Abstract:Surveya Wastewater Treatment, To assess bulking in French wastewater treatment plants we developed a three-topic Water Quality and Hydrology approach, including analysis of i) technical assistance annual reports, ii) a questionnaire, Research Unit, Cemagref, and iii) microscopic sample observations. A seasonal effect was very apparent on the Parc de Tourvoie BP 44, F-92163 Antony cedex, France average SVI (mL/g). Three situations appear to promote bulking according to statistical analysis and operators' commen… Show more
“…However, they found that a Microthirx bacterium, which is one of the most common filamentous bacteria, was most abundant in winter, although they did not observe a clear, seasonal variation in the filaments [24]. Graveleau et al [13] found no significant seasonal differences in terms of micro-organism population distribution, although they found a seasonal pattern in SVI values. However, Flowers et al [25] found that temperature was the environmental variable that best correlated with changes in bacteria species and that bacteria species cycled through a predictable, seasonal pattern yearly, which confirms the results of the present study.…”
Section: Discussionmentioning
confidence: 92%
“…In addition, previous studies [13,24,25] have sought to identify seasonal patterns in micro-organism populations.…”
Section: Discussionmentioning
confidence: 99%
“…Some studies have found seasonal variations in ASP, especially in sludge settleability, which is measured mainly as sludge volume index (SVI). For example, Graveleau et al [13], Krult et al [14] and Oerther et al [10] found that average SVI values were higher in winter than in summer. In contrast, Wilén et al [15] and Liwarska-Bizukojc [16] found no seasonal variations in settleability properties when measured as stirred SVI and SVI at municipal wastewater treatment plants (WWTPs).…”
The effect of seasonal variations on floc formation in the activated sludge process (ASP) was studied in a municipal wastewater treatment plant in Finland nearly 16 months. Floc formation was measured with an online optical monitoring device, and results were correlated with the temperature of the upcoming wastewater and the treatment efficiency of the ASP. Results showed that floc formation has a clear, seasonal pattern, with flocs in summer being larger and rounder and having fewer filaments and small particles. In addition, treatment efficiency increased in summer. The study correlated the results of image analysis with the composition (chemical oxygen demand and suspended solids content) and temperature of the wastewater before and after the ASP. Results showed that the composition of upcoming wastewater has no clear correlation with floc morphological parameters. However, the wastewater temperature clearly correlated with floc formation. Results indicated that cold winter conditions enhanced the growth of filamentous bacteria in wastewater, decreasing treatment efficiency. Furthermore, these results confirmed that floc formation has seasonal variations.
“…However, they found that a Microthirx bacterium, which is one of the most common filamentous bacteria, was most abundant in winter, although they did not observe a clear, seasonal variation in the filaments [24]. Graveleau et al [13] found no significant seasonal differences in terms of micro-organism population distribution, although they found a seasonal pattern in SVI values. However, Flowers et al [25] found that temperature was the environmental variable that best correlated with changes in bacteria species and that bacteria species cycled through a predictable, seasonal pattern yearly, which confirms the results of the present study.…”
Section: Discussionmentioning
confidence: 92%
“…In addition, previous studies [13,24,25] have sought to identify seasonal patterns in micro-organism populations.…”
Section: Discussionmentioning
confidence: 99%
“…Some studies have found seasonal variations in ASP, especially in sludge settleability, which is measured mainly as sludge volume index (SVI). For example, Graveleau et al [13], Krult et al [14] and Oerther et al [10] found that average SVI values were higher in winter than in summer. In contrast, Wilén et al [15] and Liwarska-Bizukojc [16] found no seasonal variations in settleability properties when measured as stirred SVI and SVI at municipal wastewater treatment plants (WWTPs).…”
The effect of seasonal variations on floc formation in the activated sludge process (ASP) was studied in a municipal wastewater treatment plant in Finland nearly 16 months. Floc formation was measured with an online optical monitoring device, and results were correlated with the temperature of the upcoming wastewater and the treatment efficiency of the ASP. Results showed that floc formation has a clear, seasonal pattern, with flocs in summer being larger and rounder and having fewer filaments and small particles. In addition, treatment efficiency increased in summer. The study correlated the results of image analysis with the composition (chemical oxygen demand and suspended solids content) and temperature of the wastewater before and after the ASP. Results showed that the composition of upcoming wastewater has no clear correlation with floc morphological parameters. However, the wastewater temperature clearly correlated with floc formation. Results indicated that cold winter conditions enhanced the growth of filamentous bacteria in wastewater, decreasing treatment efficiency. Furthermore, these results confirmed that floc formation has seasonal variations.
“…8,16, 19 En las PTAR el IVL es el indicador determinante de la presencia de bulking con un valor límite de 150 mL/g, no obstante el diseño de las PTAR en países como Francia, por ejemplo, permite valores hasta de 200 mL/g, siendo este el valor considerado en ese país, como el umbral más allá del cual un tanque de sedimentación no puede garantizar la adecuada separación de lodos. 18 La baja concentración de OD fue uno de los parámetros con mayor influencia en la proliferación de bacterias filamentosas, lo cual puede explicarse debido a que este grupo de microorganismos posee mayor superficie/volumen que las bacterias formadoras de floc, proporcionándoles una ventaja en la obtención de oxígeno disponible. Un lodo activado en condiciones normales generalmente tiene un OD igual o mayor a 2 mg/L, niveles que permiten controlar la proliferación de estas bacterias.…”
Introducción
Las plantas de tratamiento de aguas residuales (PTAR), que implementan el proceso de lodos activados presentan problemas de bulking filamentoso. Se ha encontrado que los morfotipos más comunes ligados al fenómeno son: Microthrix parvicella, Thiothrix spp., Nostocoida limicola, Sphaerotilus natans, Tipo 0041 y
Haliscomenobacter hydrossis. La asociación de los parámetros fisicoquímicos en el sistema con la aparición del bulking es di vergente en todos los estudios.
Objetivo
Describir los parámetros físicoquímicos que condicionan la proliferación de morfotipos bacterianos en el fenómeno de bulking filamentoso, mediante el análisis comparativo de diversos estudios a nivel mundial.
Materiales y Métodos
Se hizo una revisión sistemática a partir de artículos de investigación publicados en los últimos 18 años, en las bases de datos Science Direct, Scielo, Web of Knowledge, EBSCO, Wiley, y Springer Link.
Resultados
Se seleccionaron 15 artículos, éstos se organizaron según el tamaño de planta. Se encontró que los parámetros con mayor incidencia en la proliferación de las bacterias filamentosas son: la baja concentración de OD, la baja relación F/M, baja temperatura y el tipo de agua a tratar. Los parámetros indicadores de la presencia de bulking en la mayoría de estudios son el IVL, el IF y los morfotipos filamentosos.
Conclusión
No hay consenso en los valores de los parámetros fisicoquímicos de las PTAR asociados a la proliferación de bacterias filamentosas. Sin embargo, su proliferación puede depender de muchos factores como la entrada masiva desustrato fácilmente asimilable, las bajas temperaturas y disponibilidad de oxígeno disuelto por unidad de carga orgánica.
“…Furthermore, it was measured that, in typical Danish wastewaters, the diluted SVI (DSVI) value of 120 ml/g and above suggests a poorly settling sludge (Mielczarek et al, 2012). Moreover, Graveleau et al (2003) observed bulking at an SVI value of 180 ml/g and above. Some studies assess the total extended filament length (e.g.…”
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