Os desreguladores endócrinos são compostos micropoluentes de ação deletéria que causam efeitos aos animais e aos seres humanos. Estes vêm trazendo a várias décadas, problemas relacionados à má formação ou ainda infertilidade de várias espécies. A presença destes compostos na ordem de ng L-1 já é capaz de gerar efeitos nocivos ao sistema endócrino. Este trabalho visou à determinação da presença e quantidade de alguns destes compostos como 17α-etinilestradiol, bisfenol A e estrona entre outros, nas águas do rio Arroio Fundo, localizado em Jacarepaguá no RJ que possui um índice de qualidade de água ruim. A primeira etapa deste trabalho foi a implementação e validação de metodologia para determinação do 17α-etinilestradiol por cromatografia líquida acoplada a detector de fluorescência onde foram estabelecido limite de detecção, de quantificação e linearidade conforme orientação do Inmetro (2010). Além da avaliação das amostras ambientais através da metodologia estabelecida. Na etapa subsequente foram realizados os experimentos relativos à determinação dos desreguladores endócrinos através da espectrometria de massas por detector tipo tandem quadrupolo, onde também foram realizados os procedimentos de validação e determinação dos compostos bisfenol A e estrona que não foram suscetíveis a efeito de matriz durante a ionização, que acabou impedindo a determinação de outros desreguladores endócrinos. Os resultados indicam que não há redução da presença dos desreguladores endócrinos detectados, e de outros compostos orgânicos também detectados, mas não identificados, entre os pontos a montante e a jusante da Unidade de Tratamento do Rio Arroio Fundo. Todavia em função do grande efeito de matriz oriundo do fato da amostra ser de extrema complexidade, não foi possível realizar uma identificação e quantificação de todos os compostos alvos. / Endocrine disrupters are compounds micropollutants of deleterious effects that cause effects to animals and humans has brought these problems to several decades related to poor training or infertility of various species. The presence of these compounds in the ng L-1 order is already capable of generating negative effects on the endocrine system. This work aimed at determining the presence and amount of some of these compounds as 17α-ethinylestradiol, bisphenol A and estrone among others, in the waters of the river Arroio Fundo, located in Jacarepaguá in Rio de Janeiro that has a bad water quality index. The first stage of this work was the implementation and validation of a method for determination of 17α-ethinylestradiol by liquid chromatography-fluorescence detection which were established limit of detection, quantification and linearity as directed by Inmetro (2010). Besides the evaluation of the samples through the established methodology. In subsequent step were carried out experiments on the determination of endocrine disruptors by tandem quadrupole mass spectrometry detector, were being performed validation procedures and determination of the compounds bisphenol A and estrone, which were not susceptible to matrix effect during ionization, which prevented the determination of other endocrine disrupters. The results indicate that there is no reduction of the presence of detected endocrine disruptors and other organic compounds, also detected but not identified, between the points upstream and downstream of Arroio Fundo treatment plant. However due to the large matrix effect originating from the fact that the sample be extremely complex, could not perform an identification and quantification of all target compounds.

Due to the current rise of exposure to natural and synthetic compounds in our daily life, the debate concerning the safety of many substances is becoming increasingly relevant. The estrogenic activity of various compounds, described as xenoestrogens, is the major part of this debate. Humans beings are exposed to these substances from different environmental contaminations ranging from conscious intake of estrogenic substances, as in contraception or in hormone replace therapy (HRT), to unconscious exposure, from food, the use of synthetic material in daily life and air and water pollution. At this point the need for methods to investigate the activity and the safety of these substances is becoming increasingly important. Classical methods for the analysis of the estrogenic activity of substances, like batteries of in vivo test systems on the rat uterotrophic assay are not able to describe the different pathways of action of recently discovered estrogenic substances. This evidence was already shown by the Organization for Economic Cooperation and Development (OECD), introducing new test guidelines for the investigation of effects of endocrine disruptors (according to enhanced Test Guideline 407). As reviewed by Nilsson (Nilsson et al., 2001), after the interaction of the estrogens with the Estrogen Receptor (ER) in the cells, the mechanism of activation possible is not only via direct binding of the ER to the Estrogen Responsive Elements (EREs) present in the promoter region of the target gene, very well described for many target genes, but that also other mechanisms are used: the interaction of the ER with the AP 1, Sp 1 and NFkB modes, that are discovered but not yet comprehensively described. The aim of my work is to produce a microarray DNA chip for the investigation of the estrogenic activity of different compounds present in the environment. The chip will consist of a selection of 100 genes that are estrogen responsive and it will cover the spectrum of activities of estrogenic compounds in various organs of the body. In the gene selection, genes were chosen that are estrogen responsive in the classical target tissues of estrogens, linked to reproduction, like uterus and mammary gland, and also in tissues not related to reproduction like liver, bones and capillars. In addition, other genes are included to monitor different pathways that are related to disease states; control of cell proliferation, apoptosis or cancer related genes. Currently these kinds of investigations are already in process, but by other methods which are more time consuming and with a lower throughput e.g. the gene expression profiling using the real time RT-PCR. The use of microarray’s satisfies the need for a less time consuming, high throughput method, to obtain a fast characterization of the gene expression finger print of the candidate substances and their mechanism of action in the organism. In my work I investigated the estrogenic potency of different Xenoestrogens that commonly occur in our daily life, in rat cells and tissue using well known estrogen sensitive genes like C3, Clu, IGFBP1 and CaBP9k. I focused on their effect on cell proliferation, studying PCNA expression. For the first time sensitivity of the gene CA2 was proofed in liver and uterus. A new identified mRNA sequence, r52, was characterized for its sensitivity to estrogenic exposure. This sequence was investigated at the molecular level expanding the known nucleic sequence. I produce a microarray chip with 16 genes to investigate the estrogenic potency of different compounds. As proof of principle of the microarray method completely produced in house I compared the result of gene expression obtained by the chip to that obtained by real time RT PCR finding a similarity of results. This new established method is less sensitive than the real-time RT PCR but allows a high throughput of gene expression analysis producing at the end a more complete picture of the expression signature of a compound.

Today a lot of attention is focused on compounds called endocrine disrupters (EDs) among substances released to environment by humans. They are a group of substances which can disturb function of hormonal system of organisms including humans. Their poor removal at wastewater treatment plants (WwTP) were shown at various studies, thus they can reach the environment in water. A prospective way for the degradation of EDs at WwTP can be their removal by ligninolytic fungi. They are able to degrade lots of lignin-like aromatic substances because of their highly nonspecific enzymes. In this work growth and enzyme production capability of four ligninolytic fungal strains were monitored on three solid substrates (straw pellets, poplar sawdust mixed with straw pellets, oak sawdust with straw pellets), which may be suitable substrates for fungal growth in bioreactors for wastewater treatment. Ability of these enzymes to degrade EDs were tested in in-vitro degradation experiment. Trametes versicolor was found as best degrading strain with 20 μg/ml of bisphenol A, 17 α- ethynylestradiol and nonylphenol degraded below a quantification limit within 24 hours. Fungal strains degraded EDs well on all of the three substrates but wood sawdust seemed to be a better substrate for fungal growth because straw pellets...