It is impossible to remove methylmercury (MeHg) from biological systems because MeHg is found throughout our environment in many fresh and salt water fish. The consumption of fish is important to human nutrition and health. The mechanism of MeHg neurotoxicity must be understood to minimize adverse exposure consequences. The dissertation objective was to: 1) compare mechanisms of MeHg neurotoxicity between animals exposed as adults and those exposed during gestation, and 2) develop an in vitro test model of in vivo MeHg exposure. Total mercury (Hg) levels in tissue / cells were determined by combustion / trapping / atomic absorption. Cell death was determined by Fluoro-Jade histochemical staining and activated caspase 3 immunohistochemistry for in vivo studies, and Trypan blue exclusion, lactate dehydrogenase activity, and cytotoxicity assays for in vitro studies. Mitochondrial membrane potential (MMP), intracellular calcium ion concentration ([Ca2+]i), and production of reactive oxygen species (ROS) were determined using fluorescence microscopy or microplate reader assays. Young adult C57Bl/6 mice were exposed to a total dose of 0, 1.0, or 5.0 mg/kg body weight MeHg divided over postnatal days (P)35 to 39. Pregnant female mice were exposed to a total does of 0, 0.1, or 1.0 mg/kg body weight MeHg divided over gestational days (G)8 to 18. SY5Y cells were exposed to 0, 0.01, 0.1, or 1.0 ?M MeHg or HgCl2 for 24, 48, or 72 hours. Total Hg in brains of young adult mice, mouse pups, and SY5Y cells accumulated in a dose-dependent manner. Cell death increased in SY5Y cells exposed to the highest concentrations of MeHg and HgCl2 used in this study. Cell death increased in the molecular and granule cerebellar cell layers of young adult mice exposed to the highest doses of MeHg used in this study. P0 mouse pups showed no increase in cell death within the cerebellum following MeHg exposure. Cerebella of mice at P10 exhibited decreased dying cells only in the external germinal layer. Low concentrations of MeHg affected MMP in both in vivo and in vitro studies, but did not result in decreased MMP typically associated with higher MeHg concentrations. [Ca2+]i was increased throughout the in vivo experiments in an age- , sexand brain region-dependent manner. Generation of ROS was decreased in both in vivo and in vitro studies with both the MeHg and HgCl2 (in vitro) treatments. In summary, low and moderate MeHg exposure, both in vivo and in vitro, altered mitochondrial function, Ca2+ homeostasis, and ROS differently than what is reported in the literature for higher MeHg exposure concentrations. SY5Y cells were sensitive to low-levels of MeHg and HgCl2 and responded similarly to cells in the whole animal studies, thus making SY5Y cells realistic candidates for mechanistic MeHg studies. Cell culture and whole animal neuronal functional studies at chronic low-level MeHg exposure are limited. These data suggest that low-levels of MeHg may affect neuronal function. Therefore, further chronic low-level MeHg neuronal functional studies are warranted.

Coordenação de Aperfeiçoamento de Pessoal de Nível Superior / Mercury is an environmental contaminant, and may accumulate in living organisms causing several damage. Studies have shown that this metal causes several physiological and biochemical alterations in young rats which are prevented by zinc. Thus, this work investigated the in vivo and in vitro effects of HgCl2 and ZnCl2 on alanine aminotransferase (ALT), lactate dehydrogenase (LDH) and glucose 6-phosphatase (G6Pase) activities from liver and kidney of young rats to verify if the physiological and biochemical alterations induced by mercury, and prevented by zinc, are related to hepatic and renal metabolism. Glycemia and tissue glycogen levels (liver, kidney and muscle) were also monitored. Wistar rats were treated (s.c.) with saline or ZnCl2 (27 mg/kg/day) and with saline or HgCl2 (5.0 mg/kg/day) from 3rd to 7th and 8th to 12th days of age, respectively. Pups were sacrificed 24h after the last dose and samples were collected (blood, liver, kidney and muscle). For in vitro experimentation, the samples were collected similarly, with rats of 10 to 13 days old. Regarding in vivo experiments, the mercury treated rats presented an increase around 6 folds of the hepatic ALT activity, without alteration of renal ALT and hepatic LDH activities. Still, the mercury exposure significantly increases in 75% the G6Pase activity. The other parameters, glucose and glycogen, were not altered. The pre-exposure to zinc prevented totally the increase of liver ALT activity and partly the increase of hepatic G6Pase activity induced by mercury. In vitro results revealed that the serum and liver ALT and liver and kidney G6Pase activities were inhibited by mercury. The inhibitory effect may be related to chemical modification of sulfhydryl group of cysteine, since the mercury has great affinity for these groups, which contributes to its toxicity. Zinc inhibited liver and serum ALT activities in concentration of 100 μM. These results show that mercury induces distinct alterations in these enzymes when tested in vivo or in vitro, as well as when different sources of enzyme were used, hepatic and renal. The increased hepatic ALT and G6Pase activities suggest that animals exposed to mercury have an increased gluconeogenic activity in this tissue. Zinc prevents the in vivo effects of mercury on metabolic changes, confirming its important preventive role. / O mercúrio é um elemento tóxico, podendo acumular-se em organismos vivos causando-lhes vários danos. Estudos têm demonstrado que esse metal é capaz de causar várias alterações fisiológicas e bioquímicas em ratos jovens, as quais são prevenidas pela pré-exposição ao zinco. Assim, este trabalho investigou os efeitos in vivo e in vitro do HgCl2 e ZnCl2 sobre as atividades das enzimas alanina aminotransferase (ALT), lactato desidrogenase (LDH) e glicose 6-fosfatase (G6Pase) de fígado e rim de ratos jovens para verificar se as alterações fisiológicas e bioquímicas induzidas pelo mercúrio e impedidas pelo zinco, estão relacionados ao metabolismo hepático e renal. Os níveis glicêmicos e do glicogênio tecidual (fígado, rim e músculo) também foram monitorados. Ratos Wistar com três dias de idade foram tratados (s.c.) com salina ou ZnCl2 (27 mg/kg/dia) durante cinco dias consecutivos (do 3 o ao 7 o dia de idade) e com salina ou HgCl2 (5 mg/kg/dia) por mais cinco dias (do 8 o ao 12 o dia de idade). Os animais foram sacrificados 24 horas após a última dose e as amostras foram coletadas (sangue, fígado, rim e músculo). Para realização dos experimentos in vitro, amostras foram coletadas de maneira similar, com ratos de 10-13 dias de idade. Com relação aos experimentos in vivo, os ratos tratados com mercúrio apresentaram um aumento da atividade da ALT hepática de aproximadamente seis vezes, sem alteração da atividade da ALT renal e LDH hepática. Ainda, a exposição ao mercúrio aumentou significativamente a atividade da G6Pase em 75%. Os outros dois parâmetros, glicose e glicogênio, não foram alterados. A pré-exposição ao zinco preveniu a alteração da atividade da ALT e parcialmente a alteração da atividade da G6Pase hepática induzida pelo mercúrio. Os resultados in vitro demonstraram que as enzimas ALT e LDH sérica e hepática e G6Pase hepática e renal foram inibidas por mercúrio. O efeito inibitório pode estar relacionado às modificações químicas de grupos sulfidrílicos da cisteína, uma vez que o mercúrio tem grande afinidade por esses grupos, o que contribui para a sua toxicidade. O zinco inibiu a atividade da ALT hepática e sérica na concentração de 100 μM. Estes resultados mostram que o mercúrio induziu alterações distintas sobre essas enzimas quando testado in vivo e in vitro, bem como quando testado em enzimas provenientes de diferentes fontes, hepática e renal. O aumento da atividade das enzimas ALT e G6Pase de fígado sugerem que os animais expostos ao mercúrio apresentam um aumento da atividade gliconeogênica. O zinco previne os efeitos in vivo do mercúrio sobre as alterações metabólicas, confirmando seu papel protetor.

The goal of this project was to develop novel bacterial biomarkers for use in an industrial context. These biomarkers would be used to determine aluminium industry activity impact on a local ecosystem. Sediment bacterial communities of the Saguenay River are subjected to industrial effluent produced by industry in Jonquière, QC. In-situ responses of these communities to effluent exposure were measured and evaluated as potential biomarker candidates for exposure to past and present effluent discharge. Bacterial community structure and composition between control and affected sites were investigated. Differences observed between the communities were used as indicators of a response to industrial activity through exposure to effluent by-products. Diversity indices were not significantly different between sites with increased effluent exposure. However, differences were observed with the inclusion of algae and cyanobacteria. UniFrac analyses indicated that a control (NNB) and an affected site (Site 2) were more similar to one another with regard to community structure than either was to a medially affected site (Site 5) (Figure 2.4). We did not observe a signature of the microbial community structure that could be predicted with effluent exposure. Microbial community function in relation to bacterial mercury resistance (HgR) was also evaluated as a specific response to the mercury component present in sediments. Novel PCR primers and amplification conditions were developed to amplify merP, merT and merA genes belonging to the mer-operon which confers HgR (Table 5.6). To our knowledge, the roles of merP and merT have not been explored as possible tools to confirm the presence of the operon. HgR gene abundance in sediment microbial communities was significantly correlated (p < 0.05) to total mercury levels (Figure 3.4) but gene expression was not measurable. We could not solely attribute the release of Hg0 from sediments in bioreactor experiments to a biogenic origin. However, there was a 1000 fold difference in measured Hg0 release between control and affected sites suggesting that processes of natural remediation may be taking place at contaminated sites (Figure 3.7). Abundance measurements of HgR related genes represent a strong response target to the mercury immobilized in sediments. Biomarkers built on this response can be used by industry to measure long term effects of industrially derived mercury on local ecosystems. The abundance of mer-operon genes in affected sites indicates the presence of a thriving bacterial community harbouring HgR potential. These communities have the capacity to naturally remediate the sites they occupy. This remediation could be further investigated. Additional studies will be required to develop biomarkers that are more responsive to contemporary industrial activity such as those based on the integrative oxidative stress response.

The goal of this project was to develop novel bacterial biomarkers for use in an industrial context. These biomarkers would be used to determine aluminium industry activity impact on a local ecosystem. Sediment bacterial communities of the Saguenay River are subjected to industrial effluent produced by industry in Jonquière, QC. In-situ responses of these communities to effluent exposure were measured and evaluated as potential biomarker candidates for exposure to past and present effluent discharge. Bacterial community structure and composition between control and affected sites were investigated. Differences observed between the communities were used as indicators of a response to industrial activity through exposure to effluent by-products. Diversity indices were not significantly different between sites with increased effluent exposure. However, differences were observed with the inclusion of algae and cyanobacteria. UniFrac analyses indicated that a control (NNB) and an affected site (Site 2) were more similar to one another with regard to community structure than either was to a medially affected site (Site 5) (Figure 2.4). We did not observe a signature of the microbial community structure that could be predicted with effluent exposure. Microbial community function in relation to bacterial mercury resistance (HgR) was also evaluated as a specific response to the mercury component present in sediments. Novel PCR primers and amplification conditions were developed to amplify merP, merT and merA genes belonging to the mer-operon which confers HgR (Table 5.6). To our knowledge, the roles of merP and merT have not been explored as possible tools to confirm the presence of the operon. HgR gene abundance in sediment microbial communities was significantly correlated (p < 0.05) to total mercury levels (Figure 3.4) but gene expression was not measurable. We could not solely attribute the release of Hg0 from sediments in bioreactor experiments to a biogenic origin. However, there was a 1000 fold difference in measured Hg0 release between control and affected sites suggesting that processes of natural remediation may be taking place at contaminated sites (Figure 3.7). Abundance measurements of HgR related genes represent a strong response target to the mercury immobilized in sediments. Biomarkers built on this response can be used by industry to measure long term effects of industrially derived mercury on local ecosystems. The abundance of mer-operon genes in affected sites indicates the presence of a thriving bacterial community harbouring HgR potential. These communities have the capacity to naturally remediate the sites they occupy. This remediation could be further investigated. Additional studies will be required to develop biomarkers that are more responsive to contemporary industrial activity such as those based on the integrative oxidative stress response.

The goal of this project was to develop novel bacterial biomarkers for use in an industrial context. These biomarkers would be used to determine aluminium industry activity impact on a local ecosystem. Sediment bacterial communities of the Saguenay River are subjected to industrial effluent produced by industry in Jonquière, QC. In-situ responses of these communities to effluent exposure were measured and evaluated as potential biomarker candidates for exposure to past and present effluent discharge. Bacterial community structure and composition between control and affected sites were investigated. Differences observed between the communities were used as indicators of a response to industrial activity through exposure to effluent by-products. Diversity indices were not significantly different between sites with increased effluent exposure. However, differences were observed with the inclusion of algae and cyanobacteria. UniFrac analyses indicated that a control (NNB) and an affected site (Site 2) were more similar to one another with regard to community structure than either was to a medially affected site (Site 5) (Figure 2.4). We did not observe a signature of the microbial community structure that could be predicted with effluent exposure. Microbial community function in relation to bacterial mercury resistance (HgR) was also evaluated as a specific response to the mercury component present in sediments. Novel PCR primers and amplification conditions were developed to amplify merP, merT and merA genes belonging to the mer-operon which confers HgR (Table 5.6). To our knowledge, the roles of merP and merT have not been explored as possible tools to confirm the presence of the operon. HgR gene abundance in sediment microbial communities was significantly correlated (p < 0.05) to total mercury levels (Figure 3.4) but gene expression was not measurable. We could not solely attribute the release of Hg0 from sediments in bioreactor experiments to a biogenic origin. However, there was a 1000 fold difference in measured Hg0 release between control and affected sites suggesting that processes of natural remediation may be taking place at contaminated sites (Figure 3.7). Abundance measurements of HgR related genes represent a strong response target to the mercury immobilized in sediments. Biomarkers built on this response can be used by industry to measure long term effects of industrially derived mercury on local ecosystems. The abundance of mer-operon genes in affected sites indicates the presence of a thriving bacterial community harbouring HgR potential. These communities have the capacity to naturally remediate the sites they occupy. This remediation could be further investigated. Additional studies will be required to develop biomarkers that are more responsive to contemporary industrial activity such as those based on the integrative oxidative stress response.