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1

Rodriguez, Raul. "Upflow anaerobic sludge blanket reactor : modelling." Licentiate thesis, KTH, Kemisk apparatteknik, 2011. http://urn.kb.se/resolve?urn=urn:nbn:se:kth:diva-29521.

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Anaerobic treatment is widely used around the world as a biological stage in both domestic and industrial wastewater-treatment plants. The two principal advantages of anaerobic over aerobic treatment are the production of biogas, which can be used as fuel, and the lower rate of biomass production, which results in lower maintenance costs for the plant. The upflow anaerobic sludge blanket (UASB) reactor is an attractive alternative for regions in hot climates since it works better under mesophilic conditions and it does not need any supporting structure for the development of microorganisms, which grow in the form of granules. In this thesis, a model describing the UASB reactor behaviour with respect to substrate degradation, microorganism growth and granule formation was developed. The model is transient and is based on mass balances for the substrate and microorganisms in the reactor. For the substrate, the processes included in the model are dispersion, advection and degradation of the organic matter in the substrate. The reaction rate for the microorganisms includes the growth and decay of the microorganisms. The decay takes into account the microorganism dying and the fraction of biomass that may be dragged into the effluent. The microorganism development is described by a Monod type equation including the death constant; the use of the Contois equation for describing the microorganism growth was also addressed.  An equation considering the substrate degradation in the granule was required, since in the UASB reactor the microorganisms form granules. For this, a stationary mass balance within the granule was carried out and an expression for the reaction kinetics was then developed. The model for the granule takes into account the mass transport through the stagnant film around the granule, the intraparticle diffusion, and the specific degradation rate. The model was solved using commercial software (COMSOL Multiphysics). The model was validated using results reported in the literature from experiments carried out at pilot scale. A simplified model was also developed considering the case in which the microorganisms are dispersed in the reactor and granules are not formed. The UASB reactor is then described as formed by many well-stirred reactors in series. The model was tested using experimental results from the literature and the sensitivity of the processes to model parameters was also addressed. The models describe satisfactorily the degradation of substrate along the height in the reactor; the major part of the substrate is degraded at the bottom of the reactor due to the high density of biomass present in that region. This type of model is a useful tool to optimize the operation of the reactor and to predict its performance.
QC 20110203
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2

Yan, Jing-Qing. "Anaerobic digestion of cheese whey in an upflow anaerobic sludge blanket reactor." Thesis, University of British Columbia, 1991. http://hdl.handle.net/2429/31898.

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The anaerobic digestion of cheese whey was studied in an upfiow anaerobic sludge blanket reactor for its start-up characteristics, the effects of various process parameters, the effect of sulfate addition and the determination of optimal operating conditions. Start-up of an UASB reactor treating cheese whey was extremely difficult due to its tendency to acidify. Various start-up strategies were tested to facilitate start-up and to ensure stable operation. Among the operating parameters, sludge loading rate was the most critical for proper start-up of the UASB reactor. The initial sludge loading rate during start-up period should not exceed 0.25 g COD/g VSS. The response of whey digestion to several process parameters was investigated. Without pH-control, over 97% COD removal was obtained for influent concentrations from 5 to 28.8 g COD/1 and HRT of 5 days. However, instability was observed when the influent concentration was increased to 38.1 g COD/1. Gas production from whey is affected by organic loading rate (OLR). At an OLR less than 4 g COD/l-d, higher influent strength resulted in a higher methane production rate. When the OLR was greater than 6, higher strength feed or shorter hydraulic retention time (HRT) produced less methane. From the profiles of substrate concentration measured at various levels above the bottom of the reactor, two reaction stages, acidogenesis and methanogenesis were distinguished. It was experimentally illustrated that the rate of acidogenesis is much faster than the rate of methanogenesis in a whey anaerobic digestion system. The accumulation of VFAs in the first stage being faster than its assimilation in the second stage creates a distinct acidogenic phase in the bottom of the reactor. The instability caused by high influent concentration could be attributed to the accumulation of VFAs beyond the assimilative capacity of the methanogenic stage. A set of empirical models for accumulation and degradation of VFAs was developed using linear regression analysis. The requirement for maintaining this system in a dynamic balance was that the degradation capacity for VFA in the second stage be greater than the accumulation of VFA in the first stage. Based on this idea, the optimal influent concentration was given as between 25 to 30 g COD/1 for system stability. A hypothesis was proposed in this study that a proper amount of sulfate may be applied to moderate the detrimental influence of excess hydrogen on a stressed anaerobic reactor. The effect of sulfate was tested to study the biochemical mechanism. The permissible influent COD concentration was increased from 30 g COD/1 to 50 g COD/1 by using sulfate addition. The pH in the reactor was on the average 0.8 units higher and the concentration of butyric acid in the acidogenic phase much lower with added sulfate than without sulfate addition. The significant improvement of process stability and treatment efficiency made by the addition of sulfate clearly illustrated that sulfate acted like a stimulator which helped to maintain conditions favorable to methanogenesis. The mechanism of this stimulation is explained according to thermodynamics and hydrogen regulation which suggested that sulfate is able to promote the β-oxidation of VFAs by consuming hydrogen. A two-stage inhibition mechanism was proposed to explain the inhibition of high VFA concentrations and the stimulation of sulfate. Higher hydrogen pressure is the cause of preliminary inhibition, resulting in the accumulation of VFAs, which subsequently inhibit the activity and growth of methanogens in the second inhibition stage. The mechanism of inhibition of methanogens from VFAs was interpreted as being caused by the acidification of the internal cytoplasm and destruction of the pH gradient by non-ionized acids based on the theory of bacterial membrane transport. A new control strategy for stabilization of an anaerobic system is recommended. Under the optimal operating conditions based on the results in the first three steps, over 97% reduction of COD was achieved when the influent COD was 30 g /l using an HRT of 2 days, an OLR of 16.61 g COD/l-d and sulfate concentration of 0.2 g/1.
Applied Science, Faculty of
Chemical and Biological Engineering, Department of
Graduate
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3

Yang, Gong. "Stability and control of upflow anaerobic sludge blanket." Thesis, University of Newcastle Upon Tyne, 1992. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.386733.

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4

Ekekwe, Magnus Chibuzor. "Biodegradation of chloroform in an upflow anaerobic filter." Thesis, University of Strathclyde, 2003. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.269937.

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5

Sam-Soon, Paul Alan Li Nai Sing. "Pelletization in the upflow anaerobic sludge bed (UASB) reactor." Doctoral thesis, University of Cape Town, 1989. http://hdl.handle.net/11427/17151.

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Includes bibliography.
This investigation was prompted by a study into the feasibility of treating an apple juicing waste water in an upflow anaerobic sludge bed (UASB) reactor system. Past experience with this system suggested that a pelletized sludge would be produced due to the nature of the waste water. This indeed was observed but the system exhibited an unusual feature, a high removal of nitrogen far in excess of that normally found in normal anaerobic processes. This observation stimulated a far reaching investigation into, the behaviour of the pelletized sludge bed, the causes giving rise to pelletization, a biochemical model explaining pellet formation, verification of the biochemical model, criteria for pellet formation, pH control in the pelletized sludge bed, and a kinetic model for the UASB process.
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6

Singh, Kripa Shankar. "Municipal wastewater treatment by upflow anaerobic sludge blanket (UASB) reactors." Thesis, National Library of Canada = Bibliothèque nationale du Canada, 1999. http://www.collectionscanada.ca/obj/s4/f2/dsk1/tape8/PQDD_0018/NQ45311.pdf.

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7

McClain, Robert Earl. "Microbiotic assessment of an upflow anaerobic/aerobic swine treatment process." Diss., Mississippi State : Mississippi State University, 2001.

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8

Hwang, Seokhwan. "Anaerobic Treatment of Whey Permeate Using Upflow Sludge Blanket Bioreactors." DigitalCommons@USU, 1993. https://digitalcommons.usu.edu/etd/5400.

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Whey permeate was anaerobically digested in laboratory scale upflow anaerobic sludge blanket reactors. Nine hydraulic retention times between 5 and 0.2 days were examined with a fixed influent concentration of 10.6 ± 0.2 g COD/L. Chemical oxygen demand removal efficiency ranged from 99.0 to 18.9% and maximum production rate of methane gas was 2.67 L/L/day at a hydraulic loading rate of 12.97 kg COD/m3/day. About 70% of the chemical oxygen demand removed was converted to methane. Both the nonlinear least square method with 95% confidence interval and linear regression were used to evaluate kinetic coefficients. The maximum substrate utilization rate, k, and half saturation coefficient, KL, were determined to be 1.269 ± 0.163 Kg COD/kg VSS/day and 1.000 ± 0.179 kg COD/kg VSS/day. The yield coefficient, Y, and biomass decay rate coefficient, Kd, were also determined to be 0.160 ± 0.012 kg VSS/kg COD and 0.027 ± 0.004 day-1, respectively.
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9

Ener, Alptekin Emel. "Anaerobic Treatment Of Dilute Wastewaters." Phd thesis, METU, 2008. http://etd.lib.metu.edu.tr/upload/12609461/index.pdf.

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In this study, domestic wastewater was used to determine the anaerobic treatment performances of a dilute wastewater in one-phase upflow anaerobic sludge blanket (UASB) system and two-phase upflow anaerobic filter (UAF) and UASB system. The acidification performances of domestic wastewater were compared in UAF and UASB reactors. The degree of acidification is higher in UAF reactor (31%) compared to UASB reactor (18%) at 2 h hydraulic retention time (HRT) in the anaerobic treatment of domestic wastewaters. The effluent total volatile fatty acid (tVFA) concentration was higher in UAF reactor than that the UASB reactor at 2 h HRT. The total chemical oxygen demand (tCOD) removal is 40% in winter and 53% in summer in UAF reactor at 2 h HRT. The tCOD removals in two-phase UAF and UASB system and one-phase UASB system were 83% and 63%, respectively, in 4 h HRT. The conversion rate of COD removed to methane were between 0.005 and 0.067 Nm3 methane/kg COD removed and between 0.158 and 0.233 Nm3 methane/kg COD removed in the UAF and the UASB reactor of the two-phase system, respectively. The conversion rate of COD removed to methane varied between 0.029 and 0.199 Nm3 methane/kg COD removed in one-phase UASB reactor. The results of this study showed that the two-phase reactor system consisting from UAF and UASB reactors provide a good removal of soluble organics variations in acidification reactor and better methane productions in UASB reactor at temperatures 20°
C and 35°
C through the treatment of domestic wastewater at a HRT of 4 hours.
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10

Lu, Jinghua. "The fate of chlorinated phenols in upflow anaerobic sludge blanket reactors." Thesis, University of Ottawa (Canada), 1992. http://hdl.handle.net/10393/7640.

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Five trichlorophenols (2,3,4-, 2,3,5-, 2,3,6-, 2,4,5-, 2,4,6-trichlorophenol) and one dichlorophenol (3,5-dichlorophenol) were continuously treated in upflow anaerobic sludge blanket reactors for eight months. Their anaerobic biodegradation pathways and toxicity loading limits were determined. It was found that ortho positioned chlorine was readily removed from tri- and dichlorophenols. With acclimation, meta position chlorine was also removed from 3,4-, 3,5-dichlorophenols. Although there was no evidence of 3- and 4-monochlorophenol being degraded, the mass balance of the chlorophenols indicated that more than 50% of the 3-monochlorophenol formed from its parent compounds had disappeared, and the disappearance of 4-monochlorophenol was 20%. Acclimation and adequate alternate carbon sources reduced inhibition by chlorophenols. Inhibition was caused by: 2,4,5-trichlorophenol at a specific loading rate of 0.3 mg/g volatile suspended solids (hydraulic retention time of 3 days) and 0.9 mg/g volatile suspended solids (hydraulic retention time of 1 day); 2,3,4-trichlorophenol at a specific loading rate of 2.5 mg/g volatile suspended solids (hydraulic retention time of 1 day); 2,3,5-trichlorophenol at a specific loading rate of 1.25 mg/g volatile suspended solids (hydraulic retention time of 1 day); 3,5-dichlorophenol at a specific loading rate of 3.0 mg/g volatile suspend solids (hydraulic retention time of 1 day). The sorption isotherms of all the mono-, di- tri-chlorophenols as well as pentachlorophenol were determined. Biosorption of chlorophenols by anaerobic granular biomass fitted the Freundlich model. Biosorption of chlorophenols increased with increasing halogenation of the chlorophenols. The conditions used in batch sorption tests were similar to those in upflow anaerobic sludge blanket systems. The biosorption constants determined were successfully used to estimate the amount of chlorophenols sorbed by biomass in upflow anaerobic sludge blanket systems. Biosorption accounted for as much as 6% of the total chlorophenol removal. (Abstract shortened by UMI.)
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11

Gabr, Tarek Zeiad. "Hydraulic overload of upflow anaerobic sludge bed reactor treating landfill leachate." Thesis, University of Ottawa (Canada), 2003. http://hdl.handle.net/10393/26482.

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The impact of hydraulic shockloads on UASB reactors operating at mesophilic conditions (T = 35°C) was studied. The wastewater, landfill leachate, was pretreated by filtering it through peat moss. The reactor was 1/2 filled with sludge previously acclimated from a pulp mill wastewater treatment facility. The shockloads imposed on the reactor were hydraulic where the flowrate of the influent wastewater was increased by 2--3 times the initial flow rate at quasi steady-state (corresponding to a change of HRT from 2.5--3 to 1--1.5 d) where the influent concentration was maintained around 10 g COD/L. Two modes of shock-loading were compared: continuous versus intermittent for a total duration of 3 hours, where the intermittent operation distributed the flowrate increase over 9 hours to make a total of 3 hours. The results showed that a UASB reactor can endure a single shockload of OLR close to 9.6 +/- 1.8 g COD/L.d and recover to pre-shock conditions in a period not exceeding 30 hours. Intermittent shock feeding resulted in better effluent quality; nonetheless, it took a longer time to recover, and was more prone to solids washout. (Abstract shortened by UMI.)
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12

Tisinger, Jessi Lind. "Treatment of clam-processing wastewater using upflow anaerobic sludge blanket (UASB) technology." Thesis, This resource online, 1991. http://scholar.lib.vt.edu/theses/available/etd-10242009-020256/.

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13

Moosbrugger, Richard Engelbert. "Weak acid/bases and pH control in upflow anaerobic sludge bed reactors." Doctoral thesis, University of Cape Town, 1991. http://hdl.handle.net/11427/22041.

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Prior to the investigation into H₂CO₃*alkalinity, each waste (substrate) was studied with respect to its potential for pellet formation. During these feasibility studies, the need emerged for a simple, reliable and accurate method to monitor the H₂CO₃*alkalinity and SCFA concentration in the reactor effluent. Against the background described above, the following tasks were set: • Development of a simple method for simultaneous determination of the H₂CO₃*alkalinity (carbonate system alkalinity) and SCFA concentration in anaerobic systems to be used in, (1) assessing the H₂CO₃*alkalinity requirements of different types of wastes when treated in UASB systems, (2) monitoring process stability when treating these wastes under different operating conditions, e.g. different recycle ratios. • Assessment of H₂CO₃*alkalinity requirements for Iauter tun (brewery) waste to maintain a near neutral minimum bed pH in UASB systems. Because this waste generates very little H₂CO₃*alkalinity internally, virtually all H₂CO₃*alkalinity has to be supplied externally. It was of special interest to evaluate the effect of recycling the effluent to the influent in order to recover the effluent H₂CO₃*alkalinity and to dilute the base influent COD to an effective influent COD, CODe, defined as: base influent COD/(1 + recycle ratio). • Assessment of H₂CO₃*alkalinity requirements for wine distillery waste to maintain a near neutral- minimum bed pH in UASB systems. This waste generates a substantial mass of H₂CO₃*alkalinity internally due to deamination of proteins to ammonium/ammonia, reduction of sulfates to sulfides and removal of organic acid salts such as potassium bitartrate. Similar to the Iauter tun waste it was of interest to evaluate the effect of recycling on process performance and on the requirements of H₂CO₃*alkalinity at different recycle ratios, i.e. different CODe concentrations. • Assessment of a pure proteinaceous waste, casein: This substrate provides the opportunity to study the H₂CO₃*alkalinity generation from deamination and the effect of pH changes on process performance of systems with high levels of inorganic nitrogen. With high levels of inorganic nitrogen generated in the reactor liquid due to deamination the likelihood increases of inhibitory effects developing due to increased ammonia (NH₃) levels at higher than neutral pH values. It was of interest to evaluate the effect of pH change on process performance due to the NH₃ inhibition. Because of the differing nature of these tasks each will be dealt with separately, describing the problems encountered and the solutions achieved.
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14

Scampini, Amanda C. "Upflow anaerobic sludge blanket reactors for treatment of wastewater from the brewery industry." Thesis, Massachusetts Institute of Technology, 2010. http://hdl.handle.net/1721.1/59712.

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Thesis (S.M.)--Massachusetts Institute of Technology, Dept. of Materials Science and Engineering, 2010.
"February 2010." Cataloged from PDF version of thesis.
Includes bibliographical references (p. 61-64).
Anaerobic digestion can be utilized to convert industrial wastewater into clean water and energy. The goal of this project was to set up lab-scale anaerobic digesters to collect data that will be used to develop and validate a predictive monitoring and controls solution to improve digester performance. The research project involved the design, construction, and instrumentation of lab-scale anaerobic digestion reactors to be used for the treatment of brewery wastewater. Useful parameters for monitoring the health of the digesters were identified and techniques for measuring each parameter were evaluated to determine the best analytical methods. A synthetic brewery wastewater was prepared and the reactors were operated until a stable steady-state was achieved. Data was collected to evaluate the anaerobic digesters from start-up to steady-state, and controlled variations were implemented in order to obtain transient data for the supervisory model. Initial perturbations in organic loading rate and influent pH suggest that gas composition and gas production appear to be the best on-line monitoring parameters to indicate changes in reactor conditions.
by Amanda C. Scampini.
S.M.
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15

Batista, Kátia Bakker. "Resposta dinâmica dos reatores UASB (Upflow Anaerobic Sludge Blanket) submetidos a cargas senoidais." Universidade de São Paulo, 2000. http://www.teses.usp.br/teses/disponiveis/18/18138/tde-17072018-085123/.

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Esta pesquisa consistiu na verificação do comportamento do reator UASB de bancada (volume igual a 10,5 litros), quando submetido a variações senoidais de vazão afluente, comparando-se com a eficiência no seu funcionamento com vazão constante, através de análises de amostras de afluentes e efluentes. O reator UASB utilizado foi montado no Laboratório de Processos Biológicos da EESC-USP dentro de uma câmara com temperatura constante de 30 ± 3°C, e alimentado com esgoto sintético, com DQO de 500 mg/l, 750 mg/l e 1000 mg/l. O reator foi inoculado em abril de 1999, com 3,5 litros de lodo anaeróbio proveniente de um reator compartimentado, também situado na EESC-USP. Devido à dificuldade de atingir um valor esperado para a eficiência de remoção de Matéria orgânica, foi dada nova partida no reator, em julho de 1999, desta vez com lodo proveniente de outro UASB. Após a segunda partida, o reator operou com vazão constante e DQO afluente em torno de 500 mg/l até setembro de 1999, com média de remoção de DQO bruta de 75% no período, passando-se, então, à fase de variação senoidal de vazão de forma que o máximo e o mínimo fossem de ±30%, ±45% e ±60% da vazão média. Para este regime, obteve-se 80% de eficiência média de remoção de DQO bruta. Os valores de pH, alcalinidade e ácidos voláteis foram praticamente constantes durante a operação. Os perfis de remoção de DQO ao longo do dia mostraram uma pequena queda na eficiência do reator, aproximadamente 1,5 vezes o tempo de detenção hidráulica médio (8 horas), após os máximos de vazão para o regime de variação de vazão de ±30% e ±45% e 2,5 vezes o tempo de detenção hidráulica médio, para variação e ±60%. O mesmo experimento foi repetido para DQO afluente de 1000 mg/l e obteve-se, em média, eficiências de 65% de remoção de DQO.
This research consisted in the UASB reactor performance verification when it was submitted to sine-based variations of loading rate, in comparison to its normal operation. The UASB reactor used was set up at the Biological Process Laboratory of EESC-USP, inside a camera with temperature of 30°C ± 3°C. It was fed with synthetic sewage (COD = 500, 750 and 1000 mg/l). After start-up, the reactor was operated with constant loading rate (COD = 500 mg/l) until September 1999. The organic matter removal average in this period was 75%. Then, it was initiated the phase of sine-based variation loading rate (±30%, ±45% and ±60%). In this regime, it was obtained a medium gross COD removal efficiency of 80%. The pH values, alkalinity and volatile acids were practically constant during the operation. The COD removal profiles during the day showed a subtle fall in the reactor efficiency after 1.5 times the medium hydraulic detection time, for the loading rate variation of ±30% and ±45%. For ±60% variation, the answer time was approximately 2.5 times the medium hydraulic detection time. The efficiency of gross COD removal stay however over 78,53% until the experiment 9, witch showed that the reactor can stand the loading rate variations. The efficiency of filtered COD removal decreased on the second experiment, came back to the initial values and decreased again. The values of variation didn\'t surpass 6,6% for gross COD and 8,43% for filtered COD.
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16

Pham, Thi Tham. "Anaerobic degradation of aircraft deicing fluid (ADF) in upflow anaerobic sludge blanket (UASB) reactors and the fate of ADF additives." Thesis, University of Ottawa (Canada), 2002. http://hdl.handle.net/10393/6053.

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A central composite design was employed to methodically investigate anaerobic treatment of aircraft deicing fluid (ADF) in bench-scale Upflow Anaerobic Sludge Blanket (UASB) reactors. A total of 23 runs at 17 different operating conditions were conducted in continuous mode. The development of four empirical models describing process responses (i.e., chemical oxygen demand (COD) removal efficiency, biomass specific acetoclastic activity, methane production rate, and methane production potential) as functions of ADF concentration, hydraulic retention time (HRT), and biomass concentration is presented. Model verification indicated that predicted responses (COD removal efficiencies, biomass specific acetoclastic activity, and methane production rates and potential) were in good agreement with experimental results. Biomass specific acetoclastic activity was improved by almost two-fold during ADF treatment in UASB reactors. For the design window, COD removal efficiencies were higher than 90%. Predicted methane production potentials were close to theoretical values, and methane production rates increased as the organic loading rate (OLR) was increased. ADF toxicity effects were evident for 1.6% ADF at medium specific organic loadings (SOLR above 0.5 g COD/g VSS/d). In contrast, good reactor stability and excellent removal efficiencies were achieved at 1.2% ADF for reactor loadings approaching that of highly loaded systems (0.73 g COD/g VSS/d). Acclimation to ADF resulted in an initial reduction in the biomass settling velocity. The fate of ADF additives was also investigated. There was minimal sorption of benzotriazole (BT), 5-methyl-1 H-benzotriazole (MeBT), and 5,6-dimethyl-1 H-benzotriazole (DiMeBT) to anaerobic granules. A higher sorption capacity was measured for NP. Active transport may be one of the mechanisms for NP sorption. Ethylene glycol degradation experiments indicated that BT, MeBT, DiMeBT, and the nonionic surfactant Tergitol NP-4 had no significant effects on acidogenesis and methanogenesis at the concentration levels studied. A significant inhibition of acetoclastic activity was observed for NP at 100 mg/L, with acetic acid consumption rate at 38% of that for controls. No evidence for anaerobic degradation of benzotriazole and its derivatives was observed; however, both batch and continuous experiments suggested that anaerobic degradation of NP occurred. Kinetic analysis of operational data obtained for the anaerobic treatment of ADF in UASB reactors indicated that the substrate utilization rate was independent of the reactor biomass concentration. The maximum rate of substrate utilization and the half-velocity constants for ADF treatment were 28.4 g COD/L/d and 648 mg COD/L, respectively. For 1.2% ADF, the biomass yield and endogenous decay coefficients were 0.027 g VSS/g COD and 0.012 d-1 , respectively.
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17

Gie, Lowna-Marie. "Enhancement of the biodegradability of grain distillery wastewater to improve upflow anaerobic sludge blanket reactor efficiency." Thesis, Stellenbosch : University of Stellenbosch, 2007. http://hdl.handle.net/10019.1/2933.

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Thesis (Msc Food Sc (Food Science))--University of Stellenbosch, 2007.
The distillery industry generates large volumes of heavily polluted wastewater and thus effective wastewater treatment is essential. It has been reported that a chemical oxygen demand (COD) reduction of more than 90% can be achieved when wine distillery wastewater (WDWW) is treated in an upflow anaerobic sludge blanket (UASB) reactor. The first objective of this study was to investigate UASB treatment of WDWW and to try to enhance the efficiency by using ozonation treatments. Secondly, the impact of grain distillery wastewater (GDWW) on UASB granules was determined. The third objective was to determine whether ozonation and enzymatic treatment combinations might improve the biodegradability of GDWW and thus make GDWW more amenable to UASB treatment. It was found that UASB treatment combined with ozonation improved the WDWW treatment efficiency. When diluted WDWW (chemical oxygen demand COD = 4 000 mg.L-1) was ozonated (dose = 47 mg.L-1) in a 50 L venturi circulating contactor system, the COD reduction was 7%. When WDWW was treated in a laboratory-scale UASB reactor (substrate pH = 7.0, COD = 4 000 mg.L-1 and organic loading rate (OLR) = 4.0 kg COD.m-3.d-1), the COD reduction was 92%. When the UASB treatment was combined with either pre- or postozonation, the COD reduction was 94 and 96%, respectively. When UASB treatment was combined with pre- and post-ozonation, a COD reduction of 98% was achieved. The activity of the UASB granules was also found to improve over time, despite the addition of the ozonation treatment. It has been reported that operational problems occur when GDWW is treated in an UASB reactor as a result of the encapsulation of the granules. This was confirmed when granules from a full-scale UASB treating WDWW became encapsulated in a layer after being exposed to GDWW (COD = 4 000 mg.L-1) for 24 d. The results showed that the lipid content of the granules increased from 1.25 to 60.35 mg lipid.g-1 granule over the 24 d exposure period. Therefore, granules exposed to GDWW were encapsulated in a lipid-rich layer and as a result the contact between the GDWW and microbial consortium in the granules was reduced. The operational problems found during the industrial UASB treatment of GDWW were ascribed to the encapsulation of the granules. Combinations of ozonation (dose = 1 476 mg.L-1) generated in a 2 L bubble column and enzymatic treatments (1% FogFreeTM (FF) dosage and 2 d incubation at 35°C) were found to improve the biodegradability of GDWW. This improvement was in terms of lipid reduction in GDWW, granule activity and visual appearance of the encapsulating layer of the granules. The highest lipid reduction (90%), highest granule activity, lowest lipid content of the granules (3.74 ± 0.10 mg.g-1 granule) and best visual appearance were achieved in ozonated GDWW treated with 1% FF, followed by just ozonation. The higher lipid reduction and subsequent higher granule activity were ascribed to the reduction in lipids which resulted in the fact that fewer lipids were available to encapsulate the granules. As a result of the lipid reduction, the granule activity improved and the GDWW was made more amenable to UASB treatment. This study proved that UASB treatment combined with ozonation led to an enhancement of the treatment efficiency of WDWW. It was also found that the cause of the operational problems during UASB treatment of GDWW was as a result of the granules being encapsulated in a lipid-rich layer. It was established that treating GDWW prior to UASB treatment improved the biodegradability of GDWW. The data from the study showed that high lipid reduction in the GDWW directly led to better granule activity, lower granule lipid content and a thinner encapsulating layer. Based on the data from this study, it is recommended that GDWW be ozonated prior to other treatments because it can be done inline and the costs would be lower than that of enzymatic treatments.
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18

Van, Der Westhuizen Hendrik Schalk. "Operational enhancement of an upflow anaerobic sludge blanket reactor treating fog-reduced grain distillery wastewater." Thesis, Stellenbosch : Stellenbosch University, 2014. http://hdl.handle.net/10019.1/86423.

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Thesis (MScFoodSc)--Stellenbosch University, 2014.
ENGLISH ABSTRACT: Waste generated by the distillery industry is a major ecological concern and disposal thereof without a suitable treatment can have damaging effects on the environment. The characteristics of this type of wastewater are highly variable and dependent on the raw material used and production process followed. Grain distillery wastewater (GDWW) is also rich in fats, oils and grease (FOG). Successful treatments of distillery wastewater and GDWW have been reported using an upflow anaerobic sludge blanket (UASB) reactor technology. The aim of this study was to investigate the ability of lab-scale UASB reactor to treat FOG-reduced GDWW and the subsequent enhancement thereof following an unique feeding strategy approach. Firstly, a coagulation/flocculation-centrifugation step was developed to obtain FOG-reduced GDWW. Secondly, the efficiency of a lab-scale UASB reactor was investigated treating FOG-reduced GDWW at pre-determined operational parameters as well as the verification of biomass acclimatisation. Lastly, the effect of a unique feeding strategy of FOG-reduced GDWW to lab-scale UASB reactor granules was investigated in terms of COD, FOG-reduction and biomass acclimatisation. It was found that a coagulation/flocculation-centrifugation treatment removed sufficient amounts of FOG and TSS from GDWW. Different commercially available coagulation/flocculation products were evaluated whilst used in combination with a centrifugation step for improved sedimentation and separation. The FOG removal remained between 90 and 97% for the ferric chloride (FeCl3) and Ferrifloc 1820 treatments, respectively, whereas the TSS removal ranged between 56 and 93%, respectively. The use of a high molecular weight polymer (Ultrafloc 5000) and an aluminium chlorohydrate (Ultrafloc 3800) proved to be less effective in terms of FOG removal efficiency, ranging from 72 to 86%. It was decided to pre-treat GDWW with FeCl3 in combination with centrifugation to obtain FOG-reduced GDWW for subsequent UASB reactor treatment investigations. The FOG-reduced GDWW was fed into a laboratory-scale UASB reactor (2 L) over a period of 331 days. During the operational period different feeding parameters were attained to establish the ability of the UASB reactor to efficiently treat FOG-reduced GDWW. The COD removal increased from 60 to 85% at an organic loading rate (OLR) of ca. 5.5 kgCOD.m-3.d-1 (pH = 7.5) whilst FOG removal remained between 45 and 70%. COD removal increased to 90% with the attainment of an OLR of ca.10 kgCOD.m-3.d-1 (pH = 7.5) whereas FOG removal remained in the region of 55 and 65%. COD and FOG removal remained above 85% and 50%, respectively, when substrate pH was decreased to 6.50 (OLR ca. 10 kgCOD.m-3.d-1). A granule activity test was performed on seed and FOG-reduced GDWW fed granules to determine biomass acclimatisation. FOG-reduced GDWW fed granules showed higher activity in terms of methane production rate and cumulative methane production suggesting biomass acclimatisation. The FOG-reduced GDWW was fed to a laboratory-scale UASB reactor following a unique feeding approach. The feeding approach consisted of several feeding and starvation cycles. Improved average biogas production was observed during the feeding (0.26 to 11.3 L.d-1) and starvation (1.8 to 4.2 L.d-1) cycles as higher loading rates were obtained during each feeding cycle. After the completion of the strategic feeding the UASB reactor was continuously fed at an organic loading rate of ca. 5 kgCOD.m-3.d-1. The COD reduction efficiency improved from 70 to 80%, however, FOG removal remained in the region of 60%. Granule activity tests done on days 0, 215 and 279 showed improved UASB granule activity to FOG-reduced GDWW with operation time in terms of methane production rate and cumulative methane production. This study has proven that a coagulation/flocculation-centrifugation treatment of GDWW can remove sufficient amounts of FOG and TSS before the commencement of a UASB treatment, however, such a technique would require more refinement. It was also found that a UASB reactor can successfully treat FOG-reduced GDWW, however, it must be advised that close monitoring of the UASB reactor is required in order to maintain efficient COD reduction. A strategic feeding approach proved to be successful, but further improvement of the UASB efficiency to treat FOG-reduced GDWW in terms of stable COD and FOG reduction, stable effluent pH, improved biogas production and biomass activity must still be explored.
AFRIKAANSE OPSOMMING: Afloop water wat gegenereer word deur die distillerings-industrie veroorsaak ‘n ekologiese kommer en wegdoening daarvan sonder geskikte behandeling, kan ernstige gevolge op die omgewing hê. Die eienskappe van hierdie tipe afvalwater kan varieer en is afhanklik van die rou materiale gebruik en die produksie proses wat gevolg is. Graan distillery afloop water (GDAW) deel dieselfde eienskappe met die van distillery afloop water, alhoewel dit ook hoog is in vette, olies en ghries (VOG). Suksesvolle behandeling van distillery afloop water en GDAW met n opvloei-anaërobiese slykkombers (OAS) reaktor is deur verskeie navorsers gerapporteer. Die doel van hierdie studie was om die uitvoerbaarheid van laboratorium skaal OAS reaktor, wat VOG-verminderde GDAW behandel te ondersoek, asook die daaropvolgende verbetering deur n unieke voer strategie te volg. Eerstens, was ‘n koagulasie/flokkulasie-sentrifigasie tegniek ontwikkel om VOG-verminderde GDAW te kry. Tweendens, die effektiwiteit van ‘n lab-skaal OAS reaktor ondersoek, wat gevoer was met VOG-verminderde GDAW, by voorafbepaalde parameters. Laastens, die effek van ‘n unieke voer strategie van VOG-verminderde GDAW op lab-skaal OAS reaktor granules. Dit was vasgestel dat ‘n koagulasie/flokkulasie-sentrifigasie voor behandeling voldoende hoeveelhede VOG en TSS verwyder van GDAW. Verskillende kommersieel beskikbare koagulasie/flokkulasie produkte was in kombinasie met ‘n sentrifugasie stap geëvalueer om sedimentasie en skeiding te verbeter. Dit was nie ‘n plan om die stap te perfek nie, maar dat dit eerder sou dien as ‘n voorbehandeling stap vir opeenvolgende ondersoeke. Die VOG verwydering het tussen 90 en 97% gevariëer vir ferri chloride (FeCl3) en Ferrifloc 1820 (Chlorchem) en TSS verwydering het tussen 56 en 93% gewissel. Die gebruik van ‘n hoë molekulêre gewig polimeer (Ultrafloc 5000) en ‘n aluminium chlorohidraat (Ultrafloc 3800) was minder effektief met n VOG verwydering wat tussen 72 en 86% gewissel het. Die VOG-verminderde GDAW was in ‘n laboratorium-skaal OAS reaktor oor ‘n tydperk van 331 dae behandel. Verskillende voer doelwitte was geëvaluaeer om te bepaal of ‘n OAS reaktor GDAW suksesvol kan behandel. CSB afbraak het van 60 to 85% gestyg teen ‘n organiese lading van 5.5 kgCOD.m-3.d-1 (pH 7.50), met VOG verwydering wat tussen 45 en 70% gewissel het. Die CSB afbraak het na die bereiking van 10 kgCOD.m-3.d-1 (pH 7.50) gestyg na 90% met VOG afbraak tussen 55 en 60% gewissel het. Die CSB en VOG verwydering het bo 85% en 50% onderskeidelik gebly, met die verlaging van substraat pH na 6.50 (CSB ca. 10 kgCOD.m-3.d-1). ‘n Aktiwiteits toets is uitgevoer met saad granules en VOG-verminderde GDAW gevoerde granules. Granules (VOG-verminderde GDAW gevoer) het ‘n hoer aktiwiteit getoon teenoor saad granules in terme van metaan produksie tempo en kumulatiewe metaan produksie. Die VOG-verminderde GDAW was gevoer in ‘n OAS reaktor deur gebruik te maak van ‘n strategiese voertegniek. Die strategie het uit verskeie voer en hongersnood fases bestaan. Verbeterde biogas produksie was tydens voer (0.26 tot 11.3 L.d-1) en hongersnood (1.8 tot 4.2 L.d-1) -fases opgelet soos ‘n hoër lading bereik was. Na die voltooing van die strategiese voer fase was die OAS reaktor op ‘n deurlopende basis teen ‘n lading van 5 kgCOD.m-3.d-1 gevoer. Die CSB verwydering het van 70 na 80% verhoog terwyl VOG afbraak in die omgewing van 60% gewissel het. Biomassa aktiwiteits toetse was uitgevoer is op dag 0, 215 en 279 het verhoogde aktiwiteit vertoon, met ‘n strategiese fase en deurlopende fase teenoor die aanvanklike (ongeaklamatiseerde) granules. Hierdie studie het bewys dat ‘n flokkulasie/koagulasie-sentrifugasie behandeling van GDAW kan dien as ‘n voorbehandelings stap vir opeenvolgende OAS reaktor studies. Dit was gevind dat ‘n OAS reaktor die VOG-verminderde GDAW kan behandel, maar dit word aanbeveel dat die OAS reaktor so sorgvuldig as moontlik gemonitor word om effektiewe CSB verwydering te handhaaf. Ten slotte, ‘n strategiese voer strategie was suksesvol, maar verdere verbetering van die OAS reaktor ten opsigte van die behandeling van VOG-verminderde GDAW moet verder ondersoek word.
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19

Poon, Wing Chi. "An exploratory study of using hydrogen peroxide as oxygen source in aerobic upflow sludge blanket reactor /." View abstract or full-text, 2005. http://library.ust.hk/cgi/db/thesis.pl?CIVL%202005%20POON.

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20

McVeigh, Peter James. "Treatment of blue crab processing wastewater using Upflow Anaerobic Sludge Blanket (UASB) and air stripping technologies." Thesis, This resource online, 1995. http://scholar.lib.vt.edu/theses/available/etd-03042009-040901/.

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21

Pionapen, Johann. "Biological sulphate reduction using primary sewage sludge as energy source in an upflow anaerobic sludge bed reactor." Doctoral thesis, University of Cape Town, 2008. http://hdl.handle.net/11427/5010.

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22

Lamprecht, Corne. "UASB granulation enhancement by microbial inoculum selection and process induction." Thesis, Stellenbosch: University of Stellenbosch, 2009. http://hdl.handle.net/10019.1/1477.

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Thesis (PhD (Food Science))--University of Stellenbosch, 2009.
In the absence of anaerobic granules, anaerobically digested sewage sludge is frequently used to seed industrial upflow anaerobic sludge blanket (UASB) reactors. Because of its flocculent nature, start-up with digested sludge instead of granular sludge proceeds much slower and presents various operational problems. Any manner in which the granulation of digested sludge can be enhanced would benefit UASB reactor start-up and application in developing countries such as South Africa. The main objective of this dissertation was to improve granulation and reduce UASB reactor start-up by using pre-treated digested sludge as seed. The sludge was pre-treated based on the batch granulation-enhancement model of Britz et al. (2002). The main aim of the model was to improve extracellular polymer (ECP) production of lactate-utilising populations by applying short-term controlled organic overloading in a mechanically agitated environment. The batch granulation-enhancement (pre-treatment) process was applied to an ECP-producing digester strain, Propionibacterium jensenii S1. Non-methanogenic aggregates were formed when batch units were incubated on a roller-table instead of a linear-shake platform. Larger, more stable aggregates were obtained in the presence of apricot effluent medium. Preliminary batch granulation-enhancement studies confirmed that using the roller-table as mixing system had a positive influence on batch granulation-enhancement. The roller-table showed the most potential for handling larger volumes in comparison to a linear-shake waterbath and linear-shake platform. The addition of 450 mg.L-1 Fe2+ at the start of the study also influenced aggregate numbers positively. These studies revealed that pre-treatment results varied depending on the seed sludge source. A denaturing gradient gel electrophoresis (DGGE) method was applied for the detection of Archaea in digested sludges and UASB granules. In addition, a methanogenic marker containing methanogens important to the granulation process was constructed to aid identification. The positive influence of DMSO and “touchdown” PCR on the elimination of artifactual double bands in DGGE fingerprints were also demonstrated. Results revealed that only one of the four digested sludges tested contained Methanosaeta concilii (critical to granular nuclei formation) while it was present in all the UASB granules regardless of substrate type. Four digested sludges were obtained from stable secondary digesters. DGGE indicated the presence of M. concilii in all sludges. The Athlone 4Sb-sludge was the only sludge which exhibited measurable methanogenic activity during substrate dependent activity testing. The ST-sludge showed the highest increase in volatile suspended solids (VSS) particles ≥0.25 mm2. Laboratory-scale UASB reactor start-up was done with both sludges and start-up proceeded better in the Athlone 4Sb-reactor. Athlone 4Sb-sludge batches were pre-treated in a rolling-batch reactor in the presence of either lactate or sucrose and used to seed lab-scale UASB reactors B (sucrose seed) and C (lactate seed). Start-up efficiencies were compared to a control (Reactor A). Overall Reactor B was more efficient that the control. At the end of the study the Reactor B sludge had a higher methanogenic activity than the control reactor. It also had the highest increase in VSS ≥1.0 mm2. Pre-treatment of digested sludge in the presence of sucrose, therefore, aided granulation and reduced UASB reactor start-up time.
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23

Júnior, Emerson Marçal. "Remoção de fósforo por adição de cloreto férrico em reator anaeróbio de manta de lodo (UASB) seguido de reator aeróbio seqüencial em batelada (RSB)." Universidade de São Paulo, 2001. http://www.teses.usp.br/teses/disponiveis/18/18138/tde-22122015-165135/.

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Um sistema de tratamento de esgotos sanitários por reator UASB seguido de RSB foi operado durante 27 semanas objetivando-se verificar seu desempenho na remoção de matéria orgânica carbônácea, nitrogênio amoniacal e fósforo. O reator UASB, com 145 litros foi operado com tempo de detenção hidráulica médio de 8 horas durante todo o experimento. O reator RSB, de 106 litros, foi operado com tempos de ciclio de 24, 12 e 6 horas, em seis etapas distintas. Os tempos de ciclo no RSB variaram de 24, 12, 6, 24, 24 e 24 para as etapas 1, 2, 3, 4, 5 e 6 respectivamente. As últimas três etapas foram caracterizadas pela adição de cloreto férrico, respectivamente. O sistema UASB/RSB apresentou eficiência média de remoção de DQO de 92% nas etapas 1, 2, 5, e 6. Na etapa 3, com tempo de ciclo de 6 horas e na etapa 4, quando o RSB recebeu 50mg/L de cloreto férrico, a eficiência média de remoção de DQO foi de 83%. Quando FeCl3 foi adicionado no afluente do reator UASB, obteve-se excelente desempenho na remoção de fósforo, cujas concentrações afluentes foram da ordem de 1,0 mg/L e 4,0 mg/L para a adição de 200 e 100 mg/L de cloreto férrico, respectivamente.
The performance evaluation of a pilot scale system composed by a UASB reactor followed by an SBR reactor treating domestic sewage is presented. The UASB reactor with 145 L of volume, was operated with an average hydraulic detention period of 8 hours. The SBR reactor had a volume of 106 litters being operated with cyclic time of 24, 12, and 6 hours. These different operational conditions characterized three stages of the work from a total of six stages. The three last stages were the addition of 50, 100, and 200 mg/L of ferric chloride in the aerobic, anaerobic, and anaerobic reactors, respectively. In the three last stages the UASB reactor worked with an average hydraulic detention time of 8 hours and the aerobic reactor worked with a cyclic time of 24 hours. After 27 weeks of continuous operation, the UASB/SBR system produced very good results in terms of COD removal. The average results of the COD removal were of 92% to the first, second, fifth, and sixth stages, having a reduction to 83% on the average to the stages where the SBR received 50 mg/L of ferric chloride and in which it worked with a six hour cyclic period. The addition of ferric chloride in the anaerobic reactor had great efficiency in the phosphorus removal. It was reached absolute values of until 1 mg/L of PO43- in the aflluent of the system, promoting an average effluent of 4 mg/L of PO43- with the addition 200 mg/L of FCl3. The UASB/SBR system can become a very promising alternative for domestic sewerage treatment in Brazil, since the system can be projected with shorter times of hydraulic detention times, resulting in a low cost compact installation. Furthermore, excellent results can be gotten to the ammonium and phosphorus removal.
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24

Cangani, Max Ternero. "Tratamento anaeróbio-aeróbio de águas residuárias de suinocultura e reúso na produção de milho para silagem /." Jaboticabal : [s.n.],000681838, 2011. http://hdl.handle.net/11449/94885.

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Resumo: Neste trabalho, avaliou-se o desempenho de dois conjuntos de reatores anaeróbios de fluxo ascendente com manta de lodo (UASB) instalados em série. Os conjuntos I e II foram compostos por dois reatores UASB em série com volumes de 908 e 350 L e de 908 e 188 L, respectivamente. No conjunto II, foi realizado pós tratamento do efluente em um reator operado em batelada sequencial (RBS) com alimentação contínua, com volume de 3000 L. As cargas orgânicas volumétricas (COV) aplicadas no primeiro reator dos conjuntos I e II variaram de 8,36 a 9,95 g DQO total (L d)-1 e de 7,83 a 11,6 g DQO total (L d)-1, respectivamente. As eficiências médias de remoção de DQO total, nitrogênio Kjeldahl (NK), fósforo total (P-total) foram elevadas e variaram de 95 a 97% e de 97 a 99%, de 64 a 67% e de 53 a 69%, e de 80 a 87% e de 71 a 89%, nos conjuntos I e II, respectivamente. As eficiências também foram elevadas para os metais Cu, Fe, Mn e Zn nos conjuntos I e II e variaram de 80 a 91% e de 63 a 80%, de 59 a 80% e de 51 a 72%, de 89 a 97% e de 81 a 98%, de 87 a 98% e de 91 a 99%, respectivamente. A semeadura do milho, foi realizado na safrinha 2009 e na safra 2009/2010, ambos em sistema de plantio direto e convencional, para a confecção de silagem. Os valores do pH observados na silagem não diferiram entre os tratamentos nas duas épocas de semeadura e nos sitemas de plantio direto e convencional. A adubação do milho para confecção de silagem, com dejeto bruto de suíno, com dejetos tratados em sistema anaeróbio e com os dejetos do pós-tratamento, quando comparada com a adubação mineral, não apresentou resultados com diferenças significativas na silagem na maioria dos atributos avaliados. O reúso dos efluentes tratados e do dejeto bruto, não promoveu alterações na nutrição da planta, porém os efluentes... (Resumo completo, clicar acesso eletrônico abaixo)
Abstract: This study evaluated the performance of two sets of upflow anaerobic sludge blanket (UASB) installed in series. The sets I and II were composed of two UASB reactors in series with volumes of 908 and 350 L and 908 L and 188, respectively. In set II was conducted after the treatment of the effluent in a sequencing batch reactor (SBR) with continuous flux, with a volume of 3000 L. The volumetric organic loads (VOC) applied to the first reactor of the sets I and II ranged from 8.36 to 9.95 g total COD (L d) -1 and 7.83 to 11.6 g total COD (L d) -1, respectively. The average removal efficiencies of total COD, Kjeldahl nitrogen (NK), total phosphorus (total P) were high and ranged from 95 to 97% and 97 to 99%, 64 to 67% and 53 to 69% and 80 to 87% and 71 to 89% in clusters I and II, respectively. The efficiencies were also high for Cu, Fe, Mn and Zn in clusters I and II, and ranged from 80 to 91% and 63 to 80%, 59 to 80% and 51 to 72% from 89 to 97 and 81% to 98%, 87 to 98% and 91 to 99%, respectively. We carried out the swing of maize in the 2009 off-season and 2009/2010 season, both in no-tillage and conventional sistems for making silage. The pH values observed in the silage did not differ significantly between treatments in both seasons of swing and in the sistems of tillage and no-tillage. The fertilization of corn for silage making, with raw pig manure with waste treated in anaerobic system and the waste from the post-treatment compared to mineral fertilization, results showed no significant difference in silage in most parameters. The reuse of treated effluent and raw manure, did not promote changes in the nutrition of corn but the application of treated effluent increased concentrations of N readily available for plants in soil. Even in much larger doses applied compared to the raw waste, the treated effluent, promoted soil contamination by total coliforms and thermotolerant lower
Orientador: Roberto Alves de Oliveira
Coorientador: Ana Cláudia Ruggieri
Banca: Wanderley José de Melo
Banca: Israel Jose da Silva
Mestre
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25

Pereira, Maria Beatriz de Oliveira Coelho. "Tratamento de água negra em reator UASB /." Bauru, 2016. http://hdl.handle.net/11449/147978.

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Orientador: Gustavo Henrique Ribeiro da Silva
Banca: Adriana Ferreira Maluf Braga
Resumo: O presente trabalho estudou o tratamento de água negra simulada (esgoto sanitário com efluente suíno) em reator UASB (upflow anaerobic sludge blancket) mesofílico com DQO (demanda química de oxigênio) de entrada de 958,489 ± 489,2mg/L, TDH (tempo de detenção hidráulica) de 1,8 ± 1,8d e COV (carga organica volumética) de 0,2 ± 0,2 KgDQO/m³d. Avaliou-se, ainda, o efeito da suplementação de metais traço (Fe, Ni, Mn, Ba, Se, Co e Cu) na AME (atividade metanogênica específica) do lodo utilizado como inóculo de partida do reator. Os ensaios com metais traços foram realizados em batelada utilizando o método Plackett Burman para planejar o experimento. Foram observados valores nitrogênio amoniacal junto a entrada do reator de 197,37 ± 84,3mgN/L, no entanto, o reator apresentou remoção de DQO de 61,7% ± 15%, demonstrando que não houve efeito tóxico da amônia no meio. Os resultados dos ensaios em batelada demonstraram efeito negativo estatisticamente significativo das adições de Ba e Mn sobre a AME, contudo, o Cu e o Se apresentaram efeito positivo, embora não estatisticamente significativos, indicando que a produção de metano a partir de água negra pode ser estimulada com a suplementação desses metais
Abstract: The present work studied the treatment of simulated black water (sewage with swine wastewater) in UASB (upflow anaerobic sludge blancket) mesophilic with input COD (chemical oxygen demand) of 958,489 = 489,2 mg/L, HRT (hydraulic retention time) of 1.8 = 1.8d and OLR (organic loading rate) 0.2 = 0.2 kgCOD/m3d. This work also evaluated the effect of supplementation of trace metals (Fe, Ni, Mn, Ba, Se, Co e Cu) on the SMA (specific methanogenic activity) of the seed inoculum used in reactor startup. The trace metals assay were performed in batch mode using Plackett-Burman method of the design of the experiments. Despite of the ammonia nitrogen values at the inffluet of 197.37 = 84.3 mgN/L reactor, the reactor, the reactor presented COD removal of 61.7% = 15%, indicating no toxic effectof the addition of Ba and Mn on the SMA of the sludge, however, Cu and Se presented positive effect, although not statistically significant, which indicates that the methane production from black water might be enhanceb by the supplementation of these metals
Mestre
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26

Teer, Joseph Edward. "A study of the biodegradation of modelled iron oxalate leach liquors in an upflow anaerobic sludge blanket (UASB) reactor." Thesis, Imperial College London, 1995. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.309306.

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27

Carvalho, Karina Querne de. "Resposta dinâmica dos reatores UASB (Upflow Anaerobic Sludge Blanket) submetidos a cargas orgânicas e hidráulicas cíclicas: modelação matemática simplificada." Universidade de São Paulo, 2002. http://www.teses.usp.br/teses/disponiveis/18/18138/tde-01122016-122822/.

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Em países com condições ambientais, sócio-culturais e econômicas favoráveis à aplicação de processos anaeróbios para tratamento de esgotos sanitários, o reator UASB (Upflow Anaerobic Sludge Blanket) possui muitas vantagens, dentre os reatores anaeróbios, por permitir instalação, operação e manutenção a baixos custos, apresentar baixa geração de lodo, ser capaz de suportar sobrecargas hidráulicas e orgânicas e possuir eficiência de remoção de demanda química de oxigênio entre 70% e 80%. Contudo poucos estudos são reportados na literatura quando o reator é submetido a variações cíclicas diárias, de cargas orgânicas e hidráulicas, em períodos curtos de duração - iguais ou menores que 24 h. Para compreender os prováveis amortecimentos e atrasos nas respostas de reatores UASB quando submetidos a essas variações, desenvolveu-se um modelo matemático simplificado baseado no regime de escoamento contínuo de um tanque de mistura completa, no modelo cinético tipo Monod para remoção de DQO (Demanda Química de Oxigênio) e equacionamentos empíricos reportados na literatura. Esse modelo indicou que, mesmo apresentando baixa eficiência na remoção de demanda química de oxigênio, o reator possui capacidade de amortecer as variações impostas de vazão e respondeu com grande sensibilidade à variação de velocidade específica máxima de degradação de substrato, indicando que esse parâmetro cinético deve ser o parâmetro de calibração do modelo matemático.
In countries with favorable environmental, social, cultural and economical conditions, the use of anaerobic processes in treatment of domestic sewage. The UASB reactor (Upflow Anaerobic Sludge Blanket) has many advantages, among the anaerobic reactors, allows the installation, operation and maintenance with low costs; presents low sludge generation; is capable to support organic and hydraulic overloads and has COD removal efficiencies between 70% and 80%. However few studies are reported in the literature about reactors submitted to cyclical daily variations of organic and hydraulic loads in short periods of time - equal to or shorter than 24 hours. Aiming to understand the probable dampening and the delays in the response of the UASB reactors when submitted to these variations, it was developed a simplified mathematical model based on the continuous flow pattern of a completed stirred tank and in the Monod kinetic model for COD (Chemical Oxygen Demand) removal and empirical kinetic equations reported in the literature. The model indicated that, even when presenting low efficiency in the removal of COD, the reactor has a capacity to dampen the forced flow variations, and responded with great sensivity to the variation of qmáx., indicating that this kinetic parameter may be the calibration parameter of the mathematical model.
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28

Ndobeni, Afika. "Effect of temperature and carbon to nitrogen ratio on the performance of an upflow anaerobic sludge blanket reactor treating sugarcane molasses." Thesis, Cape Peninsula University of Technology, 2017. http://hdl.handle.net/20.500.11838/2622.

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Thesis (MTech (Chemical Engineering))--Cape Peninsula University of Technology, 2018.
The sugar industry contributes to the development of the economy in many countries, including South Africa. The wastewater generated by this industry has a high pollution load, and therefore requires treatment before discharge to the environment. The primary aims of this study were to determine the performance of an upflow anaerobic sludge blanket (UASB) reactor treating sugarcane molasses and to develop an empirical model to predict the behaviour of the UASB in terms of chemical oxygen demand (COD) removal and biogas production. A UASB (46 L working volume) was inoculated with granular sludge from the brewery industry and was used to investigate the treatment of synthetic sugar industry wastewater with an average COD of 4101 mg/L. The experiments were designed using Design-Expert® Software Version 10. The analysis of variance for the models and the optimisation of reactor temperature and feed carbon to nitrogen (C/N ratio) were carried out using response surface methodology. The UASB was operated at constant hydraulic retention time and organic loading rate of 2.04 days and 2.01 kg/m3.d, respectively. A start-up period of 22 days was required to reach steady-state. The developed empirical models for total COD removal efficiency and biogas production rate were found to be statistically significant with Prob > F values of 0.0747 and 0.0495 and the determination coefficients (R2) were found to be 0.80 and 0.65, respectively. The optimal conditions were found to be at a temperature of 38oC and C/N ratio of 22 mgTOC/mgTN. The corresponding removal efficiencies in terms of total COD, five day biological oxygen demand, total nitrogen, total phosphorus, and sulphate was 77.7, 85.9, 99.2, 44.4 and 57.2%, respectively. Biogas was produced at a rate of 0.832 L/L.d with a methane, carbon dioxide and molecular oxygen content of 65.2, 32.8 and 0.6%. Results suggest that UASBs may offer a feasible option for reducing the organic strength of sugar industry wastewater, while simultaneously generating methane-rich biogas.
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29

Griessel, Wilmare. "Anaerobic bioconversion of the organic fraction from the fruit processing industry." Thesis, Stellenbosch : Stellenbosch University, 2002. http://hdl.handle.net/10019.1/52651.

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Thesis (MSc Food Sc )--Stellenbosch University, 2002.
ENGLISH ABSTRACT: South Africa is a developing country that relies heavily on its agricultural sector for economical welfare especially in the Western Cape Province. However, development gives rise to new technologies, new products, economical stability and unfortunately also to the production of larger volumes of liquid and solid waste. Anaerobic composting is becoming a very attractive treatment option for solid waste disposal because of its unique operational advantages and two valueadded by-products, compost and biogas. Over the last decade progress has been made in anaerobic digestion of solid wastes, but no literature could be found on the anaerobic composting of apple and peach pomace. The main objective of this study was to develop a method to anaerobically compost apple and peach pomace. In the first phase important operational parameters were identified and a method was developed to optimise the parameters. In the second phase of the study, the scaling-up and optimisation of the process were the major objectives. During the first phase of this research 2 L modified glass containers were used as composting units. The most important operational parameters (leachate pH, inoculum source and size, and initial moisture levels) were identified. Anaerobic compost from previous tests, brewery granules and anaerobic sludge were also used as inocula and evaluated for the best source of microbes. After optimising all the identified parameters, good results were obtained, which included higher biogas production, good volume reductions, less bad aromas and a compost product with a neutral pH. After developing the 2 L laboratory-scale method to compost the apple pomace anaerobically, the next step was to ascertain if the method would work if larger volumes of solid fruit waste were composted. A special 20 L composting unit made of PVC was designed to suit the operational requirements of the anaerobic composting process. It was also decided to mix apple pomace and peach pulp together and to use this solid waste source as part of the composting substrate. Different inocula, including cattle manure, anaerobic sludge, brewery granules and anaerobic compost produced in the previous tests, were used. Although good results were obtained with the anaerobic compost and cattle manure as inoculum, the aim was also to decrease the composting period by shortening the pH stabilisation period. To achieve this, it was decided to add NaHC03 to the substrate to be composted to facilitate a faster pH stabilisation. The composting period was subsequently shortened to 25 days with satisfactory results, which included a volume reduction, biogas production and faster pH stabilisation. An upflow anaerobic sludge blanket (UASB) bioreactor was also used to assist the composting process by facilitating the removal of the VFA's present in the composting leachate. This proved to be a valuable addition to the composting process as the UASB bioreactor also provided the composting units with a 'moisturising liquid', which was 'enriched' with a consortium of active anaerobic bacteria when the effluent from the bioreactor was re-added to the composting units. With all the operational parameters in place, good results were obtained and these included a volume reduction of 60% (m/m), a good biogas production, a composting period of only 25 days, a compost that was free of bad aromas, a final compost pH of > 6.5, final leachate COD values of less than 3 000 rnq.l", and a final leachate VFA's concentration of between 0 and 250 rnq.l". If in future research further scaling-up is to be considered, it is recommended that the composting unit be coupled directly to the UASB bioreactor, thus making the process continuous and more practical to operate. If the operational period of the anaerobic composting set-up could be further shortened and the inoculum adapted so that the process could be used for the treatment of other difficult types of solid wastes, it would probably be advantageous for the fruit processing industry to use this method as an environmental control technology.
AFRIKAANSE OPSOMMING: Suid-Afrika is 'n ontwikkelende land wat baie afhanklik is van die sukses van die landbousektor vir ekonomiese welstand, veral in die Wes Kaap Provinsie. Ontwikkeling gaan gepaard met nuwe tegnologie, nuwe produkte, ekonomiese stabiliteit en daarmee saam gaan die produksie van groter volumes vlooiebare en soliede afvalprodukte. Anaërobiese kompostering is tans besig om opgang te maak as en doeltreffende behandelingstegnologie vir vaste afvalstowwe. Tydens die laaste dekade is baie vooruitgang gemaak in die veld van anaërobiese vertering asook kompostering van afvalmateriaal met en hoë vaste stof inhoud. Anaërobiese kompostering van appel- en perskepulp, afkomstig van die versappingsindustrie, het tot dusver min aandag geniet. Die hoofdoel van hierdie navorsing was om 'n anaërobiese komposterings metode te ontwikkel vir die beheer van vrugte afval om sodoende die basis neer te lê vir en nuwe tegnologie wat baie voordele (biogas en kompos) inhou. In die eerste fase is die belangrikste operationele parameters geïdentifiseer om sodoende beter beheer oor die anaërobiese proses uit te oefen. In die tweede fase is die anaërobiese proses wat gedurende die eerste fase ontwikkel is, opgeskaal om optimum resultate te verkry. Gedurende die eerste fase van hierdie verhandeling was 2 L gemodifiseerde glas houers gebruik as komposteringseenhede. Die belangrikste operasionele parameters (pH beheer, inokulasie grootte, vloeistofvlakke en hoeveelheid vog asook vlugtige vetsuur produksie en verwydering) vir die beheer van die anaërobiese komposteringsproses was geïdentifiseer en gebruik as uitgangspunt om 'n anaërobiese komposteringsmetode te ontwikkel. Anaërobiese slyk, brouery granules en anaërobiese kompos van vorige eksperimente was as inokula gebruik. Gedurende hierdie studies was goeie resultate verkry en het 'n hoë biogas produksie, goeie volume reduksies, vermindering van slegte aromas en kompos met 'n neutrale pH ingesluit. . Nadat hierdie goeie resultate met die 2 L laboratorium-skaal metode verkry was, was groter volumes vaste vrugte afval gebruik om te bepaal of dieselfde metode toegepas kan word op en groter skaal. Spesiale 20 L komposteringseenhede was ontwerp om aan die operasionele vereistes van 'n anaërobiese proses te voldoen. Dit was ook besluit om appel pulp met perske pulp te meng en te gebruik as deel van die komposteringssubstraat. Verskeie inokula was weereens gebruik en het die volgende ingesluit: vars beesmis, anaërobiese slyk, brouery granules en anaërobiese kompos van vorige eksperimente. Hoewel baie goeie resultate met vars beesmis en anaërobiese kompos as inokula verkry was, was 'n volgende doel gewees om die kompoterings tydperk te verkort deur die pH vinniger te stabiliseer. Daar was besluit om NaHC03 by die komposteringssubstraat te voeg en so 'n vinniger pH stabilisasie te fasiliteer. 'n UASB ('upflow anaerobic sludge blanket') bioreaktor was ook gebruik om die komposteringsproses aan te help deur die vlugtige vetsure wat in die kompostloog teenwoordig was, te verwyder. Die insluiting van die bioreaktor in die anaërobiese komposteringsproses het bygedra tot die sukses van die proses deurdat die uitvloeisel as 'n vogmiddel vir die komposteringseenhede gebruik was en 'n konsortium van aktiewe anaërobiese bakterieë bevat het. Nadat al die operationele parameters in plek was, was goeie resultate bereik en het die volgende ingesluit: 'n volume reduksie van 60% (m/m), goeie biogas produksie, 'n komposteringstyd van 25 dae, 'n kompos wat vry was van slegste aromas, 'n finale kompos pH van >6.5, finale loog CSB van <3 000 rnq.l' en 'n finale vetsuur konsentrasie van tussen 0 en 250 mq.l'. lndien verdere navorsing onderneem word, word dit aanbeveel dat die UASB bioreaktor direk aan die komposteringseenheid gekoppel word om sodoende die proses meer aaneenlopend en die proses prakties makliker uitvoerbaar te maak. Indien die operationele tydperk nog korter gemaak kan word en die inokulum aanpasbaar kan wees om moeilik verteerbare afvalprodukte te akkomodeer, sal hierdie tegnologie baie voordelig wees as 'n metode om omgewingsbesoedeling te beheer
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30

McLachlan, Tania. "Integration of a combined UASB-ozonation treatment system for cellar effluent degradation." Thesis, Stellenbosch : Stellenbosch University, 2004. http://hdl.handle.net/10019.1/53749.

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Thesis (MSc Food Sc)--Stellenbosch University, 2004.
ENGLISH ABSTRACT: The wine industry significantly contributes to South Africa's water demand and subsequent pollution of the limited resource. Wastewater is produced throughout the year with an increase in volume and organic load during the vintage season. Anaerobic digestion (AD), specifically the upflow anaerobic sludge bed (UASB) technology has been shown to be feasible in the treatment of cellar wastewater. However, the legal standard for chemical oxygen demand (COD) for disposal in a natural water resource (75 rnq.L") is often not met. The aim of the study was to conduct a laboratory-scale investigation into the feasibility of combining pre- and post-ozonation processes with AD in order to achieve a final COD closer to the legal disposal limit. While acclimatising an UASB bioreactor containing mixed anaerobic granules to a cellar wastewater with a pH set at 8.0, stable-state conditions were not reached. Sucrose additions to the substrate, increased substrate loads, heattreatment of the substrate and an addition of isolated cellar effluent bacteria to facilitate degradation prior to AD, were all unsuccessful in maintaining stable-state in terms of COD removal efficiency. Once the substrate pH was re-set to 7.5, the reactor stabilised. The lowest efficient operational pH was found to be 5.73 resulting in a COD removal of 88% at a substrate COD < 5 000 rnq.L". At a substrate pH of 6.0, the lowest efficient operational hydraulic retention time (HRT) and corresponding organic loading rate (OLR) were 19.7 hand 9.75 kg COD.m-3d-1 , respectively, with the COD removal being maintained around 84%. The reactor effluent still had a final COD of 1280 rnq.L", which was well above the legal South African limit. Dominant bacteria were isolated from raw cellar wastewater and identified as Acinetobacter haemolyticus, Burkholderia cepacia and Cryseomonas luteola. In order to investigate the possibility that ozonation improved biodegradability, the growth of the isolates at 35°C was monitored over 24 h in sterile ozonated and non-ozonated substrates from the vintage and non-vintage seasons. All the isolates increased by at least 1.5 log cycles in the control substrates from both seasons. Ozonation of the wastewater batches for 10 min at a rate of 73 rnq.L" led to slightly increased growth of the inoculants in the substrate batch from the vintage season. For the substrates from the non-vintage season, ozonation had an inhibitory effect on the bacterial growth. A 5 min ozonation treatment at a concentration of 73 rnq.L" was found to be optimal for both a pre- and post-treatment to UASB-treatment of cellar wastewater. Both UASB treatment and ozonation were effective in reducing the COD by 85% and 20%, respectively. The COD reduction was improved to 88% when UASB treatment was combined with post-ozonation. The total reduction in total suspended solids (TSS) for the combined process was 97%, compared to 80% for UASB and 73% for an ozone treatment alone. The reduction for volatile suspended solids (VSS) was 98% compared to 81% for UASB and 73% for the ozone treatment alone. The total reduction when using a pre-ozonation UASB treatment combination was an average of 86% for COD. The TSS and VSS were both reduced by 95%. Biogas production increased from 1.4 L.d-1 to 3.8 L.d-1 when an ozonated wastewater was used as substrate. When the UASB treatment was combined with both a pre- and post-ozonation treatment process, the COD was reduced by 89% while TSS and VSS were both reduced by 99%. This study showed that pre- and post-ozonation treatment processes could successfully be utilised to improve UASB treatment of cellar wastewater. Although the legal limits for discarding into a natural resource were not met, significant progress was made in reducing COD levels. Cellar wastewaters do however, vary according to season and the wastewater composition could affect the efficiency of a pre-ozonation process.
AFRIKAANSE OPSOMMING: Die wynindustrie maak "n beduidende bydrae tot die eise wat aan Suid-Afrika se waterbronne gestel word en gevolglik die besoedeling van die beperkte hulpbron. Afloopwater, wat in volume en organiese lading gedurende die parstyd toeneem, word reg deur die jaar opgelewer. Anaërobiese vertering (AV), spesifiek die "Upflow anaerobic sludge blanket" (UASB) tegnologie, is alreeds suksesvol gebruik om kelderafloop te behandel. Die wetlike vereiste vir chemiese suurstof behoefte (CSB) vir storting in "n natuurlike hulpbron (75 rnq.L"), word egter dikwels nie bereik nie. Die doel van die studie was om in "n laboratorium-skaal ondersoek AV te kombineer met voor- en na-osoneringsprossesse, om sodoende te poog om "n CSB nader aan die wetlike standaard te verkry. Terwyl"n UASB bioreaktor wat gemengde anaerobiese granules bevat het, geakklimatiseer is tot kelderafloop met "n pH gestel tot 8.0, kon stabiele toestande nie bereik word nie. Die byvoeging van sukrose tot die substraat, verhoogde substraatladings, hitte-behandeling van die substraat en die byvoeging van geïsoleerde kelderafloop bakterië om substraatafbraak voor AV aan te help, was onsuksesvol om stabiliteit in terme van CSB-verwydering, te handhaaf. "n Verstelling van die substraat pH na 7.5, het gelei tot reaktorstabiliteit. By die laagste doeltreffende bedryfs-pH van 5.73 en substraat CSB < 5 000 rnq.L", was die CSB-verwydering 88%. By "n substraat pH van 6.0 was die laagste doeltreffende bedryfs-hidroliese retensie tyd en -organiese ladingstempo 19.7 h en 9.75 kg CSB.m-3d-1, onderskeidelik, terwyl die CSB verwydering rondom 84% gehandhaaf is. Die CSB van die reaktoruitvloesel van 1 280 rnq.L", was steeds ver bo die wetlike vereiste. Dominante bakterië is uit kelderafloop geïsoleer en as Acinetobacter haemolyticus, Burkholderia cepacia en Cryseomonas luteola, geïdentifiseer. Die moontlikheid dat osonering bioafbreekbaarheid bevorder, is ondersoek deur die groei van die isolate by 35°C oor 24 h in steriele geësoneerde en ongeësoneerde substrate te monitor. Die substrate is berei vanaf kelderafloop wat in die parsseisoen sowel as die nie-parsseisoen versamel is. AI die isolate het met ten minste 1.5 log siklusse in die kontrole substrate van beide seisoene, vermeerder. Vir die kelderafloop wat in die parsseisoen versamel is, het osonering vir 10 min teen 73 rnq.L" gelei tot effens verbeterde groei van die innokulante. Osonering het 'n onderdrukkende effek op die groei van bakterië in die afloopwater versamel in die nie-parsseisoen, gehad. Osonering vir 5 min teen 'n konsentrasie van 73 rnq.L" is as optimum vir beide voor- en na-osoneringsbehandeling tot UASB-behandeling van die kelderafloop, gevind. UASB-behandeling en osonering het die CSB met 85 en 20% onderskeidelik, verminder. Die vermindering kon tot 88% verhoog word wanneer UASB-behandeling met na-osonering gekombineer is. Die vermindering in totale gesuspendeerde vastestowwe (TGV) vir die gekombineerde proses was 97%, in vergelyking met 80% vir UASB- en 73% vir osoonbehandeling alleen. Die vermindering in vlugtige gesuspendeerde vastestowwe (VGV) was 98% in vergelyking met 81% vir UASB- en 73% vir osoonbehandeling alleen. Die totale CSB verwydering vir 'n voor-osonerings UASB kombinasie was gemiddeld 86%. Die TGV en VGV is beide met 95% verminder. Biogasproduksie het ook vermeerder vanaf 1.4 L.d-1 tot 3.8 L.d-1 toe geosoneerde afloopwater as substraat gebruik is. Die kombinasie van UASB-behandeling met voor-osonering, sowel as na-osonering het gelei tot 'n CSB-verwydering van 89% terwyl TGV en VGV beide met 99% verminder is. Hierdie studie het getoon dat voor- en na-osonering suksesvol gebruik kan word om UASB-behandeling van kelderafloop te verbeter. Hoewel wetlike vereistes vir storting in 'n natuurlike hulpbron nie bereik is nie, is beduidende vordering gemaak in die verlaging van CSB-vlakke. Die verskil in die samestelling van kelderafloop gedurende die onderskeie seisoene, kan egter die doeltreffendheid van die voor-osoneringsproses beïnvloed.
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31

Leal, Bruno Quirino [UNESP]. "Avaliação da eficiência do reator UASB compartimentado (RUC) tratando esgoto sanitário de Ilha Solteira com diferentes carregamentos orgânicos." Universidade Estadual Paulista (UNESP), 2015. http://hdl.handle.net/11449/136032.

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A aplicação de reatores anaeróbios, como é o caso dos reatores UASB (Upflow Anaerobic Sludge Blanket), passou a ocupar uma posição de destaque, principalmente no Brasil, face às condições ambientais de temperatura favoráveis, baixo custo, simplicidade operacional e baixa produção de sólidos. Dentre os sistemas anaeróbios, tem-se também o Reator Anaeróbio Compartimentado (RAC), um tipo de reator com configuração simples, com divisões internas que buscam separar os tipos de microrganismos da digestão anaeróbia. No presente trabalho estudou-se o comportamento do sistema Reator UASB Compartimentado (RUC), operando com carregamento orgânico volumétrico (COV) em diferentes variações. A melhor condição operacional, relativa à remoção de carga orgânica, foi conseguida quando o RUC foi operado com uma COV de 1,30kgDQO/m3.d (Fase IV), quando apresentou uma média e desvio padrão da eficiência de remoção de DQO de 82,7±7,7% e de DBO de 78,3±3,5%. Quando operando com a maior COV de todas as fases (fase III - 2,17kgDQO/m3.d) apresentou a segunda melhor eficiência de remoção de carga orgânica, com uma média e desvio padrão da eficiência de remoção da DQO de 74,2±8,8% e da DBO de 76,9±8,2%. Com a COV de 1,70kgDQO/m3.d a média e desvio padrão da eficiência de remoção da DQO e DBO foram de 74,2±8,8% e 69,1±6,8%, respectivamente. E com a COV de 0,78kgDQO/m3.d, a média e o desvio padrão da eficiência de remoção de DQO e de DBO foram de 68,9±11% e 69,7±15,7%, respectivamente. Uma desvantagem verificada no RUC foi o arraste de lodo ocasionado pelo aumento da COV, que afetou as características finais do efluente, mas não alteraram significativamente a sua eficiência de remoção da carga orgânica
The application of anaerobic reactors, such as the UASB (Upflow Anaerobic Sludge Blanket), has come to occupy a prominent position, especially in Brazil, given the favorable environmental conditions such as temperature, low cost, operational simplicity and low production of sludge. Among the anaerobic systems, there is also the Anaerobic Baffled Reactor (ABR), a type of reactor with simple configuration, with internal divisions that seek to separate the types of microorganisms in anaerobic digestion. Thus, the present work studied the behavior of Compartmented UASB Reactor (CUR), operating with variable volumetric organic loading (VOL). The best operating condition on the removal of organic load was achieved when the CUR was operated with a VOL 1.30kgCOD/m3.day (Phase IV), the CUR had 82.7±7.7% of COD removal efficiency (average and standard deviation) and BOD were 78.3±3.5%. When operating at higher VOL (Phase III - 2.17kgCOD/m3.day) showed the second best organic load removal efficiency with average and standard deviation of the COD removal efficiency of 74.2±8.8% and 76.9±8.2 BOD%. With the VOL 1.70kgCOD/m3d average and standard deviation da the removal efficiency of COD and BOD were 74.2±8.8% and 69.1±6.8%, respectively. And the VOL 0.78kgDQO/m3.day, the average and standard deviation of the COD removal efficiency of BOD and were 68.9±11% and 69.7±15.7%, respectively. A disadvantage found in the CUR was drag sludge resulting from increased VOL, which affected the final characteristics of the effluent, but not significantly modified its removal efficiency of organic load
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32

Leal, Bruno Quirino. "Avaliação da eficiência do reator UASB compartimentado (RUC) tratando esgoto sanitário de Ilha Solteira com diferentes carregamentos orgânicos /." Ilha Solteira, 2015. http://hdl.handle.net/11449/136032.

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Orientador: Tsunao Matsumoto
Co-orientador: Liliane Lazzari Albertin
Banca: Milton Dall Aglio Sobrinho
Banca: Katia Sakihama Ventura
Resumo: A aplicação de reatores anaeróbios, como é o caso dos reatores UASB (Upflow Anaerobic Sludge Blanket), passou a ocupar uma posição de destaque, principalmente no Brasil, face às condições ambientais de temperatura favoráveis, baixo custo, simplicidade operacional e baixa produção de sólidos. Dentre os sistemas anaeróbios, tem-se também o Reator Anaeróbio Compartimentado (RAC), um tipo de reator com configuração simples, com divisões internas que buscam separar os tipos de microrganismos da digestão anaeróbia. No presente trabalho estudou-se o comportamento do sistema Reator UASB Compartimentado (RUC), operando com carregamento orgânico volumétrico (COV) em diferentes variações. A melhor condição operacional, relativa à remoção de carga orgânica, foi conseguida quando o RUC foi operado com uma COV de 1,30kgDQO/m3.d (Fase IV), quando apresentou uma média e desvio padrão da eficiência de remoção de DQO de 82,7±7,7% e de DBO de 78,3±3,5%. Quando operando com a maior COV de todas as fases (fase III - 2,17kgDQO/m3.d) apresentou a segunda melhor eficiência de remoção de carga orgânica, com uma média e desvio padrão da eficiência de remoção da DQO de 74,2±8,8% e da DBO de 76,9±8,2%. Com a COV de 1,70kgDQO/m3.d a média e desvio padrão da eficiência de remoção da DQO e DBO foram de 74,2±8,8% e 69,1±6,8%, respectivamente. E com a COV de 0,78kgDQO/m3.d, a média e o desvio padrão da eficiência de remoção de DQO e de DBO foram de 68,9±11% e 69,7±15,7%, respectivamente. Uma desvantagem verificada no RUC foi o arraste de lodo ocasionado pelo aumento da COV, que afetou as características finais do efluente, mas não alteraram significativamente a sua eficiência de remoção da carga orgânica
Abstract: The application of anaerobic reactors, such as the UASB (Upflow Anaerobic Sludge Blanket), has come to occupy a prominent position, especially in Brazil, given the favorable environmental conditions such as temperature, low cost, operational simplicity and low production of sludge. Among the anaerobic systems, there is also the Anaerobic Baffled Reactor (ABR), a type of reactor with simple configuration, with internal divisions that seek to separate the types of microorganisms in anaerobic digestion. Thus, the present work studied the behavior of Compartmented UASB Reactor (CUR), operating with variable volumetric organic loading (VOL). The best operating condition on the removal of organic load was achieved when the CUR was operated with a VOL 1.30kgCOD/m3.day (Phase IV), the CUR had 82.7±7.7% of COD removal efficiency (average and standard deviation) and BOD were 78.3±3.5%. When operating at higher VOL (Phase III - 2.17kgCOD/m3.day) showed the second best organic load removal efficiency with average and standard deviation of the COD removal efficiency of 74.2±8.8% and 76.9±8.2 BOD%. With the VOL 1.70kgCOD/m3d average and standard deviation da the removal efficiency of COD and BOD were 74.2±8.8% and 69.1±6.8%, respectively. And the VOL 0.78kgDQO/m3.day, the average and standard deviation of the COD removal efficiency of BOD and were 68.9±11% and 69.7±15.7%, respectively. A disadvantage found in the CUR was drag sludge resulting from increased VOL, which affected the final characteristics of the effluent, but not significantly modified its removal efficiency of organic load
Mestre
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33

Joubert, Hannarine. "Optimisation of propionibacterial ECP production and the influence of propionibacteria on the UASB granulation process." Thesis, Stellenbosch : Stellenbosch University, 2000. http://hdl.handle.net/10019.1/51866.

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Abstract:
Thesis (MSc)--Stellenbosch University, 2000.
ENGLISH ABSTRACT: The "classical" propionibacteria are used in a variety of natural dairy fermentations where they produce natural preservatives (propionic and acetic acids and bacteriocins) and large amounts of vitamin B12. The extracellular polysaccharide (ECP) producing ability of these bacteria also make them of special interest to the food and waste water management industries as the ECP has been illustrated to playa role in the initial granule formation in upflow anaerobic bioreactor systems. There is little known on the ECP production by propionibacteria and in this study different environmental conditions that influence ECP production were studied. Nineteen different Propionibacterium strains were examined in terms of ECP production and Propionibacterium strain 278 was identified as the best ECP producer. Further studies were only done on this strain because of its high ECP production and because it was originally isolated from an anaerobic digester. The influence of temperature, pH and sucrose concentration was determined through the measurement of ECP production and medium viscosity. It was found that more ECP was produced at temperatures lower than the optimum for growth with the optimum being between 22° and 25°C. Lower initial pH conditions of the growth medium (below pH 7.0) were found to inhibit ECP production and the influence when the initial pH values were between 7.0 and 8.5, was not significant. A higher carbon: nitrogen ratio, when 8% sucrose was added, was also found to enhance the ECP production. The upflow anaerobic sludge bed (UASB) bioreactor process depends on the upward movement of soluble matter through a blanket of active methanogenic granular sludge. The long start-up times as a result of the slow granulation process, as well as the need for a speedy replacement of granules once they have been washed out of the system, are limitations that restrict the general application of this excellent waste water treatment technology. Full exploitation of this biomass immobilisation technique can thus not be realised until the granule formation conditions are defined and optimised. The precise nature of the mechanisms involved in the formation of granules and the reason for their stability, is still not fully understood. It was hypothised by Britz et al. in 1999 that, through the implementation of environmental 'stress' conditions, a shift in the population dynamics of the anaerobic community can be obtained. This results in a concurrent increase in ECP formation that appears to enhance aggregate formation. In the second study it was found that, when 'stress' conditions were applied to already formed granules, the Gram-positive lactate-utilising acidogenic population gained an advantage and more propionic acid producing bacteria were present. The propionic and acetic acid concentrations were also found to increase, and concurrently, a decrease in the growth medium pH occurred. This confirms part of the granulation hypothesis that, when granules are 'stressed', the acidogenic population dynamics change and the lactate-utilising population responds to the gradual decrease in pH and the more acid-tolerant propionic acid producing bacteria gain a competitive advantage resulting in the increase in the propionic acid concentration. When propionibacteria were added to raw sludge during the granule production process, the granules were found to be more active than when nopropionibacteria had been added. This was probably due to the ECP formation by the propionibacteria that enhances the aggregation of the granules. Enhanced granulation was thus found in the batch systems with the fatty acids formed in correlation with the model for granulation. A good correlation was evident between the hypothesis and the experimental data and the hypothesis was partially verified in this study.
AFRIKAANSE OPSOMMING: Die "klassieke" propionibakterieë word in 'n verskeidenheid van natuurlike suiwel fermantasies gebruik waarin hulle verantwoordelik in vir die produksie van natuurlike voedsel preserveermiddels (propioonsuur, asynsuur en bakteriosiene) en groot hoeveelhede vitamiene B12. Die Ekstra Sellulêre Pollisakkaried (ESP) produserende eienskap van hierdie groep bakterieë maak hulle ook van belang in die voedsel en afvoerwater beheer industrieë, aangesien gevind is dat ESP 'n rol speel in die aanvanklike granule formasie in anaerobiese bioreaktor sisteme. Daar is nog baie min bekend oor die ESP produksie van propionibakterieë en in hierdie studie is verskeie omgewings faktore wat die ESP produksie beïnvloed, bestudeer. Negentien verskillende Propionibakterium stamme was bestudeer in terme van ESP produksie en Propionibakterium stam 278 was geïdentifiseer as die stam wat die meeste ESP produseer. Verdere studies was op hierdie stam gedoen na aanleiding van sy hoë ESP produksie en omdat dit oorspronklik uit 'n anaerobiese verteerder geisoleer is. Die invloed van termperatuur, pH en sukrose konsentrasie was bepaal deur die meting van die ESP produksie en die medium viskositeit. Dit was gevind dat meer ESP geproduseer was by temperature laer as die optimum vir groei, met die optimum temperatuur tussen 22° en 25°C. Dit is ook gevind dat laer aanvangs groei-medium pH (laer as pH 7.0), ESP produksie inhibeer. Die invloed van die aanvangs groei-medium pH tussen 7.0 en 8.5 was egter nie betekenisvol nie. Dit is ook gevind dat 'n hoër koolstof tot stikstof verhouding, verkry deur die byvoeging van 8% sukrose, die ESP produksie verhoog. Die "upflow anaerobic sludge blanket" (UASB) proses vind plaas as gevolg van die opwaarste beweging van opgeloste organiese materiaal deur 'n granule bed van aktiewe metanogeniese granulêre slyk. Die lang 'start-up' tye as gevolg van die stadige granulasie proses, en die nodigheid om 'n vinnige verplasing van granules te hê nadat dit uit die sisteem gewas is, is beperkings wat die algemene toepassing van hierdie fantastiese afvoerwater tegnologie, strem. Volle implementering van hierdie biomassa immobilisereings tegniek kan dus nie plaasvind voordat die granule formasie gedefinieer en geoptimiseer is nie. Die presiese eienskappe van die meganismes betrokke en die formasie van die granules en die rede vir hul stabiliteit word egter nog nie ten volle verstaan nie. Volgens 'n hipotese deur Britz et al. (1999), vind 'n verskuiwing in die populasie dinamika van die anaerobiese gemeenskap plaas tydens die implementasie van omgewings 'stress' toestande. Die resultaat is 'n verhoging in ESP produksie en 'n gevolglike verbetering in die granulasie proses. In die tweede studie was dit gevind dat, wanneer 'stress' toestande op die reeds gevormde granulasie toegepas word, die Gram-positiewe laktaat-benuttende asetogeniese populasie voordeel geniet en meer propioonsuur produserende bakterieë was teenwoordig. Die propioonsuur en asynsuur konsentrasies het ook verhoog en met 'n gevolglike daling in die groei-medium se pH. Dit bevestig 'n gedeelte van die hipotese dat, wanneer die granules onder 'stress' geplaas word, die asetogeniese populasie dinamika verander en die laktaat-benuttende populasie reageer tot die gedeeltelike afname in pH. Die meer suur-tolerante propioonsuur produserende bakterieë verkry 'n kompeterende voordeel en gevolglik is daar 'n verhoging in propioonsuur konsentrasie. Propionibakterieë was gevoeg by die onbehandelde slyk gedurende die granule produksie proses, en daar is gevind dat meer aktiewe granules gevorm word as andersins. Dit is moontlik as gevolg van die die ESP produksie van propionibakterieë wat die granulasie versnel het. Verbeterde granulasie was dus verkry in die sisteme waar propionibakterieë bygevoeg is. Vetsuur analises het gedui dat die gevormde vetsure ook in korrelasie was met die model van granulasie. Goeie korrelasie was dus verkry tussen die hipotese en die eksperimentele data en die hipotese is gedeeltelik bewys in hierdie studie.
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34

Tetila, Moacir Feba [UNESP]. "Uso de reator aeróbio de leito fluidizado com circulação como dispositivo de pós-tratamento do efluente de um reator uasb compartimentado tratando esgotos sanitários." Universidade Estadual Paulista (UNESP), 2015. http://hdl.handle.net/11449/134109.

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A pesquisa utilizou um Reator Aeróbio de Leito Fluidizado com Circulação (RALFC) como dispositivo de pós-tratamento do efluente de um Reator UASB Compartimentado (RUC) o qual tratou esgoto sanitário. O RUC foi constituído de 4 tubos de PVC, de diferentes diâmetros, dispostos de forma concêntrica e o RALFC por dois tubos de PVC, de diâmetros diferentes e concêntricos, e uma unidade de sedimentação na parte superior. A pesquisa foi dividida em partida e quatro fases distintas, denominadas fase 1A, 1B, 2A e 2B, nas quais foram variados os parâmetros de operação, como vazão de ar, vazão de efluentes, tempo de detenção hidráulica (TDH) e carga orgânica volumétrica (COV). De modo que durante a pesquisa foi constatado que a melhor fase de tratamento foi quando o RALFC operou com TDH de 4,7 horas e vazão de ar de 300 L/h. O sistema, nessa fase, apresentou um valor médio de DQO efluente de 55 mg/L, a partir de um valor bruto de 607 mg/L em média, gerando uma remoção total de 90%. Os parâmetros de controle como alcalinidade, pH, temperatura e ácidos orgânicos voláteis sempre estivaram dentro das recomendações da literatura, demonstrando uma baixa oscilação. Mesmo assim o sistema não apresentou bom desempenho na remoção de nutrientes, tendo em sua melhor fase de tratamento um efluente com 31 mg/L em média de nitrogênio total, a partir de um valor de entrada de 50 mg/L sendo que a maior parte desse nitrogênio foi removido durante a passagem pelo RUC. Por outro lado para o fósforo, os valores foram de 25 mg/L na entrada e no efluente 14 mg/L, do mesmo modo como ocorreu ao nitrogênio, a maior parte da remoção de fósforo foi realizada pelo RUC
The study used an aerobic fluidized bed reactor with circulation (RALFC) as the effluent post-treatment device of a UASB reactor Compartmented (RUC) which treated wastewater. The RUC was consisted of 4 PVC tubes of different diameters arranged concentrically and RALFC two PVC tubes of different diameters and concentric, and a sedimentation unit in the upper part. The research was divided into four distinct phases and starting, called Phase 1A, 1B, 2A and 2B, in which were various operating parameters such as air flow, flow of wastewater, hydraulic retention time (HRT) and volumetric organic load (VOC). So that during the research it was found that the best treatment phase was when the RALFC operated with HRT of 4.7 hours and air flow of 300 L / h. The system, at this stage, had an average effluent COD value of 55 mg/L, from the affluent valor of 607 mg/L on average, there by generating a complete removal of 90%. The control parameters as alkalinity, pH, temperature and volatile organic acids have always been within the recommended by the literature, demonstrating a low oscillation. Even so, the system hasn't showed good performance in the removal of nutrients, in their best treatment stage an effluent with 31 mg/L on average total nitrogen from an input value of 50 mg/L. The most part of nitrogen removal was during passage through the RUC. As for the phosphorus values were 25 mg/L in the effluent input and 14 mg/L, in the same as was the nitrogen, the majority of phosphorus removal was performed by RUC
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35

Tetila, Moacir Feba. "Uso de reator aeróbio de leito fluidizado com circulação como dispositivo de pós-tratamento do efluente de um reator uasb compartimentado tratando esgotos sanitários /." Ilha Solteira, 2015. http://hdl.handle.net/11449/134109.

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Orientador: Tsunao Matsumoto
Co-orientador: Lilizane Lazzarini Albertin
Banca: Dib Gebara
Banca: Miguel Mansur Aisse
Resumo: A pesquisa utilizou um Reator Aeróbio de Leito Fluidizado com Circulação (RALFC) como dispositivo de pós-tratamento do efluente de um Reator UASB Compartimentado (RUC) o qual tratou esgoto sanitário. O RUC foi constituído de 4 tubos de PVC, de diferentes diâmetros, dispostos de forma concêntrica e o RALFC por dois tubos de PVC, de diâmetros diferentes e concêntricos, e uma unidade de sedimentação na parte superior. A pesquisa foi dividida em partida e quatro fases distintas, denominadas fase 1A, 1B, 2A e 2B, nas quais foram variados os parâmetros de operação, como vazão de ar, vazão de efluentes, tempo de detenção hidráulica (TDH) e carga orgânica volumétrica (COV). De modo que durante a pesquisa foi constatado que a melhor fase de tratamento foi quando o RALFC operou com TDH de 4,7 horas e vazão de ar de 300 L/h. O sistema, nessa fase, apresentou um valor médio de DQO efluente de 55 mg/L, a partir de um valor bruto de 607 mg/L em média, gerando uma remoção total de 90%. Os parâmetros de controle como alcalinidade, pH, temperatura e ácidos orgânicos voláteis sempre estivaram dentro das recomendações da literatura, demonstrando uma baixa oscilação. Mesmo assim o sistema não apresentou bom desempenho na remoção de nutrientes, tendo em sua melhor fase de tratamento um efluente com 31 mg/L em média de nitrogênio total, a partir de um valor de entrada de 50 mg/L sendo que a maior parte desse nitrogênio foi removido durante a passagem pelo RUC. Por outro lado para o fósforo, os valores foram de 25 mg/L na entrada e no efluente 14 mg/L, do mesmo modo como ocorreu ao nitrogênio, a maior parte da remoção de fósforo foi realizada pelo RUC
Abstract: The study used an aerobic fluidized bed reactor with circulation (RALFC) as the effluent post-treatment device of a UASB reactor Compartmented (RUC) which treated wastewater. The RUC was consisted of 4 PVC tubes of different diameters arranged concentrically and RALFC two PVC tubes of different diameters and concentric, and a sedimentation unit in the upper part. The research was divided into four distinct phases and starting, called Phase 1A, 1B, 2A and 2B, in which were various operating parameters such as air flow, flow of wastewater, hydraulic retention time (HRT) and volumetric organic load (VOC). So that during the research it was found that the best treatment phase was when the RALFC operated with HRT of 4.7 hours and air flow of 300 L / h. The system, at this stage, had an average effluent COD value of 55 mg/L, from the affluent valor of 607 mg/L on average, there by generating a complete removal of 90%. The control parameters as alkalinity, pH, temperature and volatile organic acids have always been within the recommended by the literature, demonstrating a low oscillation. Even so, the system hasn't showed good performance in the removal of nutrients, in their best treatment stage an effluent with 31 mg/L on average total nitrogen from an input value of 50 mg/L. The most part of nitrogen removal was during passage through the RUC. As for the phosphorus values were 25 mg/L in the effluent input and 14 mg/L, in the same as was the nitrogen, the majority of phosphorus removal was performed by RUC
Mestre
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36

Robertson, Louise. "Optimising coagulation and ozone pre-treatments and comparing the efficacy of differently pre-treated grain distillery wastewaters in an upflow anaerobic sludge blanket (UASB) reactor." Thesis, Stellenbosch : Stellenbosch University, 2014. http://hdl.handle.net/10019.1/86286.

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Thesis (MScFoodSc)--Stellenbosch University, 2014.
ENGLISH ABSTRACT: Large volumes of high strength wastewater are generated annually by distilleries. Treatment of this wastewater is essential to increase its reuse potential. Anaerobic digestion (AD) has been widely applied as high strength wastewater treatment. Additionally, grain distillery wastewater (GDWW) is high in fats, oils and grease (FOG) which can cause problems during AD. Pre-treatment is therefore often required to make the AD process more efficient. The overall objective of this study was to investigate the operational efficiency of upflow anaerobic sludge blanket (UASB) reactors while treating GDWW as substrate. The first aim was to investigate the pre-treatment of the GDWW specifically for the removal of FOG by evaluating the effect of pH adaption, coagulant concentration and ozone (O3) dosages on the FOG reduction efficiency. Secondly, the effect of two different pre-treatments (only coagulant and coagulant and ozone) on the subsequent UASB treatment step was investigated. The pH of raw GDWW (pH 3.4) was adapted to three different pH values (5.0, 6.0, and 7.0) and the coagulant, aluminium chlorohydrate (ACH) (140 mg.L-1), was added. To make the process more economically viable, the lowering the coagulant concentration (to 100 mgACH.L-1) was also investigated. Optimal reductions for chemical oxygen demand (COD) (33.2% ± 4.93), total suspended solids (TSS) (91.9% ± 1.73) and FOG (84.1% ± 1.98) were, however, achieved at a higher coagulant concentration of 140 mgACH.L-1, and at a wastewater pH of 7.0. The effect of additional ozone treatment was also investigated. Maximum reductions for the ozone treatment were obtained at 100 mgO3.L-1 for COD (3.6% ± 4.08), and at 900 mgO3.L-1 for TSS (27.7% ± 5.58) and FOG (23.9% ± 1.83). The ozone treatment was most efficient for FOG reduction (in terms of mg FOG reduced per mg ozone) at 100 mgO3.L-1. An ozone dosage of 300 mgO3.L-1, was decided on based on economic feasibility, findings in literature on toxicity of ozone and the potential degradation of recalcitrant compounds at this dosage. The final pre-treatment thus included pH adaption to 7.0, coagulant dosage of 140 mgACH.L-1, and an ozone dosage of 300 mgO3.L-1. The second part of this study involved the operation of two 2 L laboratory scale UASB reactors for 277 days. The substrate of the first reactor contained GDWW that had only undergone coagulant pre-treatment (Rcontrol), while the substrate of the second UASB reactor consisted of GDWW that had undergone coagulant and ozone pre-treatment (Rozone). Both reactors treated the pre-treated GDWW successfully at ca. 9 kgCOD.m-3d-1. COD reductions of 96% for Rcontrol and 93% for Rozone, were achieved. FOG reductions (%) showed variations throughout the study and maximum reductions of 88% and 92% were achieved for Rcontrol and Rozone, respectively. The Rozone produced more biogas, but the methane content was similar for both reactors. The additional ozone pre-treatment did not show any added benefits to the reactor performance results. UASB granule washout in Rcontrol did, however, suggest possible toxicity of unsaturated fatty acids present in the non-ozonated substrate. The feasibility of FOG removal was shown as both reactors successfully treated pre-treated GDWW. Ozonation, after a coagulant dosage, which resulted in further reduction in the FOG content of the GDWW, is thus not essential to ensure the success of an anaerobic digestion step. Ozonation of the pre-treated GDWW could, however, be beneficial to gas production and the efficiency of a tertiary biological process.
AFRIKAANSE OPSOMMING: Groot volumes hoë-sterkte afloopwater word jaarliks deur distilleerderye opgelewer. Die behandeling van hierdie afloopwater is noodsaaklik om die hergebruiksmoontlikheid daarvan te verhoog. Die toepassing van anaërobiese vertering (AV) is wydverspreid in hoë-sterkte afloopwaterbehandeling. Graandistillerings-afloopwater (GDAW) is boonop hoog in vette, olies en ghries (VOG), wat probleme kan veroorsaak tydens AV. Voorbehandeling word dus dikwels verlang om die AV meer doeltreffend te maak. Die oorhoofse doelstelling van hierdie studie was om die doeltreffendheid van opvloei-anaërobieseslykkombers- (OAS-) reaktore wat GDAW as substraat behandel, te ondersoek. Die eerste mikpunt was om die voorbehandeling van die GDAW, te ondersoek vir die verwydering van VOG. Dit is uitgevoer deur die uitwerking van pH aanpassing, koagulantkonsentrasie en osoon(O3)dosis op VOG vermindering te evalueer. Tweedens is die uitwerking van twee verskillende voorbehandelings (slegs koagulant asook koagulant en osoonbehandeling) op die opvolgende OAS-behandelingsstap ondersoek. Die pH van rou GDAW (pH 3.4) is aangepas tot drie verskillende pH waardes (5.0, 6.0 en 7.0) en die koagulant, aluminium-chlorohidraat (ACH), is bygevoeg (140 mg.L-1). Om die proses meer ekonomies uitvoerbaar te maak is ‘n verlaagde koagulantkonsentrasie (verlaag tot 100 mgACH.L-1) ook ondersoek. Die optimale afnames vir chemiese suurstofvereiste (CSV) (33.2% ± 4.93), totale oplosbare vastestowwe (TOV) (91.9% ± 1.73) en VOG (84.1% ± 1.98) is egter bereik teen ‘n hoër koagulant konsentrasie van 140 mgACH.L-1, en teen ‘n afloopwater-pH van 7.0. Die uitwerking van ‘n bykomende osoonbehandeling is ook ondersoek. Die hoogste afnames tydens die osoonbehandeling is bereik teen 100 mgO3.L-1 vir CSV (3.6% ± 4.08), en teen 900 mgO3.L-1 vir TOV (27.7% ± 5.58) en VOG (23.9% ± 1.83). Die osoonbehandeling was mees doeltreffend vir VOG (in terme van mg VOG verwyder per mg osoon) teen 100 mgO3.L-1. Daar is besluit op ‘n van 300 mgO3.L-1, as gevolg van die ekonomiese uitvoerbaarheid, bevindinge in literatuur vir die toksisiteit van osoon, en die moontlike afbraak van moeilik-afbreekbare komponente teen hierdie dosis. Die finale voorbehandeling het dus bestaan uit ‘n aanpassing van die afloopwater-pH na 7.0, ‘n koagulantdosis van 140 mgACH.L-1, en ‘n osoondosis van 300 mgO3.L-1. Tydens die tweede gedeelte van hierdie studie is twee 2 L laboratoriumskaal OAS reaktore bedryf vir 277 dae. Die substraat van die eerste reaktor het GDAW bevat wat slegs ‘n koagulant-voorbehandeling ondergaan het (Rkontrole), terwyl die substraat van die tweede OAS-reaktor GDAW bevat het wat koagulant- en osoon-voorbehandeling ondergaan het (Rosoon). Beide reaktore het die voorbehandelde-GDAW suksesvol behandel teen ‘n organieseladingstempo van ca. 9 kgCSV.m-3d-1. Afnames in CSV van 96% vir Rkontrole en 93% vir Rosoon, is bereik. Tydens die studie is deurlopende wisseling in VOG verwydering (%) waargeneem, en die hoogste verwyderings wat bereik is, is onderskeidelik 88% en 92% vir Rkontrole en Rosoon. Die Rosoon het meer biogas geproduseer, maar die metaanpersentasie was soortgelyk vir beide reaktore. Die osoon-voorbehandeling het nie enige toegevoegde voordele getoon in die reaktorprestasie resultate nie. Die uitwas van die OAS-granules vir die Rkontrole het egter moontlike toksisiteit van onversadigdevetsure aangedui, wat moontlik teenwoordig kon wees in die nie-geösoneerde substraat. Die uitvoerbaarheid van VOG verwydering is getoon aangesien beide reaktore voorbehandelde GDAW suksesvol behandel het. Osonering, wat verdere afname in die VOG inhoud van GDAW teweeggebring het (na ‘n koagulant dosis), is dus nie noodsaaklik vir die suksesvolle verloop van ‘n anaërobiese-verteringsstap nie. Osonering van die voorbehandelde GDAW kan egter voordelig wees vir gasvorming, en kan ook verder die doeltreffendheid van ‘n tersiêre biologiese behandeling verhoog.
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37

Pukasiewicz, Sílvia Regina Machado. "Tratamento do efluente do processamento de subprodutos da indústria de produtos cárneos em filtro anaeróbio." UNIVERSIDADE ESTADUAL DE PONTA GROSSA, 2010. http://tede2.uepg.br/jspui/handle/prefix/687.

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Fundação Araucária de Apoio ao Desenvolvimento Científico e Tecnológico do Paraná
The process of anaerobic digestion is presented as an alternative for treatment of effluents from various industrial activities. In this case there is the conversion of organic matter to more stable compounds such as methane, which can be used to replace fossil fuels. This study evaluated the treatment of effluent generated by a processing company for animal feed flavors, which uses as raw material waste generated in the slaughter and processing of pigs, chickens and turkeys. It was used a biological upflow anaerobic filter, constructed of polyvinyl chloride with a volume of 980 mL and support material for biomass consisting of rings of polypropylene, with the goal of removing organic matter and produce biogas. The influent had average values with the following characteristics: 899.79 mg L-1 of COD, pH of 8.12, 377.31 mg L-1 of total nitrogen, 206.09 mg L-1 of ammoniacal nitrogen, 2.90 mg L-1 of oils and greases, 768.67 mg CaCO3 L-1 of alkalinity, 521.26 mg L-1 CH3COOH of volatile acidity and 15.11 mg L-1 content of phosphorous. The system was operated continuously at room temperature, organic loading of 0.077, 0.102, 0.154, 0.356, 0.536, 0.854, 1.083 kg DQO m-3 d-1, and HRT 240, 168, 120, 72, 48, 24 and 21 hours. The effluent had COD values between 14.43 and 849.43 mg L-1, pH between 6.32 and 8.34, total nitrogen between 95.23 and 742.14 mg L-1, ammoniacal nitrogen between 127,78 and 230.29 mg L-1, alkalinity between 268.83 and 2401.5 mg CaCO3 L-1 and volatile acidity between 27.66 and 415.30 mg L-1 CH3COOH and phosphorus content between 0 and 29, 26 mg L-1. The best results of COD removal were obtained with HRT of 24 hours, averaging 83% removal and, consequently, larger generation of biogas, 48.39 kg of methane per day. Concludes that, within the conditions employed, the anaerobic digestion process was efficient in removing COD. If the company uses the methane produced in power generation, can enter in the market of carbon credits and get an extra income.
O processo de digestão anaeróbia apresenta-se como uma alternativa para tratamento de efluentes de várias atividades industriais. Nesse processo há conversão da matéria orgânica a compostos mais estáveis como o gás metano, que pode ser utilizado em substituição aos combustíveis fósseis. Neste trabalho foi avaliado o tratamento anaeróbio dos efluentes gerados por uma empresa processadora de palatabilizantes para ração animal, que utiliza como matéria prima os subprodutos gerados no abate e processamento de suínos, frangos e perus. Foi utilizado um filtro biológico anaeróbio de fluxo ascendente, construído de policloreto de vinila com volume útil de 980 mL e material suporte para a biomassa constituído por anéis de polipropileno, com o objetivo de remover a matéria orgânica e produzir biogás. O substrato possuía valores médios com as seguintes características: DQO de 899,79 mg L-1, pH de 8,12, nitrogênio total de 377,31 mg L-1, nitrogênio amoniacal de 206,09 mg L-1, teor de óleos e graxas de 2,90 mg L-1, alcalinidade de 768,67 mg CaCO3 L-1, acidez volátil de 521,26 mg CH3COOH L-1 e teor de fósforo de 15,11 mg L-1. O filtro foi operado por 196 dias, à temperatura ambiente, com cargas orgânicas de 0,077; 0,102; 0,154; 0,356; 0,536; 0,854; 1,083 kg DQO m-3 d-1, e TRH de 240, 168, 120, 72, 48, 24 e 21 horas. O efluente tratado apresentou valores de DQO entre 14,43 e 849,43 mg L-1, pH entre 6,32 e 8,34, nitrogênio total entre 95,23 e 742,14 mg L-1, nitrogênio amoniacal igual entre 127,78 e 230,29 mg L-1, alcalinidade entre 268,83 e 2401,5 mg CaCO3 L-1 e acidez volátil entre 27,66 e 415,30 mg CH3COOH L- 1 e teor de fósforo entre 0 e 29,26 mg L-1. Os melhores resultados de remoção de DQO foram obtidos com TDH de 24 horas, com média de 83% de remoção e, conseqüentemente, maior geração de biogás, 48,39 kg de metano por dia. Concluise que, dentro das condições empregadas, o processo de digestão anaeróbia foi eficiente na remoção de DQO. Se a empresa utilizar o metano produzido na geração de energia, poderá entrar no mercado de créditos de carbono e obter uma renda extra.
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38

Trerise, Margot Alana. "Evaluation of primary and secondary treatment of distillery wastewaters." Thesis, Link to the online version, 2005. http://hdl.handle.net/10019/1246.

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39

D', Bastiani Camila. "Aplicação de modelagem multifásica para estudo de biorreatores anaeróbios." reponame:Repositório Institucional da UCS, 2017. https://repositorio.ucs.br/handle/11338/2782.

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Buscando compreender o comportamento hidrodinâmico de um reator anaeróbio de fluxo ascendente (UASB), o presente trabalho teve por objetivo desenvolver um modelo numérico utilizando ferramentas de Fluidodinâmica Computacional (CFD) para a simulação do comportamento do escoamento trifásico (líquido, gás e sólido) em um reator UASB utilizado na produção de biogás a partir da vinhaça, e validar este modelo utilizando técnicas de Velocimetria de Partículas por Imagem (PIV). Para tanto, inicialmente foi projetado o reator UASB e em seguida foram desenvolvidas a geometria e a malha. As simulações foram executadas no software Fluent, utilizando uma malha com 528.000 volumes de controle. Foram inicialmente realizadas simulações do escoamento monofásico do líquido e em seguida simulações bifásicas gás/líquido e sólido/líquido foram realizadas adotando-se uma abordagem Euleriana-Euleriana, isotérmica, transiente e tridimensional. Por fim, os modelos bifásicos já validados foram associados em um modelo trifásicos. Técnicas de PIV foram utilizadas na validação dos modelos bifásicos e do trifásico. Na etapa de validação dos modelos numéricos, foi verificada uma diferença máxima entre resultados experimentais e computacionais menor de 4% para todos os casos. Foi verificado que a força de arraste é a que exerce a maior influência no perfil do escoamento gás/líquido. Com relação ao escoamento sólido/líquido, o modelo de Gidaspow foi escolhido para o cálculo do coeficiente de arraste, após comparação com resultados experimentais. Nas simulações trifásicas, verificou-se o gás foi o principal responsável pela qualidade da mistura dentro do reator, reduzindo de 44% o percentual de zonas mortas no reator no caso sólido/líquido para 0,02% no caso trifásico e aumentando em cerca de oito vezes a magnitude da velocidade das fases sólida e líquida. O sistema de distribuição de gás exerceu forte influência no perfil do escoamento, tendo induzido recirculação interna no reator. A compreensão do escoamento permitirá otimizações no processo e no reator de forma a buscar o aumento da eficiência de tratamento bem como da geração de biogás.
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PETROBRAS, Brasil.
Aiming to understand the hydrodynamics of a Upflow Anaerobic Sludge Blanket (UASB) reactor, this work aimed to apply multiphase modeling through computational fluid dynamics (CFD) to assess the behavior of the three phase flow (liquid, gas and solid) in a UASB reactor, which is used in the biogas production using vinasse as substrate and the to validate the results using Particle Image Velocimetry (PIV) techniques. Therefore, the UASB reactor was designed and then the geometry and mesh were developed. The simulations were performed using the software Fluent and a mesh with 528.000 control volumes. Initially, monophasic simulations of the liquid phase were carried out. Next, two phase simulations were performed considering the pairs of phases gas/liquid and solid/liquid. An Eulerian-Eulerian approach was adopted, together with isothermal, transient and tridimensional conditions. After validated, the two-phase models (solid/liquid and gas/liquid) were combined into a three-phase model. PIV was used for the experimental validation of the two and three-phase models. The numerical model validation showed maximum differences lower than 4% between experimental and computational results for the three cases (gas/liquid, solid/liquid and liquid/gas/solid). Numerical results showed that the drag force plays the major role on the gas/liquid flow profile. Regarding the solid/liquid flow, Gidaspow model was chosen to estimate the drag force coefficient after comparisons between numerical and experimental results. Three-phase simulations showed that the gas was the main responsible for the mixing quality within the reactor. Dead zones were reduced from 44% in the solid/liquid simulations to 0,02% in the three-phase simulations and the liquid and solid velocity magnitude increased in about eight times. The configuration of the gas distribution system played a major role on the overall flow profile and drove liquid recirculation along the axial position. Understanding the multiphase flow within this reactor will allow optimizations on the process as well as on the reactor, in order to seek an increase on the efficiency both in the treatment and biogas in the production.
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40

Freitas, Kleber Alves de. "Co-digestão anaeróbia de águas residuárias da bovinocultura de leite e do despolpamento de frutos do cafeeiro em reatores uasb em dois estágios /." Jaboticabal, 2019. http://hdl.handle.net/11449/190796.

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Orientador: Roberto Alves Oliveira
Resumo: A co-digestão de água residuária da bovinocultura leiteira (ARBL) e água residuária do beneficiamento do café (ARC) em reatores anaeróbios de fluxo ascendente com manta de lodos (UASB, R1 e R2), em série, é inédita e importante para o desenvolvimento dos setores envolvidos. Foram utilizadas proporções de 100:0; 85:15, 70:30 e 50:50 de ARBL:ARC no afluente dos reatores UASB e aplicados tempo de detenção hidráulica (TDH) de 2 (R1) e 4 (R2) dias. Isto proporcionou cargas orgânicas volumétricas (COV) de 11,9 (valor médio obtido nos testes 1 e 2, sem adição de ARC); 12,9 (teste 3); 14,0 (teste 4) e 21,3 (teste 5) g DQOtotal (L d)-1 no R1. As maiores produções volumétricas de metano, de até 0,89 L CH4 (L reator d)-1 foram obtidas com COV de 14,0 g DQO (L d)-1. As concentrações médias de fenóis totais no afluente variaram entre 6 e 132 mg L-1 e as eficiências médias de remoção nos reatores UASB, em dois estágios, foram de 35 a 52% com concentração de 50 mg L-1 para efluente do R2 após adição de ARC que contém elevadas concentrações de fenóis totais e apresentam toxicidade ao tratamento anaeróbio podendo afetar a estabilidade do processo. O sistema foi eficiente para remoção de ovos de helmintos. Os Domínios Bacteria e Archaea, as Ordens Methanobacteriales, Methanomicrobiales e Methanosarcinales e as Famílias Methanosaetaceae e Methanosarcinaceae se apresentaram de forma sincrônica e equilibrada na co-digestão anaeróbia dos resíduos estudados.
Abstract: The co-digestion of dairy manure wastewater (DMW) and coffee processing wastewater (CPW) in up flow anaerobic sludge blanket (UASB, R1 and R2) in series is unprecedented and important for the development of the sectors involved. Proportions of 100: 0; 85:15, 70:30 and 50:50 DMW:CPW were used in the UASB reactors influent and applied hydraulic retention time (HRT) of 2 (R1) and 4 (R2) days. This provided organic loading rate (OLR) of 11.9 (mean value obtained in tests 1 and 2, without addition of CPW); 12.9 (test 3); 14.0 (test 4) and 21.3 (test 5) g CODtotal (L d) -1 on R1. The highest volumetric methane yields of up to 0.89 L CH4 (L reactor d) -1 were obtained with OLR of 14.0 g COD (L d) -1. The mean concentrations of total phenols in the affluent ranged from 6-132 mg L-1 and the mean removal efficiencies in two-stage UASB reactors were 35-52% with 50 mg L-1 concentration for R2 effluent after addition of ARC containing high concentrations of total phenols and toxicity to anaerobic treatment may affect process stability. The system was efficient for removal of helminth eggs. The Bacteria and Archaea Domains, the Methanobacteriales, Methanomicrobiales and Methanosarcinales Orders, and the Methanosaetaceae and Methanosarcinaceae families were presented in a synchronic and balanced manner in the anaerobic co-digestion of the residues studied.
Mestre
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41

Callado, Nélia Henriques. "Estudo da toxicidade do sulfato em reator anaeróbio de manta de lodo (UASB)." Universidade de São Paulo, 1992. http://www.teses.usp.br/teses/disponiveis/18/18138/tde-18122015-140702/.

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Este trabalho apresenta e discute os resultados obtidos na operação de um reator anaeróbico com manta de lodo (UASB) de 10,5 L, alimentado continuamente com substrato sintético (DQO = 2000 mg/L) e submetido ao aumento progressivo da concentração de sulfato (de 25 a 10000 mg \'SO IND.4\'POT.2-\'/L). A vazão de 16 L/dia, corresponde ao tempo de detenção hidráulico (e) de 15,6 h foi mantida constante durante os 10 meses do experimento. O monitoramento da operação do reator incluiu a determinação dos principais parâmetros do processo, visando detectar a inibição da metanogênese pelas bactérias redutoras de sulfato (BRS) que competem, com as metanogênicas, pelos mesmos substratos. Constatou-se estimulação do processo até a concentração de 400 mg \'SO IND.4\'POT.2-\'/L, a partir da qual ocorreram sequencias de quedas de eficiência seguidas de recuperação do reator, mantendo sempre a eficiência média de remoção de DQO acima de 80%. Embora a atividade metanogênica tenha sido parcialmente afetada, os balanços de \'SO IND.4\'POT.2-\' mostraram que a redução do sulfato não foi o principal responsável pela inibição ocorrida.
This thesis presents and discuss the results obtained during the operation of a 10.5 L upflow sludge blanket reactor, continuously fed with synthetic substrate (COD = 2,000 mg/L), which was subjected to step-increase of sulfate concentrations ranging from 25 to 10,000 mg \'SO IND.4\'POT.2-\'/L. The flow-rate of 16 L/d corresponding to a hydraulic detention of 15.6 h, was kept constant throughout the 10 months of experimentation. Operation monitoring included the determination of the main process parameters, aiming to detected the inhibition of lhe methanogenesis by the sulfate reducing bacteria (SRB) which autocompete the methanogens in the presence of common substrates. Stimulation effects were obseved up to the sulfate concentration of the 400 mg.\'SO IND.4\'POT.2-\'/L. Further on, sequences of falls of efficiency followed by restoration of the reactor performance defined the behavior pattern of the reactor, which maintained an average COD removal efficiency higher than 80%. Although the methanogenic activity has been parcially affected, \'SO IND.4\'POT2-\' balances showed that the sulfate reduction activity was not the main process responsible for such inhibition.
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42

Lima, Daniel Moureira Fontes. "Influência da razão de recirculação na produção de hidrogênio em reator anaeróbio de leito fixo." Universidade de São Paulo, 2011. http://www.teses.usp.br/teses/disponiveis/18/18138/tde-11052011-091202/.

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A presente pesquisa avaliou diferentes razões de recirculação do meio líquido com a finalidade de identificar a melhor condição de mistura para uma produção elevada e contínua de hidrogênio em um reator anaeróbio de leito fixo com fluxo ascendente alimentado com um meio contendo sacarose como fonte de carbono e uréia como fonte de nitrogênio. Foi utilizado polietileno de baixa densidade como meio suporte para imobilização da biomassa. O experimento foi iniciado com ensaios hidrodinâmicos (pulso, utilizando dextran blue como traçador) que determinaram as seguintes razões de recirculação em relação à vazão de alimentação utilizadas: R = 0,25, 0,5, 1,0 e 2,0. O experimento foi realizado em duas etapas, nas quais foram operados dois reatores idênticos simultaneamente, testando-se duas razões de recirculação diferentes. A DQO da água residuária foi de 2000 mg/L. O tempo de detenção hidráulica teórico foi de 2 horas e a temperatura foi mantida em 25 graus Celsius. A remoção de sacarose apresentou valores médios de 67%, 79%, 71% e 70% para R = 0,25, 0,5, 1,0 e 2,0, respectivamente. Os valores médios de rendimento de hidrogênio foram 1,14 mol \'H IND.2\'/mol sac, 1,43 mol \'H IND.2\'/mol sac, 1,34 mol \'H IND.2\'/mol sac e 0,86 mol \'H IND.2\'/.mol sac e de produção volumétrica de hidrogênio foram 74,34 mL \'H IND.2\'/(h.L), 124,78 mL \'H IND.2\'/(h.L), 96,57 mL \'H IND.2\'/(h.L) e 73,49 mL \'H IND.2\'/(h.L) para as vazões de recirculação de 0,25, 0,5, 1,0 e 2,0, respectivamente. O biogás produzido foi composto de \'H IND.2\', e \'CO IND.2\', com valores percentuais médios para \'H IND.2\', de 50%, 56%, 56% e 46% para R = 0,25, 0,5, 1,0 e 2,0, respectivamente. Não houve presença de metano em nenhuma fase de operação. Os principais produtos intermediários produzidos durante a produção de \'H IND.2\', foram ácido acético, ácido butírico e etanol, de forma similar para todas as fases de recirculação. Analisando todos os parâmetros de operação, foi possível notar que a melhor vazão de recirculação obtida foi de R = 0,5. Ajustando os dados obtidos a uma função polinomial, porém, chegou-se a um ponto de ótimo em R = 0,6. Durante os experimentos observou-se uma queda na produção do biogás, provavelmente por atuação de microrganismos consumidores deste.
The present research evaluated different recirculation rates of the liquid medium for the purpose of identify the best mixture condition for a high and continuous hydrogen production in an anaerobic upflow fixed-bed reactor fed with a medium containing sucrose as carbon source and urea as nitrogen source. Low density polyethylene was used as medium for biomass immobilization. The experiment began with hydrodynamic tests (pulse, using dextran blue as tracer) which led to the following recirculation rates related with the feed flow rate used in this work: R = 0,25, 0,5, 1,0 and 2,0. The experiment was conducted in two stages, where two identical reactors were operated simultaneously, by testing two different recirculation rates. COD from wastewater was 2000 mg/L. The theoretical hydraulic retention time was 2 hours and the temperature was maintained at 25 Celsius degrees. The average values of sucrose consumption were 67%, 79%, 71% and 70% for R = 0,25, 0,5, 1,0 and 2,0, respectively. The average values of hydrogen yield were 1,14 mol \'H IND.2\'/mol sac, 1,43 mol \'H IND.2\'/mol sac, 1,34 mol \'H IND.2\'/mol sac and 0,86 mol \'H IND.2\'/mol sac and of hydrogen production rate were 74.34 mL \'H IND.2\'/(h.L), 124.78 mL \'H IND.2\'/(h.L), 96.57 mL \'H IND.2\'/(h.L) and 73.49 mL \'H IND.2\'/(h.L) for recirculation rates of 0.25, 0.5, 1.0 and 2.0, respectively. The biogas produced was composed by \'H IND.2\', and \'CO IND.2\', with average values for \'H IND.2\', of 50%, 56%, 56% and 46% for R = 0,25, 0,5, 1,0 and 2,0, respectively. Methane was not detected. The main intermediate products produced during the hydrogen production were acetic acid, butyric acid and ethanol, similar in all stages of recirculation. Analyzing all operating parameters, it was identified that the better recirculation rate obtained during the experiments was R = 0.5. Adjusting all data obtained with a polynomial function, it was found an optimal recirculation rate of R = 0.6. During the experiments there was a drop in biogas production, probably by the activity of microrganisms consumers of this biogas.
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43

Vidal, Carlos Magno de Sousa. "Avaliação da microfiltração tangencial como alternativa de tratamento avançado de efluente gerado em sistema de tratamento de esgoto sanitário constituído de reator UASB (Upflow Anaerobic Sludge Blanket) seguido de tanque de aeração." Universidade de São Paulo, 2006. http://www.teses.usp.br/teses/disponiveis/18/18138/tde-06112006-233334/.

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A proposta desta pesquisa consistiu na avaliação da microfiltração tangencial para o tratamento avançado de efluente gerado em sistema de tratamento de esgoto sanitário constituído de reator UASB (Upflow Anaerobic Sludge Blanket) seguido de tanque de aeração. Neste trabalho foram avaliados métodos de limpeza física (retrolavagem com ar comprimido) e química (ácida e básica) das membranas, bem como análise comparativa da colmatação e do desempenho de membranas de tamanhos de poro de 0,2 e 1,0 'mü'm, quando aplicadas ao pós-tratamento de efluentes do tanque de aeração em diferentes concentrações de SST. Foram contemplados ainda estudos de desinfecção de efluentes da microfiltração por radiação UV e aplicação do processo de coagulação antecedendo a microfiltração tangencial. Os experimentos foram realizados em unidade piloto com membranas tubulares de polipropileno com área efetiva de filtração de 0,036 'M POT.2'. Constatou-se que a limpeza física foi essencial para obtenção de maiores valores de fluxo de permeado na unidade de microfiltração. A limpeza química das membranas por solução básica foi mais eficiente quando comparada a limpeza ácida. Foram obtidos melhores resultados com a membrana de 0,2 'mü'm, quando comparada a membrana de 1 'mü'm, a qual apresentou intensa colmatação interna de seus poros. Para membrana de 0,2 'mü'm obteve-se permeado de excelente qualidade microbiológica (E.Coli < 1 UFC/100 mL e Colifagos < 16 UFP/100 mL), bem como valores de turbidez inferiores a 1,46 uT e remoção praticamente completa de SST. A prévia coagulação das amostras de licor misto do tanque de aeração contribuiu para obtenção de maiores taxas e melhor remoção de P-'PO IND.4'POT.3-' e DQOt na unidade de microfiltração. Para dosagem de 40 mg/L de cloreto férrico obteve-se a maior taxa média (139,7 L/'M POT.2'.h), concentrações residuais de P-'PO IND.4'POT.3-' inferiores a 1,4 mgP/L e DQOt menor que 33 mg/L. A radiação UV permitiu inativação completa de E.Coli e Colifagos das amostras de permeado. Concluiu-se que a microfiltração tangencial apresentou grande potencialidade para ser aplicada no tratamento avançado de efluente gerado em sistema de tratamento de esgoto sanitário constituído de reator UASB (Upflow Anerobic Sludge Blanket) seguido de tanque de aeração.
The proposal of this research was to evaluate the crossflow microfiltration as an alternative for an advanced treatment of effluent generated in a system of sewage treatment composed by a UASB (Upflow Anaerobic Sludge Blanket) reactor followed by an aeration tank. This work aimed to evaluate the membranes physical cleaning methods (backwashing with compressed air) and the chemical ones (acid and basic), as well as the comparative analysis between the fouling event and the 0,2 and 1,0 'mü'm pore size membranes performance, when applied to the aeration tank effluents in a post-treatment stage at TSS different concentrations. Studies for microfiltration effluents disinfection by UV radiation and the application of the coagulation process preceding the crossflow microfiltration were also developed. The experiments were performed in a pilot unit with polypropylene tubular membranes with 0.036 'M POT.2' of effective filtration area. It was verified that the physical cleaning was essential to the attainment of higher permeate flux values in the microfiltration unit. The chemical cleaning of the membranes through basic solution was more efficient when compared to their acid cleaning. Better results were attained when the 0,2 'mü'm membrane was employed in comparison with the 1 'mü'm membrane, which presented intense internal blocking of its pores. It was attained an excellent microbiological quality (E.Coli < 1 FCU/100 mL and Coliphages < 16 FPU/100 mL) for the 0,2 'mü'm membrane, as well as turbidity levels under 1,46 uT and almost total removal of TSS. The previous mixed liquor samples coagulation of the aeration tank contributed to the attainment of higher rates and better removal of P-'PO IND.4'POT.3-' and CODt in the microfiltration unit. It was attained, for the ferric chloride 40 mg/L dosage, the higher mean rate (139,7 L/'M POT.2'.h), P-'PO IND.4'POT.3-' remaining concentrations under 1,4 mgP/L and CODt lesser than 33 mg/L. The UV radiation allowed the complete inactivation of E.Coli and Coliphages from the permeate samples. It was concluded that the crossflow microfiltration presents great possibilities of application in the advanced treatment of effluent generated in a system of sewage treatment composed by a UASB (Upflow Anaerobic Sludge Blanket) reactor followed by an aeration tank.
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44

Hadley, Sakira N. "Assessment of a Modified Double Agar Layer Method to Detect Bacteriophage for Assessing the Potential of Wastewater Reuse in Rural Bolivia." Scholar Commons, 2013. http://scholarcommons.usf.edu/etd/4500.

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Water scarcity is a global concern that impacts many developing countries, forcing people to depend on unclean water sources for domestic, agricultural, and industrial needs. Wastewater is an alternative water source that contains nutrients needed for crop growth. Wastewater reuse for agriculture can cause public health problems because of human exposure to pathogens. Pathogen monitoring is essential to evaluate the compliance of wastewater with established World Health Organization (WHO) and U.S. Environmental Protection Agency (EPA) wastewater reuse guidelines. Indicator organisms are commonly used to detect pathogens in water and wastewater because they are quick and easy to measure, non-pathogenic, and have simple and inexpensive methods of detection. The objective of this research was to develop a modified double agar layer assay method that can be conducted in the field to quantify bacteriophage to assess the quality of wastewater for agricultural reuse. Results from the modified double agar layer assay were used to investigate the potential of somatic coliphage as an indicator organism for assessing the potential presence of enteric viruses in developing world treated wastewater, and to use the criteria of a good indicator organism to compare the potential of two commonly used indicator organisms, somatic coliphage and fecal coliforms, as an indicator of enteric viruses in wastewater. A modified EPA double agar layer method was developed and deployed in a developing world rural community to effectively quantify the concentration of somatic coliphage in a community managed wastewater treatment system composed of a Upflow Anaerobic Sludge Blanket (UASB) reactor followed by two maturation lagoons. The modified method served as a good indicator of enteric viruses in the water. Somatic coliphages were easily detected and quantified in the field setting using a modified double agar layer method. Somatic coliphage was found to be a potential indicator for enteric viruses rather than fecal coliforms because of their similarity in characteristics and resistances to wastewater treatment. The concentration of somatic coliphage was only reduced by 1.05 log units across the two series maturation lagoon system. Previous literature suggested removal would range from 2.1 to 4.6 log units. Influent wastewater (previously treated by an UASB reactor) had a concentration of 4.38 E+06 PFU/ 100 mL (standard deviation = ±3.7E+06, n = 9) and the treated effluent contained 3.90 E+05 PFU/100 mL (standard deviation = ± 4.5E+05, n = 8) of somatic coliphages. Results suggest that somatic coliphage is a good potential indicator for enteric viruses in wastewater but further research needs to be done.
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45

Cameron, Michelle. "Preservation techniques and carbon and nitrogen growth enhancement of batch cultivated UASB granules." Thesis, Stellenbosch : Stellenbosch University, 2000. http://hdl.handle.net/10019.1/51886.

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Thesis (MSc Food Sc )--Stellenbosch University, 2000.
ENGLISH ABSTRACT: The potential use of the upflow anaerobic sludge blanket (UASB) bioreactor is limited by the extended start-up periods due to the time-consuming granulation process and the fact that seeding inoculum is not freely available in most developing countries like South Africa. The mass cultivation of granules would provide the waste water treatment industry with suitable seeding inoculum and, therefore, an efficient waste water treatment option would be more easily available. By applying 'stress' conditions on a bioreactor system seeded with raw anaerobic sludge, the population dynamics of the anaerobic community change and the acidogens start to produce extracellular polymers, which in turn enhance the granulation process by providing a matrix for the bacterial cells to adhere to. These "environmental stress" conditions include changes in the C:P:N ratio's. The aim of this study was, therefore, to assess the impact of different carbon and nitrogen sources on the enhancement of granulation in a batch system, and to determine the best preservation technique in terms of retainment of activity. It was found that the carbon source and concentration had a significant influence on batch granule enhancement. Low concentrations (2.g.l ̄ ¹) of glucose gave the best granule enhancement over a 14 day incubation period. Fruit cocktail effluent was found to be a cheap and effective carbon source for batch granule cultivation. It was found that different nitrogen sources did not have the same impact on granule enhancement, however, urea, at all concentrations tested, gave the best granule enhancement. A major problem encountered during the study was the standardisation of the inoculum. Significant granule enhancement comparisons between the different carbon sources were impeded by the lack of a suitable and reliable form of sludge standardisation. Future research needs to address this problem of the standardisation of the sludge inoculum as this would lead to more kinetically comparable results. Mass granule culturing will require granule preservation without risking the loss of activity. In the second study, six different preservation techniques and storage periods were evaluated in terms of the retainment of activity. These involved freeze-drying, vacuum freeze-drying, vacuum-drying, freezing, cold storage and room temperature preservation. Activity testing was used for comparing the efficiency of the different preservation techniques in terms of the tempo of biogas and methane production. Freeze-drying the granules, with storage for up to 90 days was found to give the best retainment of activity, followed by vacuum freeze-drying. The room temperature preserved samples showed a sudden increase in activity by day 120, which could possibly be explained by cell hydrolysis of the granules after day 90. The highest activity was achieved after 10 h of incubation, and it was, therefore, suggested that activity testing for evaluation purposes should use an incubation time of only 10 h. Furthermore, only the basic test medium with added glucose should be used for activity testing as it was observed that the addition of lactate and acetic acid played no decisive role in determining the level of activity of the granules. This study recommends the use of low concentrations of glucose for optimum granule enhancement during the mass cultivation of granules, and the addition of low concentrations of lactate to ensure a stable system with no acidification. It is also advisable to use a standardised sludge inoculum, as this will allow more efficient comparisons. Freeze-drying is recommended as preservationtechnique as this technique showed the best retainment of activity. A storage period of 90 days is, however, too short to be of much use for the industry. This will have to be investigated, together with the phenomenon of increased activity after 90 days as shown by the room temperature preserved granules.
AFRIKAANSE OPSOMMING: Die potensiële gebruik van die "uptflow anaerobic sludge blanket" (UASB) bioreaktor word beperk deur verlengde aansitprosedure as gevolg van die tydsame granulasieproses en die feit dat geskikte inokulums nie vrylik beskikbaar is in die meeste ontwikkelende lande, bv. Suid-Afrika nie. Die massa-kweking van granules sal die afvalwater-industrie voorsien van 'n geskikte inokulum, en sodoende 'n effektiewe opsie vir die behandeling van afvalwater beskikbaar stel. Deur die aanwending van "stres" toestande op 'n reaktor, wat geinokuleer is met rou anaerobe slyk, vind daar 'n verandering in die samestelling van die anaerobe populasie plaas. Die laktaat-benuttende asidogene begin om ekstrasellulêre polisakkariede te produseer wat die granulasieproses versnel deur 'n matriks te voorsien waaraan die bakteriële selle kan heg. Hierdie "omgewings stres" toestande sluit veranderinge in die C:P:N verhoudings in. Die doel van hierdie studie was om die invloed van verskillende koolstof- en stikstofbronne op die vermeerdering van granules te bepaal, asook om die beste preserveringstegniek in terme van die behoud van aktiwiteit te bepaal. Daar is gevind dat die koolstofbron en konsentrasie 'n betekenisvolle invloed op granule-vermeerdering het. Lae konsentrasies glukose (2 g.I ̄ ¹) het tot die grootste vermeerdering in granules oor 'n 14 dae inkubasieperiode gelei. Vrugtekelkie-afvalwater is geidentifiseer as 'n goedkoop en effektiewe koolstofbron wat ook gebruik kan word vir die kweking van granules. Voorts is gevind dat die stikstofbron en konsentrasie nie so 'n groot invloed op granule-vermeerdering het nie. Urea het nietemin die beste granule-vermeerdering vir al die konsentrasies wat getoets is, gegee. Standaardisasie van die inokulum was 'n groot probleem gedurende die studie. Betekenisvolle vergelykings tussen die granule-vermeerderings verkry met die verskeie groeimedia is bemoeilik deur die afwesigheid van 'n geskikte en betroubare standaardisasie-metode. Toekomstige navorsing moet hierdie probleem aanspreek aangesien dit sal lei tot meer kineties vergelykbare resultate. Massa-kweking van granule sal 'n metode van granule-preservering vereis sonder enige verlies van aktiwiteit. In die tweede studie is ses verskillende preserverings-tegnieke en opbergings-periodes in terme van die behoud van aktiwiteit geëvalueer. Die tegnieke sluit in: vriesdroging; vakuum-vriesdroging; vakuumdroging; bevriesing; koelopberging en kamertemperatuur-preservering. Aktiwiteitstoetsing is gebruik vir die vergelyking van die effektiwiteit tussen die verskillende preserverings-tegnieke in terme van die tempo van biogas- en metaanproduksie. Die granules wat met behulp van die vriesdroogtegniek gepreserveer is, het die beste behoud van aktiwiteit getoon, gevolg deur die vakuum-gevriesdroogde granules. Die monsters wat by kamertemperatuur gepreserveer is, het 'n skielike toename in aktiwiteit na 120 dae van opberging getoon en 'n moontlike verklaring vir hierdie verskynsel kan sel-hidrolise van die granules na 90 dae van opberging wees. Die meeste aktiwiteit is behaal na 'n 10 h inkubasietyd, en dus word hierdie inkubasietyd aanbeveel indien aktiwiteitstoetse vir evaluerings-doeleindes gedoen word. Verder word aanbeveel dat slegs die glukose-verrykte basiese toetsmedia vir aktiwiteitstoetsing gebruik word aangesien die byvoeging van laktaat en asynsuur geen noemenswaardige rol speel in die bepaling van die vlak van aktiwiteit van die granules nie. Hierdie studie beveel die gebruik van lae glukosekonsentrasies aan vir optimale vermeerdering van granules tydens die massakweking daarvan, asook die byvoeging van lae konsentrasies laktaat om 'n stabiele sisteem met geen versuring te verseker. Die gebruik van 'n gestandaardiseerde slyk-inokulum word sterk aanbeveel aangesien dit meer vergelykbare resultate lewer. Vriesdroging (as preserveringstegniek) het die beste behoud van aktiwiteit in die granules getoon en word dus as preserveringstegniek aanbeveel. 'n Opbergingsperiode van 90 dae is egter te kort om van veel waarde vir die industrie te wees. Hierdie probleem, asook die verskynsel van 'n verhoging in aktiwiteit na 90 dae van die granules wat by kamertemperatuur gepreserveer is, moet verder ondersoek word.
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46

Tavares, Aline Cardoso. "Modelagem matemática da degradação da glicose, com produção de hidrogênio, em um reator anaeróbio de leito fixo." Universidade de São Paulo, 2008. http://www.teses.usp.br/teses/disponiveis/18/18138/tde-20022009-165554/.

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Modelos matemáticos oferecem grandes benefícios para a compreensão dos mecanismos envolvidos nos processos de tratamento de águas residuárias uma vez que fornecem interpretações e possibilitam previsões de desempenho, comparações de alternativas de tratamento, otimização de futuras plantas ou o aprimoramento das existentes, podendo subsidiar a elaboração de projetos em escala real. Em virtude disto, nesta pesquisa visou-se o desenvolvimento de um modelo bioquímico-matemático para descrever o processo de degradação da glicose em um reator anaeróbio de leito fixo com fluxo ascendente, com a resultante produção biológica de hidrogênio por meio do processo de fermentação. O desenvolvimento do modelo foi baseado em estudos sobre a cinética bioquímica e as características hidrodinâmicas do sistema. Os parâmetros de ajuste do modelo aos dados experimentais foram as constantes de velocidade das reações bioquímicas envolvidas na produção de hidrogênio. A calibração foi realizada manualmente buscando minimizar o desvio global. Para a determinação dos parâmetros foi utilizada a técnica de geração de números aleatórios com distribuição de freqüência uniforme e em seguida, o método de inversão de matrizes. O modelo matemático se revelou bastante adequado para a previsão do perfil de concentrações ao longo do reator, e possibilitou a representação das rotas de utilização da matéria orgânica. A reação de oxidação do ácido propiônico pelas bactérias acidogênicas produtoras de hidrogênio constitui a principal via de produção de \'H IND.2\' no sistema.
Mathematical models bring benefits to the understanding of mechanisms involved on wastewater treatment processes because they provide interpretations and make possible performance predictions, evaluation of design alternatives, optimization of future plants or the improvement to existing systems. Therefore, in this work a mathematical model to describe the glucose degradation process, with hydrogen production through the fermentation, in an upflow anaerobic packed-bed reactor is developed. The model equations were based on studies of biochemical kinetics and hydrodynamics features of the system. The parameters considered were the rates of the biochemical reactions involved in the hydrogen production. The calibration was made through the minimization of the global deviation. The parameters determination was obtained with the use of a technique of generation of aleatory numbers, and after that, the method of matrices inversion for the solution of the system of linear equations. The mathematical model developed showed to be adequate for the concentrations prediction along the reactor, and it made possible the representation of the routes of organic material utilization. The oxidation reaction of propionic acid is the main hydrogen production route in the reactor.
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47

Cangani, Max Ternero [UNESP]. "Tratamento anaeróbio-aeróbio de águas residuárias de suinocultura e reúso na produção de milho para silagem." Universidade Estadual Paulista (UNESP), 2011. http://hdl.handle.net/11449/94885.

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Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES)
Fundação de Amparo à Pesquisa do Estado de São Paulo (FAPESP)
Neste trabalho, avaliou-se o desempenho de dois conjuntos de reatores anaeróbios de fluxo ascendente com manta de lodo (UASB) instalados em série. Os conjuntos I e II foram compostos por dois reatores UASB em série com volumes de 908 e 350 L e de 908 e 188 L, respectivamente. No conjunto II, foi realizado pós tratamento do efluente em um reator operado em batelada sequencial (RBS) com alimentação contínua, com volume de 3000 L. As cargas orgânicas volumétricas (COV) aplicadas no primeiro reator dos conjuntos I e II variaram de 8,36 a 9,95 g DQO total (L d)-1 e de 7,83 a 11,6 g DQO total (L d)-1, respectivamente. As eficiências médias de remoção de DQO total, nitrogênio Kjeldahl (NK), fósforo total (P-total) foram elevadas e variaram de 95 a 97% e de 97 a 99%, de 64 a 67% e de 53 a 69%, e de 80 a 87% e de 71 a 89%, nos conjuntos I e II, respectivamente. As eficiências também foram elevadas para os metais Cu, Fe, Mn e Zn nos conjuntos I e II e variaram de 80 a 91% e de 63 a 80%, de 59 a 80% e de 51 a 72%, de 89 a 97% e de 81 a 98%, de 87 a 98% e de 91 a 99%, respectivamente. A semeadura do milho, foi realizado na safrinha 2009 e na safra 2009/2010, ambos em sistema de plantio direto e convencional, para a confecção de silagem. Os valores do pH observados na silagem não diferiram entre os tratamentos nas duas épocas de semeadura e nos sitemas de plantio direto e convencional. A adubação do milho para confecção de silagem, com dejeto bruto de suíno, com dejetos tratados em sistema anaeróbio e com os dejetos do pós-tratamento, quando comparada com a adubação mineral, não apresentou resultados com diferenças significativas na silagem na maioria dos atributos avaliados. O reúso dos efluentes tratados e do dejeto bruto, não promoveu alterações na nutrição da planta, porém os efluentes...
This study evaluated the performance of two sets of upflow anaerobic sludge blanket (UASB) installed in series. The sets I and II were composed of two UASB reactors in series with volumes of 908 and 350 L and 908 L and 188, respectively. In set II was conducted after the treatment of the effluent in a sequencing batch reactor (SBR) with continuous flux, with a volume of 3000 L. The volumetric organic loads (VOC) applied to the first reactor of the sets I and II ranged from 8.36 to 9.95 g total COD (L d) -1 and 7.83 to 11.6 g total COD (L d) -1, respectively. The average removal efficiencies of total COD, Kjeldahl nitrogen (NK), total phosphorus (total P) were high and ranged from 95 to 97% and 97 to 99%, 64 to 67% and 53 to 69% and 80 to 87% and 71 to 89% in clusters I and II, respectively. The efficiencies were also high for Cu, Fe, Mn and Zn in clusters I and II, and ranged from 80 to 91% and 63 to 80%, 59 to 80% and 51 to 72% from 89 to 97 and 81% to 98%, 87 to 98% and 91 to 99%, respectively. We carried out the swing of maize in the 2009 off-season and 2009/2010 season, both in no-tillage and conventional sistems for making silage. The pH values observed in the silage did not differ significantly between treatments in both seasons of swing and in the sistems of tillage and no-tillage. The fertilization of corn for silage making, with raw pig manure with waste treated in anaerobic system and the waste from the post-treatment compared to mineral fertilization, results showed no significant difference in silage in most parameters. The reuse of treated effluent and raw manure, did not promote changes in the nutrition of corn but the application of treated effluent increased concentrations of N readily available for plants in soil. Even in much larger doses applied compared to the raw waste, the treated effluent, promoted soil contamination by total coliforms and thermotolerant lower
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48

Stets, Maria Isabel. "AVALIAÇÃO DA INFLUÊNCIA DO MATERIAL SUPORTE E CARACTERIZAÇÃO DA DIVERSIDADE MICROBIANA DE REATORES ANAERÓBIOS PARA O TRATAMENTO DE EFLUENTE DE ABATEDOURO." UNIVERSIDADE ESTADUAL DE PONTA GROSSA, 2008. http://tede2.uepg.br/jspui/handle/prefix/663.

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The effluent generated in abattoirs has a high concentration of organic matter and need treatment before being discarded in the water bodies. Anaerobic biological filters are considered a good technique for the treatment of industrial effluents; however, choosing the correct support media is extremely important to ensure the success of the reactor. In the same way, the study of microbial diversity can optimize the performance and the operation of these systems. In this work it was evaluated the efficiency of the treatment of the effluent from slaughterhouse, using three upflow anaerobic biological filters, and it was compared the microbial diversity of these filters. The reactor called A, B and C were built in chloride polivinile and filled with rings of polypropylene, polyurethane foam, or pieces of clay brick, respectively. These reactors were operated at room temperature and the used Hydraulic Retention Times of (HRTs) were of 30, 20, 18, 14, 10, 8, 6, 5, 4, 3, 2, 1.5 and 1 day. To monitor the efficiency of the process, the pH, alkalinity, acidity, Chemistry Oxygen Demand (COD), and total solids content of volatile solids, nitrogen and phosphorus substrate and effluents of each reactor were analyzed. The values of pH decreased with the reduction of HRT and the ratio volatile acidity / alkalinity remained below 0.13 during the majority of the analyzed period. In the one day’s HRT, the reactor C was more effective reaching 80.76 of removal. There was a high rate of nitrogen removal probably due to its low concentration in the substrate. High phosphorus removals also occurred: there was a decrease of phosphorus removal when the HRT declines in reactors A and B, the same did not occur in the reactor C. The three reactors behaved similarly regarding to the collecting sites and there was no difference between these sites when COD removal, volatile acidity / alkalinity ratio and pH were analyzed. To evaluate the effect of different media support in the microbial community, the reactors DNA biomass was extracted, quantified and used as template in an amplification reaction of 16S rDNA gene from bacteria and metanogenic. The amplified fragments of approximately 1500 bp were treated with HinfI, RsaI and HaeIII restriction enzymes to obtain the reactors ARDRA (Amplified Ribossomal DNA Restriction Analysis) profiles. The indices of richness, richness modified, Shannon-Weaver diversity index and similarity dendogram, determined from ARDRA, grouped the reactors A and B, and left the reactor C isolated due to its dissimilarity. The Hierarchical Cluster Analysis (HCA) also grouped the reactors that way, however, that group has less than 0.1% of similarity, suggesting a low interference in the reactors media support in microbial communities.
O efluente gerado em abatedouros possui uma elevada concentração de matéria orgânica e necessita de tratamento antes de ser descartado nos corpos hídricos. Os filtros biológicos anaeróbios são considerados uma boa técnica para tratamento de efluentes industriais, porém, a escolha correta do meio suporte é extremamente importante para garantir o sucesso do reator. Da mesma forma, o estudo da diversidade microbiana pode otimizar o desempenho e a operação desses sistemas. Neste trabalho, foi realizada a avaliação da eficiência do tratamento de efluente de abatedouro, utilizando-se três filtros biológicos anaeróbios de fluxo ascendente, bem como a comparação da diversidade microbiana desses filtros. Os reatores denominados A, B e C foram construídos em cloreto de polivinila e preenchidos com anéis de polipropileno, espuma de poliuretano ou pedaços de tijolo de argila, respectivamente. Esses reatores foram operados à temperatura ambiente e os Tempos de Retenção Hidráulica (TRHs) utilizados foram de 30; 20; 18; 14; 10; 8; 6; 5; 4; 3; 2; 1,5 e 1 dia. Para monitorar a eficiência do processo, foram analisados no substrato e efluente de cada reator pH, alcalinidade, acidez, Demanda Química de Oxigênio (DQO), teor de sólidos totais e sólidos voláteis, nitrogênio efósforo. Os valores de pH do efluente dos reatores decresceram com a redução do TRH. A relação acidez volátil/alcalinidade ficou abaixo de 0,13 durante a maior parte do período analisado. No TRH de 1 dia o reator C foi o mais eficiente alcançando 80,76 de remoção de DQO. Observou-se uma elevada taxa de remoção de nitrogênio em todos os reatores provavelmente devido à sua baixa quantidade no substrato. Também ocorreram elevadas remoções de fósforo, mas houve decréscimo dessa remoção com a diminuição do TRH nos reatores A e B, o mesmo não ocorrendo no reator C. Quando se analisaram as amostras retiradas em quatro diferentes alturas dos reatores, observou-se que os três se comportaram de forma similar quanto aos pontos de coleta e não houve diferença entre esses pontos quanto à remoção de DQO, relação acidez volátil/alcalinidade e pH. Para avaliar o efeito dos diferentes meios suporte na comunidade microbiana, o DNA da biomassa dos reatores foi extraído, quantificado e usado como molde numa reação de amplificação do gene 16S rDNA de bactérias e archaeas metanogênicas. Os fragmentos de aproximadamente 1500 pb amplificados foram tratados com as enzimas de restrição HinfI, RsaI e HaeIII para obtenção dos perfis de ARDRA (Análise da Restrição de rDNA Amplificado) dos reatores. Os índices de riqueza, riqueza modificada, diversidade de Shannon-Weaver e dendograma de similaridade, determinados a partir da ARDRA, agruparam os reatores A e B, ficando o reator C isolado devido à sua dessemelhança. A Análise de Agrupamento Hierárquico (HCA) também agrupou os reatores dessa forma, entretanto, esse agrupamento possui menos que 0,1% de similaridade, sugerindo uma baixa interferência do meio suporte nas comunidades microbianas.
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49

Sato, Cibele Midori [UNESP]. "Avaliação do desempenho de um reator anaeróbio compartimentado no tratamento de esgoto doméstico." Universidade Estadual Paulista (UNESP), 2013. http://hdl.handle.net/11449/115840.

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A aplicação de reatores UASB (Upflow Anaerobic Sludge Blanket) passou a ocupar uma posição de destaque, principalmente no Brasil, face às condições ambientais de temperatura favoráveis, baixo custo, simplicidade operacional e baixa produção de sólidos. Com o intuito de aprimorá-lo, este estudo aliou as características construtivas e operacionais destes reatores com as dos Reatores Anaeróbios Compartimentados (RAC), caracterizados por oferecerem a possibilidade de separação das fases que ocorrem na digestão anaeróbia e o aumento do tempo de contato entre a biomassa e o efluente. Assim, foi projetado e construído um reator vertical, contendo dois tubos concêntricos em seu interior, visando à separação das etapas acidogênica e metanogênica, a partir da cinética de crescimento dos microrganismos presentes. A pesquisa teve como objetivo principal estudar o comportamento e avaliar o desempenho do reator UASB compartimentado sob nova configuração, no período de partida e operação, tratando esgoto doméstico. O monitoramento do sistema foi dividido em duas etapas: partida e operação. Durante a partida, os valores de pH e alcalinidade mantiveram-se estáveis dentro de uma faixa adequada. Os resultados apresentados durante seu monitoramente indicaram ainda, que o inóculo utilizado promoveu condições adequadas para a partida do reator, com remoção média de DQO de 53,8%, chegando a atingir 82,8% ao final desta etapa. Na segunda etapa de monitoramento, ocorreram diversos problemas relacionados à operação do sistema, ocasionando sua paralisação durante alguns dias. Os valores de pH encontraram-se dentro da faixa adequada, contudo, a alcalinidade sofreu variações quando houve interrupção no sistema. A remoção de matéria orgânica apresentou-se estável, mesmo após tais interrupções, com eficiência média de remoção de 80% para a DQO e 78% para a DBO. Além disso, ambas chegaram a alcançar 90% na ...
Application of UASB (Upflow Anaerobic Sludge Blanket) reactor has come to occupy a prominent position, especially in Brazil, due to favorable climatic conditions, low cost, operational simplicity and low production solids. In order to improve it, this study combined constructional and operational features of these reactors with the Compartmented Anaerobic Reactor (CAR), characterized by offering the possibility of phase separation occurring in the anaerobic digestion and increase the contact time between the biomass and effluent. Thus a vertical reactor was designed and constructed containing two concentric tubes inside, in order to separate the acidogenic and methanogenic steps from the kinetics of growth of microrganisms present. The research aimed to study the behavior and evaluate the performance of the UASB compartmentalized reactor under new configuration during starting and operation, treating domestic wastewater. The monitoring system was divided into two stages: starting and operating. During the start-up, the values of pH and alkalinity remained stable within a proper range. The results presented during its monitoring also indicated that the inoculum used promoted conditions for starting the reactor, with average COD removal of 53,8%, reaching 82,8% at the end of this step. In the second stage of monitoring, there were several problems related to system operation, causing a stoppage for a few days. The pH values were within the appropriate range, however, the alkalinity variations experienced when there was an interruption in the system. The removal of organic matter remained stable even after such interruption, with average removal efficiency of 80% to 78% for COD and BOD. Moreover, both even reached 90% removal efficiency
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50

Sato, Cibele Midori. "Avaliação do desempenho de um reator anaeróbio compartimentado no tratamento de esgoto doméstico /." Ilha Solteira, 2013. http://hdl.handle.net/11449/115840.

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Orientador: Tsunao Matsumoto
Banca: Liliane Lazzari Alberti
Banca: Marc Arpad Boncz
Resumo: A aplicação de reatores UASB (Upflow Anaerobic Sludge Blanket) passou a ocupar uma posição de destaque, principalmente no Brasil, face às condições ambientais de temperatura favoráveis, baixo custo, simplicidade operacional e baixa produção de sólidos. Com o intuito de aprimorá-lo, este estudo aliou as características construtivas e operacionais destes reatores com as dos Reatores Anaeróbios Compartimentados (RAC), caracterizados por oferecerem a possibilidade de separação das fases que ocorrem na digestão anaeróbia e o aumento do tempo de contato entre a biomassa e o efluente. Assim, foi projetado e construído um reator vertical, contendo dois tubos concêntricos em seu interior, visando à separação das etapas acidogênica e metanogênica, a partir da cinética de crescimento dos microrganismos presentes. A pesquisa teve como objetivo principal estudar o comportamento e avaliar o desempenho do reator UASB compartimentado sob nova configuração, no período de partida e operação, tratando esgoto doméstico. O monitoramento do sistema foi dividido em duas etapas: partida e operação. Durante a partida, os valores de pH e alcalinidade mantiveram-se estáveis dentro de uma faixa adequada. Os resultados apresentados durante seu monitoramente indicaram ainda, que o inóculo utilizado promoveu condições adequadas para a partida do reator, com remoção média de DQO de 53,8%, chegando a atingir 82,8% ao final desta etapa. Na segunda etapa de monitoramento, ocorreram diversos problemas relacionados à operação do sistema, ocasionando sua paralisação durante alguns dias. Os valores de pH encontraram-se dentro da faixa adequada, contudo, a alcalinidade sofreu variações quando houve interrupção no sistema. A remoção de matéria orgânica apresentou-se estável, mesmo após tais interrupções, com eficiência média de remoção de 80% para a DQO e 78% para a DBO. Além disso, ambas chegaram a alcançar 90% na ...
Abstract: Application of UASB (Upflow Anaerobic Sludge Blanket) reactor has come to occupy a prominent position, especially in Brazil, due to favorable climatic conditions, low cost, operational simplicity and low production solids. In order to improve it, this study combined constructional and operational features of these reactors with the Compartmented Anaerobic Reactor (CAR), characterized by offering the possibility of phase separation occurring in the anaerobic digestion and increase the contact time between the biomass and effluent. Thus a vertical reactor was designed and constructed containing two concentric tubes inside, in order to separate the acidogenic and methanogenic steps from the kinetics of growth of microrganisms present. The research aimed to study the behavior and evaluate the performance of the UASB compartmentalized reactor under new configuration during starting and operation, treating domestic wastewater. The monitoring system was divided into two stages: starting and operating. During the start-up, the values of pH and alkalinity remained stable within a proper range. The results presented during its monitoring also indicated that the inoculum used promoted conditions for starting the reactor, with average COD removal of 53,8%, reaching 82,8% at the end of this step. In the second stage of monitoring, there were several problems related to system operation, causing a stoppage for a few days. The pH values were within the appropriate range, however, the alkalinity variations experienced when there was an interruption in the system. The removal of organic matter remained stable even after such interruption, with average removal efficiency of 80% to 78% for COD and BOD. Moreover, both even reached 90% removal efficiency
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