Ação biocida do Poliquilgerm® derivado dom óleo de Ricinus Communis L. (mamona) sobre bactérias contaminantes da fermentação etanólica

Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq)

Bacterial and chemical leaching of chalcopyrite concentrates as affected by the redox potential and ferric/ferrous iron ratio at 22 degrees C

Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq)

Dynamics of biofilm formation and the interaction between candida albicans and methicillin-susceptible (MSSA) and -resistant staphylococcus aureus (MRSA)

Coordenação de Aperfeicoamento de Pessoal de Nivel Superior (CAPES)

Dynamics of biofilm formation and the interaction between candida albicans and methicillin-susceptible (MSSA) and -resistant staphylococcus aureus (MRSA)

Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES)

Effect of tyrosol on adhesion of Candida albicans and Candida glabrata to acrylic surfaces

The prevention of adhesion of Candida cells to acrylic surfaces can be regarded as an alternative to prevent denture stomatitis. The use of quorum sensing molecules, such as tyrosol, could potentially interfere with the adhesion process. Therefore, the aim of this study was to assess the effect of tyrosol on adhesion of single and mixed cultures of Candida albicans and Candida glabrata to acrylic resin surfaces. Tyrosol was diluted in each yeast inoculum (10(7) cells/ml in artificial saliva) at 25, 50, 100, and 200 mM. Then, each dilution was added to wells of 24-well plates containing the acrylic specimens, and the plates were incubated at 37°C for 2 h. After, the effect of tyrosol was determined by total biomass quantification, metabolic activity of the cells and colony-forming unit counting. Chlorhexidine gluconate (CHG) was used as a positive control. Data were analyzed using analysis of variance (ANOVA) and the Holm-Sidak post hoc test (α = 0.05). The results of total biomass quantification and metabolic activity revealed that the tyrosol promoted significant reductions (ranging from 22.32 to 86.16%) on single C. albicans and mixed cultures. Moreover, tyrosol at 200 mM and CHG significantly reduced (p < 0.05) the number of adhered cells to the acrylic surface for single and mixed cultures of both species, with reductions ranging from 1.74 to 3.64-log10. In conclusion, tyrosol has an inhibitory effect on Candida adhesion to acrylic resin, and further investigations are warranted to clarify its potential against Candida infections.

Exploração racional da rizosfera de Senna spectabilis: interações entre as bactérias Pseudoxanthomonas indica e Shigella sp.

Pós-graduação em Química - IQ

Interação entre bactérias cariogênicas

Fundação de Amparo à Pesquisa do Estado de São Paulo (FAPESP)

Bioremediation of PAHs - Limitations and soultions

Introduction 1.1 Occurrence of polycyclic aromatic hydrocarbons (PAH) in the environment Worldwide industrial and agricultural developments have released a large number of natural and synthetic hazardous compounds into the environment due to careless waste disposal, illegal waste dumping and accidental spills. As a result, there are numerous sites in the world that require cleanup of soils and groundwater. Polycyclic aromatic hydrocarbons (PAHs) are one of the major groups of these contaminants (Da Silva et al., 2003). PAHs constitute a diverse class of organic compounds consisting of two or more aromatic rings with various structural configurations (Prabhu and Phale, 2003). Being a derivative of benzene, PAHs are thermodynamically stable. In addition, these chemicals tend to adhere to particle surfaces, such as soils, because of their low water solubility and strong hydrophobicity, and this results in greater persistence under natural conditions. This persistence coupled with their potential carcinogenicity makes PAHs problematic environmental contaminants (Cerniglia, 1992; Sutherland, 1992). PAHs are widely found in high concentrations at many industrial sites, particularly those associated with petroleum, gas production and wood preserving industries (Wilson and Jones, 1993). 1.2 Remediation technologies Conventional techniques used for the remediation of soil polluted with organic contaminants include excavation of the contaminated soil and disposal to a landfill or capping - containment - of the contaminated areas of a site. These methods have some drawbacks. The first method simply moves the contamination elsewhere and may create significant risks in the excavation, handling and transport of hazardous material. Additionally, it is very difficult and increasingly expensive to find new landfill sites for the final disposal of the material. The cap and containment method is only an interim solution since the contamination remains on site, requiring monitoring and maintenance of the isolation barriers long into the future, with all the associated costs and potential liability. A better approach than these traditional methods is to completely destroy the pollutants, if possible, or transform them into harmless substances. Some technologies that have been used are high-temperature incineration and various types of chemical decomposition (for example, base-catalyzed dechlorination, UV oxidation). However, these methods have significant disadvantages, principally their technological complexity, high cost , and the lack of public acceptance. Bioremediation, on the contrast, is a promising option for the complete removal and destruction of contaminants. 1.3 Bioremediation of PAH contaminated soil & groundwater Bioremediation is the use of living organisms, primarily microorganisms, to degrade or detoxify hazardous wastes into harmless substances such as carbon dioxide, water and cell biomass Most PAHs are biodegradable unter natural conditions (Da Silva et al., 2003; Meysami and Baheri, 2003) and bioremediation for cleanup of PAH wastes has been extensively studied at both laboratory and commercial levels- It has been implemented at a number of contaminated sites, including the cleanup of the Exxon Valdez oil spill in Prince William Sound, Alaska in 1989, the Mega Borg spill off the Texas coast in 1990 and the Burgan Oil Field, Kuwait in 1994 (Purwaningsih, 2002). Different strategies for PAH bioremediation, such as in situ , ex situ or on site bioremediation were developed in recent years. In situ bioremediation is a technique that is applied to soil and groundwater at the site without removing the contaminated soil or groundwater, based on the provision of optimum conditions for microbiological contaminant breakdown.. Ex situ bioremediation of PAHs, on the other hand, is a technique applied to soil and groundwater which has been removed from the site via excavation (soil) or pumping (water). Hazardous contaminants are converted in controlled bioreactors into harmless compounds in an efficient manner. 1.4 Bioavailability of PAH in the subsurface Frequently, PAH contamination in the environment is occurs as contaminants that are sorbed onto soilparticles rather than in phase (NAPL, non aqueous phase liquids). It is known that the biodegradation rate of most PAHs sorbed onto soil is far lower than rates measured in solution cultures of microorganisms with pure solid pollutants (Alexander and Scow, 1989; Hamaker, 1972). It is generally believed that only that fraction of PAHs dissolved in the solution can be metabolized by microorganisms in soil. The amount of contaminant that can be readily taken up and degraded by microorganisms is defined as bioavailability (Bosma et al., 1997; Maier, 2000). Two phenomena have been suggested to cause the low bioavailability of PAHs in soil (Danielsson, 2000). The first one is strong adsorption of the contaminants to the soil constituents which then leads to very slow release rates of contaminants to the aqueous phase. Sorption is often well correlated with soil organic matter content (Means, 1980) and significantly reduces biodegradation (Manilal and Alexander, 1991). The second phenomenon is slow mass transfer of pollutants, such as pore diffusion in the soil aggregates or diffusion in the organic matter in the soil. The complex set of these physical, chemical and biological processes is schematically illustrated in Figure 1. As shown in Figure 1, biodegradation processes are taking place in the soil solution while diffusion processes occur in the narrow pores in and between soil aggregates (Danielsson, 2000). Seemingly contradictory studies can be found in the literature that indicate the rate and final extent of metabolism may be either lower or higher for sorbed PAHs by soil than those for pure PAHs (Van Loosdrecht et al., 1990). These contrasting results demonstrate that the bioavailability of organic contaminants sorbed onto soil is far from being well understood. Besides bioavailability, there are several other factors influencing the rate and extent of biodegradation of PAHs in soil including microbial population characteristics, physical and chemical properties of PAHs and environmental factors (temperature, moisture, pH, degree of contamination). Figure 1: Schematic diagram showing possible rate-limiting processes during bioremediation of hydrophobic organic contaminants in a contaminated soil-water system (not to scale) (Danielsson, 2000). 1.5 Increasing the bioavailability of PAH in soil Attempts to improve the biodegradation of PAHs in soil by increasing their bioavailability include the use of surfactants , solvents or solubility enhancers.. However, introduction of synthetic surfactant may result in the addition of one more pollutant. (Wang and Brusseau, 1993).A study conducted by Mulder et al. showed that the introduction of hydropropyl-ß-cyclodextrin (HPCD), a well-known PAH solubility enhancer, significantly increased the solubilization of PAHs although it did not improve the biodegradation rate of PAHs (Mulder et al., 1998), indicating that further research is required in order to develop a feasible and efficient remediation method. Enhancing the extent of PAHs mass transfer from the soil phase to the liquid might prove an efficient and environmentally low-risk alternative way of addressing the problem of slow PAH biodegradation in soil.

Mikrobiologie der Fermentation in NawaRo-Biogasanlagen unter besonderer Berücksichtigung des Abbaus von Propionsäure

In NawaRo-Biogasanlagen (BGA) kann es durch das Angebot an leicht fermentierbaren Kohlenstoff¬quel¬len zu einer bakteriell bedingten Übersäuerung durch unerwünschte kurzkettige Fettsäuren kommen. Häufiger kommt es zur Akkumulation von Propionsäure. Methanogene Archaea können bei niedrigen pH-Werten nicht mehr wachsen. Somit kann der gesamte Prozess der mikrobiellen Bildung von Biogas zum Erliegen kom¬men, was für die Biogasbetreiber zu erheblichen finanziellen Verlusten führt. Das Ziel dieser Disserta¬tion war die Aufklärung der anaeroben bakteriellen Population, die in Biogasanlagen Propionsäure ab¬bauen kann. Aus Propionat entsteht dabei Acetat und Wasserstoff. Da dieser anaerobe Prozess endergon verläuft, kann Propionsäure anaerob nur abgebaut werden, wenn der Wasserstoffpartialdruck niedrig ge¬halten wird. Diese Aufgabe erfüllen in Biogasanalgen methanogene Archaea. Die sog. sekundären Gärer leben somit in synthropher Kultur mit methanogenen Archaea.rnIn dieser Arbeit wurden die Mikroorganismen von Propionsäure-abbauenden Anreicherungskulturen aus vier NawaRo-BGA‘s identifiziert und ihr Substrat- und Produktspektrum analysiert. Die Anreicherungskul¬turen wurden vom Prüf- und Forschungsinstitut e. V. in Pirmasens zur Verfügung gestellt. Durch Analyse der bakteriellen 16S rDNA-Sequenzen der erhaltenen stabilen Propionsäure-abbauenden Mischkulturen wurde gezeigt, dass sich unter den Bakterien hauptsächlich Verwandte von den Clostridiales, aber auch Bacteroides sp., δ-, ε- so¬wie γ-Proteobakterien, Spirochäten, Synergistales und ungewöhnlicher Weise auch Thermotogales befanden. Aus Propionsäure-abbauenden Mischkulturen und aus Fermentern mesophiler NawaRo-Biogasanlagen wurden anaerobe Bakterien und methanogene Archaea angereichert und isoliert. Es wurden aus den Propionsäure-abbauenden Mischkulturen Stämme in Reinkultur erhalten, die entsprechend der 16S rDNA-Analyse als Clostridium sartagoforme Stamm Ap1a520 und Proteiniphilum acetatigenes Stamm Fp1a520 identifiziert wurden. Sowohl aus Fermentern und Nachgärern von drei NawaRo-BGA‘s als auch aus zwei Laborfermentern des Leibniz-Instituts für Agrartechnik in Potsdam-Bornim e.V. (ATB) wurden Reinkulturen von methanogenen Archaea erhalten. Diese konnten den Species Methanobacterium formicicum, Metha¬noculleus bourgensis, Methanosarcina barkeri, Methanosarcina mazei, Methanosarcina sp., Methanosaeta concilii und Methanomethylovorans sp. zugeordnet werden. Damit wurden in dieser Arbeit unter anderem die typischen bisher nur durch molekularbiologische Methoden identifizierten Species methanogener Ar¬chaea aus unterschiedlichen Fermentern in Reinkultur erhalten. Dabei wurde gezeigt, dass die specifically amplified polymorphic DNA-PCR (SAPD-PCR) eine geeignete Methode darstellt, Stämme der gleichen Art methanogener Archaea voneinander zu unterscheiden. Die Methanproduktion der kultivierten methanoge¬nen Archaea wurde gaschromatographisch analysiert. Es zeigte sich, dass die hydrogenotrophe Metha¬nogenese der effizientere und ergiebigere Weg zur Bildung von Methan ist. Mit der Bestimmung der Zellzahl des Isolates Methanoculleus bourgensis Stamm TAF1.1 bei gleichzeitiger Messung der Methanbildung wurde gezeigt, dass die Methanbildung nicht zwangsläufig mit dem Wachstum korreliert. Ne-ben Pflanzenfasern beinhalteten das hergestellte Reaktorfiltrat in den Kultivierungsansätzen Acetat, die essentielle Aminosäure Valin und den Zuckeralkohol Glycerol. Gezielte Misch¬kul¬turen von sekundären Gärern mit methanogenen Isolaten ergaben einen fördernden Einfluss auf diese Bak¬terien durch hydrogenotrophe Archaea. Diese Bakterien bauten Substrate ab oder bildeten Produkte, die sie unter den gegebenen Bedingungen ohne hydrogenotrophe Archaea nicht umsetzen konnten.

Mikrobielle Prozesskontrolle in Biogasanlagen durch Monitoring der Kohlenstoff-Isotopenverhältnisse im Gasbereich

Der zunehmende Anteil von Strom aus erneuerbaren Energiequellen erfordert ein dynamisches Konzept, um Spitzenlastzeiten und Versorgungslücken aus der Wind- und Solarenergie ausgleichen zu können. Biogasanlagen können aufgrund ihrer hohen energetischen Verfügbarkeit und der Speicherbarkeit von Biogas eine flexible Energiebereitstellung ermöglichen und darüber hinaus über ein „Power-to-Gas“-Verfahren bei einem kurzzeitigen Überschuss von Strom eine Überlastung des Stromnetzes verhindern. Ein nachfrageorientierter Betrieb von Biogasanlagen stellt jedoch hohe Anforderungen an die Mikrobiologie im Reaktor, die sich an die häufig wechselnden Prozessbedingungen wie der Raumbelastung im Reaktor anpassen muss. Eine Überwachung des Fermentationsprozesses in Echtzeit ist daher unabdingbar, um Störungen in den mikrobiellen Gärungswegen frühzeitig erkennen und adäquat entgegenwirken zu können. rnBisherige mikrobielle Populationsanalysen beschränken sich auf aufwendige, molekularbiologische Untersuchungen des Gärsubstrates, deren Ergebnisse dem Betreiber daher nur zeitversetzt zur Verfügung stehen. Im Rahmen dieser Arbeit wurde erstmalig ein Laser-Absorptionsspektrometer zur kontinuierlichen Messung der Kohlenstoff-Isotopenverhältnisse des Methans an einer Forschungsbiogasanlage erprobt. Dabei konnten, in Abhängigkeit der Raumbelastung und Prozessbedingungen variierende Isotopenverhältnisse gemessen werden. Anhand von Isolaten aus dem untersuchten Reaktor konnte zunächst gezeigt werden, dass für jeden Methanogenesepfad (hydrogeno-troph, aceto¬klastisch sowie methylotroph) eine charakteristische, natürliche Isotopensignatur im Biogas nachgewiesen werden kann, sodass eine Identifizierung der aktuell dominierenden methanogenen Reaktionen anhand der Isotopen-verhältnisse im Biogas möglich ist. rnDurch den Einsatz von 13C- und 2H-isotopen¬markierten Substraten in Rein- und Mischkulturen und Batchreaktoren, sowie HPLC- und GC-Unter¬suchungen der Stoffwechselprodukte konnten einige bislang unbekannte C-Flüsse in Bioreaktoren festgestellt werden, die sich wiederum auf die gemessenen Isotopenverhältnisse im Biogas auswirken können. So konnte die Entstehung von Methanol sowie dessen mikrobieller Abbauprodukte bis zur finalen CH4-Bildung anhand von fünf Isolaten erstmalig in einer landwirtschaftlichen Biogasanlage rekonstruiert und das Vorkommen methylotropher Methanogenesewege nachgewiesen werden. Mithilfe molekularbiologischer Methoden wurden darüber hinaus methanoxidierende Bakterien zahlreicher, unbekannter Arten im Reaktor detektiert, deren Vorkommen aufgrund des geringen O2-Gehaltes in Biogasanlagen bislang nicht erwartet wurde. rnDurch die Konstruktion eines synthetischen DNA-Stranges mit den Bindesequenzen für elf spezifische Primerpaare konnte eine neue Methode etabliert werden, anhand derer eine Vielzahl mikrobieller Zielorganismen durch die Verwendung eines einheitlichen Kopienstandards in einer real-time PCR quantifiziert werden können. Eine über 70 Tage durchgeführte, wöchentliche qPCR-Analyse von Fermenterproben zeigte, dass die Isotopenverhältnisse im Biogas signifikant von der Zusammensetzung der Reaktormikrobiota beeinflusst sind. Neben den aktuell dominierenden Methanogenesewegen war es auch möglich, einige bakterielle Reaktionen wie eine syntrophe Acetatoxidation, Acetogenese oder Sulfatreduktion anhand der δ13C (CH4)-Werte zu identifizieren, sodass das hohe Potential einer kontinuierlichen Isotopenmessung zur Prozessanalytik in Biogasanlagen aufgezeigt werden konnte.rn

Neurotoxicity of glia activated by gram-positive bacterial products depends on nitric oxide production

The present study examined the mechanism by which bacterial cell walls from two gram-positive meningeal pathogens, Streptococcus pneumoniae and the group B streptococcus, induced neuronal injury in primary cultures of rat brain cells. Cell walls from both organisms produced cellular injury to similar degrees in pure astrocyte cultures but not in pure neuronal cultures. Cell walls also induced nitric oxide production in cultures of astrocytes or microglia. When neurons were cultured together with astrocytes or microglia, the cell walls of both organisms became toxic to neurons. L-NAME, a nitric oxide synthase inhibitor, protected neurons from cell wall-induced toxicity in mixed cultures with glia, as did dexamethasone. In contrast, an excitatory amino acid antagonist (MK801) had no effect. Low concentrations of cell walls from either gram-positive pathogen added together with the excitatory amino acid glutamate resulted in synergistic neurotoxicity that was inhibited by L-NAME. The induction of nitric oxide production and neurotoxicity by cell walls was independent of the presence of serum, whereas endotoxin exhibited these effects only in the presence of serum. We conclude that gram-positive cell walls can cause toxicity in neurons by inducing the production of nitric oxide in astrocytes and microglia.

RESPONSES OF INDICATOR AND PATHOGENIC BACTERIA TO THE PRESENCE OF CARBARYL IN WATER

Biodegradability is a desirable, if not a necessary characteristic of pesticides. Carbaryl, as Sevin, is one of the more widely used insecticides for the control of agricultural pests and has been reported to be readily degraded by microorganisms. Because of its broad application, the concentration of Sevin in surface waters has been reported to reach nearly four parts per million (PPM) in surface waters, where it has been reported to affect the growth and metabolic rates of aquatic bacterial populations. Following these reports, it is of public health importance to determine the effects of this insecticide on the growth and metabolic rates of bacteria used to indicate water pollution, and on pathogenic organisms which are found in polluted water.^ This study was conducted to determine the effect of carbaryl on the growth and metabolic rates of indicator and pathogenic organisms. Escherichia coli and Streptococcus faecalis were used as indicators, while Staphylococcus aureus and Salmonella typhimurium were the pathogens studied. Pure and mixed cultures of these organisms were exposed to two concentrations of carbaryl (Sevin).^ The study demonstrated that the fecal pollution indicator organisms, E. coli and S. faecalis respond differently to the presence of small concentrations of carbaryl in water as do the two pathogens tested, (S. typhimurium and S. aureus). The growth of all test organisms as measured by spread plate counts, was reduced by the presence of either one mg/l or five mg/l carbaryl within a period of eight days. Survival of the organisms in the presence of five mg/l carbaryl varied dependent upon whether the organism was in pure or mixed culture. In the presence of five mg/l carbaryl, both pure and mixed culture of E. coli showed longer survival. S. faecalis survived for more than eight days in pure culture, neither S. typhimurium nor S. aureus survived for eight days in pure culture.^ The metabolic rate of S. faecalis and S. aureus was reduced by both five mg/l and one mg/l Sevin concentrations, contrary to E. coli and S. typhimurium which had reduced metabolic rate with the introduction of five mg/l Sevin but showed an increase in the metabolic rate with one mg/l Sevin. There was no difference between the test and control when mixed populations were exposed to five mg/l Sevin and the metabolic rate tested. A mixture of E. coli and S. typhimurium populations showed a respiration increase over the control when exposed to one mg/l Sevin concentration. If similar effects occur in polluted surface waters, misleading results from bacteriological water quality testing may occur. ^

Proceedings of the 14th Annual Biochemical Engineering Symposium

The Annual Biochemical Engineering Symposium series is devoted to presentations by students on their research topics. The fourteenth event, held in 1984, was organized at the University of Missouri–Columbia. It was attended by the biochemical engineering faculty and the students from Colorado State University, Iowa State University, Kansas State University, University of Missouri–Columbia, University of Missouri–Rolla and Washington University, St. Louis. Contents"Estimation of Product Formation Kinetics and Microbial Yield Parameters for Anaerobic Organic Acid and Solvent Production," M.D. Oner, Kansas State University "Characterization of Soy Protein Texturization in a Complex Bioreactor," J.L. Ibave, Colorado State University "Acid and Solvent Fermentations Using Mixed Cultures," D. Stevens, University of Missouri–Columbia "Preliminary Process Design for Ethanol from Sweet Sorghum Ensilage Feedstock," Keith D. Lange, Colorado State University "Lamella Settlers in Ethanol Fermentation," Yong Jayanata, University of Missouri–Columbia "Bubble Size Distribution in the Down Flow Section of an Air-Lift Column," Snehal A. Patel and C.H. Lee, Kansas State University "The Sensitivity of Plant Cells to Shear Stress," Morris Z. Resenberg and Eric H. Dunlap, Washington University, St. Louis "Estimation of Growth Yield Parameters Associated with Microbial Growth," Hyeon Y. Lee, Kansas State University "Capillary Gas Chromatography of Trimethylsilylated Trisaccharides," Etienne J.M. Selosse, Iowa State University "Subsite Mapping of an Endo-Xylanase Labeled Xylooligo-saccharides," Bernard Y. Tao, Iowa State University "Cellulase Enzyme Recycle," Kate M.V. Baptie, Colorado State University "Non-Homogeneous Poisson Renewal Reward Process for Modelling Enzymatic Hydrolysis of Cellulose," M.M. Gharpuray and L.T. Fan, Kansas State University

Cell-cell communication regulates the effects of protein aspartate phosphatases on the phosphorelay controlling development in Bacillus subtilis.

Rap phosphatases are a recently discovered family of protein aspartate phosphatases that dephosphorylate the Spo0F--P intermediate of the phosphorelay, thus preventing sporulation of Bacillus subtilis. They are regulators induced by physiological processes that are antithetical to sporulation. The RapA phosphatase is induced by the ComP-ComA two-component signal transduction system responsible for initiating competence. RapA phosphatase activity was found to be controlled by a small protein, PhrA, encoded on the same transcript as RapA. PhrA resembles secreted proteins and the evidence suggests that it is cleaved by signal peptidase I and a 19-residue C-terminal domain is secreted from the cell. The sporulation deficiency caused by the uncontrolled RapA activity of a phrA mutant can be complemented by synthetic peptides comprising the last six or more of the C-terminal residues of PhrA. Whether the peptide controls RapA activity directly or by regulating its synthesis remains to be determined. Complementation of the phrA mutant can also be obtained in mixed cultures with a wild-type strain, suggesting the peptide may serve as a means of communication between cells. Importation of the secreted peptide required the oligopeptide transport system. The sporulation deficiency of oligopeptide transport mutants can be suppressed by mutating the rapA and rapB genes or by introduction of a spo0F mutation Y13S that renders the protein insensitive to Rap phosphatases. The data indicate that the sporulation deficiency of oligopeptide transport mutants is due to their inability to import the peptides controlling Rap phosphatases.

Avaliação da contaminação conjunta de Dekkera bruxellensis e Lactobacillus fermentum sobre a fermentação alcoólica: efeito do substrato e formas de controle

As contaminações por leveduras selvagens e por bactérias no processo de produção de etanol combustível no Brasil causam prejuízos ao rendimento fermentativo e aumento de custos pelo uso de biocidas. No entanto, poucos estudos tem focado no efeito das contaminações conjuntas de leveduras selvagens e bactérias e as possíveis interações entre os micro-organismos, especialmente em função dos diferentes substratos de fermentação e das formas de controle. Este trabalho teve por objetivos verificar o efeito do substrato (caldo de cana e melaço) sobre o desenvolvimento das contaminações pela levedura da espécie Dekkera bruxellensis e pela bactéria Lactobacillus fermentum, em co-culturas com Saccharomyces cerevisiae (linhagem industrial PE-2) e possíveis formas de controle do crescimento dos contaminantes (pelo uso de metabissulfito de potássio e adição de etanol ao tratamento ácido) sem afetar a levedura do processo. Os testes foram realizados em condições de crescimento (substrato com 4 °Brix, culturas agitadas) e fermentação com reciclo celular (substrato com 16 °Brix, culturas estáticas). Houve interação entre as leveduras e a bactéria quando crescidas em caldo de cana 4 °Brix. A levedura industrial não foi afetada pela presença dos micro-organismos contaminantes, no entanto, para D. bruxellensis a presença de L. fermentum interferiu positivamente no crescimento, com aumento no número de UFC, e consequentemente inibição do crescimento da bactéria. Em melaço, houve um estímulo ao crescimento de L. fermentum quando em co-cultura com S. cerevisiae. Houve influência das contaminações sobre os parâmetros avaliados no experimento (pH, açúcar redutor total, etanol, glicerol e crescimento das células) e a contaminação conjunta de L. fermentum e D. bruxellensis potencializou o efeito das contaminações pelos micro-organismos isoladamente, tanto em caldo quanto em melaço. A adição de 13% de etanol à solução de ácido sulfúrico pH 2,0 no tratamento celular resultou em uma diminuição significativa no número de UFC de D. bruxellensis (entre 90-99%). A levedura PE-2 foi pouco afetada pelo tratamento proposto. A bactéria L. fermentum teve seu crescimento afetado em todas as combinações testadas. Como os experimentos foram feitos em co-culturas, verificouse que pode haver influência de um micro-organismo sobre a viabilidade do outro, dependendo da reação ao tratamento ácido-etanol. O metabissulfito de potássio (MBP), no intervalo entre 200-400 mg/L, foi eficaz para controlar o crescimento de D. bruxellensis dependendo do meio de cultura e linhagem. Quando adicionado (250 mg/L) à solução ácida (pH 2,0) no tratamento celular, um efeito significativo foi observado nas culturas mistas, pois ocorreu a inativação do SO2 pela S. cerevisiae e uma provável proteção das células de D. bruxellensis, não sendo essa levedura prejudicada pelo MBP. A resposta fisiológica de S. cerevisiae na presença de MBP pode explicar a diminuição significativa na produção de etanol. Quando o MBP foi adicionado ao meio de fermentação, resultou no controle da D. bruxellensis mas não em sua morte, com efeito menos intensivo sobre a eficiência fermentativa. Em cocultura com a adição de MBP, a eficiência fermentativa foi significativamente menor do que na ausência de MBP.