Iron reduction is an important redox reaction in anaerobic environments for both biological and chemical cycling of elements such as carbon. However, the controls on the rate and extent of iron reduction are poorly understood and unlike other major terminal electron accepting processes, iron reduction has the added complexity that its oxidized form (ferric iron) exists primarily as one of several solid phases in environments with pH greater than 3. Thus, the distribution and form of ferric iron minerals are important controls on iron reduction in natural systems. For the first phase of this research a series of sequential chemical extractions was performed on a core taken from a landfill-leachate-contaminated wetland-aquifer system at the Norman Landfill, Norman, OK. The phases targeted by the sequential extractions consist of easily water soluble salts and ions present in the soil solution; weakly acid soluble iron (such as siderite and ankerite); easily reducible iron (such as ferrihydrite and lepidocrocite); moderately reducible iron (such as goethite, akageneite, and hematite); organically bound iron; magnetite; and pyrite. The second phase of this research involved creating in situ microcosm experiments that exposed native microbial communities to a test solution amended with 2-line ferrihydrite (Fe5HO8∙4H2O), electron donor (lactate and acetate), and a conservative tracer for a period of eleven days. The kinetics of iron reduction were then evaluated over time and the resulting changes in microbial community structure documented through DNA and RNA analysis. Results document the spatial distribution of iron phases at the contaminated wetland-aquifer interface. Results of the sequential extractions indicate that ferrihydrite was present throughout the core. Accordingly, ferrihydrite was used in subsequent experiments on in situ microcosms to evaluate the kinetic controls on the microbial reduction of ferrihydrite. The results of these experiments show that microbial communities actively responded to the introduction of the amended ferrihydrite solution by increasing their community size and reducing ferrihydrite to an iron (II) phase in increasing amounts over an eleven day period.

Gallium arsenide (GaAs), cadmium selenide (CdSe), and cadmium telluride (CdTe) are semiconductor materials with remarkable opto-electronic properties that make them suitable for a wide variety of applications including, light emitting diodes (LEDs), mobile phones, tablets, and solar panels. Due to the growing demand and the short lifespan of these electronic devices, a remarkable amount of electronic waste (e-waste) has been produced in the last decades. An important fate of e-waste is landfill disposal; therefore, there is an increasing concern about the release of toxic elements into the landfill environment and the potential risks for human health and the environment. Among the elements constituting GaAs, CdTe, and CdSe, tellurium (Te) has gained increasing attention in recent years. Tellurium is a scarce element on the earth’s crust, and a shortage in its supply might compromise the development of new advanced technology, particularly in the energy and defense fields. For these reasons, the US Department of Energy and the European Union regard Te as a critical element, and have urged the need to develop efficient and cost-effective processes to recover Te from waste streams. This thesis dissertation explored different aspects related to the fate and impact of the widely used semiconductor materials, GaAs, CdSe and CdTe in municipal mixed solid waste (MSW) landfills. Furthermore, it investigated the removal of the Te oxyanions, tellurite (Teᴵⱽ, TeO₃²⁻) and tellurate (Teⱽᴵ, TeO₄²⁻), from aqueous streams and the recovery of this strategic metalloid as biogenic, elemental tellurite (Te⁰) nanoparticles (NPs). In the first part this work, the dissolution of GaAs was evaluated under a range of redox conditions, pH levels, ionic strength, and the presence of organic constituents commonly found in landfills. Our results indicated that aerobic conditions and mildly alkaline pH conditions favor the dissolution and release of high levels of soluble arsenic (As) and gallium (Ga) to the synthetic leaching solutions. The rate of As and Ga dissolution in long-term exposure experiments was initially constant but later progressively decreased due to the formation of a passivating layer on the surface of GaAs. The leaching behavior of CdSe and CdTe was also investigated under different pH and redox conditions in solutions simulating landfill leachates. CdTe and CdSe were subjected to two different standardized leaching tests, the federal Toxicity Characteristic Leaching Procedure (TCLP) and the California Waste Extraction Test (WET). CdTe showed a very high leaching potential in both tests and the concentrations of Cd released were 1500- and 260-times higher than the regulatory limit (1 mg Cd L⁻¹), respectively. In contrast, CdSe was relatively stable and dissolved selenium (Se) in both leaching tests was below the regulatory threshold (1 mg Se L⁻¹). Tests performed under different pH and redox conditions confirmed a marked enhancement in CdTe and CdSe dissolution both under acidic pH and aerobic conditions, which is consistent with thermodynamic predictions. Due to the high leaching potential observed for CdTe in the previous batch experiments, leaching studies were designed to investigate the potential release of soluble Cd and Te from a commercially available CdTe thin-film solar panel under different chemical and biogeochemical conditions commonly found in landfills. The solar panel was subjected to two standardized batch leaching tests (i.e., TCLP and WET), and to a continuous column test designed to investigate the dissolution of CdTe under conditions simulating the acidic- and the methanogenic circumneutral phases of a MSW landfill. A negligible amount of Cd and Te was measured in the synthetic leachate of both batch tests. On the other hand, a significant amount of Cd and Te was released from the panel to the synthetic leachate of the column simulating an acid landfill after 30 days (73% and 21% of the total Cd and Te, respectively). In contrast, the amount of Cd or Te detected in the effluent of the column operated at circumneutral pH values was negligible. The marked difference in the leaching behavior of CdTe in both columns is related to the different aqueous pH and redox conditions promoted by the microbial communities in the columns. The microbial toxicity of the soluble species that can be released from CdTe and CdSe was also assessed as a part of this work. The toxicity of cadmium (Cdᴵᴵ), selenite (Seᴵⱽ), selenate (Seⱽᴵ), Teᴵⱽ, and Teⱽᴵ was evaluated in bioassays with different microbial targets, including acetoclastic and hydrogenotrophic methanogenic populations in a mixed microbial culture, similar to those involved in the stabilization of organic waste stabilization in a landfill, and the bioluminescent marine bacterium, 𝐴𝑙𝑖𝑖𝑣𝑖𝑏𝑟𝑖𝑜 𝑓𝑖𝑠𝑐ℎ𝑒𝑟𝑖 (Microtox® test). The acetoclastic methanogens were most sensitive to the presence of the various soluble species, with the toxicity decreasing in the following order: Cdᴵᴵ, Teᴵⱽ, Teⱽᴵ, Seᴵⱽ, while Seⱽᴵ was only toxic at non-environmentally relevant concentration. Hydrogenotrophic methanogens were highly inhibited by Cdᴵᴵ and Seᴵⱽ, but Teᴵⱽ and Teⱽᴵ only had a moderate toxic impact. The bacterium 𝐴. 𝑓𝑖𝑠𝑐ℎ𝑒𝑟𝑖 was very sensitive to inhibition by Cdᴵᴵ and Seᴵⱽ, and Teᴵⱽ. In the last part of this work, the potential recovery of insoluble, elemental Te⁰ NPs from aqueous solutions containing soluble Teᴵⱽ or Teⱽᴵ was investigated in batch- and continuous flow bioreactors inoculated with a methanogenic granular mixed culture. In the batch experiments, the capacity of the culture to catalyze the reduction of the Te oxyanions and to produce Te⁰ NPs internally and externally to the cells was demonstrated. The granular sludge was found to contain enough endogenous substrates to provide the electron equivalents required to reduce both Te oxyanions and the reduction rates were only modestly increased by an exogenous electron-donor (e-donor) such as H₂. The effect of several redox mediators (RM), namely, anthraquinone-2,6-disulfonate (AQDS), hydroxocobalamin, riboflavin, and lawsone, was also tested. Riboflavin and lawsone caused a remarkable increase of the rate of Teᴵⱽ and Teⱽᴵ reduction, respectively, and also enhanced the fraction of Te recovered as extracellular Te⁰ NPs. The morphology and localization of the Te⁰ NPs were also impacted by the presence of a particular RM and e-donor in the system, suggesting that NP production can be tailored for a particular application. Finally, the feasibility of utilizing upflow anaerobic sludge bed (UASB) bioreactors to reduce Teᴵⱽ oxyanions to non-toxic Te⁰ NPs was also investigated. Two reactors were supplied with ethanol as the external e-donor source to promote the biological reduction of Teᴵⱽ. Riboflavin, a redox mediator, was supplied to one of the reactors to enhance Teᴵⱽ bioreduction. Continuous formation of Te⁰ NPs using an UASB was found to be feasible and remarkably improved by addition of riboflavin at the low Teᴵⱽ:riboflavin molar ratio of 4:1. This flavonoid enhanced the conversion rate of Teᴵⱽ and reduced the toxic impact of Teᴵⱽ towards the methanogenic consortium. Overall, the evidence found in this work indicates that recycling of decommissioned devices containing GaAs, CdTe, or CdSe is desirable to prevent the potential environmental release of toxic metals and metalloids in MSW landfills, but also to allow the recovery of critical resources. Microbial processes offer potential for the removal and recovery of soluble metals and metalloid ions leached from decommissioned semiconductor materials. In particular, this study demonstrated the feasibility of utilizing continuous UASB bioreactors for the removal of Teᴵⱽ from aqueous streams and the recovery of this valuable metalloid as biogenic Te⁰ NPs.

The effects of thermosonication (high intensity ultrasound coupled with thermal treatment), on the reduction of thermophilic spore-forming microorganisms and its effects on the solubility index in reconstituted skim milk powder (RSMP) were evaluated. Thermosonication was applied to RSMP at various solids concentrations, temperatures, and lengths of time based on commercial milk powder processing conditions. Microbial counts were determined prior to and after treatments to determine the log reduction of Geobacillus stearothermophilusvegetative cells and spores. Log reductions were recorded, and data were analyzed by response surface analysis. The log reductions induced by temperature and time without high intensity ultrasound (HIU) were compared to reductions observed with HIU. Thermosonication was also applied to RSMP to determine effects on solubility using a continuous flow cell system. Thermosonication yielded a significantly higher level of microbial destruction for both vegetative cells and spores than heat treatment alone. For experiments involving vegetative cells, the interaction of treatment time and temperature proved to have the greatest influence on microbial inactivation. In comparison, the interaction of total solids content and length of HIU treatment demonstrated the greatest effect on the increased log reductions for spores. The solubility of RSMP treated with HIU did not significantly differ from the solubility of RSMP not treated with HIU. Further data showed the implementation of HIU, or thermosonication, during milk powder processing would be most effective before and after the evaporation stage when the total solids content of product is 9.2% and 50% at 75°C and 60°C, respectively. Based on preliminary data, it is assumed HIU applied for 10 s at these two locations would produce an additive effect, thereby reducing overall microbial counts by 5.76 log and 0.51 log for G. stearothermophilus vegetative cells and spores, respectively, in the product prior to entering the drying stage. All research findings and observations suggest HIU, or thermosonication, to be a successful method for reducing microbial populations during milk powder processing without sacrificing skim milk powder solubility

Einleitung: Salmonellen und Yersinien haben als zweit- und dritthäufigste Verursacher bakterieller Gastroenteritiden in Deutschland und Europa im Jahr 2017 eine große Bedeutung als Lebensmittelinfektionserreger. Übertragen werden sie hauptsächlich durch den Verzehr roher, unzureichend gekühlter oder ungenügend erhitzter Schweinefleischerzeugnisse (Schweinemett, Hackepeter, kurz gereifte Rohwürste). Der Eintrag in die Lebensmittelkette erfolgt über symptomlose Trägertiere, die am Schlachthof in der Lebendund Fleischuntersuchung nicht als solche identifizierbar sind. Durch Kreuzkontaminationen kann es zur Verschleppung der Erreger auf die Schlachttierkörperoberflächen eigentlich gesunder Tiere kommen. Die vorherrschenden Hygienemaßnahmen am Schlachthof haben bisher nicht zu einer Verringerung des Auftretens dieser Bakterien geführt. Alternativ könnte gepulstes Licht (GL) als zusätzliches Dekontaminationsverfahren zum Einsatz kommen. Dessen antimikrobielle Wirksamkeit wurde bereits in zahlreichen Studien nachgewiesen. In der Literatur fehlten jedoch bislang Daten zur Inaktivierung von Salmonella ssp. auf Schwarte und Schweinelachs. Bezüglich Yersinia ssp. lagen noch gar keine Studien vor. Ziel der Untersuchungen: Ziel dieser Arbeit war es, die Inaktivierung beider Erreger auf oben genannten Matrices zu testen und, unter Berücksichtigung chemischer und sensorischer Attribute der Produkte sowie die Eignung des Verfahrens für die Praxis abzuschätzen. Material und Methoden: Für die Untersuchungen mit künstlich inokulierten Schwarte- und Schweinefleischproben wurden die humanpathogenen Bakterien S. Typhimurium und Y. enterocolitica (Biotyp 4) verwendet. Die antimikrobielle Wirkung von GL wurde bei Fluences zwischen 0,52 und 19,11 J/cm² geprüft. Farb- bzw. Temperaturveränderungen auf der Probenoberfläche wurden mit Hilfe eines Spektrophotometers (CM 600 d, Konica Minolta) respektive eines Infrarotthermometers (104 IR, Testo) ermittelt. Zur Beurteilung der Lipidoxidation wurde die TBARS-Methode angewandt und die Proben maximal 10 Tage bei 4° C gelagert. Veränderungen bezüglich des Geruchs wurden bei Fluences von 0.52, 4.96 und 12.81 J/cm² mittels eines Konsensprofils beurteilt. Ergebnisse: Auf Schwarte konnten innerhalb von Sekunden Reduktionen von 1,73-3,16 log (S.) und von 1,48-4,37 log (Y.), auf Schweinelachs hingegen 1,7 log-Stufen für beide Mikroorganismen erreicht werden. Moderate bis starke Behandlungsregime (≥7,36 J/cm²) führten zu einer deutlich wahrnehmbaren Farbveränderung (E*ab ≥ 3) von Schwarte, ab 9,66 J/cm² zu einem signifikanten Verlust des roten Farbanteils von Schweinelachs. Zur Bewertung einer forcierten Fettoxidation wurde Malondialdehyd (MDA) in den Proben quantitativ bestimmt. Keine der getesteten Einstellungen hatte eine Überschreitung des Grenzwertes von 0,5 μg/g, ab dem Testpersonen die Produkte als ranzig wahrnehmen, zur Folge. Eine Überprüfung des Geruches erfolgte anhand von drei getesteten Fluences, die eine niedrige (0,52 J/cm²), moderate (4,96 J/cm²) und starke (12,81 J/cm²) Behandlung repräsentieren sollten. Mit 0,52 J/cm² bestrahlte Schwarte wurde von den Panel-Mitgliedern als weniger nach Schwein und weniger fettig riechend bewertet und somit als angenehm empfunden, ansonsten wurden chemische Gerüche wahrgenommen. Schlussfolgerungen: Aus den erzielten Daten geht hervor, dass sich gepulstes Licht in niedrigen Dosen (≤0,52 J/cm²) zur Dekontamination von Schwarte eignet. Praktisch umsetzbar wäre dies am Schlachthof als geschlossene Behandlungskammer, unmittelbar nach der Eviszeration. Somit könnte der noch nicht geteilte Schlachtkörper oberflächlich behandelt werden, ohne das unter der Haut befindliche Fleisch zu erreichen und die oben genannten Veränderungen hervorzurufen. Notwendig ist hierbei die Gewährleistung des Arbeitsschutzes. In diesem Zusammenhang muss entstehendes Ozon unschädlich beseitigt werden und das Tragen einer UV-Schutzbrille in der unmittelbaren Umgebung des Gerätes angeordnet werden. Abschließend ist hervorzuheben, dass das GL als zusätzliche, unterstützende Maßnahme zur Bekämpfung von Lebensmittelinfektionserregern zu sehen ist und keine bestehenden Hygienemaßnahmen (gute Hygienepraxis) ersetzen darf. Aufgrund der geringeren Wirksamkeit auf Schweinelachs und den damit verbundenen geruchlichen Veränderungen ist eine Applikation auf Schweinefleisch ohne weiterführende Untersuchungen nicht zielführend.:Inhaltsverzeichnis ABKÜRZUNGSVERZEICHNIS ..............................................................................................III 1 EINLEITUNG ........................................................................................................... 1 2 LITERATURÜBERSICHT ........................................................................................ 3 2.1 Gepulstes Licht und gesetzliche Rahmenbedingungen ............................................. 3 2.2 Wirk- und Reparaturmechanismen, Resistenzbildung und Inaktivierungskinetik ....... 7 2.2.1 Photochemischer Effekt ................................................................................... 7 2.2.2 Photoreaktivierung ........................................................................................... 8 2.2.3 Photothermischer Effekt ................................................................................... 8 2.2.4 Physikalischer Effekt ........................................................................................ 9 2.2.5 Resistenzbildung .............................................................................................. 9 2.2.6 Inaktivierungskinetik ......................................................................................... 9 2.3 Einflussparameter ................................................................................................... 10 2.3.1 Mikroorganismus .............................................................................................10 2.3.2 Zeitpunkt der Bestrahlung ...............................................................................12 2.3.3 Matrix ..............................................................................................................12 2.4 Gepulstes Licht zur Inaktivierung von lebensmittelassoziierten Erregern in Fleischwaren .......................................................................................................... 13 2.5 Zielstellung dieser Arbeit ......................................................................................... 17 3 VERÖFFENTLICHUNG ..........................................................................................18 3.1 Eigenanteil zur Veröffentlichung ............................................................................. 18 3.2 Publikation .............................................................................................................. 18 4 ÜBERGREIFENDE DISKUSSION ..........................................................................46 4.1 Eignung des Verfahrens „Gepulstes Licht“ zur Dekontamination von Schwarte und Schweinelachs ................................................................................................. 46 4.2 Vergleich von GL mit anderen Dekontaminationsverfahren .................................... 49 4.2.1 Chemische Dekontamination ...........................................................................49 4.2.2 Physikalische Dekontamination .......................................................................49 4.2.3 Biologische Dekontamination ..........................................................................50 4.3 Alternativer Einsatz von GL..................................................................................... 51 4.4 Schlussfolgerungen ................................................................................................ 51 5 ZUSAMMENFASSUNG ..........................................................................................53 6 SUMMARY .............................................................................................................55 7 LITERATURVERZEICHNIS ....................................................................................57 ANHANG ..............................................................................................................................66 DANKSAGUNG ....................................................................................................................72 / Introduction: Since Salmonella ssp. and pathogenic Yersinia ssp. were the second and third most frequent causes for bacterial gastroenteritis in Germany and throughout Europe in 2017 they are of high significance as foodborne infectious agents. They are mainly transmitted by consumption of raw, inadequately cooled or insufficiently heated pork meat products (ground pork, minced pork, shortly ripened raw sausages). Subclinically infected pigs, so-called “carriers”, cannot be detected during ante- and post-mortem inspection in the slaughterhouse. Cross-contamination can lead to bacterial dissemination onto actually S.- or Y.-free carcasses. Prevailing hygienic measures could not reduce bacterial prevalence in the abattoir so far. Thus, pulsed light (PL) may be used as an additional decontamination procedure. Its antimicrobial potential was proven in numerous studies. However, there are no data in the scientific literature about inactivation of Salmonella ssp. on pork skin and loin. Moreover, no experiments with Yersinia in connection with pulsed light have been performed until now. Aim of this study: Hence, the aim of this work was to investigate the inactivation of both microorganisms on above-mentioned matrices and to assess the suitability of the PL treatment for implementation in a slaughterhouse considering chemical and sensory alterations of the products. Materials and Methods: For experiments with artificially inoculated pork skin and loin samples human-pathogenic bacteria S. Typhimurium and Y. enterocolitica (Biotype 4) were used. The antimicrobial effect of PL was tested at fluences between 0.52 and 19.11 J/cm². Color and temperature changes on the sample surface were determined by means of a spectrophotometer (CM 600 d, Konica Minolta) or an infrared thermometer (104 IR, Testo). The TBARS method was used to assess lipid per-oxidation and the samples were stored at 4° C for a maximum of 10 days. Odor changes were appraised at fluences of 0.52, 4.96 and 12.81 J/cm² using consensus profiling. Results: On pork skin reductions of 1.73-3.16 log (S.) and of 1.48-4.37 log (Y.) were achieved within seconds. In contrast, on pork loin only 1.7 log of both microorganisms were maximally inactivated. Moderate to strong treatments (≥7.36 J/cm²) led to distinct color changes (E*ab ≥ 3) in pork skin, fluences above 9.66 J/cm² to a significant loss of red color in pork loin. For evaluation of possible accelerated lipid peroxidation malondialdehyde (MDA) was analyzed quantitatively in samples. None of the tested parameter combinations resulted in threshold value exceedance of 0.5 μg MDA/g which is the point where panel members start to perceive products as rancid. Odor appraisal was carried out using three fluences representing a mild (0.52 J/cm²), moderate (4.96 J/cm²) and strong (12.81 J/cm²) treatment. Pork skin treated with 0.52 J/cm² was assessed as less porky, less fatty and, thus, pleasant by panel members, apart from that chemical odors were perceived. Conclusions: From the available data it appears that pulsed light could be used in mild doses (≤0.52 J/cm²) for pork skin decontamination. Practically, a PL-unit could be designed as a closed chamber, implemented directly after the evisceration in the abattoir. This way, the not yet separated carcass could be treated superficially without reaching the meat surface preventing the above-mentioned alterations. Guarantee of safety at work also plays an important role. Emerging ozone must be evacuated safely and UV-protection glasses should be worn in direct proximity to the PL-system. Finally, one needs to consider, that PL should be regarded as an additional, supportive measure to control foodborne pathogens and not as a replacement for existing hygiene standards (good hygiene practice). An application on pork meat does not seem to be conducive because of its lower effect on pork loin and the associated odor changes.:Inhaltsverzeichnis ABKÜRZUNGSVERZEICHNIS ..............................................................................................III 1 EINLEITUNG ........................................................................................................... 1 2 LITERATURÜBERSICHT ........................................................................................ 3 2.1 Gepulstes Licht und gesetzliche Rahmenbedingungen ............................................. 3 2.2 Wirk- und Reparaturmechanismen, Resistenzbildung und Inaktivierungskinetik ....... 7 2.2.1 Photochemischer Effekt ................................................................................... 7 2.2.2 Photoreaktivierung ........................................................................................... 8 2.2.3 Photothermischer Effekt ................................................................................... 8 2.2.4 Physikalischer Effekt ........................................................................................ 9 2.2.5 Resistenzbildung .............................................................................................. 9 2.2.6 Inaktivierungskinetik ......................................................................................... 9 2.3 Einflussparameter ................................................................................................... 10 2.3.1 Mikroorganismus .............................................................................................10 2.3.2 Zeitpunkt der Bestrahlung ...............................................................................12 2.3.3 Matrix ..............................................................................................................12 2.4 Gepulstes Licht zur Inaktivierung von lebensmittelassoziierten Erregern in Fleischwaren .......................................................................................................... 13 2.5 Zielstellung dieser Arbeit ......................................................................................... 17 3 VERÖFFENTLICHUNG ..........................................................................................18 3.1 Eigenanteil zur Veröffentlichung ............................................................................. 18 3.2 Publikation .............................................................................................................. 18 4 ÜBERGREIFENDE DISKUSSION ..........................................................................46 4.1 Eignung des Verfahrens „Gepulstes Licht“ zur Dekontamination von Schwarte und Schweinelachs ................................................................................................. 46 4.2 Vergleich von GL mit anderen Dekontaminationsverfahren .................................... 49 4.2.1 Chemische Dekontamination ...........................................................................49 4.2.2 Physikalische Dekontamination .......................................................................49 4.2.3 Biologische Dekontamination ..........................................................................50 4.3 Alternativer Einsatz von GL..................................................................................... 51 4.4 Schlussfolgerungen ................................................................................................ 51 5 ZUSAMMENFASSUNG ..........................................................................................53 6 SUMMARY .............................................................................................................55 7 LITERATURVERZEICHNIS ....................................................................................57 ANHANG ..............................................................................................................................66 DANKSAGUNG ....................................................................................................................72

Durante o preparo químico-cirúrgico são utilizados instrumentos e substâncias químicas, que constituem um binômio indivisível e necessário para alcançar a modelagem e a sanificação dos canais radiculares. Assim, propõe-se com este trabalho avaliar in vivo, por meio de método molecular de PCR quantitativo, baseado em DNA (qPCR), a eficiência do preparo químico-cirúrgico empregando como agente de irrigação o Hipoclorito de Sódio (NaOCL) a 2,5% ou o Gel de Endo PTC associado ao Hipoclorito de Sódio a 1,0% na redução bacteriana de canais radiculares de dentes portadores de periodontite apical primária. Foram selecionados 30 pacientes portadores de infecção endodôntica primária, totalizando 30 dentes, com rarefação óssea periapical visível na radiografia, sem tratamento endodôntico prévio. Os pacientes foram divididos de forma randomizada em dois grupos distintos, de acordo com a substância química auxiliar utilizada durante a instrumentação, NaOCL 1% + Endo-PTC leve ou NaOCL 2,5%. Em todos os casos empregou-se instrumentos Reciproc R40 ou R50 e as coletas foram realizadas antes (S1) e após o prepare químico-cirúrgico (S2). A análise de aderência foi realizada por meio do teste de Kolmogorov-Smirnov, as análises intragrupo foram realizadas com teste de Wilcoxon para amostras relacionadas e as comparações entre os dois grupos foram realizadas com o teste de Mann-Whitney, para a análise quantitativa de bactérias. Em ambos os grupos, houve diminuição significativa no número de bactérias entre S1 e S2 (p<0,05). No grupo NaOCL 1% + Endo-PTC leve, houve redução de 3,7x105(S1) para 5,7x104 (S2). No grupo NaOCl 2,5%, redução de 1,3x105 (S1) para 1,1x104(S2). Na comparação entre grupos, o NaOCL a 2,5% (91,62%) promoveu maior redução bacteriana do que o grupo NaOCL 1% + Endo-PTC (84,60%) (p<0,05). / During the chemomechanical preparation, instruments and chemical substances are used, which constitute an indivisible and necessary binomial to achieve modeling and sanification. Knowing the auxiliary chemical substances, understanding their mechanisms of action, being able to use them efficiently, is fundamental, so that the chemical-surgical preparation is well performed by the clinician. Thus, the purpose of this study is to evaluate in vivo, the efficiency of the chemomechanical preparation using as the irrigant agent 2,5% sodium hypochlorite and Endo-PTC gel, associated to 1% sodium hypochlorite, to assess the bacterial reduction of root canals of teeth with primary apical periodontitis, using a molecular quantitative method DNA-based - polymerase chain reaction (qPCR). Were selected 30 patients with primary infection totaling 30 teeth, with visible periapical bone rarefaction on the radiography, without previous endodontic treatment. Patients were randomly divided into two distinct groups according to the auxiliary chemical substances used during the instrumentation, 1% sodium hypochlorite associated with Endo-PTC gel or 2,5% sodium hypochlorite. In all cases, reciproc instruments R40 or R50 were used and the samples were taken before (S1) and after chemical surgical preparation (S2). The adherence analysis was performed using the Kolmogorov-Smirnov test, intragroup analysis were performed with Wilcoxon test for related samples and comparisions between the two groups were performed with the Mann-Whitney test for the quantitative analysis of bacteria. In the both groups, there was a significant decrease in the number of bacteria between S1 and S2 (p<0,05), the inicial sample (S1) of the group Endo-PTC, the median 3,7x105, reduced to 5,7x104. In the other group of NaOCl, the median in S1 was 1,3x105 that reduced to 1,1x104 . In the comparision between groups, the 2,5% NaOCl promoted a greater microbial reduction of 91,62%, than the Endo-PTC associated with 1% NaOCl (p<0,05) 84,60%.

Durante o preparo químico-cirúrgico são utilizados instrumentos e substâncias químicas, que constituem um binômio indivisível e necessário para alcançar a modelagem e a sanificação dos canais radiculares. Assim, propõe-se com este trabalho avaliar in vivo, por meio de método molecular de PCR quantitativo, baseado em DNA (qPCR), a eficiência do preparo químico-cirúrgico empregando como agente de irrigação o Hipoclorito de Sódio (NaOCL) a 2,5% ou o Gel de Endo PTC associado ao Hipoclorito de Sódio a 1,0% na redução bacteriana de canais radiculares de dentes portadores de periodontite apical primária. Foram selecionados 30 pacientes portadores de infecção endodôntica primária, totalizando 30 dentes, com rarefação óssea periapical visível na radiografia, sem tratamento endodôntico prévio. Os pacientes foram divididos de forma randomizada em dois grupos distintos, de acordo com a substância química auxiliar utilizada durante a instrumentação, NaOCL 1% + Endo-PTC leve ou NaOCL 2,5%. Em todos os casos empregou-se instrumentos Reciproc R40 ou R50 e as coletas foram realizadas antes (S1) e após o prepare químico-cirúrgico (S2). A análise de aderência foi realizada por meio do teste de Kolmogorov-Smirnov, as análises intragrupo foram realizadas com teste de Wilcoxon para amostras relacionadas e as comparações entre os dois grupos foram realizadas com o teste de Mann-Whitney, para a análise quantitativa de bactérias. Em ambos os grupos, houve diminuição significativa no número de bactérias entre S1 e S2 (p<0,05). No grupo NaOCL 1% + Endo-PTC leve, houve redução de 3,7x105(S1) para 5,7x104 (S2). No grupo NaOCl 2,5%, redução de 1,3x105 (S1) para 1,1x104(S2). Na comparação entre grupos, o NaOCL a 2,5% (91,62%) promoveu maior redução bacteriana do que o grupo NaOCL 1% + Endo-PTC (84,60%) (p<0,05). / During the chemomechanical preparation, instruments and chemical substances are used, which constitute an indivisible and necessary binomial to achieve modeling and sanification. Knowing the auxiliary chemical substances, understanding their mechanisms of action, being able to use them efficiently, is fundamental, so that the chemical-surgical preparation is well performed by the clinician. Thus, the purpose of this study is to evaluate in vivo, the efficiency of the chemomechanical preparation using as the irrigant agent 2,5% sodium hypochlorite and Endo-PTC gel, associated to 1% sodium hypochlorite, to assess the bacterial reduction of root canals of teeth with primary apical periodontitis, using a molecular quantitative method DNA-based - polymerase chain reaction (qPCR). Were selected 30 patients with primary infection totaling 30 teeth, with visible periapical bone rarefaction on the radiography, without previous endodontic treatment. Patients were randomly divided into two distinct groups according to the auxiliary chemical substances used during the instrumentation, 1% sodium hypochlorite associated with Endo-PTC gel or 2,5% sodium hypochlorite. In all cases, reciproc instruments R40 or R50 were used and the samples were taken before (S1) and after chemical surgical preparation (S2). The adherence analysis was performed using the Kolmogorov-Smirnov test, intragroup analysis were performed with Wilcoxon test for related samples and comparisions between the two groups were performed with the Mann-Whitney test for the quantitative analysis of bacteria. In the both groups, there was a significant decrease in the number of bacteria between S1 and S2 (p<0,05), the inicial sample (S1) of the group Endo-PTC, the median 3,7x105, reduced to 5,7x104. In the other group of NaOCl, the median in S1 was 1,3x105 that reduced to 1,1x104 . In the comparision between groups, the 2,5% NaOCl promoted a greater microbial reduction of 91,62%, than the Endo-PTC associated with 1% NaOCl (p<0,05) 84,60%.