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UNIVERSIDADE FEDERAL DO AMAZONAS PRÓ-REITORIA DE PESQUISA E PÓS-GRADUAÇÃO INSTITUTO DE CIÊNCIAS BIOLÓGICAS PROGRAMA MULTI-INSTITUCIONAL DE PÓS-GRADUAÇÃO EM BIOTECNOLOGIA - PPGBIOTEC CARACTERIZAÇÃO DO POTENCIAL DE DEGRADAÇÃO DE UM ISOLADO BACTERIANO ORIUNDO DA REGIÃO AMAZÔNICA DIOGO PEREIRA DE CASTRO MANAUS - AMAZONAS 2015 UNIVERSIDADE FEDERAL DO AMAZONAS PRÓ-REITORIA DE PESQUISA E PÓS-GRADUAÇÃO INSTITUTO DE CIÊNCIAS BIOLÓGICAS PROGRAMA MULTI-INSTITUCIONAL DE PÓS-GRADUAÇÃO EM BIOTECNOLOGIA - PPGBIOTEC DIOGO PEREIRA DE CASTRO CARACTERIZAÇÃO DO POTENCIAL DE DEGRADAÇÃO DE UM ISOLADO BACTERIANO ORIUNDO DA REGIÃO AMAZÔNICA Tese apresentada ao Programa Multi- Institucional de Pós-Graduação em Biotecnologia da Universidade Federal do Amazonas como parte do pré-requisito para obtenção do título de Doutor em Biotecnologia na área de concentração “Agroflorestal”. Orientadora: Dra. Patrícia Puccinelli Orlandi Co-Orientador: Dr. José Odair Pereira MANAUS - AMAZONAS 2015 ii Ficha Catalográfica Ficha catalográfica elaborada automaticamente de acordo com os dados fornecidos pelo(a) autor(a). Castro, Diogo Pereira de C355c Caracterização do potencial de degradação de um isolado bacteriano oriundo da região Amazônica / Diogo Pereira de Castro. 2015 154 f.: il. color; 31 cm. Orientador: Patrícia Puccinelli Orlandi Coorientador: José Odair Pereira Tese (Doutorado em Biotecnologia) - Universidade Federal do Amazonas. 1. pETRÓLEO. 2. Biorremediação. 3. Degradação de Hidrocarbonetos. 4. Proteômica. I. Orlandi, Patrícia Puccinelli II. Universidade Federal do Amazonas III. Título DIOGO PEREIRA DE CASTRO CARACTERIZAÇÃO DO POTENCIAL DE DEGRADAÇÃO DE UM ISOLADO BACTERIANO ORIUNDO DA REGIÃO AMAZÔNICA Tese apresentada ao Programa Multi- Institucional de Pós-Graduação em Biotecnologia da Universidade Federal do Amazonas como parte do pré-requisito para obtenção do título de Doutor APROVADA EM:______/______/______ em Biotecnologia na área de concentração “Agroflorestal”. BANCA EXAMINADORA _______________________________________________ Profa. Dra. Patrícia Puccinelli Orlandi, Presidente Centro de Pesquisas Leônidas e Maria Deane - FIOCRUZ Amazônia _______________________________________________ Profa. Dra. Ieda Hortêncio Batista Universidade do Estado do Amazonas - UEA _______________________________________________ Profa. Dra. Ana Frazão Teixeira Universidade do Estado do Amazonas - UEA _______________________________________________ Prof. Dr. Donat Alexander De Chapeaurouge Fundação Oswaldo Cruz – FIOCRUZ/IOC _______________________________________________ Prof. Dr. Jorge Luis López-Lozano Fundação Oswaldo Cruz – FIOCRUZ MANAUS – AMAZONAS 2015 iii “A minha esposa Paula Taquita, a meus familiares, a meus amigos e a todos que me ajudaram nessa jornada”. Dedico iv AGRADECIMENTOS Agradeço a Deus pela coragem e força para estar nessa jornada; Minha esposa Paula Taquita pela dedicação, companheirismo, entre outras qualidades - que são inúmeras - sem ela não conseguiria chegar até onde cheguei; A meus pais e minha sogra pelo apoio nessa etapa de vida; A minha orientadora Dra. Patrícia Orlandi pela orientação, paciência e amizade; Ao meu co-Orientador Dr. José Odair Pereira pela orientação e apoio no desenvolvimento da tese; Aos professores Dr. Paulo Afonso Nogueira, Dra. Priscila Aquino, Dra. Tainá Raiol Alencar pelas orientações e apoio cientifico; Ao Dr. Jefferson Rocha pela orientação e colaboração; Ao Dr. Fabrício Klerynon Marchini pelo apoio científico e colaboração; Ao Programa de Pós Graduação em Biotecnologia (PPGBIOTEC) pela oportunidade de estudo; A Sra. Nubiane pela amizade e apoio pedagógico; A todos os amigos do Laboratório da FIOCRUZ-ILMD pelo apoio científico, momentos alegres e ajuda nos experimentos; A Fundação Oswaldo Cruz (FIOCRUZ) ILMD pelo espaço para desenvolvimento do nosso estudo; A FAPEAM e CnPQ agradeço pelo apoio financeiro fornecido no decorrer deste projeto. v “Devemos ter fé. Não existem esforços inúteis se empregados em prol do bem comum”. Getúlio Vargas vi RESUMO A biorremediação é a utilização de microrganismos capazes de metabolizar contaminantes e transforma-los em produtos menos tóxicos. Em estudos anteriores, foi realizado o isolamento de bactérias provenientes de área contaminada por resíduos de petróleo na Amazônia. Apesar de possuírem o potencial de degradação de petróleo, a aplicação de bactérias em ambientes contaminados pode interferir em seu equilíbrio ecológico. Este estudo propôs-se a seleção de uma linhagem bacteriana para promover estudos de caracterização gênica, identificação do potencial de degradação de hidrocarbonetos e definição das proteínas envolvidas no processo de degradação. Para alcançar os objetivos, foram identificadas substâncias degradadas por cromatografia gasosa e proteínas envolvidas por proteômica; A análise do genoma permitiu a caracterização dos genes relacionados a degradação de compostos xenobióticos através da revisão da literatura. A cepa foi identificada como Pseudomonas putida S16. Foram detectadas 51 substâncias por cromatografia gasosa, destas, 23 foram completamente degradadas, incluindo HPAs contendo naftaleno (100%), antraceno (11,49%) e fenantreno (7,41%). Foram identificados 89 genes relacionados a degradação de xenobíoticos no genoma da P. putida S16 AM, genes capazes de degradar naftaleno, antraceno e fenantreno (nah, phn, fdx, catA), produção de citocromo e quimiotaxia. Na análise proteômica, foram expressas proteínas de óxido-redução, processos metabólicos, poliaminas, aldeído desidrogenase, armazenamento de carbono, quimiotaxia e síntese de aminoácidos. Foram identificadas 355 proteínas com redundância expressas durante o contato de 7h da P. putida S16 AM (I4) com o petróleo, e 268 no contato de 75h; Para o glicerol, foram identificadas 467 na interação de 7h, e 228 no contato de 75h. A presença de proteínas relacionadas ao metabolismo e óxido- redução quando a cepa em estudo esteve em contato com o petróleo evidenciam a utilização deste como fonte de carbono para o metabolismo bacteriano. Estes estudos são importantes devido à identificação de genes e proteínas que possuem o potencial de se tornarem produtos biotecnológicos de aplicação prática. Palavras-chave: Petróleo; Biorremediação; Degradação de Hidrocarbonetos; Proteômica. vii ABSTRACT Bioremediation is the use of microorganisms capable of metabolizing contaminants and converts them into less toxic products. In previous studies, we performed bacteria isolation from contaminated area for oil waste in Amazon. Despite its oil degradation potential, the application of bacteria in contaminated sites may interfere with their ecological balance. This study aimed to promote studies of gene characterization and hydrocarbon degradation potential with a selected bacterial strain and identify and define the proteins involved in degradation process. To achieve this objectives degraded substances have been identified by gas chromatography and proteins involved by proteomics; Genome analysis allowed characterization of genes related to xenobiotics degradation. The strain was identified as Pseudomonas putida S16. 51 substances were detected by gas chromatography, of these, 23 were completely degraded, including PAH containing naphthalene (100%), anthracene (11.49%) and phenanthrene (7.41%). We identified 89 genes related to xenobiotic degradation in P. putida S16 AM genome, genes capable of degrading naphthalene, anthracene and phenanthrene (nah, phn, fdx, catA), cytochrome production and chemotaxis. In proteome analysis, proteins were expressed oxidation-reduction, metabolic processes, polyamines, aldehyde dehydrogenase, carbon storage, chemotaxis and amino acid synthesis. 355 proteins were identified with redundancy expressed during 7h contact to P. putida S16 AM (I4) with petroleum, and 268 during 75h contact; For glycerol, 467 were identified in 7h interaction, and 228 in 75h contact. The presence of proteins related to metabolism and oxidation- reduction when the strain under study was in contact to the petroleum suggest the use of this as a carbon source for bacterial metabolism. These studies are important because of identification of genes and proteins with potential to become practical application of biotechnology products. Keywords : Petroleum; Bioremediation; Degradation of Hydrocarbons; Proteomics. viii LISTA DE FIGURAS Figura 1. Biodegradação de um n-alcano.... ............................................................................ 22 Figura 2. Degradação inicial do benzeno por oxigenases como exemplo de biodegradação de substâncias aromáticas. ............................................................................................................. 22 Figura 3. Degradação do catecol pelas vias de orto e meta clivagem. .................................... 23 Figura 4. Degradação de Naftaleno. ........................................................................................ 26 Figura 5. Rota de degradação do fenantreno. .......................................................................... 27 Figura 6. Degradação de antraceno proposto para bactérias aeróbicas ................................... 28 Figura 7. Ion Torrent. Reação de incorporação de uma base pela polimerase. ....................... 31 Figura 8. Esquema do processo de Cromatografia Gasosa acoplada a Espectro de Massa .... 32 Figura 9. Esquema de um espectrômetro de massas ............................................................... 33 Figura 10. Micro gotas expelidas pelo cone de Taylor ..........................................................
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    letters to nature Received 7 July; accepted 21 September 1998. 26. Tronrud, D. E. Conjugate-direction minimization: an improved method for the re®nement of macromolecules. Acta Crystallogr. A 48, 912±916 (1992). 1. Dalbey, R. E., Lively, M. O., Bron, S. & van Dijl, J. M. The chemistry and enzymology of the type 1 27. Wolfe, P. B., Wickner, W. & Goodman, J. M. Sequence of the leader peptidase gene of Escherichia coli signal peptidases. Protein Sci. 6, 1129±1138 (1997). and the orientation of leader peptidase in the bacterial envelope. J. Biol. Chem. 258, 12073±12080 2. Kuo, D. W. et al. Escherichia coli leader peptidase: production of an active form lacking a requirement (1983). for detergent and development of peptide substrates. Arch. Biochem. Biophys. 303, 274±280 (1993). 28. Kraulis, P.G. Molscript: a program to produce both detailed and schematic plots of protein structures. 3. Tschantz, W. R. et al. Characterization of a soluble, catalytically active form of Escherichia coli leader J. Appl. Crystallogr. 24, 946±950 (1991). peptidase: requirement of detergent or phospholipid for optimal activity. Biochemistry 34, 3935±3941 29. Nicholls, A., Sharp, K. A. & Honig, B. Protein folding and association: insights from the interfacial and (1995). the thermodynamic properties of hydrocarbons. Proteins Struct. Funct. Genet. 11, 281±296 (1991). 4. Allsop, A. E. et al.inAnti-Infectives, Recent Advances in Chemistry and Structure-Activity Relationships 30. Meritt, E. A. & Bacon, D. J. Raster3D: photorealistic molecular graphics. Methods Enzymol. 277, 505± (eds Bently, P. H. & O'Hanlon, P. J.) 61±72 (R. Soc. Chem., Cambridge, 1997).
  • The Microbiota-Produced N-Formyl Peptide Fmlf Promotes Obesity-Induced Glucose

    The Microbiota-Produced N-Formyl Peptide Fmlf Promotes Obesity-Induced Glucose

    Page 1 of 230 Diabetes Title: The microbiota-produced N-formyl peptide fMLF promotes obesity-induced glucose intolerance Joshua Wollam1, Matthew Riopel1, Yong-Jiang Xu1,2, Andrew M. F. Johnson1, Jachelle M. Ofrecio1, Wei Ying1, Dalila El Ouarrat1, Luisa S. Chan3, Andrew W. Han3, Nadir A. Mahmood3, Caitlin N. Ryan3, Yun Sok Lee1, Jeramie D. Watrous1,2, Mahendra D. Chordia4, Dongfeng Pan4, Mohit Jain1,2, Jerrold M. Olefsky1 * Affiliations: 1 Division of Endocrinology & Metabolism, Department of Medicine, University of California, San Diego, La Jolla, California, USA. 2 Department of Pharmacology, University of California, San Diego, La Jolla, California, USA. 3 Second Genome, Inc., South San Francisco, California, USA. 4 Department of Radiology and Medical Imaging, University of Virginia, Charlottesville, VA, USA. * Correspondence to: 858-534-2230, [email protected] Word Count: 4749 Figures: 6 Supplemental Figures: 11 Supplemental Tables: 5 1 Diabetes Publish Ahead of Print, published online April 22, 2019 Diabetes Page 2 of 230 ABSTRACT The composition of the gastrointestinal (GI) microbiota and associated metabolites changes dramatically with diet and the development of obesity. Although many correlations have been described, specific mechanistic links between these changes and glucose homeostasis remain to be defined. Here we show that blood and intestinal levels of the microbiota-produced N-formyl peptide, formyl-methionyl-leucyl-phenylalanine (fMLF), are elevated in high fat diet (HFD)- induced obese mice. Genetic or pharmacological inhibition of the N-formyl peptide receptor Fpr1 leads to increased insulin levels and improved glucose tolerance, dependent upon glucagon- like peptide-1 (GLP-1). Obese Fpr1-knockout (Fpr1-KO) mice also display an altered microbiome, exemplifying the dynamic relationship between host metabolism and microbiota.
  • Solarbio Catalogue with PRICES

    Solarbio Catalogue with PRICES

    CAS Name Grade Purity Biochemical Reagent Biochemical Reagent 75621-03-3 C8390-1 3-((3-Cholamidopropyl)dimethylammonium)-1-propanesulfonateCHAPS Ultra Pure Grade 1g 75621-03-3 C8390-5 3-((3-Cholamidopropyl)dimethylammonium)-1-propanesulfonateCHAPS 5g 57-09-0 C8440-25 Cetyl-trimethyl Ammonium Bromide CTAB High Pure Grade ≥99.0% 25g 57-09-0 C8440-100 Cetyl-trimethyl Ammonium Bromide CTAB High Pure Grade ≥99.0% 100g 57-09-0 C8440-500 Cetyl-trimethyl Ammonium Bromide CTAB High Pure Grade ≥99.0% 500g E1170-100 0.5M EDTA (PH8.0) 100ml E1170-500 0.5M EDTA (PH8.0) 500ml 6381-92-6 E8030-100 EDTA disodium salt dihydrate EDTA Na2 Biotechnology Grade ≥99.0% 100g 6381-92-6 E8030-500 EDTA disodium salt dihydrate EDTA Na2 Biotechnology Grade ≥99.0% 500g 6381-92-6 E8030-1000 EDTA disodium salt dihydrate EDTA Na2 Biotechnology Grade ≥99.0% 1kg 6381-92-6 E8030-5000 EDTA disodium salt dihydrate EDTA Na2 Biotechnology Grade ≥99.0% 5kg 60-00-4 E8040-100 Ethylenediaminetetraacetic acid EDTA Ultra Pure Grade ≥99.5% 100g 60-00-4 E8040-500 Ethylenediaminetetraacetic acid EDTA Ultra Pure Grade ≥99.5% 500g 60-00-4 E8040-1000 Ethylenediaminetetraacetic acid EDTA Ultra Pure Grade ≥99.5% 1kg 67-42-5 E8050-5 Ethylene glycol-bis(2-aminoethylether)-N,N,NEGTA′,N′-tetraacetic acid Ultra Pure Grade ≥97.0% 5g 67-42-5 E8050-10 Ethylene glycol-bis(2-aminoethylether)-N,N,NEGTA′,N′-tetraacetic acid Ultra Pure Grade ≥97.0% 10g 50-01-1 G8070-100 Guanidine Hydrochloride Guanidine HCl ≥98.0%(AT) 100g 50-01-1 G8070-500 Guanidine Hydrochloride Guanidine HCl ≥98.0%(AT) 500g 56-81-5