PROJETO DE REATOR ANAERÓBIO DE FLUXO ASCENDENTE (RAFA) PARA TRATAMENTO DE VINHAÇA

Brazil is the largest sugar and alcohol producer in the world, consequently, it is also a major vinasse producer, which is a problem, as it has a high potential for pollution, severely impacting the soil and water, despite being used in fertigation of cane fields. When treated in anaerobic conditions, however, it can produce energy and be used as a biofertilizer for the soil. This treatment can be performed by an Upflow Anaerobic Sludge Blanket (UASB), considered efficient by the literature. Based on this, this article tries to gather equations and collect data, reviewing the scientific literature with the objective of designing an UASB for the treatment of vinasse, exposing an alternative of suitable final disposal for this by-product. The results show good opportunities, with a great potential for reducing BOD and COD and producing biogas, electricity and biofertilizer, in addition to providing a compilation of equations and important data for future calculations.

Novas concepções para reatores anaeróbios de manta de lodo: uso de mistura mecânica ou hidráulica com decantação lamelar e sem separador trifásico

RESUMO Neste artigo, apresenta-se uma abordagem conceitual sobre propostas de alternativas para a concepção de sistemas com reator anaeróbio de manta de lodo. Em essência, propõem-se: i) a eliminação dos separadores de gás, líquido e sólido que constam em reatores upflow anaerobic sludge blanket reactors e sua substituição por unidade de sedimentação de alta taxa em setor incluso ou externo ao volume do reator biológico; ii) a recirculação de parcela do lodo retido no sedimentador, transformando o conjunto em um sistema semelhante ao de lodo ativado, porém preservando a manta de lodo no reator anaeróbio (activated anaerobic sludge blanket system) e, assim, viabilizando melhor controle do tempo de retenção celular; e iii) a simplificação (menor número de entradas) do sistema de distribuição do afluente junto ao fundo da zona de reação, mediante duas alternativas: agitação mecânica ou agitação hidráulica com jatos — em ambos os casos, intermitentes. As propostas, conforme apresentadas, constituem resumo de pesquisa baseada em reatores de bancada sucedida pela operação e testes em duas unidades-piloto paralelas (volume total: 20,8 m3, incluindo volumes de reação e de sedimentação). Constatou-se que é possível remover sólidos suspensos do efluente da região de reação sem a necessidade do separador trifásico e, também, que é possível manter-se a manta de lodo mesmo com a agitação na região de reação. Foram obtidos bons resultados na remoção de sólidos suspensos totais, demanda bioquímica de oxigênio e demanda química de oxigênio nos sedimentadores com valores de taxa de aplicação superficial de 34,0 até 81,6 m3m-2dia. Constatou-se, também, que valores bastante baixos de gradiente de velocidade (G £ 20s-1) são suficientes para promover a manutenção da manta de lodo e que a intermitência na agitação é favorável ao processo biológico. Os resultados relacionados com a remoção de demanda química de oxigênio, demanda bioquímica de oxigênio e sólidos suspensos totais foram comparados com os de outros estudos sobre reatores upflow anaerobic sludge blanket reactors convencionais. Contudo, aqueles relacionados com o tempo de reação celulat foram os mais significativos para as conclusões desta pesquisa. Quando o reator foi operado com tempo de detenção hidráulica de 8,2 h e velocidade ascensional no reator biológico de 0,69 mh-1, o tempo de reação celular do sistema resultou em 175 dias. Com velocidade ascensional menores, os valores de tempo de reação nuclear foram ainda maiores (por exemplo: velocidade ascensional = 0,39 mh-1; tempo de reação celular = 363 dias). Os resultados deste trabalho abrem perspectivas para novas pesquisas e novos horizontes para projeto de sistemas com reatores anaeróbios de manta de lodo e decantadores de alta taxa.

Enhancement of Bioreactor Performance Using Acclimatised Seed Sludge in Anaerobic Treatment of Chicken Slaughterhouse Wastewater: Laboratory Achievement, Energy Recovery, and Its Commercial-Scale Potential

Lack of good management practice of chicken slaughterhouse wastewater (CSWW) has caused pollution into water bodies. In this study, the potential of seed sludge acclimatised modified synthetic wastewater (MSWW) on bioreactor performance and energy recovery of CSWW treatment was investigated. Two sets of upflow anaerobic sludge blanket (UASB) reactors were employed. The seed sludge in UASB 2 was acclimatised with MSWW for 30 days. In UASB 1, no acclimatisation process was undertaken on seed sludge for control purposes. After the acclimatisation process of UASB 2, both reactors were supplied with CSWW under the same condition of organic loading rate (OLR = 0.5 to 6 gCOD/L/d) and mesophilic condition (37 °C). COD removal efficiencies of UASB 2 were >80% all through the steady-state of the OLR applied. Meanwhile, a drastic decrease in overall performance was observed in UASB 1 when the OLR was increased to 3, 4, 5, and 6 gCOD/L/d. Energy recovery from laboratory scale and projected value from commercial-scale bioreactor were 0.056 kWh and 790.49 kWh per day, respectively. Preliminary design of an on-site commercial-scale anaerobic reactor was proposed at a capacity of 60 m3.

Quali-quantitative characterization of biogas with the temporal behavior of organic load on wastewater treatment plant with upflow anaerobic sludge blanket reactors through measurement in full‑scale systems

This study aims to present the time behavior of wastewater flow parameters, organic matter, biogas flow, biogas composition, and its relations, measured through online sensors, in a municipal wastewater treatment plant (WWTP) operating full-scale upflow anaerobic sludge blanket (UASB) reactors, installed in the south of Brazil. WWTP has online measurement devices to evaluate some physicochemical variables of the sewage and the biogas. The COD analyzer (UV– Vis probe), ultrasonic flow meter, biogas flow meter, and biogas composition analyzer were the equipment used. The monitoring occurred for two time periods each of 72 h and one time period for 48 h in the year 2018. Data were checked with descriptive statistics, data independence was checked through the autocorrelation Box– Ljung test, normality behavior was checked with several tests (Shapiro– Wilk, Kolmogorov–Smirnov, Lilliefors, Anderson–Darling, D’Agostino K2, and Chen–Shapiro), and Spearman’s correlation coefficient was used to evaluate the correlations among the parameters. The mean sewage flow was 345 ± 120 L.s-1; removed organic load was, in average, 48%; biogas quality values were 82.32% ± 3.62% v/v (CH4), 2.66% ± 1.19% v/v (CO2), and 3453 ± 1268 ppm (H2S); and the production per capita obtained was 4.51 ± 1.65 NL.hab-1.d-1. It was estimated an electric power generation of 3118.6 kWh.d-1, which is equivalent to an installed power of 130 KW. The behavior of removed organic load and biogas flow (Nm3.h-1), produced in the treatment plant, showed variable, periodic, and nonstationary time behavior.