En Europe, le nombre de cancers est en constante augmentation et explique l’augmentation des traitements. Les bases de ces traitements sont la chimiothérapie et la radiothérapie, seules ou en association. Les chimiothérapies sont effectuées à l’aide de médicaments anticancéreux qui ont des propriétés toxiques pour les cellules. Après administration des traitements aux patients, les médicaments sont excrétés et se concentrent dans les effluents hospitaliers et les réseaux d’égouts. Bien que beaucoup de ces composés soient éliminés dans les stations d’épuration, certains sont difficilement biodégradables et sont directement rejetées dans le milieu naturel où ils représentent un risque toxique pour la flore, la faune et l’Homme. Bien que les concentrations soient faibles (ng/L - μg/L), très peu de données sont disponibles sur leurs impacts écotoxicologiques. Leur présence dans l’environnement est d’autant plus préoccupante que les produits de métabolisation sont souvent plus toxiques que la substance d’origine. L’objectif de la thèse a été d’évaluer le risque (éco)toxicologique induit par de faibles doses de médicaments rejetés seuls ou en mélanges dans les effluents hospitaliers, urbains et dans l’environnement. De par leur utilisation courante dans les traitements anticancéreux, trois molécules ont été sélectionnées pour notre étude : la ciprofloxacine (antibiotique), le tamoxifène (perturbateur endocrinien), et le cyclophosphamide (anticancéreux). Des gammes de concentrations représentatives des effluents hospitaliers, station d’épuration et de l’environnement ont été testées à l’aide de bioessais appliqués à des organismes aquatiques (V. fischeri, P. subcapitata, L. minor) et de biomarqueurs appliqués à une levure (S. cerevisiae) et des cellules humaines hépatiques et mammaires. La viabilité cellulaire (test MTS) et la génotoxicité (cassures à l’ADN et adduit à l’ADN) ont été comparés aux tests standardisés Microtox ®, Algaltoxkit F™, ainsi que d’inhibition de croissance de Lemna minor. Le potentiel perturbateur endocrinien a été évalué en parallèle à l’aide du test YES/YAS. Cette batterie de tests a ensuite été appliquée a des effluents bruts (hospitaliers, station d’épuration) pour en évaluer le potentiel (géno)toxique. Des échantillons à proximité de l’hôpital de Gérone (Espagne) ont été prélevés en sortie de l’hôpital, en entrée et en sortie de station d’épuration, pendant trois mois consécutifs. Plusieurs effets de toxicité ont été observés sur les modèles d’étude, comme notamment l’apparition de phénomènes d’hormèses sur la viabilité des cellules hépatiques exposée au tamoxifène et à la ciprofloxacine, seuls ou en mélange. Le même schéma est observé pour les mélanges avec le test Microtox®. D’autre part, l’exposition respective des cellules hépatiques et mammaires aux médicaments n’entraîne pas de cassures de l’ADN et entraine l’apparition d’adduits seulement avec le tamoxifène, alors qu’on note une augmentation dose-dépendant des cassures et des adduits à l’ADN après exposition aux mélanges. De même, une réponse positive est observée avec le test Algaltox F™. Concernant les effluents, les effets dépendent à la fois du type d’organisme et du temps d’exposition. Les tests Microtox®, Algaltox F™ et le post-marquage des adduits à l’ADN sont apparus être les pertinents pour l’analyse. Les interactions observées entre les composés mettent en avant la nécessité d’évaluer les effets des contaminants à petites doses en mélanges, à plusieurs temps d’exposition et avec différents tests. L’application d’une telle batterie de tests à des échantillons environnementaux permet de qualifier les effluents et de suivre l’efficacité de moyens d’épuration. A terme, son application pourrait permettre de mieux appréhender les risques (éco)toxiques associés aux rejets de médicaments dans l’environnement et pouvant être à l’origine de cancer secondaire chez l’Homme. / In Europe, cancers rate is constantly raising, which explain the increase in treatments. They are usually chemotherapy and radiotherapy, alone or combine. Chemotherapy is done with anticancer drugs with toxic characteristics on cells. After administer the treatments to the patients, some of the drugs are excreted in significant proportion and released in hospital and communal effluents. Even though a lot of the compounds are either removed by adsorption or bio-degradation in waste water treatment plant (WWTP), some of their are not are directly released in the environment and represent a toxic risk for aquatic organisms and the Human health. Despite low concentrations (ng/L-μg/L), few data are available about the ecotoxicological impact. The importance of chemical compounds pollutants, especially anticancer drugs, are a real concern because the metabolites of the chemicals are even more toxic than the original substance. The aim of the thesis is to develop a battery based approach to evaluate the risks induct by low doses of drugs released independently or in mixture, in hospital waste water. Because of their common use in anticancer treatment procedures, three molecules have been chosen for our study: ciprofloxacin (antibiotic), tamoxifen (endocrine disruptor), cyclophosphamide (anticancer). Concentrations were range from hospital sewers and WWTP to the environment have been tested with a battery base approach using standardized bioassays applied on aquatic organisms (V fischeri, S. subcapitata, L. minor) and biomarker applied on yeast (S. cerevisia), hepatic and mammary human cell lines. Cell viability (test MTS) and genotoxicity (DNA breaks, DNA adducts) were compared with the standardized bioassays Microtox®, Algaltoxkit F™, and Lemna minor growth inhibition. In parallel, the endocrine disruptor activity was estimated the YES/YAS assay. The battery assay was then applied to evaluate the (geno)toxicity of raw effluents (hospital, wastewater-treatment plant). Samples from the hospital of Girona (Spain) were taken got out of it from the hospital, in entrance and got out of it from water-treatment plant, during three consecutive months. Several toxic effects have been observed during this work on aquatic organisms and both human cell lines. Results show especially hormetic effect on viability of hepatic cell line exposed to ciprofloxacin and tamoxifen alone or in mixture. Same results were observed the Microtox assays after mixtures exposures. On the other hand, the individually hepatic and mammary cell exposure to the drugs doesn’t induce DNA break, and induce DNA adduct only with the tamoxifen. Furthermore, we observe a dose-dependent increasing of the DNA break and adduct if the cells are exposed in mixture. Same results were observed with Algaltox F™. Concerning the effluents, effects depending on the kind of organisms and time exposure. The Microtox ®, Algaltox F ™ and the DNA adducts post-labelling appeared to be the most relevant for the analysis. The interactions observed between drugs pinpoint the necessity to assess the effect of contaminants in low doses mixtures, at many exposure times, and using different tools. The application of this battery with environmental raw samples is in use to rank outflows toxicity and follow the WWTP efficiency, which could lead to a better understanding of the human health risks.

Les méthodes actuellement disponibles pour la surveillance de la qualité du milieu se réfèrent au suivi de composés définis par les réglementations et ne permettent pas d’appréhender l’(éco)toxicité réelle de tous les composés présents dans l’environnement (e.g. composés inconnus, produits de transformation, effets de mélange…). Dans ce contexte, une méthode d’analyse pluridisciplinaire intégrative, l’analyse dirigée par l’effet (EDA), a été développée. Cette approche bio-analytique vise à établir un lien de causalité entre une exposition aux contaminants et l’effet biologique observé. La démarche est basée sur la simplification séquentielle d’un échantillon guidée par les bio-essais afin d’individualiser puis identifier, par des techniques analytiques chimiques performantes, les composés biologiquement actifs. Les objectifs de cette thèse ont porté sur (1) le développement et la validation d’une méthodologie, allant du pré-traitement jusqu’au fractionnement, adaptée à différentes matrices environnementales ; (2) la mise en place d’une stratégie d’identification moléculaire par spectrométrie de masse haute résolution ; (3) l’application de la démarche EDA à plusieurs échantillons afin d’illustrer l’adaptabilité et l’apport d’une telle méthode à des problématiques environnementales. Ces travaux de thèse permettent de disposer aujourd’hui d’une démarche bio-analytique complète de la préparation d’échantillon à l’identification de molécules, et adaptée à tous types d’échantillons. Les différentes études environnementales réalisées au cours de ces travaux ont permis, entre autre, d’établir une liste de composés diverses non recherchés pouvant représenter un risque pour l’environnement. / To date, environmental risk assessment is based on targeted chemical analyses. These analyses allow the detection of known active compounds and this preselected set does not often explain the observed toxic effects in complex environmental samples (e.g. unknown compounds, transformation product, cocktail effect...). For an integrative contamination assessment, a multidisciplinary approach, Effect-Directed Analysis (EDA) was developed. This approach combining biological tools and chemical analyses allows determining active compounds and identitying them in such environmental complex mixtures. EDA aims at the establishment of cause-effect relationships by sequential reduction of the complexity of environmental mixtures, eventually to individual toxicants. The aims of this thesis were (1) to develop and to validate the EDA-based strategy on various environmental complex samples; (2) to set up an identification strategy for identifying non targeted or unknown molecules using high resolution mass spectrometry; (3) to prove the usefulness of EDA approach for the identification of active compounds in environnemental complex samples. This thesis work provides to a complet bio-analytical approach from the preparation step of samples to the identification of molecules. The potential of this tool was fully confirmed on various environmental studies. These investigations allowed establishing a list of non-target compounds which can represent a risk for the environment.

Florescimentos de cianobactérias têm sido cada vez mais frequentemente detectados em reservatórios do Estado de São Paulo, especialmente naqueles da bacia do Médio rio Tietê. A presença de cianobactérias pode acarretar prejuízos à qualidade da água nestes ambientes, em razão de seu potencial tóxico à biota aquática, incluindo riscos à saúde humana. O presente estudo teve por objetivo analisar a estrutura da comunidade zooplanctônica de três reservatórios do Médio rio Tietê, SP (Barra Bonita, Bariri e Ibitinga) e sua relação com as cianobactérias presentes nas florações, com ênfase nos efeitos da toxicidade destas sobre o dafinídeo Ceriodaphnia silvestrii, uma espécie nativa. Para tanto, amostragens foram realizadas nos períodos de junho e setembro de 2008, e janeiro e maio de 2009. Foram efetuadas medições de diversos parâmetros físicos, químicos e biológicos em cada reservatório. As florações de cianobactérias foram coletadas com redes de plâncton, e armazenadas para análise e quantificação de cianotoxinas e também para a realização de ensaios ecotoxicológicos. Verificou-se que a comunidade zooplanctônica dos reservatórios é dominada por copépodos e rotíferos na maior parte das camadas de água dos reservatórios. Os copépodes Cyclopoida foram mais abundantes que os Calanoida, com grande representatividade de formas jovens (náuplios e copepoditos). A espécie de Cladocera Bosminam longirostris e grande parte das espécies de rotifera, como Brachionus calyciflorus foram frequentes em todas as represas, indicando que podem ter estratégias para coexistir com as toxinas dos blooms de cianobactérias. As concentrações de microcistinas LR foram detectadas em todas as amostras de florações dos reservatórios do médio rio Tietê, com concentrações variando e 18,2 a 100 \'mü\'g/L. Os testes de toxicidade aguda revelaram que os extratos brutos das florações de cianobactérias foram tóxicos ao dafínideo Ceriodaphnia silvestrii, provocando inibição dos movimentos natatórios mesmo em baixas concentrações de microcistina-LR, podendo portanto influenciar negativamente a biota aquática. / Cyanobacteria blooms are increasingly being detected in São Paulo state reservoirs, particularly in those of middle Tietê river basin. The presence of cyanobacteria can cause deterioration of water quality in these systems due to its potential toxicity to the aquatic biota, and also risks to human health. The aim of the present srtudy was to analyse the structure of the zooplankton community in three reservoirs placed in middle Tietê river basin, SP (Barra Bonita, Bariri and Ibitinga) and its relationships with blooms of cyanobacteria, with emphasis on its toxic effects upon the daphnid Ceriodaphnia silvestrii, a native species. Sampling was carried out in June and September 2008 and January and May 2009. Measurements of several physical, chemical and biological parameters were carried out in each reservoir. Samples of cyanobacteria blooms were taken with phytoplankton nets and properly kept for posterior analysis of species composition, cyanotoxin quantification and also for acute toxicity testing. It was found that zooplankton communities in the reservoirs are dominated by rotifers and copepods in most of the water layers sampled. The cyclopoid copepods were more abundant than calanoid ones with great representativiness of the young forms (nauplii and copepodids). The Cladocera species Bosmina longirostris and some species of Rotifera as Brachionus calyciflorus were frequent in all reservoirs, indicating that they might have strategies to cope with the cyanobacteria bloom toxicity. Microcystin LR concentrations were detected in all samples of blooms from Middle Tietê River reservoirs with concentrations varying from 18,2 to 100 \'mü\'g/ L. Acute toxicity tests revealed that raw extracts from cyanobacteria scums were toxic to the daphnid Ceriodaphnia silvestrii, causing immobilization of natatory movements even at low LR microcystin concentrations, thus negatively affecting the aquatic biota.

Para atestar a imunogenicidade de vacinas contra raiva, os testes de titulação e de soroneutralização de vírus rábico em células BHK-21 foram validados quanto à linearidade, precisão, exatidão e robustez. Cinco esquemas de imunização com diferentes concentrações, vias de inoculação e intervalos entre as doses foram avaliados em camundongos com vacina contra raiva em células Vero. O grupo II que recebeu um esquema de 2 doses e intervalos maiores (0 e 60 dias) apresentou títulos de anticorpos neutralizantes [ACN] mais elevados (46,1 UI/mL) do que o Grupo I (19,4 UI/mL), de 3 doses e intervalos menores (0,7 e 28 dias). O grupo III, que recebeu 2 doses, sendo a 1ª diluída 1/10, apresentou ACN semelhantes ao grupo II (39,2 UI/mL), sendo igualmente eficaz. Nenhum animal do grupo IV, imunizado por via oral (VO) apresentou ACN, indicando supressão e todos os do grupo V, imunizados VO com antígeno adsorvido/encapsulado em sílica nanoestruturada SBA-15, apresentaram títulos de ACN detectáveis, mostrando que o antígeno foi protegido da degradação no trato gastrointestinal. / To assure the reliability of the results of immunogenicity of rabies vaccines, tests of virus titration and neutralization in BHK-21 cells were validated for linearity, precision, accuracy and robustness. Five schemes of immunization with different concentrations, routes of inoculation and intervals between doses were evaluated in mice with rabies vaccine in Vero cells. Group II, immunized with 2 doses and enlarged interval (0 and 60 days) presented higher levels of neutralizing antibody (NAs) (46,1 IU/mL) than group I (19,4 IU/mL), with 3 doses and shorter intervals (0,7 and 28 days). Group III, which received 2 doses, the 1st diluted to 1/10, presented results similar to group II (39,2 IU/mL). None mouse of Group IV, immunized by oral route, presented NAs, indicating suppression and all mice of group V, immunized by oral route with vaccine adsorbed/encapsulated in nanostructured SBA-15 silica presented detectable NAs titers, showing that the SBA-15 silica prevented the antigen degradation in the gastrointestinal tract.

MSCAGR / Department of Plant Production

Coal mining and coal utilization in Mpumalanga have increased over the years due to national reliance on coal as a source of power generation. In general, this has caused significant deterioration of water quality wherever streams are impacted by acid mine drainage (AMD). The aim of this research was to assess the use of in vitro bioassays as a complement to, or potential future replacement of, waste effluent testing in whole animals from AMD impacted watersheds subjected to passive and active treatment, correlating observed changes with water chemistry analysis. To accomplish this goal, water samples were collected and in vitro bioassays carried out to investigate generation of reactive oxygen species by the water samples and cytotoxicity against Vero kidney cells, C3A liver cells and trout RTgill-W1 cells. Primary fish gill cultures were established and used as sensitive in vitro models for assessing possible contaminants in water, measuring the induction of cytochrome P450 (CYP) 1A and resultant increase in 7-ethoxyresorufin-o-deethylase activity as a potential biomarker in fish gill cells exposed to polycyclic aromatic hydrocarbons. The genotoxic potential of AMD water on commercially available cell lines was also determined. / The study site was an impacted stream located downstream of a coal mine discharge point whose effluent flowed away from the mine. Water chemistry results suggested high AMD impact evidenced by acidity, elevated sulphates, increased conductivity and presence of heavy metals. Al, Fe, Zn, Mn and Si were the major metals of potential concern in the AMD impacted stream; sulphates and major ions like Ca, K, Na and Mg were present at levels above target water quality range (TWQR) for effluents in receiving stream. The AMD impacted stream caused increased generation of reactive oxygen species (ROS) detectable in vitro in selected cell lines (Vero, C3A and RTgill-W1 cell lines), an indication of oxidative stress. In-stream, active treatment with caustic soda was efficient at reducing metal burden, with subsequent reduction in ROS generation in fish gill cell lines. For in vitro cytotoxicity tests, passive and active treated AMD water was cytotoxic to cell lines (Vero and RTgill-W1), with the fish RTgill-W1 cells exhibiting greater sensitivity compared to the mammalian Vero cells. Mitochondria played a larger role in observed loss in cellular viability (increased vacuolization, mitochondrial membrane swelling and damage), which was detected using mitochondrial specific stains, and by transmission electron microscopy (TEM). Increased dose- dependent cytotoxicity was observed in the fish gill and mammalian cell lines. Cells exposed to water samples (AMD and reference sites) revealed significant differences (p < vi 0.05) between the AMD impacted watershed and a relatively pristine site (reference site) where exposure to the same cells maintained approximately 100% viability at all concentrations for up to 72h exposure. The observed differences in effect in this study demonstrate that the effluent from the coal mine negatively impacted surface water quality, resulting in toxicity to cell lines, therefore creating an environment that would not be conducive for the survival of biological aquatic communities and potentially of concern for downstream human end users. / The induction of cytochrome P450 (CYP) 1A and resultant increase in 7- ethoxyresorufin-o-deethylase activity in primary fish gill cultures exposed to polycyclic aromatic hydrocarbons B[a]P, a known AhR agonist contaminant associated with coal mining, showed that there was as increase in EROD activity which was not observed using the RTgill-W1 cell lines. Gill epithelial cells isolated from the gills of Tilapia fish (Oreochromis mossambicus) bear close similarities to fish gills in vivo and their capacity to respond to the presence of AhR indicates that they may serve as a simple, cost-effect screening tool for assessing PAHs and dioxin-like compounds in fresh water. / For genotoxicity evaluation, the Ames test performed without metabolic activation using bacterium Salmonella typhimurium TA98 and TA100 strains revealed no indication of genotoxic activity in any of the water samples. Genotoxicity assessment of all water samples using the comet assay however exposed DNA damage to Vero and RTgill-W1 cell lines. A significant reduction in DNA damage was observed following active treatment. The results suggest that neither treatment technologies employed were efficient at removing all potential genotoxicants so further improvements are required. The comet assay proved sensitive enough to detect genotoxicity in reference water samples despite no known untoward effluent inputs at the site, suggesting potential for this assay to be integrated into an environmental monitoring framework. / The results obtained support the use of in vitro bioassays for evaluating toxicity of industrial effluent through biological responses in test systems elicited following exposure, improving ability to detect AMD polluted water. This could be beneficial when assessing the degree and extent of impact of AMD in natural water sources, and the possible environmental impact resulting from hazardous elements present in effluent water. In conclusion, these results suggest that in vitro techniques involving cell lines and primary cultures from fish may serve vii as simple, rapid and cost-effective tools for assessing risk and potential toxic effects of contaminants in AMD waters. / Thesis (PhD)--University of Pretoria, 2016. / The National Research Foundation / Department of Paraclinical Sciences (University of Pretoria) / Schlumberger Stichting Fund, Netherlands / Paraclinical Sciences / PhD / Unrestricted

Food contact materials are materials that are intended to come into contact with food, and we are exposed to different types of chemicals that exist in the packages on a daily basis. In this study, a battery of effect‑based in vitro cellular bioassays was used to evaluate the presence of bioactive compounds in commonly used food contact materials made of paper and cardboard, retrieved from the Swedish market. Sample extracts were tested at concentrations 0.3, 1, 3 and 10 mg food contact material/mL cell culture medium. The use of effect-based bioassays allowed for screening of multiple health-relevant endpoints in a non-targeted approach. Hence, taking unknown substances and mixtures into consideration when addressing potential toxicity of the materials. In essence, detection of bioactivity could be considered as moderate to high in assays of positive effects. Antiandrogenic and antiestrogenic effects were found in 72% of the samples, followed by 47% bioactivity in the Nrf2 assay. No androgenic effect was detected. Usage of effect-based bioassays allows for high sensitivity and low detection limits, and these can be used as a first approach to evaluate package materials to ensure the safety of consumers. / Livsmedelsförpackningar är material som är avsedda att komma i kontakt med livsmedel. Vi exponeras för olika typer av kemikalier som existerar i dessa förpackningar varje dag. I denna studie användes ett batteri av effektbaserade in vitro bioanalytiska metoder för att undersöka förekomst av bioaktiva ämnen i vanligen använda livsmedelsförpackningar tillverkade av papper och kartong, insamlade från den svenska marknaden. Provextrakten testades i koncentrationerna 0.3, 1, 3 och 10 mg livsmedelsförpackning/mL cellmedium. Att använda effektbaserade bioanalyser möjliggör undersökning av flertalet hälsorelevanta effekter genom en icke-riktad strategi. På så sätt tas okända substanser och komplexa blandningar i beaktande. Andelen bioaktiva prover kan anses måttlig till hög för positiva analyser. Antiandrogena och antiöstrogena effekter detekterades i 72% av proverna, följt av 47% bioaktivitet i Nrf2 analysen. Ingen agonistisk androgen effekt observerades. Att använda effektbaserade bioanalyser möjliggör hög sensitivitet och detektion vid låga koncentrationer, därför kan dessa användas som ett första steg för att evaluera förpackningsmaterial för att säkra konsumenternas hälsa.

No description available.

No description available.

Passive sampling, as opposed to the conventional spot or bottle water sampling technique, has shown to be reliable and efficient in monitoring the toxicologically relevant, freely dissolved (e.g. bioavaialable) concentrations of a wide range of organic contaminants in water. At the same time, partitioning controlled delivery (passive dosing; PD) techniques promise to overcome many of the challenges associated with toxicity testing of hydrophobic substances that may bias the interpretation of toxicity data. The present study investigated the feasibility of coupling silicone rubber passive sampling devices (SR-PSDs) with bioassay techniques for both chemical and ecotoxicological assessment of complex mixtures of organic contaminants in the aquatic environment. SR-PSDs were deployed in water at various locations within the Ythan catchment (north east, Scotland, UK), Forth estuary and the Firth of Forth (east coast of central Scotland, UK) for 7 to 9 weeks. Following retrieval, extracts from the SR-PSDs were analysed for dissolved concentrations of a variety of organic contaminants including PAHs and PCBs using GC-MS and GC-ECD respectively and were screened for a wide range of pesticides using GC-MS/MS and LC-MS/MS. The extracts were further evaluated for acute cytotoxicity (i.e. neutral red uptake assay) and EROD induction potential using rainbow trout liver cell line (Oncorhynchus mykiss; RTL-W1) and for phytotoxicity and developmental toxicity potential using algal growth inhibition test (with a marine phytoplankton, Diacronema lutheri) and fish embryo toxicity test (with embryos from zebrafish Danio rerio) respectively. Overall, the individual and total dissolved concentrations of PAHs (ΣPAH40; parent and branched) and PCBs (ΣPCB32; ortho and mono-ortho) measured in water from the Ythan, Forth estuary and Firth of Forth were relatively low compared with other studies using PSDs. A number and level of pesticides, including insecticides, herbicides and fungicides of varying hydrophobicity (log KOWs ~2.25 to ~5.31) were detected in the silicone rubber (SR) extracts from the Ythan catchment, the Forth estuary and the Firth of Forth, suggesting input mainly from agricultural run-off and possibly from direct discharges. No statistically significant (p<0.05) acute cytotoxicity was observed following 48 h exposure of RTL-W1 cells to SR extracts from the Ythan catchment. But, on a sublethal level, for every site, statistically significant EROD activity was observed to some degree following 72 h exposure. In addition, developmental and algal toxicities on embryos of D. rerio and D. lutheri respectively, were measured in all the deployed samples compared with the procedural controls (undeployed samples). Interestingly, extracts of SR-PSDs from the Forth estuary and the Firth of Forth exhibited growth inhibitions on D. lutheri that were similar to those of extracts from the Ythan, even though, fewer numbers of pesticides were detected in the Forth estuary and Firth of Forth than the Ythan. This suggests that pesticides were not solely responsible for the observed effects in the Ythan catchment. To further improve data from toxicity testing of hydrophobic substances, the study identified the use of SR O-rings as a suitable passive dosing format in in vitro toxicity tests and was partially validated through their use in dosing RTL-W1 cells with two individual PAHs and subsequently determining cytotoxicity and EROD-activity.