Publicado
Remoción anaerobia del colorante azul directo brl en Reactor Anaerobio de Flujo Ascendente UASB (Upflow Anaerobic Sludge Blanket) con carbón activado
Anaerobic removal of the brl direct blue dye in Upflow Anaerobic Sludge Blanket (UASB) with activated carbon
DOI:
https://doi.org/10.15446/rev.colomb.biote.v17n2.54276Palabras clave:
Bacterial, consortium, removal, COD, IPRS, SSV, Consorcio bacteriano, remoción, DQO, PIRS (es)Título en ingles: Anaerobic removal of the brl direct blue dye in Upflow Anaerobic Sludge Blanket (UASB) with activated carbon
En esta investigación se utilizó el colorante azul directo brl para remoción anaerobia con un consorcio bacteriano aislado de efluentes industriales del Parque Industrial río Seco (PIRS), Arequipa, Perú; en un reactor anaerobio de flujo ascendente UASB con carbón activado. El reactor tuvo una capacidad de 14.4 Lcon lodos y carbón activado del 40% de volumen, con una carga orgánica de 6 KgDQO/m3•día y un tiempo de retención hidráulica de 1 día con un flujo ascendente. El objetivo fue medir la eficiencia de la remoción anaerobia del colorante en un tiempo de 28 días. Los resultados demostraron un incremento del 41% de los Sólidos Suspendidos Volátiles (SSV) de 12894 mg•L-1 a 21546 mg•L-1 bajo las condiciones del experimento, con una remoción del 57% de la Demanda Química de Oxigeno (DQO) de 484 mg•L-1 a 122 mg•L-1 y una remoción del 87% del colorante azul directo brl de 69.61 mg•L-1 a 9 mg•L-1. Los resultados con el carbón activado granular solamente, demostraron una remoción del 61% del colorante azul directo brl de 70.67 mg•L-1 a 27.83 mg•L-1 a los 28 días.
In this research the brl direct blue dye was used for anaerobic removal with a bacterial consortium of industrial effluents from Industrial Park Río Seco (IPRS), Arequipa, Peru; in an anaerobic reactor of UASB Upflow with activated carbon. The reactor had a capacity of 14.4 L with sludge and activated carbon of 40% of volume, with an organic load of 6 Kg COD/m3•dia and a hydraulic retention time of 1 day with an upward flow. The objective was to measure the efficiency of the anaerobic removal of coloring in a time of 28 days. The results showed an increase of 41% of the solids suspended volatile (SSV) 12894 mg•L-1 up to 21546 mg•L-1 under the conditions of the experiment, with a removal of 57% of the chemical demand of oxygen (COD) from 484 mg•L-1 to 122 mg•L-1 and a removal of 87% of the dye Blue direct the 69.61 brl mg•L-1 to 9 mg•L-1. Results with activated charcoal granular only, they showed a removal of 61% of the dye Blue direct 70.67 brl mg•L-1 to 27.83 mg•L-1 at 28 days.
Key words: Bacterial consortium, removal, COD, IPRS, SSV.
Referencias
APHA, (1992). Standard Methods for the Examination of Water and Wastwater, 18th ed. American Public Health Association, Washington, DC, USA.
APHA, (1998). Standard Methods for the examination of Water and Wastewater, 20th ed. American public health association American water works association/water environment federation, Washington DC, USA.
Brás, R., Gomes, A., Ferra, M.I.A., Pinheiro, H.M., Gonçalves, I.C. (2005). Monoazo and diazo dye decolourisation studies in a methanogenic UASB reactor. Journal of Biotechnology, 115, 57–66.
Cortazar, A., Gonzalez, C.A., Coronel, C., Escalante, J.A., Castro, J., Villagómez, J.R. (2012). Biotecnología aplicada a la degradación de colorantes de la industria textil. Revista Universidad y Ciencia, 28(2),187-199.
Chinwetkitvanich, S., Tuntoolvest, M., Panswad, T. (2000). Anaerobic decolorization of reactive dyebath effluents by a two-stage UASB system with tapioca as a co-substrate. Water Research, 34 (8), 2223-2232.
Conceição, V., Bentes, F., Querne de Carvalho, K. (2013). Treatment of textile effluent containing indigo blue dye by a UASB reactor coupled with pottery clay adsorption. Acta Scientiarum. Technology: Acta Sci. Technol., 35(1), 53-58.
Dafale, N., Rao, N.N., Meshram, S.U. , Wate, S.R. (2008). Decolorization of azo dyes and simulated dye bath wastewater using acclimatized microbial consortium - Biostimulation and halo tolerance. Bioresource Technology, 99, 2552-2558.
Droste, R.L. (1997). Theory and Practice of Water and Wastewater Treatment, 800 pages, J. Wiley & Sons (now in 3rd printing and in Chinese and Korean translation).
González, L., Escamilla, E. (2006). Estudio de la degradación de un colorante azo rojo reactivo en un biorreactor anaerobio de flujo ascendente In: Retos de la investigación del agua en México, pp.413-428. Edition: Primera, UNAM, Editors: Úrsula Oswald Spring,
Işik, M., Sponza, D. (2005). Effects of alkalinity and co-substrate on the performance of an upflow anaerobic sludge blanket (UASB) reactor through decolorization of Congo Red azo dye. Bioresource Technology. 96, 633–643.
Kalyani, D.C., Telke, A.A., Dhanve, R.S., Jadhav, J.P. (2008). Ecofriendly biodegradation and detoxification of reactive red 2 textile dye by newly isolated Pseudomonas sp. SUK1. Journal of Hazardous Materials. 163, 735-742.
Karataş, M., Dursun, S. (2007). Bio-decolourization of azo-dye under anaerobic batch conditions. J. Int. Environmental Application & Science, 2, 20-25.
Lettinga, G., Van Velsen, A. F. M., Hobma, S. W., De Zeeuw, W., Klapwijk, A. (1980). Use of the upflow sludge blanket (USB) reactor concept for biological wastewater treatment, especially for anaerobic treatment. Biotechnology and Bioengineering, 22, 699-734.
McMullan, G.; Meehan, C.; Conneely, A.; Kirby, N.; Robinson, T.; Nigam, P.; Banat, I.M.;
Manu, B., Chaudhari, S. (2002). Anaerobic decolorisation of simulated textile wastewater containing azo dyes. Bioresource Technology. 82, 225-231.
Marchant, R. Y Smyth, W.F. (2001). Applied Microbiology and Biotechnology, 56, 81
Metcalf, L., Eddy, H. (2003). Wastewater Engineering, fourth ed. McGraw Hill, New York.
O'Neill, C., Hawkes, F. R., Hawkes, D. L., Esteves, S., Wilcox, S. J. (2000). Anaerobic-aerobic biotreatment of simulated textile effluent containing varied ratios of starch and azo dye. Water Research. 34 (8), 2355-2361.
Razo-Flores, E., Luijten, M., Donlon, B., Lettinga, G., Field, J. (1997). Biodegradation of selected azo dyes under methanogenic conditions. Water Science and Technology, 36(6-7), 65-72.
Senthilkumar, M., Gnanapragasam, G., Arutchelvan, V., Nagarajan, S. (2011). Treatment of textile dyeing wastewater using two-phase pilot plant UASB reactor with sago wastewater as co-substrate. Chemical Engineering Journal, 166, 10–14.
Sponza, D., Işik, M. (2005). Reactor performances and fate of aromatic amines through decolorization of Direct Black 38 dye under anaerobic/aerobic sequentials. Process Biochemistry, 40, 35–44
Toorisaka, E., Ong, S.A., Hirata, M., Hano, T. (2005). Biodegradation of redox dye Methylene Blue by up-flow anaerobic sludge blanket reactor. Journal of hazardous materials, 124(1), 88-94.
Van Der Zee, F.P., Bisschops, I.A., Lettinga, G., Field, J.A. (2003). Activated carbon as an electron acceptor and redox mediator during the anaerobic biotransformation of azo dyes. Environ. Sci. Technol., 37, 402-408.
Van Lier, J.B, Van Der Zee, F.P., Tan, N.C.G., Rebac, S., Kleerebezem, R. (2001). Advances in high rate anaerobic treatment: staging of reactor systems. Water Science & Technology. 44 (8), 15–25.
Yu, J., Wang, X., Yue, P.L. (2001). Optimal decolorization and kinetic modeling of synthetic dyes bye Pseudomonas strains. Water Res., 35(15),3579-86.
Dimensions
PlumX
Visitas a la página del resumen del artículo
Descargas
Cómo citar
Licencia
Derechos de autor 2015 Revista Colombiana de Biotecnología
Esta obra está bajo una licencia internacional Creative Commons Atribución 4.0.
Esta es una revista de acceso abierto distribuida bajo los términos de la Licencia Creative Commons Atribución 4.0 Internacional (CC BY). Se permite el uso, distribución o reproducción en otros medios, siempre que se citen el autor(es) original y la revista, de conformidad con la práctica académica aceptada. El uso, distribución o reproducción está permitido desde que cumpla con estos términos.
Todo artículo sometido a la Revista debe estar acompañado de la carta de originalidad. DESCARGAR AQUI (español) (inglés).
