic environment leads to alterations in post-exercise BP regulatory mechanisms.

Examination of the swimming capabilities of fish is increasingly being considered as an effective method for determining sublethal toxicity. Acute toxicant exposure is known to cause decreases in swim performance in fish but less is known about how developmental exposure can cause persistent effects that hinder swimming. In addition, little is known about how triglyceride levels fluctuate during fish swimming upon both acute and developmental exposure to toxicant. In this thesis, two studies, one acute and one developmental, were carried out using two different toxicants in order to address these issues.<p> In order to examine acute effects, adult zebrafish (Danio rerio) were exposed to ethanol vehicle or increasing concentrations of 2,4-dinitrophenol (DNP), a mitochondrial electron transport chain uncoupler, for a 24 h period. Following exposure, fish were placed in a swim tunnel for critical swimming speed (Ucrit) determination and swim motion analysis. Whole body triglyceride levels were then determined. Ucrit was decreased in a concentration dependent manner in both the 6 mg/L and 12 mg/L DNP exposure groups, with 6 mg/L DNP being considered sublethal and 12 mg/L approaching the LC50. A decrease in tail beat frequency was observed and is likely the main cause for the decrease in Ucrit in the DNP exposure groups. Triglyceride levels were elevated in a concentration dependent manner in the DNP exposure groups. This increase in triglyceride stores may be due to a behavioral adaption limiting swimming capabilities or due to a direct toxic action of DNP on lipid catabolism.<p> The second study examined whether developmental 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) exposure would cause persistent toxic effects. Zebrafish embryos were exposed to dimethyl sulfoxide control or increasing concentrations of TCDD between 2-4 days post fertilization (dpf). At 5 dpf, cytochrome P450 1A (CYP1A) activity was determined. Fish were raised to 90 dpf with mortalities and deformities being recorded at 5 dpf, 10 dpf, and 90 dpf. At 90 dpf, fish were placed in swim tunnel and Ucrit , swimming motion, and aerobic scope (oxygen consumption rate during exercise minus oxygen consumption rate during rest) were determined. Following swimming, some fish were used for whole body triglyceride analysis while others were used for histological examination. Ucrit was shown to be decreased in the two highest sublethal TCDD exposure groups (0.1 and 1 ng/L) but not in the lowest TCDD exposure group (0.01 ng/L). The exact cause of the decrease in Ucrit is not known, but may be linked to the observed decrease in dorsal aorta diameter, an inability to mobilize triglyceride stores, behavioral adaptations limiting swimming, decreased body length, or a combination of these factors. This TCDD related defect in swimming ability is not due to any increases in gross deformity or mortality rates, nor does it appear that CYP1A induction is required to mediate the toxic effects. Thus, it appears that examination of swim performance may serve as an effective measure of both sublethal acute and developmental toxicities.

Since Sweden can be considered to be a secular society it is interesting to investigate how different actors experience swimming education in the course syllabus of sports and health education, for practicing Muslim girls in middle and high schools. The investigation is based on qualitative interviews with sports teachers, practicing Muslim girls and the staff of the public swimming center in Växjö. The result shows that swimming education can be somewhat problematic, since the Muslim girls only want to attend lessons that are gender separated. In the public swimming center, there are no pools exclusively intended for women, and there are only a few times available for women every week. However, the teachers stress opportunities instead of obstacles, and the students’ experience that their teachers are trying to create possibilities for them to have a gender separated swimming education. The question of swimming education for Muslim girls is analyzed by using Berger’s theories on secularization, pluralism and privatization, as well as discussions on gender and intersectionality. The school and the public swimming center can be seen as secular arenas, which are characterized by secular values and standards. This may lead to consequences, since the swimming education is not designed according to the wishes of the practicing Muslim girls. The subject of swimming education is to some extent negotiated in society, but the swimming education is not fundamentally changing. However there are some possibilities for the Muslim girls to attend, but this may be problematic based on a gender view.

The purpose of this study was to analyze specific biomechanical and physiological variables in disabled swimmers performing a functional backcrawl. The effect of selectively placed flotation devices on the body position, exercise heart rate, and perceived exertion of the swimmer was compared to swimming with no flotation. The participants in the study included eight able-bodied males 21.5 (+2.51) yrs. and four disabled males 29.25 (+2.22) yrs. Each subject performed the backcrawl for 3 consecutive lengths of a 25 meter pool under four separate trial conditions: free swimming, swimming with the hip flotation device, the knee flotation device, and the ankle flotation device. Immediately following each trial a post-exercise heart rate was taken and the subject was asked to rate perceived exertion. Full recovery was allowed after each trial. Trials were video taped and digitized to determine the mean angles at the neck, trunk, hip, and knee during one complete stroke cycle. The investigator recognizes that this generalization presents the possibility for a bias in the data and that further study would warrant the utilization of the different phases of the stroke for determination of body angles. The results of the study demonstrated that a significant difference did exist between the disabled and able-bodied hip angle during free swimming. Within the disabled group, no significant differences were evident when comparing the body angles during free swimming to the same angles while swimming with each of the flotation devices. Correlations between heart rate and ratings of perceived exertion for all subjects (n=12) were significant in each of the four trial conditions. / School of Physical Education

Examination of the swimming capabilities of fish is increasingly being considered as an effective method for determining sublethal toxicity. Acute toxicant exposure is known to cause decreases in swim performance in fish but less is known about how developmental exposure can cause persistent effects that hinder swimming. In addition, little is known about how triglyceride levels fluctuate during fish swimming upon both acute and developmental exposure to toxicant. In this thesis, two studies, one acute and one developmental, were carried out using two different toxicants in order to address these issues.<p> In order to examine acute effects, adult zebrafish (Danio rerio) were exposed to ethanol vehicle or increasing concentrations of 2,4-dinitrophenol (DNP), a mitochondrial electron transport chain uncoupler, for a 24 h period. Following exposure, fish were placed in a swim tunnel for critical swimming speed (Ucrit) determination and swim motion analysis. Whole body triglyceride levels were then determined. Ucrit was decreased in a concentration dependent manner in both the 6 mg/L and 12 mg/L DNP exposure groups, with 6 mg/L DNP being considered sublethal and 12 mg/L approaching the LC50. A decrease in tail beat frequency was observed and is likely the main cause for the decrease in Ucrit in the DNP exposure groups. Triglyceride levels were elevated in a concentration dependent manner in the DNP exposure groups. This increase in triglyceride stores may be due to a behavioral adaption limiting swimming capabilities or due to a direct toxic action of DNP on lipid catabolism.<p> The second study examined whether developmental 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) exposure would cause persistent toxic effects. Zebrafish embryos were exposed to dimethyl sulfoxide control or increasing concentrations of TCDD between 2-4 days post fertilization (dpf). At 5 dpf, cytochrome P450 1A (CYP1A) activity was determined. Fish were raised to 90 dpf with mortalities and deformities being recorded at 5 dpf, 10 dpf, and 90 dpf. At 90 dpf, fish were placed in swim tunnel and Ucrit , swimming motion, and aerobic scope (oxygen consumption rate during exercise minus oxygen consumption rate during rest) were determined. Following swimming, some fish were used for whole body triglyceride analysis while others were used for histological examination. Ucrit was shown to be decreased in the two highest sublethal TCDD exposure groups (0.1 and 1 ng/L) but not in the lowest TCDD exposure group (0.01 ng/L). The exact cause of the decrease in Ucrit is not known, but may be linked to the observed decrease in dorsal aorta diameter, an inability to mobilize triglyceride stores, behavioral adaptations limiting swimming, decreased body length, or a combination of these factors. This TCDD related defect in swimming ability is not due to any increases in gross deformity or mortality rates, nor does it appear that CYP1A induction is required to mediate the toxic effects. Thus, it appears that examination of swim performance may serve as an effective measure of both sublethal acute and developmental toxicities.