Submitted by Automa??o e Estat?stica (sst@bczm.ufrn.br) on 2016-03-09T23:41:38Z No. of bitstreams: 1 WedinaRodriguesDeLima_DISSERT.pdf: 1359852 bytes, checksum: 947641e57effa75408f6f9568cca76ff (MD5) / Approved for entry into archive by Arlan Eloi Leite Silva (eloihistoriador@yahoo.com.br) on 2016-03-14T19:51:43Z (GMT) No. of bitstreams: 1 WedinaRodriguesDeLima_DISSERT.pdf: 1359852 bytes, checksum: 947641e57effa75408f6f9568cca76ff (MD5) / Made available in DSpace on 2016-03-14T19:51:43Z (GMT). No. of bitstreams: 1 WedinaRodriguesDeLima_DISSERT.pdf: 1359852 bytes, checksum: 947641e57effa75408f6f9568cca76ff (MD5) Previous issue date: 2015-02-20 / As lagoas de estabiliza??o s?o sistemas de tratamento biol?gico que constituem alternativa vantajosa, ao possibilitarem elevada remo??o de mat?ria org?nica e microrganismos patog?nicos, al?m de sua opera??o e manuten??o ser de forma simplificada e com baixo custo. A pesquisa foi realizada em sete sistemas de lagoas de estabiliza??o em s?rie, localizados no Estado do Rio Grande do Norte, compostos por uma lagoa facultativa (LF), seguida de duas lagoas de matura??o (M1 e M2). Com o objetivo de monitorar e avaliar a efici?ncia das lagoas em s?rie, bem como verificar a remo??o de cianobact?rias e microcistina no tratamento, foram realizadas coletas do efluente tratado diretamente nas caixas de sa?da das lagoas facultativas e matura??es, bem como o esgoto bruto (EB) que chegava ?s esta??es. As vari?veis analisadas foram: pH, temperatura, oxig?nio dissolvido, s?lidos suspensos totais, clorofila ?a? , cor aparente, demanda bioqu?mica de oxig?nio (DBO), demanda qu?mica de oxig?nio (DQO), f?sforo total, nitrog?nio org?nico, nitrog?nio amoniacal, nitrog?nio total Kjeldahl, turbidez, densidade de cianobact?rias e concentra??es de microcistina. Foram realizadas an?lises de vari?ncia (ANOVA- an?lise de um fator), observando as premissas utilizando o teste de Tukey. Nos efluentes finais foram verificadas remo??es de DBO de 48,8% (Pipa) a 75,8% (Cai?ara do Rio do Vento) e DQO 57,5% (Pipa) a 83,0% (Santo Ant?nio), respectivamente. As concentra??es m?dias da densidade de cianobact?rias das LF variaram entre 62 x 103 cels.mL-1 (Pedro Velho Ro?a) a 2 x 106 cels.mL-1 (Ponta Negra), enquanto os efluentes finais apresentaram entre a faixa de 9 x 103 cels.mL-1 (Pedro Velho Ro?a) a 1,9 x 106 cels.mL-1 (Macau ? Ilha de Santana). A concentra??o m?xima do efluente final de microcistina foi 0,13 ?g.L-1 (S?o Gon?alo). Em s?ntese, as esta??es de tratamento de esgoto avaliadas, apresentaram uma baixa efici?ncia na remo??o da mat?ria org?nica e de nutrientes. Mas em contrapartida, na maioria das esta??es, foi verificado um bom desempenho referente ? remo??o da densidade de cianobact?rias, bem como o baixo n?vel de concentra??es de microcistina. / Stabilization ponds are biological treatment systems in that stabilization of organic matter is performed by the bacterial oxidation and / or reduction of photosynthetic algae. This study aimed to monitor and evaluate the efficiency of stabilization ponds in the Rio Grande do Norte State. Collections were made of the treated effluent, made directly in the output boxes of facultative lagoons and maturation (M1 and M2) and raw sewage (EB) that arrived at the stations. The variables analyzed were: pH, temperature, dissolved oxygen, total suspended solids, chlorophyll "a", apparent color, total phosphorus, organic nitrogen, ammonia nitrogen, Kjeldahl nitrogen, turbidity, cyanobacteria density and concentrations of microcystin. Variance analysis (ANOVA one way) observing the premises using the Tukey test, so as to check differences between treatments. The evaluate the stations found to COD removals in the bands of 48,8% (Pipa) to 75,8% (Cai?ara Rio do Vento) and 57,5% (Pipa) to 83,0% (Santo Ant?nio), respectively. The mean concentrations of cyanobacteria varied from LFs density of 62,545 cels.mL-1 (Pedro Velho Ro?a) cels.mL-1 to 2,669,048 (Ponta Negra), while the final effluent showed range between 9,072 Cels.mL- 1 (Pedro Velho Ro?a) to 1,899,981 cels.mL-1 (Macau ? Ilha de Santana) and the average concentrations of microcystin the final effluent ranged from 0.02 ?g.L-1 (Ponta Negra) to 0.15 ?g.L-1 (Macau ? Ilha de Santana) at the studied the stations.

Submitted by Jorge Silva (jorgelmsilva@ufrrj.br) on 2017-05-11T18:56:39Z No. of bitstreams: 1 2014 - Bruno Botelho Saleh.pdf: 2346129 bytes, checksum: fe906738dca9a661de96e77fdb8c304a (MD5) / Made available in DSpace on 2017-05-11T18:56:39Z (GMT). No. of bitstreams: 1 2014 - Bruno Botelho Saleh.pdf: 2346129 bytes, checksum: fe906738dca9a661de96e77fdb8c304a (MD5) Previous issue date: 2014-07-17 / CAPES / The city of Rio Verde-GO has excelled for having important agro-industrial units with important breeding of cattle, poultry and pigs. The swine farms handle the liquid waste stabilization ponds with or without digesters systems, accumulating them for 2 months to 4 months, and then applied in areas of approximately 100 to 300 acres. Floating gas collection chambers, where the samples are captured biogas emitted to the atmosphere of stabilization ponds and then analyzed the samples in the laboratory of Embrapa Agrobiology were installed, in addition, to conduct sampling of swine manure (DLS) itself to quantification of elements present in it. It was found in this study that the largest emissions of methane (CH4) were in the following descending order of magnitude: 205.3 ? 68.79 Mg CH4 yr-1 for the fattening farm without biodigester (4,000 swines); 123.94 ? 39.17 Mg CH4 yr-1 in the fattening farm with a biodigester (4,000 swines); 11.22 ? 3.0 ton CH4 year-1 for the producing piglets farm with a biodigester (1,008 matrices swines) and 2.75 ? 0.89 Mg CH4 yr-1 in the producing piglets farm with two biodigesters (728 matrices swines), thus proving expected to their farms in production. Interaction in methane (CH4 Mg yr-1) and concentration (mg L-1) macronutrients (N, P and K) present in the DLS was observed for nitrogen (Ntotal) a linear equation y = 0.1797x ? 111.81 (R2 0.9844); for phosphorus (P) is the linear equation y = 1.4905x ? 25.224 (R2 0.9436); whereas for potassium (K) a linear equation y = 0.0693 ? 35.934 (R2 0.9337). / A cidade de Rio Verde-GO tem se destacado por contar com importantes unidades agroindustriais com importante plantel de bovinos, av?cola e de su?nos. As granjas de su?nos manejam os res?duos l?quidos em sistemas de lagoas de estabiliza??o com ou sem biodigestores, acumulando-os durante 2 meses a 4 meses, sendo ent?o aplicados em ?reas de aproximadamente 100 a 300 hectares. Foram instaladas c?maras flutuantes de coleta de gases, onde foram capturadas as amostras do biog?s emitido para atmosfera das lagoas de estabiliza??o e ent?o analisadas as amostras no laborat?rio da Embrapa Agrobiologia, al?m, da realiza??o de coletas de amostras do pr?prio dejeto l?quido de su?no (DLS) para quantifica??o dos elementos presentes no mesmo. Verificou-se na presente pesquisa que as maiores emiss?es de metano (CH4) ocorreram na seguinte ordem de grandeza decrescente: 205,3 ? 68,79 Mg CH4 ano-1 para a granja em termina??o sem biodigestor (4.000 su?nos); 123,94 ? 39,17 Mg CH4 ano-1 na granja de termina??o com um biodigestor (4.000 su?nos); 11,22 ? 3,0 Mg CH4 ano-1para a granja de produ??o de leit?es com um biodigestor (1.008 matrizes em produ??o) e 2,75 ? 0,89 Mg CH4 ano-1 na granja de produ??o de leit?es com dois biodigestores (728 matrizes em produ??o), comprovando assim o esperado para as respectivas granjas em produ??o. Na intera??o das emiss?es de metano (Mg CH4 ano-1) e a concentra??o (mg L-1) de macronutrientes (N, P e K) presentes nos DLS observou-se para o nitrog?nio (NTotal) uma equa??o linear ? = 0,1797? ? 111,81 (R2 de 0,9844); em rela??o ao f?sforo (P) esta equa??o linear ? = 1,4905? ? 25,224 (R2 de 0,9436); enquanto que para o pot?ssio (K) uma equa??o linear ? = 0,0693? ? 35,934 (R2 de 0,9337).

Submitted by Rodrigo Martins Cruz (rodrigo.cruz@ufvjm.edu.br) on 2015-02-27T13:30:32Z No. of bitstreams: 5 23.pdf: 968729 bytes, checksum: 708a2fc2af8284a6b22a75db644cadea (MD5) license_url: 49 bytes, checksum: fd26723f8d7edacdb29e3f03465c3b03 (MD5) license_text: 20904 bytes, checksum: e09bf99e64678e4285abf3ef3e05412d (MD5) license_rdf: 23422 bytes, checksum: b145eda3d84bdc4f56b389c0ab98d368 (MD5) license.txt: 2109 bytes, checksum: aa477231e840f304454a16eb85a9235f (MD5) / Approved for entry into archive by Rodrigo Martins Cruz (rodrigo.cruz@ufvjm.edu.br) on 2015-02-27T16:52:06Z (GMT) No. of bitstreams: 5 23.pdf: 968729 bytes, checksum: 708a2fc2af8284a6b22a75db644cadea (MD5) license_url: 49 bytes, checksum: fd26723f8d7edacdb29e3f03465c3b03 (MD5) license_text: 20904 bytes, checksum: e09bf99e64678e4285abf3ef3e05412d (MD5) license_rdf: 23422 bytes, checksum: b145eda3d84bdc4f56b389c0ab98d368 (MD5) license.txt: 2109 bytes, checksum: aa477231e840f304454a16eb85a9235f (MD5) / Made available in DSpace on 2015-02-27T16:52:06Z (GMT). No. of bitstreams: 5 23.pdf: 968729 bytes, checksum: 708a2fc2af8284a6b22a75db644cadea (MD5) license_url: 49 bytes, checksum: fd26723f8d7edacdb29e3f03465c3b03 (MD5) license_text: 20904 bytes, checksum: e09bf99e64678e4285abf3ef3e05412d (MD5) license_rdf: 23422 bytes, checksum: b145eda3d84bdc4f56b389c0ab98d368 (MD5) license.txt: 2109 bytes, checksum: aa477231e840f304454a16eb85a9235f (MD5) Previous issue date: 2010 / Conselho Nacional de Desenvolvimento Cient?fico e Tecnol?gico (CNPq) / A distribui??o como biofertilizantes ? uma alternativa vi?vel para a destina??o dos dejetos produzidos na suinocultura, j? que eles possuem nutrientes tais como f?sforo, nitrog?nio, entre outros. Diante disso, o objetivo deste trabalho foi caracterizar os par?metros f?sico-qu?micos de dejetos l?quidos de su?nos (DLS), tratados em sistema de lagoas em s?rie e avaliar as altera??es nos atributos microbiol?gicos de um solo cultivado com caf? ap?s aplica??o de diferentes doses de DLS. O estudo foi conduzido na Granja Campo Alegre e na Fazenda Yamaguchi, no Munic?pio de Diamantina, Minas Gerais. Os DLS foram coletados em v?rios pontos: sa?da das instala??es, sa?da da lagoa anaer?bia, sa?da da primeira lagoa facultativa e sa?da da segunda lagoa facultativa, sendo analisados: Demanda Qu?mica de Oxig?nio (DQOt), Demanda Bioqu?mica de Oxig?nio (DBO5), Concentra??o de S?lidos Totais (ST), Nitrog?nio Total (N-Total), F?sforo, Pot?ssio, Zinco e Cobre. Ap?s an?lise, os dejetos foram aplicados em um cafeeiro, em experimento, constitu?do por cinco tratamentos com cinco repeti??es. As amostras de solo foram coletadas, na camada de 0-10 cm, de profundidade. Foram avaliados a respira??o basal, o carbono da biomassa microbiana e determinado o quociente metab?lico. Os resultados permitiram constatar que o sistema de lagoas de estabiliza??o em s?rie apresenta 88% de efici?ncia na remo??o de DQOt e 91% na remo??o de DBO5. As fra??es de s?lidos apresentaram comportamento semelhante e a efici?ncia de remo??o de N-Total correspondeu a 24,2%. O uso de dejetos l?quidos de su?nos no solo, antes e 30 dias ap?s sua aplica??o, aumentou a biomassa microbiana do solo e a atividade microbiana. Os resultados obtidos permitem concluir que o sistema de lagoas de estabiliza??o em s?rie demonstra ser eficiente na remo??o do excesso de nutrientes. Ressalte-se que o tratamento demonstrou caracter?sticas favor?veis ao reaproveitamento dos dejetos como biofertilizante. / Disserta??o (Mestrado) ? Programa de P?s-Gradua??o em Produ??o Vegetal, Universidade Federal dos Vales do Jequitinhonha e Mucuri, 2010. / ABSTRACT The distribution in biofertilizer form is a feasible alternative for disposal of waste produced by pigs, since they have nutrients such as phosphorus, nitrogen, among others. Therefore, the objective of this study was to characterize the physical and chemical parameters of pig slurry (DLS), treated in a system of ponds in series and evaluate the changes in the microbial soil of a coffee plantation after applying different doses of pig slurry. The study was conducted in the Campo Alegre Farm and Ranch Yamaguchi in the city of Diamantina, Minas Gerais. The DLS were collected at various points: exit of the facilities, exit of the anaerobic pond, exit of the first facultative pond, exit of the second facultative pond, and analyzed: Chemical Oxygen Demand (DQOt), Biochemical Oxygen Demand (BOD5) concentration Total Solids (DS), Total Nitrogen (Total-N), Phosphorus, Potassium, Zinc, and Copper. After analysis, the pig manure were applied in a coffee plantation, in an experiment consisting of five treatments with five replications. Soil samples were collected at 0-10 cm depth. It was evaluated the basal respiration, microbial biomass carbon and metabolic quotient determined. The results show that the system of stabilization ponds in series features 88% efficiency in removing DQOt and 91% for BOD5 removal. The fractions of solids showed similar behavior and t removal efficiency of Total-N accounted for 24.2%. Use of pig slurry in soil, before and 30 days after application, amplified the soil microbial biomass and microbial activity. The results showed that the system of stabilization ponds in series proves to be effective in removing excess nutrients. It is noteworthy that treatment showed favorable characteristics for reuse of wastes as biofertilizers.

Made available in DSpace on 2014-12-17T15:03:21Z (GMT). No. of bitstreams: 1 DanielDVM.pdf: 2848336 bytes, checksum: 2d942e41371b022b9b35b5e7499260d3 (MD5) Previous issue date: 2009-08-20 / Coordena??o de Aperfei?oamento de Pessoal de N?vel Superior / Because of disability in public policy development in mind to attend issues of sanitation in the municipalities, companies known as "clean-blue" appeared proposing to solve a simple collection and management of wastewater produced in single or multifamily residences, commercial, hospitals, etc. In the case of an activity in which there are no worries about the fate of sewage, emerged some doubts about the degree of health and environmental safety in these companies. Traditionally, most of them makes the provision of waste depleted soil or wetland, open, usually located on the outskirts of cities (MENESES, 2001). In turn, the sludge from septic tanks exhausted, provided no technical criteria - in the soil, rivers and as an agricultural fertilizer put in risk the health of the population and environmental quality. This work was entered in the search network 5 of the Notice of the Research Program in Sanitation - PROSAB-5, aimed to study the theme 'Characterization and study of alternative ways of treating sludge from septic tanks in the city of Natal, RN', proposing to evaluate the performance of the use of stabilization ponds as a system to handle waste from septic tanks exhausted. A series of lakes studied belong to one of the largest clean-pit of Natal, consisting of two anaerobic ponds, one facultative and maturation, and a tank disinfection, the wastewater being released in the Potengi River. Samples were collected between the months of October 2007 to October 2008, at six points previously defined and judged as more appropriate to what is proposed study. The analysis results in field and laboratory showed the most significant removal of COD (88.93%), total suspended solids (94.87%), organic nitrogen (66.87%) and thermotolerant coliforms (99.88%). Some results have not reached the expected because the system under study had operating problems that have undermined the efficiency of the reactors / Por causa da defici?ncia na elabora??o de pol?ticas p?blicas em aten??o ao atendimento ?s quest?es do esgotamento sanit?rio dos munic?pios, empresas conhecidas como limpa-fossa surgiram propondo solucionar de forma simples a coleta e o manejo dos efluentes l?quidos produzidos em resid?ncias uni ou multifamiliares, com?rcio, hospitais, etc. Em se tratando de uma atividade em que n?o h? preocupa??es quanto ao destino dos esgotos, surgiram questionamentos referentes ao grau de seguran?a sanit?ria e ambiental nessas empresas. Tradicionalmente, a maioria delas faz a disposi??o dos res?duos esgotados no solo ou em ?reas inund?veis, a c?u aberto, normalmente localizadas na periferia das cidades (MENESES, 2001). Por sua vez, o lodo esgotado de fossas s?pticas, disposto sem qualquer crit?rio t?cnico no solo, em rios e como adubo na agricultura , coloca em risco a sa?de da popula??o e a qualidade ambiental. O presente trabalho, inserido na rede de pesquisa do Edital 5 do Programa de Pesquisas em Saneamento B?sico PROSAB-5, objetivou o estudo do tema Caracteriza??o e estudo de alternativas de tratamento de lodos de fossa s?ptica na cidade do Natal, RN , propondo a avalia??o do desempenho do uso das lagoas de estabiliza??o como sistema de tratamento dos res?duos esgotados das fossas s?pticas. A s?rie de lagoas estudada pertence a uma das maiores empresas limpa-fossa da cidade de Natal, composta por duas lagoas anaer?bias, uma facultativa e uma de matura??o, al?m de um tanque de desinfec??o, sendo o efluente final lan?ado no Rio Potengi. As coletas foram realizadas entre os meses de outubro de 2007 a outubro de 2008, em seis pontos previamente definidos e julgados como mais adequados ao que se prop?s estudar. Os resultados das an?lises em campo e em laborat?rio apontaram remo??es mais significativas de DQO (88,93%), s?lidos suspensos totais (94,87%), nitrog?nio org?nico (66,87%) e coliformes termotolerantes (99,88%). Alguns resultados obtidos n?o atingiram o esperado, pois o sistema em estudo apresentou problemas de opera??o que prejudicaram a efici?ncia dos reatores

Made available in DSpace on 2014-12-17T15:03:27Z (GMT). No. of bitstreams: 1 DayanaMT_DISSERT.pdf: 5461193 bytes, checksum: e14ad35e988326c6b2deb98ea1ef274e (MD5) Previous issue date: 2011-06-17 / Coordena??o de Aperfei?oamento de Pessoal de N?vel Superior / Stabilization pond system consisting in more sewage treatment used in Rio Grande do Norte (RN), Brazil, representing about 90% of all systems. Fecal bacteria are removed mainly facultative ponds and in maturation ponds. Many factors influence bacterial decay, such as the levels of pH and DO, temperature, light intensity, HDT and nutrient availability. The bacterial decay rate (Kb) is calculated considering many variables, but the hydraulic regime is a significant influence for microorganisms removal, and the dispersed flow which best characterizes a stabilization pond. However, some authors developed equations for the Kb accordant plug flow and complete mixing. This research study aimed to evaluate the bacterial decay of fecal coliform and Enterococcus sp. in stabilization ponds designed to treat domestic sewage, full-scale, in RN. All systems have assessed pretreatment, a facultative pond (LF) followed by two maturation (LM1 and LM2). The parameters availed were: temperature, pH, DO, BOD5, COD, fecal coliform, Enterococcus sp., Chlorophyll a, total suspended solids, fixed and volatile. In general, there were not significant differences for pH, DO and temperature in the ponds, except for the new systems, since they have low flow and hydraulic loads. The removal of organic matter in the ponds was low, about 70%, and nearly all are overloaded organic and operational problems. The bacterial removals were low, with average 96% for LF for fecal coliform, and 98% for Enterococcus sp.; LM1 were in itself a removal for fecal coliform about 71%, and 81% for Enterococcus sp.; LM2 have efficiency of 69% for fecal coliform, and 68% for Enterococcus sp. The equation proposed by Von Sperling (1999), according to the dispersed flow regime, generated empirical values of Kb more approximate to calculated values of Kb. On average, the calculated Kb to coliforms in the LF was 0.31 d-1, and for both maturation ponds were 0.35 d-1. For Enterococcus sp. the average was 0.40 d-1 for LF, 0.55 d-1 for LM1, and 0.58 d-1 for LM2. These results also showed that the Kb obtained in full-scale systems are smaller than those found in pilot-scale ponds. Moreover, one can say that the equation proposed by Marais (1974), according to the complete-mix regime, overestimates Kb. Actual results of Kb indicated that fecal coliforms are more resistant to adverse conditions present in stabilization ponds than Enterococcus sp., therefore, an indicator of microbiological safety and efficiency. The factors significant interventions in the rate of bacterial decay were concentrations of COD, the organic loading and HDT. The few Kb relationship between pH, DO and temperature were not significant. Finally, we conclude that it s essential to correct operation and maintenance, for not performing these activities is one of the main factors contributing to low rates of bacterial decay. / Lagoas de estabiliza??o consistem no sistema de tratamento de esgotos mais utilizado no Rio Grande do Norte (RN), Brasil, correspondendo a cerca de 90% de todos os sistemas. As bact?rias fecais s?o removidas principalmente nas lagoas facultativas e de matura??o. Muitos fatores influenciam no decaimento de bact?rias, como: os n?veis de pH e OD, temperatura, intensidade luminosa, TDH e disponibilidade de alimento. A taxa de decaimento bacteriano (Kb) ? calculada a partir de muitas vari?veis, mas o regime hidr?ulico possui significativa influ?ncia na remo??o de microorganismos, sendo o de fluxo disperso o que melhor caracteriza uma lagoa de estabiliza??o. Todavia, alguns autores elaboraram equa??es para o Kb conforme o regime de mistura completa. Essa pesquisa teve como objetivo avaliar o decaimento bacteriano de coliformes termotolerantes e Enterococcus sp. em lagoas de estabiliza??o destinadas ao tratamento de esgotos dom?sticos, em escala real, no RN. Todos os sistemas avaliados possuem tratamento preliminar, uma lagoa facultativa (LF), seguida de duas de matura??o (LM1 e LM2). Os par?metros avaliados foram: temperatura, pH, OD, DBO5, DQO, coliformes termotolerantes, Enterococcus sp., clorofila a, s?lidos em suspens?o totais, fixos e vol?teis. N?o foram identificadas diferen?as significativas entre os valores de pH, OD e temperatura nas lagoas, exceto para os sistemas mais novos, j? que eles possuem baixas vaz?es e cargas hidr?ulicas. A remo??o de mat?ria org?nica nos sistemas de tratamento foi baixa, cerca de 70%, e praticamente todas est?o com sobrecarga org?nica e com problemas operacionais. As remo??es bacterianas tamb?m foram baixas, com m?dia para as LF de 96% para coliformes termotolerantes, e de 98% para Enterococcus sp.; nas LM1 obteve-se remo??o para coliformes termotolerantes de 71%, e para Enterococcus sp. de 81%; e, nas LM2 a efici?ncia foi de 69% para coliformes termotolerantes e de 68% para Enterococcus sp. A equa??o proposta por Von Sperling (1999), segundo o regime de fluxo disperso, foi a que gerou valores de Kb emp?ricos mais aproximados dos valores de Kb calculados a partir de dados reais. Em m?dia, o Kb calculado com base nos dados reais para coliformes termotolerantes nas LF foi de 0,31 d-1, e em ambas as lagoas de matura??o foram de 0,35 d-1. Para Enterococcus sp. a m?dia nas LF foi de 0,40 d-1, nas LM1 foi igual a 0,55 d-1, e nas LM2 de 0,58 d-1. Esses resultados tamb?m demonstraram que os Kb obtidos em sistemas em escala real s?o menores do que os verificados em lagoas em escala piloto. Al?m disso, pode-se afirmar que a equa??o proposta por Marais (1974), segundo o regime de mistura completa, superestima o Kb. Os resultados dos Kb calculados indicaram que os coliformes termotolerantes s?o mais resistentes ?s condi??es adversas presentes em lagoas de estabiliza??o do que os Enterococcus sp., sendo, portanto, um indicador microbiol?gico mais eficiente e seguro. Os fatores de significativa interven??o na taxa de decaimento bacteriano foram as concentra??es de DQO, a carga org?nica e o TDH. As poucas rela??es existentes entre Kb com pH, OD e temperatura n?o foram estatisticamente significativas. Por fim, conclui-se que ? fundamental a opera??o e manuten??o corretas, pois a n?o realiza??o dessas atividades consiste em um dos principais fatores que contribuem para as baixas taxas de decaimento bacteriano.

Made available in DSpace on 2014-12-17T15:03:28Z (GMT). No. of bitstreams: 1 OdeniaALS_DISSERT.pdf: 3500566 bytes, checksum: bcbbd86a88f2dade1ad704684123cb31 (MD5) Previous issue date: 2011-10-24 / Coordena??o de Aperfei?oamento de Pessoal de N?vel Superior / Stabilization pond is the main technology used for treatment wastewater, in northeast Brazil, due to lower cost of deployment, operation and maintenance compared to other technologies. Most systems of stabilization ponds has been in operation for some time, on average 10 years of operation, receiving high organic loads and do not have good removal efficiencies of the main parameters for which have been designed. Therefore it is necessary to work to quantify the efficiency of current systems. This study evaluated the biodegradability of organic matter in raw sewage, the removal of organic matter in reactors and determination of the kinetic constant removal of organic matter (k), both in reactors and in raw sewage, based on the analysis made in the laboratory and through mathematical methods proposed in the literature, in nine systems stabilization ponds, located in Rio Grande do Norte. In relation the degradation kinetics in stabilization ponds, it was observed that many papers published in the literature were obtained in pilot-scale systems, which often, due to the action of external factors such as wind and temperature, these can t be considered as a reference in the analysis of the kinetic constant K, so the need for more research into systems of scale. This study had three distinct phases and simultaneous, routine monitoring, study of the daily cycle and the determination of kinetic constant of degradation of organic matter (K). The monitoring showed that the removal efficiencies of organic matter on most systems were lower than suggested by the literature, the best efficiencies of around 76% (BOD) and 72% (COD) and the worst of the order of 48% (BOD) and 55% (COD). The calculation of K in raw sewage (Ke) was within the range of variation expected in the literature (0.35 to 0.60 days-1). Already for the results obtained for K in the reactors (Kr), there were well below the values recommended in the literature (0.25 to 0.40 d-1 for complete mix and from 0.13 to 0.17 d-1 for flow dispersed), in line with the overloads that organic systems are subject / Lagoa de estabiliza??o ? a principal tecnologia utilizada para tratamento de esgotos dom?sticos no Nordeste brasileiro, devido ao menor custo de implanta??o, opera??o e manuten??o, quando comparada com outras tecnologias. A maioria dos sistemas de lagoas de estabiliza??o est? em opera??o h? bastante tempo, em m?dia 10 anos de opera??o, recebem altas cargas org?nicas e n?o apresentam boas efici?ncias de remo??o dos principais par?metros a qual foram projetadas. Portanto, faz-se necess?rio um trabalho que quantifique a efici?ncia atual desses sistemas. O presente estudo avaliou a biodegradabilidade da mat?ria org?nica no esgoto bruto, a remo??o da mat?ria org?nica nos reatores e a determina??o da constante cin?tica de remo??o de mat?ria org?nica (k), tanto nos reatores quanto no esgoto bruto, baseadas nas an?lises feitas em laborat?rio e atrav?s dos m?todos matem?ticos propostos pela literatura, em nove sistemas de lagoas de estabiliza??o, no Rio Grande do Norte. Em rela??o ? cin?tica de degrada??o em lagoas de estabiliza??o, observou-se que muitos trabalhos publicados na literatura foram obtidos em sistemas em escala piloto, o que muitas vezes, devido ? a??o de fatores externos, tais como vento e temperatura, esses n?o podem ser considerados como refer?ncia na an?lise da constante cin?tica K, por isso a necessidade de se pesquisar mais em sistemas de escala real. Essa pesquisa teve tr?s fases distintas e simult?neas: monitora??o de rotina, estudo do ciclo di?rio e a determina??o da constante cin?tica de degrada??o da mat?ria org?nica (K). O monitoramento mostrou que as efici?ncias de remo??o de mat?ria org?nica, na maioria dos sistemas, estavam abaixo do sugerido pela literatura, sendo as melhores efici?ncias da ordem de 76% (DBO) e de 72% (DQO) e as piores da ordem de 48% (DBO) e 55% (DQO). O calculo do K no esgoto bruto (Ke) mostrou-se dentro da faixa de varia??o prevista na literatura (0,35 a 0,60 dia-1). J? para os resultados obtidos para K nos reatores (Kr), verificaram-se valores bem abaixo do preconizado pela literatura (0,25 a 0,40 d-1 para mistura completa e 0,13 a 0,17 d-1 para fluxo disperso), em conson?ncia com as sobrecargas org?nicas a que os sistemas est?o sujeitos

Made available in DSpace on 2014-12-17T15:03:32Z (GMT). No. of bitstreams: 1 CeresVCD_DISSERT.pdf: 2077286 bytes, checksum: e92bca4faf414c0d0c184dc10f694c85 (MD5) Previous issue date: 2013-05-24 / Coordena??o de Aperfei?oamento de Pessoal de N?vel Superior / Experience in the use of stabilization ponds shows that this is a system with low cost, easy operation and maintenance and suitable for tropical countries. One of its disadvantages is due to high concentrations of suspended solids, mainly due to algal biomass in the effluents. Accordingly, the dissolved air flotation has been shown to be an efficient post-treatment technology. However, the efficiency of this process is related to coagulation and flocculation steps, as well as the adjustment of the involved variables in the process. The objective of this work was to evaluate the algae removal efficiency from wastewater stabilization ponds and the influence of the factors involved in the process using dissolved air flotation. For this, we used primary facultative and maturation effluents of ETE Ponta Negra in Natal. We did tests of coagulation, flocculation and flotation with the samples, using the equipment flotatest. In this process were tested coagulants aluminum sulfate and ferric chloride, and varied the factors pH, coagulant concentration, polymer concentration and rate of recirculation. At the end of the experiments were analyzed turbidity, suspended solids, color, COD and chlorophyll "a". These results were submitted to descriptive statistics to verify the efficiency of the process in general, and regression analysis to identify models that describe the process and demonstrate the factors that have greater influence on flotation. After step methodology, high values were found removal efficiency of suspended solids, reaching values greater than 90% in the best cases. It was concluded that flotation is more efficient in the facultative pond effluent using ferric chloride, and the variability of algae may negatively influence the process. Regression analyzes showed that pH is the most influential variable in the coagulation-flocculation-flotation, and its optimal value among the tested is 5.5 for both coagulants / A experi?ncia no uso de lagoas de estabiliza??o mostra que esse ? um sistema que apresenta baixo custo, f?cil opera??o e manuten??o e adequado a pa?ses tropicais. Apesar disso, uma de suas desvantagens est? relacionada ?s elevadas concentra??es de s?lidos suspensos, devido principalmente ? biomassa das algas nos efluentes. Com o objetivo de remover tais algas, a flota??o por ar dissolvido tem se mostrado como uma eficiente t?cnica de p?s-tratamento. No entanto, a efici?ncia desse processo est? relacionada ?s etapas de coagula??o e flocula??o pr?vias, bem como ao ajuste das vari?veis envolvidas no processo. Nesse contexto, o presente trabalho objetivou avaliar a efici?ncia de remo??o de algas de efluente de lagoas de estabiliza??o bem como a influ?ncia dos fatores envolvidos utilizando o processo de flota??o por ar dissolvido. Para isso, foi utilizado efluente das lagoas facultativa prim?ria e de matura??o da ETE Ponta Negra, em Natal. As amostras coletadas foram submetidas a ensaios de coagula??o, flocula??o e flota??o com vistas ? remo??o de s?lidos suspensos, utilizando-se o equipamento flotateste. Nesse processo foram testados os coagulantes sulfato de alum?nio e cloreto f?rrico, e variados os fatores pH, concentra??o de coagulante, concentra??o de pol?mero e taxa de recircula??o da ?gua saturada. Ao fim dos experimentos, foram analisados turbidez, s?lidos suspensos, cor, DQO e clorofila a . Esses resultados foram submetidos a estat?stica descritiva para verifica??o da efici?ncia do processo em geral, e an?lise de regress?o para identificar modelos que descrevam o processo e demonstrem os fatores que apresentam maior influ?ncia na flota??o. Ap?s o desenvolvimento dos ensaios, foram encontradas altas efici?ncias de remo??o de s?lidos suspensos, chegando a valores superiores a 90% nos melhores casos. Concluiu-se que a flota??o ? mais eficiente no efluente de lagoa facultativa utilizando-se o cloreto f?rrico, e que a variabilidade de algas pode influenciar negativamente no processo. As an?lises de regress?o demonstraram que o pH ? a vari?vel de maior influ?ncia na coagula??o-flocula??o-flota??o, sendo que o seu valor ?timo dentre os testados foi 5,5 para os dois coagulantes

Made available in DSpace on 2014-12-17T15:03:33Z (GMT). No. of bitstreams: 1 MoisesAFQ_DISSERT.pdf: 1322817 bytes, checksum: d69733a37de991cb265f0cf0939bee27 (MD5) Previous issue date: 2014-02-28 / Coordena??o de Aperfei?oamento de Pessoal de N?vel Superior / This research evaluated the microalgae removal produced in a stabilization pond system using biofilters as post-treatment, besides characterizing the effluents of stabilization ponds and filters in relation to concentrations of algal biomass (chlorophyll a and suspended solids), organic matter (BOD and COD), total phosphorus, orthophosphate, pH and dissolved oxygen, and tried to correlate physicochemical parameters with chlorophyll "a". It was held at the Ponta Negra ETE which is constituted by three stabilization ponds, with a primary facultative pond and two of maturation. For the algae removal were used two submerged bio-filters: the filter FPF (Facultative Pond Filter), fed with facultative pond effluent; and the filter MPF (Maturation Pond Filter), fed with second maturation pond effluent. The filling material of both filters was predominantly gravel no. 2, although it contains portions of gravel no. 1 and no. 3. The filters operating conditions were bad, they were nearly 10 years without maintenance, without cleaning or removal of sludge since the time of its construction, and part of the filling material may be obstruct. Despite poor operating conditions were obtained satisfactory results, in level of posttreatment. Removal efficiencies in relation to BOD and COD were 7 and 25% in FPF and 9 and 19% and in MPF, respectively. In relation to TSS efficiencies in MPF and FPF were 37 and 20%, respectively. As for the chlorophyll "a" removal, the FPF efficiency was 44% and the MPF was 40%. There was 50% of consumption of dissolved oxygen, on average, within the filters. Two profiles were performed in the filters, and it was possible to conclude that variations throughout the day were not statistically significant, and that, regardless of the time of collection, they would have the same representation comparing to the time of data collection (7 am) and the daily average, although individual variations throughout the day have been shown to be significant. Another important observation is that the correlations between Chlorophyll a and TSS were bigger and more significant in the effluent of the filters than in the effluent of the ponds / A pesquisa avaliou a remo??o das microalgas produzidas em um sistema de lagoas de estabiliza??o utilizando biofiltros como p?s-tratamento, al?m de caracterizar os efluentes de lagoas de estabiliza??o e dos filtros no tocante ?s concentra??es de biomassa algal (clorofila a e s?lidos suspensos), mat?ria org?nica (DBO e DQO), ortofosfato, f?sforo total, pH e oxig?nio dissolvido, e buscou correlacionar os par?metros f?sico-qu?micos com a clorofila a . Foi realizada na ETE Ponta Negra que ? constitu?da por tr?s lagoas de estabiliza??o, sendo uma lagoa facultativa prim?ria e duas de matura??o. Para a remo??o das algas, foram utilizados dois biofiltros submersos: o filtro FLF -alimentado com efluente da lagoa facultativa; e o filtro FLM - alimentado com efluente da segunda lagoa de matura??o. O material de enchimento de ambos os filtros foi predominantemente brita n? 2, apesar de conter por??es de brita n? 1 e n? 3. As condi??es operacionais dos filtros eram p?ssimas, pois estavam h? quase 10 anos sem manuten??o, sem limpeza ou remo??o do lodo desde a ?poca da constru??o, podendo parte do material de enchimento estar colmatado. Apesar das condi??es operacionais prec?rias foram obtidos resultados satisfat?rios, em n?vel de p?s-tratamento. As efici?ncias de remo??o em rela??o ? DBO e DQO foram de 7 e 25% no FLF e 9 e 19% no FLM, respectivamente. Em rela??o aos SST as efici?ncias no FLF e FLM foram de 37 e 20%, respectivamente. Quanto ? remo??o de clorofila a , a efici?ncia no FLF foi de 44% e no FLM foi de 40%. Houve o consumo de 50% do oxig?nio dissolvido, em m?dia, no interior dos filtros. Foram realizados dois perfis nos filtros, e foi poss?vel concluir que as varia??es ao longo do dia n?o foram estatisticamente significativas, e que, independentemente do hor?rio da coleta, teriam a mesma representatividade ao comparar com o hor?rio da coleta da pesquisa (7 horas da manh?) e a m?dia di?ria, embora as varia??es pontuais ao longo do dia tenham se mostrado expressivas. Outra importante observa??o foi que as correla??es entre Clorofila a e SST foram maiores e mais significativas nos efluentes dos filtros do que nos efluentes das lagoas

Made available in DSpace on 2014-12-17T15:03:34Z (GMT). No. of bitstreams: 1 MiltonBV.pdf: 1188933 bytes, checksum: 0027ba3da37c2c26ef04d16c288622a2 (MD5) Previous issue date: 2006-11-30 / Waste stabilization ponds are the main technology in use for domestic sewage treatment in Rio Grande do Norte State (RN), northeast Brazil. The are around 80 systems, constructed mainly by municipal city halls, being series comprised by a primary facultative pond followed by two maturation ponds the most used configuration. Due to problems related with the production and destination of sludge and generation of bad odors, the designers have avoided the use of anaerobic lagoons. The majority of systems are rarely monitored to verify their efficiencies and to get new project parameters for future designing. This work has as purpose to make a diagnosis of efficiency of three series of waste stabilization pond series (WSPS) of Jardim Lola 1, Jardim Lola 2 and Beira Rio, located in the North Zone of the city of the Natal/RN, treating domestic raw sewage, on the removal of organic matter and thermotolerant coliform, comparing the operational conditions of the systems this inside of the bands foreseen in the project, through parameters BOD5, QOD, thermotolerant coliforms, dissolved oxygen, pH, temperature, ammoniac nitrogen, total and suspended solids. The work was carried through in the WSPS, all constituted by a primary facultative pond followed by two maturation ponds. Socioeconomic characteristics of population are predominantly low and all the plants are very near of the contributing basins. The series were monitored from of May the November of 2002, totalizing 20 collections of grab samples of raw sewage and ponds effluents between 8:00 and 9:50 h. The main aspect to be detached by the results was the great concentration of organic matter (BOD and COD) and microorganisms the raw sewage which were around two times more concentrated than those values foreseen one in project. Considering all series the highest removals of organic matter were observed in system Beira Rio (84 and 78% of BOD and COD, respectively), which presented high hydraulic detention time (TDH = 89 days). On the other hand, Jardim Lola 1 and Jardim Lola 2 presented a much lower values of HDT (36 days and 18 days respectively) and their removals of BOD and COD were the same (76% and 60%, respectively). The Beira Rio WSPS, was the most efficient verified in relation to solids and ammonia, proving the great influence of the operational variables such as HDT and applied surface organic loadings on the performance of pond series. Although the treatment plants have reached efficiencies of thermotolerant coliforms around 99,999%, the concentrations in the final effluent can be considered very high for launching in aquatic bodies, particularly those produced by Jardim Lola 1 and Jardim Lola 2 series / O sistema de lagoas estabiliza??o ? o tipo de tratamento de esgoto dom?stico mais utilizado no Estado do Rio Grande do Norte, contando com 80 sistemas, constru?dos principalmente pelas prefeituras municipais, sendo o sistema de lagoas em s?rie constitu?das de lagoa facultativa prim?ria seguida de lagoas de matura??o um dos mais utilizados. Devido aos problemas relacionados com a produ??o e destino de lodo e gera??o de maus odores, os projetistas t?m evitado o uso de lagoas anaer?bias. Vale salientar que tais sistemas de lagoas comumente n?o s?o monitorados de forma adequada para verificar suas efici?ncias e obter dados para futuros projetos. Este trabalho tem como finalidade fazer um diagn?stico da efici?ncia de tr?s s?ries de lagoas de estabiliza??o na grande Natal, Jardim Lola 1, Jardim Lola 2 e Beira Rio, na remo??o de mat?ria org?nica e coliformes termotolerantes e, verificar se as condi??es operacionais dos sistemas esta dentro das faixas previstas no projeto, atrav?s dos par?metros DBO5, DQO, coliformes termotolerantes, oxig?nio dissolvido, pH, temperatura, nitrog?nio amoniacal, s?lidos totais e suspensos. Os sistemas estudados s?o constitu?dos por uma lagoa facultativa prim?ria seguida de duas lagoas de matura??o, que atendem a uma popula??o predominante de baixa renda a qual est? bem pr?xima da esta??o de tratamento de esgoto. As tr?s ETE s foram monitoradas no per?odo de maio a novembro de 2002, totalizando 20 coletas de amostras pontuais de esgoto bruto e efluentes das lagoas entre 8:00 e 9:50 h. Os principais aspectos a serem destacados no monitoramento foram a grande concentra??o de mat?ria org?nica e microrganismos nos esgoto brutos afluentes em rela??o ao previsto em projeto. Considerando toda a s?rie as maiores remo??es de mat?ria org?nica ocorreram no sistema Beira Rio (84 e 78% de DBO e DQO, respectivamente), que apresentava um TDH de 89 dias enquanto que os sistemas de Jardim Lola 1 e 2 eram de 36 dias e 18 dias respectivamente, foram determinadas remo??es semelhantes de DBO (76%) e de DQO em torno de 60%. O sistema Beira Rio tamb?m foi o mais eficiente na remo??o de s?lidos e de nitrog?nio amoniacal, comprovando a grande influ?ncia das vari?veis operacionais tais como tempo de deten??o hidr?ulica e carga org?nica aplicada, no desempenho dos sistemas de tratamento. Embora as esta??es de tratamento tenham atingido efici?ncias de coliformes termotolerantes em torno de 99,999%, as concentra??es nos efluentes finais podem ser consideradas muito elevadas para lan?amento em corpos aqu?ticos, particularmente as de Jardim Lola 1 e 2