Anatoxin-a (ANTX) is a neurotoxin produced by several freshwater cyanobacteria and has been implicated in the death of livestock and domestic animals from consumption of tainted surface waters. ANTX is unstable under normal conditions and is somewhat problematic to extract and study. Accelerated solvent extraction (ASE) combined with liquid chromatography-mass spectrometry (LC/MS) was used to develop an efficient extraction and analytical method for both ANTX and the more commonly encountered hepatotoxic microcystins produced by cyanobacteria. The effects of nitrogen supply on the cellular production and release of ANTX was investigated in Aphanizomenon issatschenkoi (Ussaczew) Proschkina-Lavrenko (Nostocales). In contrast to the predictions of the carbonnutrient balance hypothesis, the maximum production was observed under moderate N stress. In addition, steady state fugacity-based models were employed to investigate ANTX’s distribution and fate in freshwater ecosytems. ANTX was not found to be very persistent in aquatic ecosystems and did not appear to bioaccumulate in fish, at least not from the dissolved phase.

No description available.

Cyanobacteria can form nuisance proliferations and produce large concentrations of toxins that pose a health hazard. This thesis investigates cyanotoxin production by New Zealand benthic cyanobacteria. Cyanobacteria were sampled from lakes, reservoirs, streams, and rivers. Thirty-five strains were isolated into culture and screened for genes involved in the biosynthesis of common cyanotoxins. Positive results were confirmed and cyanotoxin concentrations quantified using analytical chemistry techniques. Genes involved in anatoxin a/homoanatoxin a biosynthesis were detected in nine out of ten Phormidium cf. uncinatum strains isolated from a single mat. Anatoxin a was confirmed in these strains by LC–MS/MS at concentrations from 0.3 to 6.4 mg kg⁻¹. One strain also produced homoanatoxin-a. Anatoxin-a variation between strains may explain the wide range in anatoxin a concentrations previously observed in New Zealand. The sxtA gene involved in saxitoxin biosynthesis was identified in Scytonema cf. crispum strains. Saxitoxin was confirmed in strains and environmental samples by Jellett PSP Rapid Test and HPLC–FD. Gonyautoxins, neosaxitoxin, and decarbamoyl derivatives were also detected. This study is the first identification of these compounds in Scytonema and in New Zealand cyanobacterial strains. These strains were isolated from recreational and pre-treatment drinking water reservoirs, highlighting the risk benthic cyanobacteria pose to human and animal health. Experiments were undertaken using cultures of Phormidium and Scytonema to determine how growth influences cyanotoxin production. The effects of iron and copper stress on P. autumnale were also investigated. High iron concentrations disrupted attachment mechanisms. Iron and copper had a significant effect on growth, without significantly affecting anatoxin a production. However, the maximum anatoxin a quota was consistently observed during early exponential growth. Scytonema cf. crispum produced higher saxitoxin quota throughout exponential growth than during the stationary phase. Both the Phormidium and Scytonema growth experiments indicate that high toxin quota can be expected early in benthic mat development, making early detection of these proliferations important.

Avec la hausse mondiale de la fréquence des floraisons de cyanobactéries (CB), dont certaines produisent des cyanotoxines (CT), le développement d’une méthode de détection/quantification rapide d’un maximum de CT s’impose. Cette méthode permettrait de faire un suivi quotidien de la toxicité de plans d’eau contaminés par des CB et ainsi d’émettre rapidement des avis d’alerte appropriés afin de protéger la santé publique. Une nouvelle technologie utilisant la désorption thermique induite par diode laser (LDTD) couplée à l’ionisation chimique sous pression atmosphérique (APCI) et reliée à la spectrométrie de masse en tandem (MS/MS) a déjà fait ses preuves avec des temps d'analyse de l’ordre de quelques secondes. Les analytes sont désorbés par la LDTD, ionisés en phase gazeuse par APCI et détectés par la MS/MS. Il n’y a donc pas de séparation chromatographique, et la préparation de l’échantillon avant l’analyse est minimale selon la complexité de la matrice contenant les analytes. Parmi les quatre CT testées (microcystine-LR, cylindrospermopsine, saxitoxine et anatoxine-a (ANA-a)), seule l’ANA-a a généré une désorption significative nécessaire au développement d’une méthode analytique avec l’interface LDTD-APCI. La forte polarité ou le poids moléculaire élevé des autres CT empêche probablement leur désorption. L’optimisation des paramètres instrumentaux, tout en tenant compte de l’interférence isobarique de l’acide aminé phénylalanine (PHE) lors de la détection de l’ANA-a par MS/MS, a généré une limite de détection d’ANA-a de l’ordre de 1 ug/L. Celle-ci a été évaluée à partir d’une matrice apparentée à une matrice réelle, démontrant qu’il serait possible d’utiliser la LDTD pour effectuer le suivi de l’ANA-a dans les eaux naturelles selon les normes environnementales applicables (1 à 12 ug/L). Il a été possible d’éviter l’interférence isobarique de la PHE en raison de sa très faible désorption avec l’interface LDTD-APCI. En effet, il a été démontré qu’une concentration aussi élevée que 500 ug/L de PHE ne causait aucune interférence sur le signal de l’ANA-a. / Within the context of the worldwide increasing frequency of cyanobacterial (CB) blooms, some containing cyanotoxins (CT), the development of a detection/quantification method for the fast analysis a maximum of CT is necessary. This method would allow daily tracking of the toxicity of CB-contaminated water such that, as warranted, appropriate measures can be taken quickly to protect public health. A new technology using laser diode thermal desorption (LDTD) coupled to atmospheric pressure chemical ionization (APCI)-tandem mass spectrometry (MS/MS) has shown great potential to reduce analysis time to seconds. Analytes are desorbed by the LDTD, ionized in gas-phase by APCI and detected by MS/MS. Therefore, there is no chromatographic separation and sample treatment prior to analysis is minimal, depending on the complexity of the sample matrix. Among the four CT tested (microcystin-LR, cylindrospermopsin, saxitoxin and anatoxin-a (ANA-a)), only ANA-a exhibited sufficient desorption which is necessary to develop an analytical method with the LDTD-APCI interface. The strong polarity or high molecular weight of the other CT probably inhibited their efficient desorption. Optimization of instrumental parameters, while accounting for the isobaric interference caused by the acid amino phenylalanine (PHE) in the detection of ANA-a by MS/MS, generated a detection limit of the order of 1 ug/L ANA-a. This value was obtained in a simulated natural matrix, demonstrating that it would be possible to use LDTD to monitor ANA-a in natural waters within the range of current applicable environmental guidelines (1 to 12 ug/L). Because PHE desorption is limited with the LDTD-APCI interface, this method avoids its interference on ANA-a analysis, even at PHE concentrations as high as 500 ug/L.

As cianobactérias apresentam distribuição variada e podem ocorrer desde as regiões frias do ártico até os trópicos, em corpos dágua doce e no ambiente marinho. Algumas espécies de cianobactérias produzem compostos com conhecida toxidade, podendo causar efeitos deletérios em seres humanos e animais. Entre estes compostos estão os com atividade neurotóxica devido aos mais variados mecanismos de ação. O objetivo geral deste projeto é a obtenção por via sintética de algumas neurotoxinas e variantes, entre elas a β-N-metil-L-alanina (L-BMAA), anatoxina-a e anatoxina-a(s), bem como algumas aplicações. Para a L-BMAA, foi buscada a determinação de rotas sintéticas viáveis para a obtenção deste aminoácido modificado sob a forma racêmica e enantiomericamente pura, além de um possível produto cíclico que pode ser gerado naturalmente a partir da L-BMAA. Algumas rotas estratégicas foram determinadas com êxito para a síntese destes compostos. Entre as aplicações dos produtos obtidos podem ser citados: (i) a determinação de um método analítico para a determinação deste aminoácido por RMN de 1H; (ii) um método analítico por LC-MS utilizando D3-L-BMAA como padrão interno e (iii) a indicação de um possível mecanismo de neurotoxidade ligado a neurodegeneração via um intermediário produzido naturalmente do equilíbrio entre L-BMAA e íons bicarbonato. Duas rotas sintéticas estratégicas foram traçadas para a anatoxina-a. Na primeira, que não foi bem sucedida, partiu-se de um biciclo já formado e em sua etapa chave deveria ocorrer à expansão de um anel tropânico que conduziria ao biciclo 1:2:4. Na segunda, tentou-se a síntese a partir de uma molécula extremamente simples, o 1,5- ciclooctadieno, e após cinco passos reacionais obteve-se a síntese total da anatoxina-a sob a forma racêmica. A etapa mais importante para essa rota foi a ciclização utilizando-se paládio divalente. Entre as possíveis aplicações dos produtos obtidos sugere-se: (i) o desenvolvimento de um método analítico por LC-MS utilizando D3-anatoxina-a como padrão interno e (ii) ensaios biológicos com os análogos para se determinar potencial agonista, antagonista ou agonista parcial de receptores nicotínicos para esses compostos. A anatoxina-a(s) apresentou um grande desafio para a sua síntese total. Por se tratar de um organofosforado com uma parte alquílica heterocíclica, buscou-se primeiramente a sua síntese parcial. Assim, foi possivel a síntese da guanidina cíclica sob a forma racêmica e quiral, além da obtenção de alguns compostos análogos inéditos. Para a síntese da N-hidroxiguanidina cíclica traçou-se duas diferentes rotas, uma enantioseletiva, partindo do aminoácido asparagina, e outra racêmica, com a utilização de álcool benzílico como material de partida. No entanto, apesar da produção de intermediários e análogos, não foi possível a obtenção do produto final. Entre as aplicações dos produtos sintéticos obtidos estão: (i) o desenvolvimento e validação de um método analítico para a quantificação indireta de anatoxina-a(s) utilizando a N-hidroxiguanidina cíclica como padrão e (ii) a utilização destes intermediários sintéticos em ensaios para se determinar os mecanismos de ação tóxicos, especialmente como inibidores de colinesterases. / Cyanobacteria are aquatic and photosynthetic organisms that can be present in cold areas, such as the Arctic, as well as in tropical waters, in both marine and freshwater environment. They are important species for aquatic life and terrestrial ecosystems since they are on the base of the food web. However, some cyanobacterial species can produce toxic secondary metabolites that have deleterious effects for animals and human. These toxic metabolites are also called cyanotoxins and show different mechanisms of action ranging from hepatotoxic to neurotoxic effects. The aim of this study is the organic synthesis of some common neurotoxins, including some analogues, such as β-N-methyl-L-alanine (L-BMAA), anatoxin-a and anatoxin-a(s). Moreover, focus was given for some possible application of these compounds, especially as analytical standards for water monitoring. Some synthetic routes were carried out in order to produce L-BMAA in both racemic and enantiomerically pure forms. Also, it was synthesized a possible cyclic analogue that may be formed in vivo from L-BMAA. The racemate and the pure L-BMAA were successfully obtained. Some possible application of these compounds were suggested: (i) the development of an analytical method based on 1H NMR analyses for the determination of L-BMAA in environmental and biological samples; (ii) the development of an analytical method based on LC-MS for the determination of L-BMAA, using D3-L-BMAA as an internal standard, in different matrices and (iii) the indication of a cyclic derivative formed in vivo that can be involved in the neurotoxicity of L-BMAA. Two strategies were planned in order to produce anatoxin-a. The first one was not successful and was started by using the bicyclic precursor. The crucial step was the expansion of tropanic ring to produce the 1:2:4 byciclic anatoxin-a precursor. The second strategy was initiated with the 1,5 cyclicoctadiene and after five reaction steps anatoxin-a was finally synthesized in its racemic form. The most important step for this route was the use of palladium. Similar applications were suggested for anatoxin-a: (i) the development of an analytical method based on LC-MS for the determination of anatoxin-a using D3-anatoxin-a as an internal standard in different matrices and (ii) the screening of anatoxin-a and analogues in bioassays based on nicotinic receptors in order to determine their agonistic and antagonistic mechanism of action. The total synthesis of anatoxin-a(s) is still a challenge. This cyanotoxin is a natural organophosphate with an alkylic heterocyclic chain. Therefore, the first step was the production of the cyclic guanidine in both racemic and enantiomerically pure forms. Some cyclic guanidine derivatives were prepared via asparagine and/or benzilic alcohol. However, anatoxin-a(s) was not achieved. The use of the cyclic guanidine can be recommended for: (i) the development of an analytical method based on LC-MS for the indirect determination of anatoxin-a(s) using its alkylic chain as a standard after sample alkalinization and (ii) the screening of anatoxin-a(s) derivatives in cholinesterase assays to determine their toxicity and mechanisms of action.

As cianobactérias apresentam distribuição variada e podem ocorrer desde as regiões frias do ártico até os trópicos, em corpos dágua doce e no ambiente marinho. Algumas espécies de cianobactérias produzem compostos com conhecida toxidade, podendo causar efeitos deletérios em seres humanos e animais. Entre estes compostos estão os com atividade neurotóxica devido aos mais variados mecanismos de ação. O objetivo geral deste projeto é a obtenção por via sintética de algumas neurotoxinas e variantes, entre elas a β-N-metil-L-alanina (L-BMAA), anatoxina-a e anatoxina-a(s), bem como algumas aplicações. Para a L-BMAA, foi buscada a determinação de rotas sintéticas viáveis para a obtenção deste aminoácido modificado sob a forma racêmica e enantiomericamente pura, além de um possível produto cíclico que pode ser gerado naturalmente a partir da L-BMAA. Algumas rotas estratégicas foram determinadas com êxito para a síntese destes compostos. Entre as aplicações dos produtos obtidos podem ser citados: (i) a determinação de um método analítico para a determinação deste aminoácido por RMN de 1H; (ii) um método analítico por LC-MS utilizando D3-L-BMAA como padrão interno e (iii) a indicação de um possível mecanismo de neurotoxidade ligado a neurodegeneração via um intermediário produzido naturalmente do equilíbrio entre L-BMAA e íons bicarbonato. Duas rotas sintéticas estratégicas foram traçadas para a anatoxina-a. Na primeira, que não foi bem sucedida, partiu-se de um biciclo já formado e em sua etapa chave deveria ocorrer à expansão de um anel tropânico que conduziria ao biciclo 1:2:4. Na segunda, tentou-se a síntese a partir de uma molécula extremamente simples, o 1,5- ciclooctadieno, e após cinco passos reacionais obteve-se a síntese total da anatoxina-a sob a forma racêmica. A etapa mais importante para essa rota foi a ciclização utilizando-se paládio divalente. Entre as possíveis aplicações dos produtos obtidos sugere-se: (i) o desenvolvimento de um método analítico por LC-MS utilizando D3-anatoxina-a como padrão interno e (ii) ensaios biológicos com os análogos para se determinar potencial agonista, antagonista ou agonista parcial de receptores nicotínicos para esses compostos. A anatoxina-a(s) apresentou um grande desafio para a sua síntese total. Por se tratar de um organofosforado com uma parte alquílica heterocíclica, buscou-se primeiramente a sua síntese parcial. Assim, foi possivel a síntese da guanidina cíclica sob a forma racêmica e quiral, além da obtenção de alguns compostos análogos inéditos. Para a síntese da N-hidroxiguanidina cíclica traçou-se duas diferentes rotas, uma enantioseletiva, partindo do aminoácido asparagina, e outra racêmica, com a utilização de álcool benzílico como material de partida. No entanto, apesar da produção de intermediários e análogos, não foi possível a obtenção do produto final. Entre as aplicações dos produtos sintéticos obtidos estão: (i) o desenvolvimento e validação de um método analítico para a quantificação indireta de anatoxina-a(s) utilizando a N-hidroxiguanidina cíclica como padrão e (ii) a utilização destes intermediários sintéticos em ensaios para se determinar os mecanismos de ação tóxicos, especialmente como inibidores de colinesterases. / Cyanobacteria are aquatic and photosynthetic organisms that can be present in cold areas, such as the Arctic, as well as in tropical waters, in both marine and freshwater environment. They are important species for aquatic life and terrestrial ecosystems since they are on the base of the food web. However, some cyanobacterial species can produce toxic secondary metabolites that have deleterious effects for animals and human. These toxic metabolites are also called cyanotoxins and show different mechanisms of action ranging from hepatotoxic to neurotoxic effects. The aim of this study is the organic synthesis of some common neurotoxins, including some analogues, such as β-N-methyl-L-alanine (L-BMAA), anatoxin-a and anatoxin-a(s). Moreover, focus was given for some possible application of these compounds, especially as analytical standards for water monitoring. Some synthetic routes were carried out in order to produce L-BMAA in both racemic and enantiomerically pure forms. Also, it was synthesized a possible cyclic analogue that may be formed in vivo from L-BMAA. The racemate and the pure L-BMAA were successfully obtained. Some possible application of these compounds were suggested: (i) the development of an analytical method based on 1H NMR analyses for the determination of L-BMAA in environmental and biological samples; (ii) the development of an analytical method based on LC-MS for the determination of L-BMAA, using D3-L-BMAA as an internal standard, in different matrices and (iii) the indication of a cyclic derivative formed in vivo that can be involved in the neurotoxicity of L-BMAA. Two strategies were planned in order to produce anatoxin-a. The first one was not successful and was started by using the bicyclic precursor. The crucial step was the expansion of tropanic ring to produce the 1:2:4 byciclic anatoxin-a precursor. The second strategy was initiated with the 1,5 cyclicoctadiene and after five reaction steps anatoxin-a was finally synthesized in its racemic form. The most important step for this route was the use of palladium. Similar applications were suggested for anatoxin-a: (i) the development of an analytical method based on LC-MS for the determination of anatoxin-a using D3-anatoxin-a as an internal standard in different matrices and (ii) the screening of anatoxin-a and analogues in bioassays based on nicotinic receptors in order to determine their agonistic and antagonistic mechanism of action. The total synthesis of anatoxin-a(s) is still a challenge. This cyanotoxin is a natural organophosphate with an alkylic heterocyclic chain. Therefore, the first step was the production of the cyclic guanidine in both racemic and enantiomerically pure forms. Some cyclic guanidine derivatives were prepared via asparagine and/or benzilic alcohol. However, anatoxin-a(s) was not achieved. The use of the cyclic guanidine can be recommended for: (i) the development of an analytical method based on LC-MS for the indirect determination of anatoxin-a(s) using its alkylic chain as a standard after sample alkalinization and (ii) the screening of anatoxin-a(s) derivatives in cholinesterase assays to determine their toxicity and mechanisms of action.

Avec la hausse mondiale de la fréquence des floraisons de cyanobactéries (CB), dont certaines produisent des cyanotoxines (CT), le développement d’une méthode de détection/quantification rapide d’un maximum de CT s’impose. Cette méthode permettrait de faire un suivi quotidien de la toxicité de plans d’eau contaminés par des CB et ainsi d’émettre rapidement des avis d’alerte appropriés afin de protéger la santé publique. Une nouvelle technologie utilisant la désorption thermique induite par diode laser (LDTD) couplée à l’ionisation chimique sous pression atmosphérique (APCI) et reliée à la spectrométrie de masse en tandem (MS/MS) a déjà fait ses preuves avec des temps d'analyse de l’ordre de quelques secondes. Les analytes sont désorbés par la LDTD, ionisés en phase gazeuse par APCI et détectés par la MS/MS. Il n’y a donc pas de séparation chromatographique, et la préparation de l’échantillon avant l’analyse est minimale selon la complexité de la matrice contenant les analytes. Parmi les quatre CT testées (microcystine-LR, cylindrospermopsine, saxitoxine et anatoxine-a (ANA-a)), seule l’ANA-a a généré une désorption significative nécessaire au développement d’une méthode analytique avec l’interface LDTD-APCI. La forte polarité ou le poids moléculaire élevé des autres CT empêche probablement leur désorption. L’optimisation des paramètres instrumentaux, tout en tenant compte de l’interférence isobarique de l’acide aminé phénylalanine (PHE) lors de la détection de l’ANA-a par MS/MS, a généré une limite de détection d’ANA-a de l’ordre de 1 ug/L. Celle-ci a été évaluée à partir d’une matrice apparentée à une matrice réelle, démontrant qu’il serait possible d’utiliser la LDTD pour effectuer le suivi de l’ANA-a dans les eaux naturelles selon les normes environnementales applicables (1 à 12 ug/L). Il a été possible d’éviter l’interférence isobarique de la PHE en raison de sa très faible désorption avec l’interface LDTD-APCI. En effet, il a été démontré qu’une concentration aussi élevée que 500 ug/L de PHE ne causait aucune interférence sur le signal de l’ANA-a. / Within the context of the worldwide increasing frequency of cyanobacterial (CB) blooms, some containing cyanotoxins (CT), the development of a detection/quantification method for the fast analysis a maximum of CT is necessary. This method would allow daily tracking of the toxicity of CB-contaminated water such that, as warranted, appropriate measures can be taken quickly to protect public health. A new technology using laser diode thermal desorption (LDTD) coupled to atmospheric pressure chemical ionization (APCI)-tandem mass spectrometry (MS/MS) has shown great potential to reduce analysis time to seconds. Analytes are desorbed by the LDTD, ionized in gas-phase by APCI and detected by MS/MS. Therefore, there is no chromatographic separation and sample treatment prior to analysis is minimal, depending on the complexity of the sample matrix. Among the four CT tested (microcystin-LR, cylindrospermopsin, saxitoxin and anatoxin-a (ANA-a)), only ANA-a exhibited sufficient desorption which is necessary to develop an analytical method with the LDTD-APCI interface. The strong polarity or high molecular weight of the other CT probably inhibited their efficient desorption. Optimization of instrumental parameters, while accounting for the isobaric interference caused by the acid amino phenylalanine (PHE) in the detection of ANA-a by MS/MS, generated a detection limit of the order of 1 ug/L ANA-a. This value was obtained in a simulated natural matrix, demonstrating that it would be possible to use LDTD to monitor ANA-a in natural waters within the range of current applicable environmental guidelines (1 to 12 ug/L). Because PHE desorption is limited with the LDTD-APCI interface, this method avoids its interference on ANA-a analysis, even at PHE concentrations as high as 500 ug/L.

No description available.

Made available in DSpace on 2016-06-02T19:29:57Z (GMT). No. of bitstreams: 1 5307.pdf: 3018065 bytes, checksum: 4a4ed79b44dafeeb1204798dc8f70256 (MD5) Previous issue date: 2013-06-03 / Universidade Federal de Sao Carlos / This thesis aimed to evaluate the use of cholinesterases (ChE) of the cladoceran species Pseudosida ramosa and Daphnia magna as a biochemical biomarker of the presence and effects of anatoxin-a(s) at different levels of biological organization (molecular, individual and population), besides the combined effects of the mixtures of the hepatotoxic (microcystins) and neurotoxic (anatoxin-a(s)) extracts in D. magna. A microplate assay was adapted and optimized for measuring the ChE activity of P. ramosa, in order to produce an assay protocol for this species. The analysis on the performance of ChE assays in P. ramosa showed that these are suitable for the quantifying of enzymatic activity in this species. P. ramosa showed to be an adequate alternative to the exotic cladoceran D. magna. Thus, it was proposed an assay protocol, which it meets the best combination of parameters for the using of ChE activity of P. ramosa as a biochemical biomarker. The ChE activity of P. ramosa and D. magna were specific for the indication of the presence of anatoxin-a(s), since no effect on the enzymatic activity of these species was observed when they were exposed to the microcystins. In the acute exposures (48-h) to the anatoxin-a(s) extract and to the paraoxon-methyl, P. ramosa was more sensitive than D. magna for ChE activity and survival endpoints. Also, P. ramosa was more sensitive than D. magna when exposed to the anatoxin-a(s) extract for 7 days. When the relationships between the ChE inhibition and individual and populational endpoints were evaluated, different responses were observed for the studied species. The ChE inhibition in P. ramosa had a very close relationship with the survival in the acute exposures to the anatoxin-a(s) extract and to the paraoxon-methyl. For D. magna, on the other hand, this relationship was not linear, being high levels of ChE inhibition associated with almost no mortality. The ChE activity in P. ramosa was also a good predictor of the chronic effects of anatoxin-a(s) extract at higher levels of biological organization, since ChE inhibition (48 h) was linearly linked to the sub-lethal effects on the reproduction (21 days) and on the population growth rate (21 days). For D. magna, these relationships could not be established, possibly due to species-specific differences in the affinities of both acetylcholinesterase and pseudocholinesterases to the toxicants. Thus, for the using of ChE as a biochemical biomarker in the risk assessments of neurotoxic cyanobacteria blooms in tropical regions, it is recommended the use of native species, especially of P. ramosa, since the model species D. magna could overestimate the risk to the local species. When the effects of the mixtures of the hepatotoxic and neurotoxic extracts were evaluated on the survival and feeding rates of D. magna, additive and synergistic responses were only observed on the feeding rates. Therefore, since different types of cyanotoxins are found in the natural environments in combination, the risks of these toxins on the zooplanktonic community should be evaluated not only individually, but also as mixtures. / Esta tese teve como objetivo avaliar o uso das colinesterases (ChE) das espécies de cladóceros Pseudosida ramosa e Daphnia magna como um biomarcador bioquímico da presença e dos efeitos de anatoxina-a(s) em diferentes níveis de organização biológica (molecular, individual e populacional), além dos efeitos combinados das misturas dos extratos hepatotóxicos (microcistinas) e neurotóxicos (anatoxina-a(s)) em D. magna. Um ensaio de microplacas foi adaptado e otimizado para medir a atividade de ChE da P. ramosa, a fim de produzir um protocolo de ensaio para esta espécie. A análise sobre o desempenho dos ensaios de ChE em P. ramosa mostrou que estes são adequados para a quantificação da atividade enzimática nesta espécie. P. ramosa mostrou ser uma alternativa adequada para o cladócero exótico D. magna. Assim, foi proposto um protocolo de ensaio, o qual reúne a melhor combinação de parâmetros para a utilização da atividade de ChE da P. ramosa como um biomarcador bioquímico. A atividade de ChE da P. ramosa e da D. magna foram específicas para a indicação da presença de anatoxinaa( s), uma vez que nenhum efeito sobre a atividade enzimática dessas espécies foi observado quando elas foram expostas às microcistinas. Nas exposições agudas (48 h) ao extrato de anatoxina-a(s) e ao paraoxon-metil, P. ramosa foi mais sensível do que D. magna para os parâmetros atividade de ChE e sobrevivência. Também, P. ramosa foi mais sensível do que D. magna quando exposta ao extrato de anatoxina-a(s) por sete dias. Quando as relações entre a inibição de ChE e os parâmetros individuais e populacionais foram avaliados, diferentes respostas foram observadas para as espécies estudadas. A inibição de ChE em P. ramosa teve uma relação muito próxima com a sobrevivência nas exposições agudas ao extrato de anatoxina-a(s) e ao paraoxon-metil. Para D. magna, por outro lado, esta relação não foi linear, sendo níveis altos de inibição de ChE associados com quase nenhuma mortalidade. A atividade de ChE em P. ramosa foi também um bom preditor dos efeitos crônicos do extrato de anatoxina-a(s) em níveis mais elevados de organização biológica, uma vez que a inibição de ChE (48 h) foi associada linearmente aos efeitos sub-letais na reprodução (21 dias) e na taxa de crescimento populacional (21 dias). Para D. magna, essas relações não puderam ser estabelecidas, possivelmente devido a diferenças espécie-específicas nas afinidades da acetilcolinesterase e das pseudocolinesterases aos tóxicos. Assim, para a utilização de ChE como um biomarcador bioquímico nas avaliações de risco de florescimentos de cianobactérias neurotóxicas em regiões tropicais, recomenda-se o uso de espécies nativas, especialmente da P. ramosa, uma vez que a espécie modelo D. magna poderia superestimar o risco para as espécies locais. Quando os efeitos das misturas dos extratos hepatotóxicos e neurotóxicos foram avaliados sobre a sobrevivência e as taxas alimentares da D. magna, respostas aditivas e sinergísticas foram observadas apenas nas taxas alimentares. Portanto, uma vez que diferentes tipos de cianotoxinas são encontrados nos ambientes naturais em combinação, os riscos dessas toxinas sobre a comunidade zooplanctônica deveriam ser avaliados não apenas individualmente, mas também como misturas.

Les cyanobactéries ont une place très importante dans les écosystèmes aquatiques et un nombre important d’espèces considéré comme nuisible de par leur production de métabolites toxiques. Ces cyanotoxines possèdent des propriétés très variées et ont souvent été associées à des épisodes d’empoisonnement. L’augmentation des épisodes d’efflorescence d’origine cyanobactériennes et le potentiel qu’ils augmentent avec les changements climatiques a renchéri l’intérêt de l’étude des cyanobactéries et de leurs toxines. Considérant la complexité chimique des cyanotoxines, le développement de méthodes de détection simples, sensibles et rapides est toujours considéré comme étant un défi analytique. Considérant ces défis, le développement de nouvelles approches analytiques pour la détection de cyanotoxines dans l’eau et les poissons ayant été contaminés par des efflorescences cyanobactériennes nuisibles a été proposé. Une première approche consiste en l’utilisation d’une extraction sur phase solide en ligne couplée à une chromatographie liquide et à une détection en spectrométrie de masse en tandem (SPE-LC-MS/MS) permettant l’analyse de six analogues de microcystines (MC), de l’anatoxine (ANA-a) et de la cylindrospermopsine (CYN). La méthode permet une analyse simple et rapide et ainsi que la séparation chromatographique d’ANA-a et de son interférence isobare, la phénylalanine. Les limites de détection obtenues se trouvaient entre 0,01 et 0,02 μg L-1 et des concentrations retrouvées dans des eaux de lacs du Québec se trouvaient entre 0,024 et 36 μg L-1. Une deuxième méthode a permis l’analyse du b-N-méthylamino-L-alanine (BMAA), d’ANA-a, de CYN et de la saxitoxine (STX) dans les eaux de lac contaminés. L’analyse de deux isomères de conformation du BMAA a été effectuée afin d’améliorer la sélectivité de la détection. L’utilisation d’une SPE manuelle permet la purification et préconcentration des échantillons et une dérivatisation à base de chlorure de dansyle permet une chromatographie simplifiée. L’analyse effectuée par LC couplée à la spectrométrie de masse à haute résolution (HRMS) et des limites de détections ont été obtenues entre 0,007 et 0,01 µg L-1. Des échantillons réels ont été analysés avec des concentrations entre 0,01 et 0,3 µg L-1 permettant ainsi la confirmation de la présence du BMAA dans les efflorescences de cyanobactéries au Québec. Un deuxième volet du projet consiste en l’utilisation d’une technologie d’introduction d’échantillon permettant des analyses ultra-rapides (< 15 secondes/échantillons) sans étape chromatographique, la désorption thermique à diode laser (LDTD) couplée à l’ionisation chimique à pression atmosphérique (APCI) et à la spectrométrie de masse (MS). Un premier projet consiste en l’analyse des MC totales par l’intermédiaire d’une oxydation de Lemieux permettant un bris de la molécule et obtenant une fraction commune aux multiples congénères existants des MC. Cette fraction, le MMPB, est analysée, après une extraction liquide-liquide, par LDTD-APCI-MS/MS. Une limite de détection de 0,2 µg L-1 a été obtenue et des concentrations entre 1 et 425 µg L-1 ont été trouvées dans des échantillons d’eau de lac contaminés du Québec. De plus, une analyse en parallèle avec des étalons pour divers congénères des MC a permis de suggérer la possible présence de congénères ou d’isomères non détectés. Un deuxième projet consiste en l’analyse directe d’ANA-a par LDTD-APCI-HRMS pour résoudre son interférence isobare, la phénylalanine, grâce à la détection à haute résolution. La LDTD n’offre pas de séparation chromatographique et l’utilisation de la HRMS permet de distinguer les signaux d’ANA-a de ceux de la phénylalanine. Une limite de détection de 0,2 µg L-1 a été obtenue et la méthode a été appliquée sur des échantillons réels d’eau avec un échantillon positif en ANA-a avec une concentration de 0,21 µg L-1. Finalement, à l’aide de la LDTD-APCI-HRMS, l’analyse des MC totales a été adaptée pour la chair de poisson afin de déterminer la fraction libre et liée des MC et comparer les résultats avec des analyses conventionnelles. L’utilisation d’une digestion par hydroxyde de sodium précédant l’oxydation de Lemieux suivi d’une purification par SPE a permis d’obtenir une limite de détection de 2,7 µg kg-1. Des échantillons de poissons contaminés ont été analysés, on a retrouvé des concentrations en MC totales de 2,9 et 13,2 µg kg-1 comparativement aux analyses usuelles qui avaient démontré un seul échantillon positif à 2 µg kg-1, indiquant la possible présence de MC non détectés en utilisant les méthodes conventionnelles. / Cyanobacteria have a very important place in aquatic ecosystems and a significant number of species are considered harmful given their production of toxic metabolites. These cyanotoxins have various chemical proprieties and have often been associated with poisoning episodes. The frequency of cyanobacterial blooms is increasing and the study of cyanobacteria and their toxins is of increasing interest, especially considering the potential increase associated with climate changes. Given the chemical complexity of the cyanotoxins, the development of simple, sensitive and fast detection methods is an analytical challenge. Considering these issues, the development of new analytical approaches for the detection of cyanotoxins in water and fish samples contaminated with harmful cyanobacterial blooms have been proposed. A first approach consists of the use of an on-line solid phase extraction coupled to liquid chromatography and tandem mass spectrometry (SPE-LC-MS/MS) for the analysis of six microcystins (MCs), anatoxin-a (ANA-a) and cylindrospermopsin (CYN). This method allows a simple and rapid analysis and enables the chromatographic separation of ANA-a and its isobaric interference, phenylalanine. The detection limits ranged from 0.01 to 0.02 µg L-1 and concentrations in lake waters were found between 0.024 and 36 µg L-1. A second method consists of using manual solid phase extraction (SPE) coupled to high resolution mass spectrometry (HRMS) for the determination of b-N-methylamino-L-alanine (BMAA), ANA-a, CYN and saxitoxin (STX) in contaminated lake water. The analysis of two conformational isomers of BMAA was done to improve the selectivity. Dansyl chloride-based derivatization allows simplified chromatography. The detection limits were obtained between 0.007 and 0.01 µg L-1. The analysis of bloom water samples detected concentrations of cyanotoxins between 0.01 and 0.3 µg L-1 allowing the confirmation of the presence of BMAA in algal blooms in Québec. A second part of the project consists in the use of an alternative sample introduction technology for MS analysis. It enables ultra-fast analysis (< 15 seconds/sample) without the use of a chromatographic step, and is called laser diode thermal desorption (LDTD) coupled with atmospheric pressure chemical ionization (APCI). The first LDTD project consists of the analysis of total MCs via Lemieux oxidation in order to obtain a common moiety of all MCs existing congeners. This fraction, the MMPB, is analyzed after a liquid-liquid extraction step, with the LDTD-APCI-MS/MS. A value of 0.2 µg L-1 was obtained for detection limit and concentrations between 1 and 425 µg L-1 have been found in contaminated water samples. In addition, a comparison with a parallel analysis using MCs congeners’ standards suggested the possible presence of undetected MCs or isomers. A second project involves the direct analysis of ANA-a using LDTD-APCI-HRMS in order to solve the isobaric interference, phenylalanine, which is possible due to the high resolution detection. The LDTD offers no chromatographic separation and by using HRMS, we can distinguish ANA-a signals from those of phenylalanine. A value of 0.2 µg L-1 was obtained as detection limit and the method has been applied on water bloom samples with a positive concentration of 0.21 µg L-1. Finally, using the LDTD-APCI-HRMS combination, analysis of total MCs has been adapted to fish tissues to determine the unbound and bound MCs and compare the results with standard analysis. The use of digestion with sodium hydroxide prior to Lemieux oxidation followed by SPE purification yielded a detection limit of 2.7 µg kg-1. Total MCs concentrations were found between 2.9 and 13.2 µg kg-1 in real field-collected contaminated fish samples and comparison was made with standard analysis which yield a single positive sample with a concentration of 2 µg kg-1. This indicates the possible presence of undetected MCs using conventional analytical methods.