Respiration rates of ectothermic organisms are affected by environmental temperatures, and sustainable metabolism at high temperatures sometimes limits heat tolerance. Organisms are hypothesized to exhibit acclimatory metabolic compensation effects, decelerating their metabolic processes below Arrhenius expectations based on temperature alone. We tested the hypothesis that either heritable or plastic heat tolerance differences can be explained by metabolic compensation in the eurythermal freshwater zooplankton crustacean Daphnia magna. We measured respiration rates in a ramp-up experiment over a range of assay temperatures (5-37°C) in eight genotypes of D. magna representing a range of previously reported acute heat tolerances and, at a narrower range of temperatures (10-35°C), in D. magna with different acclimation history (either 10 or 25°C). We discovered no difference in temperature-specific respiration rates between heat-tolerant and heat-sensitive genotypes. In contrast, we observed acclimationspecific compensatory differences in respiration rates at both extremes of the temperature range studied. Notably, there was a deceleration of oxygen consumption at higher temperature in 25°Cacclimated D. magna relative to their 10°C-acclimated counterparts, observed in active animals, a pattern corroborated by similar changes in filtering rate and, partly, by changes in mitochondrial membrane potential. A recovery experiment indicated that the reduction of respiration was not caused by irreversible damage during exposure to a sublethal temperature. Response time necessary to acquire the respiratory adjustment to high temperature was lower than for low temperature, indicating that metabolic compensation at lower temperatures requires slower, possibly structural changes.

Thèse numérisée par la Direction des bibliothèques de l'Université de Montréal.

Metacommunity ecology explicitly incorporates processes at multiple spatial scales to explain the assembly and dynamics of a community. In a metacommunity, local communities interact with one another through the dispersal of individuals across a region. As such, metacommunities are molded by two sets of processes: local and regional. Local factors are those that directly impact a single local community, such as environmental conditions, competition, and predation. On the other hand, regional factors affect communities across a landscape and include mechanisms such as, immigration and emigration. The potential interactions between local and regional factors make metacommunity dynamics a unique body of theory when compared to classic community theory. However, while the direct influence of dispersal on metacommunity dynamics continues to be a well-researched topic, how dispersal interacts with local factors to shape metacommunity dynamics is a more open topic. In particular, one continuing gap in my knowledge is how dispersal interacts with biotic effect how it may affect metacommunities. One type of local biotic process that can directly affect communities is a strong interactive species, i.e., a species that affects community structure and diversity, and to the best of my knowledge, the interaction between dispersal and strongly interactive species has not been directly addressed experimentally. In the following study, I investigated the interaction of dispersal and a strong interactive species on metacommunity diversity and assembly. I chose Daphnia magna as my strong interacting species due to its biological and physical traits. Dispersal is known to create predictable patterns of diversity as it increases in a metacommunity. We made logical predictions based off of my knowledge of these patterns, and my inclinations regarding how dispersal would interact with a strong interacting species. The following predictions were made in relation to the control: 1) Alpha diversity would be the highest during low dispersal as new species would be introduced and maintained above the extinction threshold. I also predicted beta diversity would decrease with increased dispersal due to the homogenization of communities. 2) In the presence of D. magna, beta diversity would only increase during low dispersal due to possible rescue effects. 3) Temporal variability would decrease for the low dispersal treatment and increase for the high dispersal treatment in the absence of D. magna. 4) Temporal variability would overall increase across all treatments in the presence of D. magna. To carry out the study, I assembled outdoor mesocosms using a 2x3x3x4 factorial design (Daphnia Treatment: no addition of D. magna, addition of D. magna; Dispersal Treatment: no dispersal, low dispersal, high dispersal; three buckets were equivalent to one metacommunity; 4 replicates). There was a significant interaction between D. magna and dispersal. Over time, beta diversity decreased as communities became homogenized; however, the no dispersal treatment homogenized at a slower rate compared to the other treatments. In addition, D. magna appeared to create local selection for certain taxa resulting in the increase of Bosmina and Simocephalus while other taxa decreased, for example Streblocerus. This trend was likely due to the feeding and grazing habits of D. magna which is known to outcompete other large zooplankton for larger phytoplankton taxa. Lastly, D. magna directly influenced temporal variability of metacommunities in the experiment. In particular, the low dispersal treatment increased in temporal variability in the presence of D. magna. Again, this result could likely be attributed to D. magna effects selecting for certain taxa, or by the re-introduction of new or dying species with each dispersal through rescue effects. Overall, the results in my study supported majority of my predictions. It is clear that D. magna had an effect on communities as taxa abundances increased and beta diversity in the no dispersal treatment did not decrease as quickly. This result suggests that the introduction of D. magna as an invasive to non-local waters could pose a threat to local community dynamics. It is important to understand how a strong interactive species can affect communities across a landscape as they can greatly alter diversity and composition. Future studies should focus on expanding the dispersal gradient and incorporating a local strong interactive species and non-local strong interactive species to understand how they may change community dynamics. / Master of Science

Three suspended solids types containing a range of physicochemical characteristics were used to determine the effect of suspended solids on the bioavailability of acenaphthene, 1,2,4,5-tetrachlorobenzene, zinc, and chlordane to Daphnia magna and Pimephales promelas. Generally, the bioavailability of zinc and chlordane decreased due to interactions with all suspended solids types while bioavailability of acenaphthene and 1,2,4,5-tetrachlorobenzene were not clearly reduced. Partition coefficients and slope of dose-response curves related chemical characteristics and organism sensitivity, respectively, to experimentally determined results. It is believed that the biologically available form of these chemicals to Daphnia magna and Pimephales promelas resides in the aqueous phase.

The aim of this diploma thesis is to explore the coagulation phase in water treatment process from two perspectives, the removal of cyanotoxin microcystin and the responses of ecotoxicological indicator species Daphnia magna to different concentration of this toxin, contained in a sample of cyanobacterial water bloom, which was extracted from a dam and was dominated by cyanobacteria Microcystis aeruginosa. The sample was administered in three environmentally relevant concentrations to 6 clones of Daphnia magna, 3 of which had previous experience with M. aeruginosa. Coagulation process was performed under optimal conditions: pH = 6.36; KNK4,5 = 0.26 mmol.l-1 ; Fe = 0.162 mg.l-1 ; DOC = 2.83 mg.l-1 using 10 ml of 0.125M NaHCO3 in two litres of ultrapure water. Individual forms of microcystin were detected in this ratio: 31.6 % MC-LR, 53.6 % MC-RR and 14.8 % MC-YR. The study has shown that under these conditions coagulation does not remove microcystin, e.g. the efficiency of the process is zero. In ecotoxicological study, with growing concentration of cyanobacterial mixture the negative impact on Daphnia magna increased. We have found interclonal variability in responses of D. magna, however, the previous experience with M. aeruginosa had no effect. With growing concentration of cyanobacterial water...

Multi-walled carbon nanotube aggregates can be suspended in the aqueous phase by natural organic matter. These aggregates are ingested by filter feeding zooplankton. Ingested aggregates result in decreased growth and decreased reproduction. These effects may be caused by reduction in energy input from normal feeding behavior. pH alters natural organic matter structure through changes in electrostatic repulsion. Altered natural organic matter structure changes multi-walled carbon nanotube aggregate size. This size variation with variation in pH is significant, but not large enough a change in size to alter toxicity, as the aggregate size range remains well within the particle size selection of the organisms.

Alquilbenzeno Linear Sulfonado (LAS) é o surfactante aniônico mais utilizado no mundo e é encontrado constantemente em esgoto doméstico e águas residuárias de lavanderia. A remoção de LAS em reatores foi comprovada em estudos anteriores, mas pouco se sabe sobre a toxicidade desse composto em amostras mais complexas para a biota aquática. Neste trabalho, objetivou-se avaliar duas Hipóteses; A: O LAS padrão causa efeitos negativos na biota aquática, e B: O tratamento em reator de leito fluidificado de amostra complexa contendo LAS (água residuária de lavanderia comercial combinada com esgoto doméstico bruto) diminui os efeitos negativos na biota aquática. Ambas as hipóteses foram avaliadas por meio de bioensaios de toxicidade com: Chironomus sancticaroli, Allonais inaequalis e Daphnia magna, analisados a partir da mortalidade dos organismos e análises estatísticas, para determinar os efeitos tóxicos dos LAS padrão e das amostras do reator, comparados ao controle. Para avaliar a Hipótese A foram realizados testes de toxicidade aguda, crônica e crônica de gerações com o LAS padrão. No teste de toxicidade crônica de gerações, com a espécie C. sancticaroli, foram analisados a deformidade bucal, comprimento das larvas, tamanho das asas das fêmeas e fecundidade potencial com o LAS padrão em 3 gerações. Para responder a Hipótese B, foram realizados bioensaios de toxicidade aguda e crônica com os afluentes, efluentes e diluições dos efluentes nas seis fases de operação do reator. C. sancticaroli foi a espécie mais tolerante tanto em teste de toxicidade aguda como crônica com LAS padrão (CL50-96h 25,25 mg.L-1 e CL50-10dias 18,11 mg.L-1), seguido de A. inaequalis (CL50-96h 8,13 mg.L-1 e CL50-10dias 8,56 mg.L-1). A espécie mais sensível ao LAS foi D. magna (CE50-48h 6,11mg.L-1 e CE50-21dias 3,21 mg.L-1). No teste de toxicidade crônica de longa duração, não existiu diferença estatística entre as gerações para o desenvolvimento das larvas do inseto C. sancticaroli, entretanto evidenciaram diferença estatística entre as gerações quanto ao tamanho das asas das fêmeas, indicando que esses organismos podem sofrer alterações fisiológicas quando a exposição ao contaminante é contínua, confirmando a Hipótese A. Os resultados ecotoxicológicos com o reator evidenciaram toxicidade de 100% de todos afluentes e efluentes para A. inaequalis e D. magna. Já C. sancticaroli apresentou menor toxicidade nas primeiras fases de operação (de 20 a 100% de mortalidade). Em geral, foi identificado diferença de toxicidade das fases do reator por meio das diluições. Nas fases menos tóxicas, a diminuição da mortalidade era observada a partir de diluição de 50%; nas fases mais tóxicas, a partir de 20%. É possível concluir que a Fase VIb de operação do reator apresentou diminuição da toxicidade. Entretanto, ao se analisar testes de toxicidade crônica nessa fase, conclui-se que o efluente mesmo depois do tratamento em reator causa efeito negativo nos organismos-teste avaliados, dessa forma é possível refutar a Hipótese B. A partir dos resultados apresentados, é possível concluir que o LAS causa impacto ambiental, principalmente em exposição continua, e que mesmo com remoção em sistema biológico de efluentes reais (água residuária de lavanderia comercial combinada com esgoto doméstico) existe impacto, possivelmente com a interação entre os diversos compostos tóxicos e o LAS. / Linear Alkylbenzene Sulfonate (LAS) is the most commonly utilized anionic surfactant in the world and it is present in domestic sewage and laundry wastewater. Removal of LAS in reactors has been proven in previous studies, but little is known about the toxicity to the aquatic biota. The objectives of this study were tested into two Hypotheses, A: The standard surfactant LAS causes negative effects on aquatic biota, and B: Treatment in complex sample fluidized bed reactor containing LAS (commercial laundry wastewater combined with raw domestic sewage) diminishes the negative effects on aquatic biota. Both Hypotheses were evaluated toxicity bioassays using three test organisms: Chironomus sancticaroli, Allonais inaequalis and Daphnia magna. To evaluate the Hypothesis A, acute, chronic and long-term chronic toxicity tests were performed with standard LAS. In the long-term chronic tests with C. sancticaroli organisms, we analyzed the oral deformity, larval length, female wing size and potential fecundity in contact with the standard LAS in 3 generations. Acute and chronic bioassays with affluents, effluents and effluent dilutions in the VI operating phases of the fluidized bed reactor were proceeded to evaluate the Hypothesis B. The results were analyzed from the mortality of the organisms, and statistical analysis were performed to determine the similarity of the toxic effects of the LAS and reactor samples, compared to the control. The species C. sancticaroli was the most tolerant species in both acute and chronic trials with standard LAS (LC50-96h 25.25 mg.L-1 and LC50- 10 days 18.11 mg.L-1), followed by species of A. inaequalis (LC50-96h 8.13 mg.L-1 and LC50-10 days 8.56 mg.L-1). The species most sensitive to LAS was D. magna (CE50-48h 6.11mg.L-1 and CE50-21dias 3.21mg.L-1). In the long-term chronic test, there is no statistical difference between the generations for the development of C. sancticaroli insect larvae. However, they showed a statistical difference between the generations regarding the size of the female wings, indicating that these organisms may undergo physiological changes when exposure to the contaminant is continuous. From these results it is possible to confirm Hypothesis A. The ecotoxicological results with the reactor showed toxicity of 100% of all tributaries and effluents for A. inaequalis and D. magna. The C. sancticaroli species had low toxicity in the first stages of operation (from 20 to 100% mortality). In general, toxicity difference of the reactor phases was identified by half of the dilution analysis. In the less toxic phases, the decrease in mortality was observed from 50% dilution; in the most toxic phases, from 20%. It is also possible to conclude that Phase VIb showed a decrease in the mortality of the test organisms where a chronic test was performed. However, when analyzing the chronic tests, it can be concluded that the effluent even after the treatment in the reactor causes a negative effect on the test organisms evaluated, so it is possible to refute the Hypothesis B. From the results presented, it is possible to conclude that the LAS causes environmental impact, mainly in continuous exposure, and that even with treatment of actual effluents (commercial laundry wastewater combined with domestic sewage) there is an impact, possibly with the interaction between the various toxic compounds and the LAS.

No presente estudo, a capacidade da zeólita sintetizada a partir de cinzas de carvão na remoção do corante remazol vermelho RB de solução aquosa foi investigada por meio de processo descontínuo. O equilíbrio foi alcançado após 360 min de tempo de contato. A velocidade de adsorção seguiu o modelo cinético de pseudo-segunda-ordem. Os dados de equilíbrio obtidos se ajustaram à isoterma de adsorção de Langmuir apresentando capacidade de adsorção máxima de 1,20 mg g-1. A eficiência de adsorção estava entre 75 a 91 % no tempo de equilíbrio. Visando obter as melhores condições de remoção do corante, verificou-se a influência dos seguintes parâmetros: concentração inicial do corante, pH da solução aquosa, dose do adsorvente e temperatura. Os parâmetros termodinâmicos foram avaliados indicando que o processo de adsorção do remazol vermelho sobre a zeólita é de natureza espontânea. Experimentos adicionando-se NaCl e Na2SO4 foram realizados com o objetivo de simular as reais condições dos efluentes de banhos de tingimento e avaliar a influência destes compostos quimicos no fenômeno de adsorção. Os dados de equilíbrio de adsorção do remazol vermelho sobre a zeólita foram alcançados em um tempo menor na presença de concentrações crescentes dos sais em solução e houve um aumento na capacidade de adsorção. A eficiência do estudo como tratamento foi avaliada quanto à toxicidade aguda utilizando o microcrustáceo Daphnia similis. / In this study, the capacity of zeolite synthesized from coal ash in the removal of Remazol Red dye aqueous solution was investigated by batch mode operation. The equilibrium was attained after 360 min of contact time. The adsorption rate followed the kinetic model of pseudo-second-order. The equilibrium data obtained fitted to Langmuir adsorption isotherm showing the adsorption capacity of up to 1.20mg g-1. The efficiency of adsorption was between 75 to 91% in the equilibrium time. In order to obtain the best conditions for removal of this dye, the influence of the following parameters was: initial concentration of the dye, pH of the aqueous solution, dose of adsorbent and temperature. The thermodynamic parameters were evaluated showing that the adsorption of Remazol red on the zeolite is of a spontaneous nature. Experiments by adding NaCl and Na2SO4 were carried out to simulate the real conditions of the effluents from the dyeing bath and to evaluate the influence of these chemical compounds in the phenomenon of adsorption. The equilibrium data of adsorption of Remazol red on the zeolite was achieved in a shorter time in the presence of increasing concentrations of salts in solution and an increase in adsorption capacity. The efficiency of the study was evaluated as a treatment for acute toxicity using Daphnia similis microcrustacean.

No presente estudo, a capacidade da zeólita sintetizada a partir de cinzas de carvão na remoção do corante remazol vermelho RB de solução aquosa foi investigada por meio de processo descontínuo. O equilíbrio foi alcançado após 360 min de tempo de contato. A velocidade de adsorção seguiu o modelo cinético de pseudo-segunda-ordem. Os dados de equilíbrio obtidos se ajustaram à isoterma de adsorção de Langmuir apresentando capacidade de adsorção máxima de 1,20 mg g-1. A eficiência de adsorção estava entre 75 a 91 % no tempo de equilíbrio. Visando obter as melhores condições de remoção do corante, verificou-se a influência dos seguintes parâmetros: concentração inicial do corante, pH da solução aquosa, dose do adsorvente e temperatura. Os parâmetros termodinâmicos foram avaliados indicando que o processo de adsorção do remazol vermelho sobre a zeólita é de natureza espontânea. Experimentos adicionando-se NaCl e Na2SO4 foram realizados com o objetivo de simular as reais condições dos efluentes de banhos de tingimento e avaliar a influência destes compostos quimicos no fenômeno de adsorção. Os dados de equilíbrio de adsorção do remazol vermelho sobre a zeólita foram alcançados em um tempo menor na presença de concentrações crescentes dos sais em solução e houve um aumento na capacidade de adsorção. A eficiência do estudo como tratamento foi avaliada quanto à toxicidade aguda utilizando o microcrustáceo Daphnia similis. / In this study, the capacity of zeolite synthesized from coal ash in the removal of Remazol Red dye aqueous solution was investigated by batch mode operation. The equilibrium was attained after 360 min of contact time. The adsorption rate followed the kinetic model of pseudo-second-order. The equilibrium data obtained fitted to Langmuir adsorption isotherm showing the adsorption capacity of up to 1.20mg g-1. The efficiency of adsorption was between 75 to 91% in the equilibrium time. In order to obtain the best conditions for removal of this dye, the influence of the following parameters was: initial concentration of the dye, pH of the aqueous solution, dose of adsorbent and temperature. The thermodynamic parameters were evaluated showing that the adsorption of Remazol red on the zeolite is of a spontaneous nature. Experiments by adding NaCl and Na2SO4 were carried out to simulate the real conditions of the effluents from the dyeing bath and to evaluate the influence of these chemical compounds in the phenomenon of adsorption. The equilibrium data of adsorption of Remazol red on the zeolite was achieved in a shorter time in the presence of increasing concentrations of salts in solution and an increase in adsorption capacity. The efficiency of the study was evaluated as a treatment for acute toxicity using Daphnia similis microcrustacean.

Hybridizing species of the Daphnia longispina complex are key taxa in plankton communities of many European lakes. In several of these lakes, it has been documented that the taxonomic structure of the complex during the 20th century has substantially changed following human-mediated environmental changes, particularly eutrophication and re-oligotrophication and fish stock changes. We characterize these changes in Lago Maggiore (Italy/Switzerland), a southern pre-alpine lake, which also passed through the human-mediated environmental changes. Lago Maggiore is one of best and longest studied European lakes so a large number of historical Daphnia samples from regular monitoring are available. Because local Daphnia do not form dormant egg banks suitable for genetic analysis (being able to overwinter in the water column), we used a combination of morphology and geometric morphometrics (elliptic Fourier analysis) to evaluate the taxonomic and phenotypic changes in the Daphnia longispina complex in Lago Maggiore since the mid-20th century (1948-2012), and attampted to characterize the impact of environmental changes over the respective period on Daphnia body shape and size. Examination of Daphnia phenotype indicates indeed the prevailing presence of D. longispina (hyalina morph) in the 1940s, dominance of...