Orientador: João Neudenir Arioli Filho / Resumo: A interação física direta entre o consultório odontológico e o laboratório de prótese representa um enorme obstáculo para um controle eficaz de infecção cruzada entre estes ambientes. Com isso, neste trabalho foi proposto analisar a influência das técnicas alternativas de desinfecção no tempo de presa, estabilidade dimensional linear e reprodução de detalhes de modelos em gesso. Para isso, foram confeccionadas amostras em gessos pedra tipo IV (Fugi Rock - GC América) com soluções desinfetantes (hipoclorito de sódio 1,0%, glutaraldeído 2% e clorexidina 2%) incorporadas à sua composição em duas concentrações (50 e 100%). Com base nos resultados obtidos, concluiu-se que a adição das soluções desinfetantes alterou de maneira estatisticamente significante o tempo de presa, porém a alteração encontrada no grupo com adição de hipoclorito de sódio demonstrou-se fora dos padrões exigidos pela I.S.O. Com relação à reprodução de detalhes e estabilidade dimensional, a adição de glutaraldeído e clorexidina comportou-se de maneira semelhante ao grupo controle, já o grupo com hipoclorito de sódio provou alterar negativamente tais características. / Abstract: The direct physical interaction between the dental Office and the prosthetics lab represents an enormous obstacle for the efficient control of the cross infection between those two places. The aim of this paper was to analyze the influence of the alternative disinfection techniques during the cast die stone setting time, the linear dimension stability and the reproduction details on cast model. For that samples of die stone type IV Fugi Rock - GC America) with disinfection solutions (Sodium Hypochlorite 1%, Glutaraldeído 2,0% and clorhexidine 2%) incorporated into its compositions in two concentrations (50 and 100%). It was concluded, with base on the results obtained, that the addition of glutaraldeído and clorhexidine did not promote significant alterations on the evaluated properties, however, the addition of sodium hypochlorite in both dilutions significantly altered negatively all the evaluated properties. It was concluded that the incorporation of glutar and clorhexidine, on the evaluated concentrations, can be used on the disinfection of cast model, not promoting alterations on the setting time, dimensional linear alteration and detail reproduction. / Mestre

Resumo: A atividade antimicrobiana do laser Er:YAG foi avaliada sobre biofilme bacteriano constituído por Escherichia coli ATCC 8739, Escherichia coli ATCC 25922, Staphylococcus aureus ATCC 6538 e 3 cepas de Fusobacterium nucleatum e sobre biofilme de microrganismos salivares. Os biofilmes foram submetidos à ação do laser a 1,2 W e 10 Hz por 5, 10, 15, 20, 30 e 60 s e fez-se a avaliação da microbiota residual em ágar sangue, em anaerobiose. O biofilme salivar se mostrou mais sensível nos primeiros tempos de irradiação. A redução microbiana em relação ao controle foi estatisticamente significativa entre todos os tempos testados. Avaliou-se também a ação do laser Er:YAG sobre 7 cepas de Fusobacterium nucleatum inoculadas sobre a superfície de corpos-de-prova (5mmX4mm) de dentes extraídos. Fez-se a aplicação do laser nos mesmos parâmetros físicos mencionados anteriormente, durante 15 s, levando à eliminação total do conteúdo séptico. O estudo avaliou também a irradiação do laser de Er:YAG durante tempos subinibitórios sobre a atividade hemolítica e susceptibilidade de 9 cepas de Fusobacterium nucleatum a amoxicilina, eritromicina, metronidazol e tetraciclina. Após a irradiação do laser, determinou-se a concentração inibitória mínima (CIM) para as drogas através do método de diluição em ágar. A ação do laser sobre a atividade hemolítica foi determinada em sangue humano. Verificou-se que o laser Er:YAG não afetou a atividade hemolítica de Fusobacterium nucleatum, que se mostrou α-hemolítica, tampouco a susceptibilidade a drogas dos isolados testados. / Abstract: Antimicrobial activity of Er:YAG laser was evaluated on a bacterial biofilm constituted by Escherichia coli ATCC 8739, Escherichia coli ATCC 25922, Staphylococcus aureus ATCC 6538 and 3 strains of Fusobacterium nucleatum and on biofilm produced by salivary microorganisms. Biofilms were irradiated by Er:YAG laser, 1,2 W and 10 Hz, for 5, 10, 15, 20, 30, and 60 s and the evaluation of residual contamination was performed on blood agar, under anaerobiosis. It was verified that salivary biofilm showed to be more susceptibility to the Er:YAG laser in shorter periods of laser irradiation. Bacterial reduction was significative in all tested periods of irradiation. The activity of Er:YAG laser was also evaluated on 7 strains of Fusobacterium nucleatum inoculated on samples of human dentin (5mm X 4mm), obtained from extracted teeth. The laser was used following the same physical parameters, as previously described, for 15 s, leading to complete elimination of their septic content. The study also evaluated the effects of subinibitory irradiation of Er:YAG laser on bacterial susceptibility of 9 strains of Fusobacterium nucleatum to antimicrobial drugs (amoxicillin, erythromycin, metronidazole, tetracycline) and hemolysis. Thus, after laser irradiation, the minimal inhibitory concentration of antimicrobial drugs was determined by using an agar dilution method. The influence of laser on hemolysis was carried out on human blood. It was verified that Er:YAG laser did not produce any measurable effect on hemolytic activity and the microbial susceptibility to tested antimicrobial drugs. / Orientador: José Ricardo Kina / Coorientador: Elerson Gaetti Jardim Júnior / Mestre

Orientador: Marcelo Coelho Goiato / Banca: Adriana Cristina Zavanelli / Banca: Mário Alexandre Coelho Sinhoreti / Resumo: Este estudo teve como objetivo avaliar a estabilidade dimensional, reprodução e manutenção de detalhes, dureza "Shore A", deterioração e estabilidade de cor, de um silicone facial, com distintas pigmentações, sob a influência da desinfecção e do envelhecimento acelerado. Para isso foram obtidos 60 corpos-de-prova, utilizando o silicone Silastic MDX 4- 4210, divididos em 3 grupos: sem pigmentação, pigmentado com pó de maquiagem e pigmentado com cerâmica. Metade dos corpos-de-prova de cada grupo foram submetidas à desinfecção com Efferdent e a outra metade com sabão neutro por 60 dias. Após esse período todos os corpos-de-prova (n=10) foram levados a uma câmara de envelhecimento acelerado para corpos não metálicos. Os ensaios de deterioração, estabilidade dimensional, reprodução e manutenção de detalhes, dureza "Shore A" e estabilidade de cor foram realizados após sua confecção, desinfecção e nos intervalos de cada ciclo de envelhecimento acelerado (252, 504 e 1008 horas). Os corpos-de-prova foram analisados, em computador pelo sistema AutoCAD para verificação da alteração dimensional linear e observados, em lupa estereoscópica para a análise da reprodução de detalhes. A dureza dos materiais foi analisada em durômetro Shore A e pesados em balança digital de precisão para análise da deterioração. A estabilidade de cor foi analisada por meio de espectrofotometria. Os valores encontrados dos testes de estabilidade dimensional, reprodução e manutenção de detalhes, dureza "Shore a" e estabilidade de cor foram submetidos à análise de variância e teste de Tukey em nível de 1% de probabilidade. Para a análise da reprodução e manutenção de detalhes foi utilizado escore. Pôde-se observar que os fatores desinfecção química e o envelhecimento acelerado influenciaram estatisticamente na deterioração, estabilidade dimensional, dureza... (Resumo completo, clicar acesso eletrônico abaixo) / Abstract: The aim of this study was to evaluate the dimensional stability, reproduction and maintenance of details, Shore A hardness, deterioration and color stability of facial silicone, with different pigmentation, on the influence of the disinfection and accelerated wheatering. 60 samples were obtained, using silicone Silastic MDX 4-4210, divided in 3 groups: nonpigmented, pigmented with make-up powder and pigmented with ceramics. The half of the samples of each group was submitted to the disinfection with Efferdent and another one with neutral soap per 60 days. After this period all the samples were taken to a chamber of accelerated wheatering for not metallic bodies (n=10). The tests of deterioration, dimensional stability, maintenance of the details, Shore A hardness and color stability were realized after the confection, disinfection and in the intervals of each cycle of accelerated wheatering (252, 504 e 1008 horas). Samples were weighty in digital balance for analysis of deterioration. Analyzed, in computer by the AutoCAD system to verification of the linear dimensional alteration and observed, in stereoscopic magnifying glass for analysis of the reproduction of details. Materials hardness was analyzed in Shore A durometer and the color stability by means of spectrophotometer. The values had been submitted to the analysis of variance and Tukey test (1%). It can be observed that the factors: chemical disinfection and the accelerated wheatering had influenced statistically in deterioration, dimensional stability, Shore A hardness and color stability of the materials independently of the pigmented. With relation to the reproduction and maintenance of details, the values did not change independently of the pigmented, disinfection and accelerated wheatering. / Mestre

Universidade Federal do Cearà / A possÃvel presenÃa de microorganismos potencialmente patogÃnicos em prÃteses dentÃrias recÃm-chegadas dos laboratÃrios protÃticos deve ser considerada. Este estudo avaliou o nÃvel de contaminaÃÃo bacteriana e fÃngica de espÃcimes de resina acrÃlica confeccionados em 14 laboratÃrios de prÃtese dentÃria, inscritos no Conselho Regional de Odontologia do CearÃ, na cidade de Fortaleza. Cada laboratÃrio foi solicitado a confeccionar 10 espÃcimes de resina acrÃlica, a partir de modelos padronizados de silicona de adiÃÃo estÃreis, desconhecendo os objetivos da pesquisa. Os espÃcimes recebidos dos laboratÃrios foram colocados em tubos individuais contendo BHI caldo e incubados a 37ÂC por 48 horas e, em seguida, removidos, lavados, colocados em soluÃÃo salina estÃril e agitados para desprendimento microbiano. A suspensÃo obtida foi diluÃda em 1:100, 1:1000 e semeada em placas com Ãgar Sangue, Sabouraud Dextrose Ãgar e HICrome UTI ÃgarÂ, para incubaÃÃo por 48 horas a 37ÂC. Foi obtido o nÃmero de unidades formadoras de colÃnias (UFC) bacterianas e fÃngicas viÃveis, alÃm da identificaÃÃo e quantificaÃÃo de algumas espÃcies de bactÃrias, comparando-se os laboratÃrios por meio dos testes de Kruskall-Wallis e Dunn (&#945;=0.05). Houve contaminaÃÃo advinda de todos os laboratÃrios analizados, com uma contagem de UFC mÃdia de 101438 de bactÃrias e 71047 de fungos. Pseudomonas spp foi o microorganismo a mais prevalente identificado (p<0,05). Foi concluido que existe risco de contaminaÃÃo por bactÃrias potencialmente patogÃnicas e fungos em dispositivos protÃticos recÃm chegados dos laboratÃrios. / The possible presence of potentially pathogenic microorganisms in denture newly arrived from prosthetic laboratories should be considered. This study evaluated the level of bacterial and fungal contamination of specimens of acrylic resin made in 14 dental laboratories registered with the Regional Council of Dentistry of CearÃ, Fortaleza. Each laboratory was asked to fabricate 10 specimens of acrylic resin, from standard models of sterile silicone addition, unaware of the research objectives. Specimens received from laboratories were placed in individual tubes containing BHI broth, incubated at 37ÂC for 48 hours and then removed, washed and placed in sterile saline and stirred for microbial detachment. The suspension obtained was diluted (1:100, 1:1000) and plated on blood agar plates, and Sabouraud Dextrose Agar and Agar HiCrome ICU by incubation for 48 hours at 37ÂC. The number of colony forming units (CFU) bacterial and fungal viable was obtained, besides the identification and quantification of some species of bacteria, comparing the laboratory by means of the Kruskal-Wallis and Dunn (&#945; = 0.05) tests. There was contamination originating from all laboratories analyzed, with a mean CFU counts of 101438 bacteria and 71047 fungi. Pseudomonas spp was the most prevalent microorganism identified (p < 0.05). It was concluded that there is a risk of contamination with potentially pathogenic bacteria and fungi in prosthetic devices newly arrived from dental laboratories.

Leung, Tsz Yan. / Thesis (M.Phil.)--Chinese University of Hong Kong, 2008. / Includes bibliographical references (leaves 132-146). / Abstracts in English and Chinese. / Acknowledgements --- p.i / Abstract --- p.ii / Table of Contents --- p.vii / List of Figures --- p.xii / List of Plates --- p.xiv / List of Tables --- p.xvii / Abbreviations --- p.xviii / Equations --- p.xxi / Chapter 1. --- Introduction --- p.1 / Chapter 1.1 --- Water crisis and water disinfection --- p.1 / Chapter 1.2 --- Common disinfection methods --- p.2 / Chapter 1.2.1 --- Chlorination --- p.2 / Chapter 1.2.2 --- Ozonation --- p.4 / Chapter 1.2.3 --- Ultraviolet-C (UV-C) irradiation --- p.6 / Chapter 1.2.4 --- Solar disinfection (SODIS) --- p.7 / Chapter 1.2.5 --- Mixed disinfectants --- p.9 / Chapter 1.2.6 --- Other disinfection methods --- p.10 / Chapter 1.3 --- Advanced oxidation processes (AOPs) --- p.11 / Chapter 1.4 --- Photocatalytic oxidation (PCO) --- p.13 / Chapter 1.4.1 --- Understanding of PCO process --- p.15 / Chapter 1.4.2 --- Proposed disinfection mechanism of PCO --- p.18 / Chapter 1.4.3 --- Titanium dioxide (Ti02) photocatalyst --- p.21 / Chapter 1.4.4 --- Irradiation sources --- p.22 / Chapter 1.4.5 --- Bacterial species --- p.23 / Chapter 1.4.5.1 --- Escherichia coli K12 --- p.23 / Chapter 1.4.5.2 --- Shigella sonnei --- p.24 / Chapter 1.4.5.3 --- Alteromonas alvinellae --- p.25 / Chapter 1.4.5.4 --- Photobacterium phosphoreum --- p.26 / Chapter 1.4.6 --- Bacterial defense mechanism towards oxidative stress --- p.27 / Chapter 1.4.6.1 --- Superoxide dismutase (SOD) activity --- p.28 / Chapter 1.4.6.2 --- Catalase (CAT) activity --- p.29 / Chapter 1.4.6.3 --- Fatty acid (FA) profile --- p.30 / Chapter 1.4.7 --- Significance of the project --- p.31 / Chapter 2. --- Objectives --- p.34 / Chapter 3. --- Material and Methods --- p.36 / Chapter 3.1 --- Chemicals --- p.36 / Chapter 3.2 --- Screening of freshwater and marine bacterial culture --- p.36 / Chapter 3.3 --- Photocatalytic reaction --- p.39 / Chapter 3.3.1 --- Preparation of reaction mixture --- p.39 / Chapter 3.3.2 --- Preparation of bacterial culture --- p.39 / Chapter 3.3.3 --- Photocatalytic reactor --- p.41 / Chapter 3.3.4 --- PCO disinfection reaction --- p.42 / Chapter 3.3.4.1 --- Effect of initial pH --- p.44 / Chapter 3.3.4.2 --- Effect of reaction temperature --- p.45 / Chapter 3.3.4.3 --- Effect of growth phases --- p.45 / Chapter 3.4 --- Measurement of superoxide dismutase (SOD) activity --- p.47 / Chapter 3.5 --- Measurement of catalase (CAT) activity --- p.49 / Chapter 3.6 --- Fatty acid (FA) profile --- p.50 / Chapter 3.7 --- Bacterial regrowth test --- p.51 / Chapter 3.8 --- Atomic absorption spectrophotometry (AAS) --- p.52 / Chapter 3.9 --- Total organic carbon (TOC) analysis --- p.53 / Chapter 3.10 --- Chlorination --- p.55 / Chapter 3.11 --- UV-C irradiation --- p.56 / Chapter 3.12 --- Transmission electron microscopy (TEM) --- p.56 / Chapter 4. --- Results --- p.60 / Chapter 4.1 --- Screening of UV-A resistant freshwater and marine bacteria --- p.60 / Chapter 4.2 --- Control experiments --- p.62 / Chapter 4.3 --- Treatment experiments --- p.65 / Chapter 4.3.1 --- UV-A irradiation from lamps --- p.65 / Chapter 4.3.2 --- Fluorescent light from fluorescent lamps --- p.65 / Chapter 4.3.3 --- Effect of initial pH --- p.67 / Chapter 4.3.4 --- Effect of reaction temperature --- p.70 / Chapter 4.3.5 --- Effect of growth phases --- p.70 / Chapter 4.4 --- Factors affecting bacterial sensitivity towards PCO --- p.73 / Chapter 4.4.1 --- Superoxide dismutase (SOD) and catalase (CAT) activities --- p.73 / Chapter 4.4.2 --- Superoxide dismutase (SOD) and catalase (CAT) induction --- p.74 / Chapter 4.4.3 --- Fatty acid (FA) profile --- p.75 / Chapter 4.5 --- Bacterial regrowth test --- p.78 / Chapter 4.6 --- Disinfection mechanisms of fluorescent light-driven photocatalysis --- p.79 / Chapter 4.6.1 --- Atomic absorption spectrophotometry (AAS) --- p.79 / Chapter 4.6.2 --- Total organic carbon (TOC) analysis --- p.81 / Chapter 4.6.3 --- Transmission electron microscopy (TEM) --- p.83 / Chapter 4.7 --- Chlorination --- p.89 / Chapter 4.7.1 --- Disinfection efficiency --- p.89 / Chapter 4.7.2 --- Transmission electron microscopy (TEM) --- p.92 / Chapter 4.8 --- UV-C irradiation --- p.96 / Chapter 4.8.1 --- Disinfection efficiency --- p.96 / Chapter 4.8.2 --- Transmission electron microscopy (TEM) --- p.96 / Chapter 5. --- Discussions --- p.103 / Chapter 5.1 --- Screening of UV-A resistant freshwater and marine bacteria --- p.103 / Chapter 5.2 --- Comparison of PCO coupled with UV-A lamps and fluorescent lamps --- p.103 / Chapter 5.3 --- Effect of initial pH --- p.105 / Chapter 5.4 --- Effect of reaction temperature --- p.106 / Chapter 5.5 --- Effect of growth phases --- p.107 / Chapter 5.6 --- Factors affecting bacterial sensitivity towards PCO --- p.108 / Chapter 5.6.1 --- Superoxide dismutase (SOD) and catalase (CAT) activities --- p.108 / Chapter 5.6.2 --- Superoxide dismutase (SOD) and catalase (CAT) induction --- p.110 / Chapter 5.6.3 --- Fatty acid (FA) profile --- p.110 / Chapter 5.6.4 --- Cell wall structure --- p.112 / Chapter 5.6.5 --- Bacterial size --- p.114 / Chapter 5.6.6 --- Other possible factors --- p.114 / Chapter 5.7 --- Bacterial regrowth test --- p.115 / Chapter 5.8 --- Disinfection mechanisms of fluorescent light-driven photocatalysis --- p.116 / Chapter 5.8.1 --- Atomic absorption spectrophotometry (AAS) --- p.116 / Chapter 5.8.2 --- Total organic carbon (TOC) analysis --- p.117 / Chapter 5.8.3 --- Transmission electron microscopy (TEM) --- p.118 / Chapter 5.9 --- Chlorination --- p.122 / Chapter 5.9.1 --- Disinfection efficiency --- p.122 / Chapter 5.9.2 --- Transmission electron microscopy (TEM) --- p.122 / Chapter 5.10 --- UV-C irradiation --- p.123 / Chapter 5.10.1 --- Disinfection efficiency --- p.123 / Chapter 5.10.2 --- Transmission electron microscopy (TEM) --- p.124 / Chapter 5.11 --- Comparisons of three disinfection methods --- p.124 / Chapter 6. --- Conclusions --- p.126 / Chapter 7. --- References --- p.132

So, Wai Man. / Thesis submitted in: October 2007. / Thesis (M.Phil.)--Chinese University of Hong Kong, 2008. / Includes bibliographical references (leaves 112-124). / Abstracts in English and Chinese. / Acknowledgements --- p.i / Abstract --- p.ii / Table of Contents --- p.vi / List of Figures --- p.x / List of Plates --- p.viii / List of Tables X --- p.v / Abbreviations --- p.xvii / Equations --- p.xix / Chapter 1. --- Introduction --- p.1 / Chapter 1.1 --- Importance of water disinfection --- p.1 / Chapter 1.2 --- Conventional disinfection methods --- p.2 / Chapter 1.2.1 --- Chlorination --- p.2 / Chapter 1.2.2 --- Ozonation --- p.3 / Chapter 1.2.3 --- Ultraviolet-C (UV-C) irradiation --- p.4 / Chapter 1.2.4 --- Sunlight irradiation --- p.5 / Chapter 1.2.5 --- Others --- p.6 / Chapter 1.3 --- Photocatalytic oxidation --- p.7 / Chapter 1.3.1 --- Reactions in PCO --- p.8 / Chapter 1.3.2 --- Disinfection mechanism of PCO --- p.11 / Chapter 1.3.3 --- Photocatalysts --- p.14 / Chapter 1.3.3.1 --- Titanium dioxide (TiO2) --- p.14 / Chapter 1.3.3.2 --- Modification of TiO2 --- p.15 / Chapter 1.3.3.2.1 --- Sulphur cation-doped TiO2 (S-TiO2) --- p.17 / Chapter 1.3.3.2.2 --- Copper(I) oxide-sensitized P-25 (Cu20/P-25) --- p.18 / Chapter 1.3.3.2.3 --- Silicon dioxide-doped TiO2 (SiO2-TiO2) --- p.18 / Chapter 1.3.3.2.4 --- Nitrogen-doped TiO2 (N-TiO2) --- p.19 / Chapter 1.4 --- Bacterial defense systems against oxidative stress --- p.20 / Chapter 1.5 --- Bacterial species --- p.22 / Chapter 1.5.1 --- Salmonella typhimurium --- p.23 / Chapter 1.5.2 --- Klebsiella pneumoniae --- p.24 / Chapter 1.5.3 --- Bacillus thuringiensis --- p.25 / Chapter 1.5.3 --- Bacillus pasteurii --- p.26 / Chapter 2. --- Objectives --- p.27 / Chapter 3. --- Material and Methods --- p.28 / Chapter 3.1 --- Culture media and diluents --- p.28 / Chapter 3.2 --- Screening of target bacteria --- p.28 / Chapter 3.3 --- PCO disinfection reaction --- p.29 / Chapter 3.3.1 --- Photocatalysts --- p.29 / Chapter 3.3.2 --- Bacterial cultures --- p.31 / Chapter 3.3.3 --- PCO reactor --- p.32 / Chapter 3.3.4 --- PCO efficacy test --- p.34 / Chapter 3.3.5 --- Comparison of different photocatalysts --- p.35 / Chapter 3.4 --- Optimization of PCO disinfection conditions --- p.35 / Chapter 3.5 --- Transmission electron microscopy (TEM) --- p.39 / Chapter 3.6 --- Superoxide dismutase (SOD) activity assay --- p.42 / Chapter 3.7 --- Catalase (CAT) activity assay --- p.44 / Chapter 3.8 --- Spore staining --- p.45 / Chapter 3.9 --- Atomic absorption spectrophotometry (AAS) --- p.45 / Chapter 3.10 --- X-ray photoelectron spectrometry (XPS) --- p.46 / Chapter 4. --- Results --- p.47 / Chapter 4.1 --- Screening of wastewater bacteria --- p.47 / Chapter 4.2 --- PCO efficacy test --- p.49 / Chapter 4.3 --- PCO under visible light irradiation --- p.53 / Chapter 4.3.1 --- Fluorescence lamps with UV filter --- p.53 / Chapter 4.3.2 --- Solar lamp with UV filter --- p.61 / Chapter 4.3.3 --- Sunlight with UV filter --- p.67 / Chapter 4.4 --- Optimization of PCO disinfection conditions --- p.75 / Chapter 4.4.1 --- Effect of visible light intensities --- p.75 / Chapter 4.4.2 --- Effect of photocatalyst concentrations --- p.77 / Chapter 4.4.3 --- Optimized conditions --- p.79 / Chapter 4.5 --- Transmission electron microscopy (TEM) --- p.79 / Chapter 4.6 --- Superoxide dismutase (SOD) activity assay --- p.83 / Chapter 4.7 --- Catalase (CAT) activity assay --- p.84 / Chapter 4.8 --- Spore staining --- p.85 / Chapter 4.9 --- Studies on Cu20/P-25 --- p.88 / Chapter 4.9.1 --- Atomic absorption spectrophotometry (AAS) --- p.88 / Chapter 4.9.2 --- X-ray photoelectron spectrometry (XPS) --- p.88 / Chapter 5. --- Discussion --- p.90 / Chapter 5.1 --- Screening of wastewater bacteria --- p.90 / Chapter 5.2 --- PCO efficacy test --- p.90 / Chapter 5.3 --- Comparison between different light sources --- p.90 / Chapter 5.4 --- Comparison between different photocatalysts --- p.93 / Chapter 5.5 --- Optimization of PCO disinfection conditions --- p.95 / Chapter 5.5.1 --- Effect of visible light intensities --- p.95 / Chapter 5.5.2 --- Effect of photocatalyst concentrations --- p.96 / Chapter 5.6 --- Transmission electron microscopy (TEM) --- p.97 / Chapter 5.7 --- Comparison between different bacterial species --- p.99 / Chapter 5.8 --- Possible factors affecting susceptibility of bacteria towards PCO --- p.99 / Chapter 5.8.1 --- Formation of endospores --- p.99 / Chapter 5.8.2 --- Differences in cell wall structure --- p.100 / Chapter 5.8.3 --- SOD and CAT activities --- p.101 / Chapter 5.9 --- Dark control of Cu20/P-25 --- p.103 / Chapter 5.10 --- Studies on Cu20/P-25 --- p.104 / Chapter 6. --- Conclusion --- p.107 / Chapter 7. --- References --- p.112 / Chapter 8. --- Appendix --- p.125 / Chapter 8.1 --- Production of S-Ti02 --- p.125 / Chapter 8.2 --- Production of Si02-Ti02 --- p.125 / Chapter 8.3 --- Production of N-Ti02 --- p.125

Tendo em vista a existência de muitas comunidades no Estado de São Paulo (e em outros estados do Brasil), que utilizam água muitas vezes com qualidade imprópria ao consumo humano, o presente trabalho visa o desenvolvimento de uma instalação de filtração utilizando Carvão Ativado Impregnado com Prata (CAIP) com o intuito de eliminar alguma contaminação na água tratada devido à problemas tais como anomalias operacionais na ETA, tecnologia de tratamento inadequada, contaminação da rede de distribuição, reservação, dentre outros. Para a investigação experimental foram preparados três tipos de água de estudo, com baixos valores de turbidez e cor aparente. A água tipo I era isenta de contaminação, as águas tipo II e III apresentaram coliformes totais e fecais, sendo que a água tipo III utilizada na simulação da instalação como filtro domiciliar. Os ensaios realizados apresentaram taxa de filtração entre 200 e 250 m3/m2*d. Os resultados indicam que o CAIP apresentou propriedades adsorventes e é um poderoso agente desinfetante, reduzindo significativamente o NMP de coliformes totais e fecais de águas contaminadas. Porém, a desinfecção não foi completa e ocorreu excessivo desprendimento da prata do CAIP, inviabilizando o uso deste CAIP nesta instalação desenvolvida. / Minding the existence of many communities within the state of São Paulo (and other Brazilian states) which often use water unfit for human consumption, this work aims at the development of a filtering installation that uses Activated Carbon supporting Silver (AC(Ag)) in an attempt to eliminate any contamination in treated water. Such water contamination problems include, operational anomalies in the WTP, inadequate treatment technologies, contamination in the distribution net, and other filter specific problems. For the experimental investigation three types of test water were prepared, with low turbidity and apparent color values. Water type I was contarnination-free, water type II and III had total and fecal coliforms, and water type III was used in the simulation of domestic filtering installation. Tests showed a filtering rate between 200 and 250 m3/m2*d. Results point that AC(Ag) has adsorbent capabilities, in addition to being a powerful disinfection agent, and reduced significantly the number of total and fecal coliforms of contaminated waters. However, disinfection was not thoroughly, and silver was excessively dragged away, from the Activated Carbon, thus rendering the use of AC(Ag) unadvisable in the developed installation.

Orientador: Rogério de Castilho Jacinto / Coorientador: Frederico Canato Martinho / Banca: Eloi Dezan Junior / Banca: Giselle Prisiclla Cruz Abi Rached / Resumo: O objetivo deste estudo clínico foi avaliar a eficácia de dois sistemas rotatórios: HyFlex CM e ProTaper Next na remoção de bactérias cultiváveis e endotoxinas de canais radiculares infectados. Vinte e quatro canais radiculares de molares e pré-molares com necrose pulpar e lesão periapical foram selecionados e divididos aleatoriamente em 2 grupos: HyFlex CM (n = 12); e ProTaper Next (n = 12). As amostras foram coletadas antes e após o preparo biomecânico e inoculadas em frascos específicos. A irrigação foi realizada com hipoclorito de sódio a 2,5%. Um teste turbidimétrico LAL (Pyrogent 5000 - Lonza, Walkersville, MD, EUA) foi utilizado para quantificar endotoxinas. Cultura microbiológica foi utilizada para determinar a contagem de unidades formadoras de colônias bacterianas (UFC/mL). Os dados coletados foram analisados estatisticamente usando SigmaPlot 12.0 para Windows (Systat Software Inc., San Jose, CA). Foi realizado o teste estatístico de Two-Way ANOVA e o nível de significância foi de 5%. Nas coletas antes do preparo biomecânico, bactérias cultiváveis e endotoxinas foram evidenciadas em 100% das amostras. A análise de cultura revelou que não houve uma diferença estatisticamente significativa na redução bacteriana entre os dois sistemas de instrumentação. As endotoxinas estavam presentes em 100% dos canais após a instrumentação e não houve diferença estatística entre os dois sistemas na redução de endotoxinas. Assim, concluímos que ambos os sistemas de instrumentação for... (Resumo completo, clicar acesso eletrônico abaixo) / Abstract: The aim of this clinical study was to compare the effectiveness of two rotary systems: HyFlex CM and ProTaper Next on the removal of cultivable bacteria and endotoxins from primarily infected root canals. Twenty-four root canals of molars and premolars with pulp necrosis were selected and randomly divided into 2 groups: HyFlex CM (n = 12); and ProTaper Next (n = 12). Samples were collected before and after the biomechanical preparation and inoculated in specific flasks. Irrigation was performed using 2.5% sodium hypochlorite. A kinetic turbidimetric lysate assay of limulus amoebocytes was used to quantify endotoxins. Microbiological culture was used to determine the count of bacterial colony forming units (CFU/mL). Data collected were statistically analyzed using SigmaPlot 12.0 for Windows (Systat Software Inc, San Jose, CA). The Two-Way ANOVA statistical test was performed and the level of significance was 5%. In the samples before the biomechanical preparation, cultivable bacteria and endotoxins were evidenced in 100% of the cases. The culture analysis revealed that there was no statistically significant difference in the bacterial reduction between the two instrumentation systems. Endotoxins were present in 100% of the canals after instrumentation, and there was no statistical difference between the two systems in endotoxin reduction. Thus, it was concluded that both instrumentation systems were effective in reducing root canal bacteria and endotoxins with primary endodont... (Complete abstract click electronic access below) / Mestre

Thesis (MTech (Chemistry))--Cape Peninsula University of Technology, 2018. / Trihalomethanes (THMs) are a group of four compounds that are formed, along with other disinfected by-products. This happens when chloride or other disinfectants are used to control microbial contamination in drinking water, which then reacts with natural organic or inorganic substances in water. Trihalomethanes are better known by their common names such as chloroform, bromodichloromethane, chlorodibromomethane and bromoform. These four compounds are known to be classified as cancer group B carcinogens (shown to cause cancer in laboratory animals). Trihalomethane levels tend to increase with pH, temperature, time and the level of “precursors" present. Precursors are known to be organic substances which react with chloride to form THMs. One significant way of reducing the amount of THMs in water is to eliminate or reduce chlorination before filtrations and reduce precursors. There are guideline limits for THMs in the SANS 241:2015 document, but they are not continuously monitored and their levels in natural water are not known. The aim of this study is to develop a rapid, fast and reliable liquid-liquid microextraction technique, to determine the presence of THMs in natural water sources. This study particularly focuses on different water sources e.g. river, underground, borehole and chlorinated water. Chlorinated water is the water that has been presumably treated for bacteria and fungus growth. The results that were obtained for chlorinated water are as follow, 10.120 μg/L − 11.654 μg/L for chloroform, 2.214 μg/L - 2.666 μg/L for bromodichloromethane, 0.819 μg/L − 0.895 μg/L chlorodibromomethane and 0.103 μg/L - 0.135 μg/L for bromoform from validation data. All these THMs concentrations have been found to be below the SANS 241:2015 limits. Natural water shows a very high affinity for chloroform. This is what is expected under normal conditions as chloroform is the most abundant THM of all THMs present in natural water. The liquid-liquid microextraction technique that was optimized and used for the determination of THMs in this study is a rapid, simple and inexpensive technique that provides low limits of detection (LOD) e.g. 0.1999 μg/L chlorodibromomethane and 0.2056 μg/L bromoform and wide dynamic range (LOQ) of 0.6664 μg/L chlorodibromomethane and 0.6854 μg/L bromoform for the determination of THMs.

Background: Blood-borne infections are common problem in healthcare. Informations about the prevalence in dental care are limitet. Healthcare professionals in South Africa are particularly vulnerable to blood-borne infections. The best way to minimize blood-borne infections is to increase compliance to infection control. Objective: To describe and compare compliance to infection control routines and knowledge of blood-borne infections among  different groups of dental students at a university in Ga-Rankuwa, South Africa. Materials and method: A quantitative cross-section web-based survey. The participants were dental students who were registered in 2019, dental hygienist, dental therapist students, 3ed year and dental students 4th year. Non Parametric – Chi - Square and Fisher's test was used to analyze data. Result: Majority of the students had  compliance regarding the use of gloves and mask during patient treatment, changing gloves and disinfection of  unit between patients. Compliance was less at other parts where approximately half (49%) had the correct answer concerning: gloves, using of  gloves, clinical uniform and using of mobile and accessories. Correct answers to the knowledge of blood-borne infections för all dental students was 67%. Conclusions: The participants had better results on knowledge of blood-borne infections than on compliance to infection kontrol. No significant difference was found among the student dental groups