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Inactivation of electoplanting sludge by vitrification
1997
Karlovic, E. | Dalmacija, B. | Kovacevic, S. (Prirodno-matematicki fakultet, Novi Sad (Yugoslavia). Institut za hemiju)
The work is concerned with the possibility of inactivation of galvanic sludge formed in treatment of wastewaters of electroplanting plants by imbedding the waste in a glass material. Glass can be synthesized in contact with the waste by mixing and heating with glass constituents. The efficiency of inactivation was monitored by leaching the obtained materials. The results of leaching tests showed that the highest amount of electroplanting sludge (about 30%) can be inactivated by vitrification of the following mixtures: 26.3% of electoplanting sludge, 43.7% of sand, and 30.0% of Na2CO3 at 1000 deg C; 30% of galvanic sludge, 49% of sand and 21% of Na2CO3 at 1100 deg C.
Show more [+] Less [-]Possibilities and potentials of anaerobic wastewater treatment with emphasis on the UASB-system
1992
Lettinga, G. | Rinzema, A. | Hulshoff Pol, L.W. (Agricultural Univ. of Wageningen (Netherlands). Dept. of Environmental Engineering)
Impact of liquid wastes on surface and groundwater resources and their elimination through proper treatment and reuse
1991
Hartmann, L. (Karlsruhe Univ., Karlsruhe (Germany). Institute for Bioengineering and Technology of Wastewater)
A short historical review shows that treatment plants have been developed only after problems have occurred. The high diversity pollutants of totally different origins and natures, and chemical and biological characteristics require different tools. A good approach is to select one basic tool and try to integrate tools for other tasks within this main tool. The main tool will be in almost every case (for municipal wastewaters) an activated sludge plant surrounded by other elements of polishing or for the elimination of nitrogen, phosphorus, etc., according to the local situation. Some tasks like elimination of pathogens or eggs of intestinal worms, are automatically performed to a high degree in connection with the task of eliminating degradable organics. Special wastewaters with certain pollutants have to be treated at the place of their origins. For wastewater of agricultural production direct or indirect recycling should be favoured. For wastewater of industrial background containing toxicants, treatment must be economically included in the production process of the main product. Besides this, there appears a multitude of organics of unknown chemical composition and environmental significance. They should be permitted for public application only after lab tests have proved their degradability and the conditions of their degradation. Finally, one should always be aware that treatment plants have to be composed according to local conditions. Depending on the amount and composition of wastes, an integration of tool has to be found that not only meets the demands stemming from the wastewaters but also can be integrated into the existing economical and ecological frame
Show more [+] Less [-]Microbiological characterization of the biological treatment of aircraft paint stripping wastewater
1995
Arquiaga, M.C. | Canter, L.W. | Robertson, J.M. (Environmental and Ground Water Institute, University of Oklahoma, Norman, Oklahoma 73019 (USA))
Biological nutrient removal in suspended growth system
1997
Wisjnurapto, IR.
A series of experiments on biological nutrient removal using suspended growth bioreactor with a various reactor configuration have been conducted during the last five years. The first configuration applied a contact stabilization flowed by a denitrification processes in two sludge system. The two sludge systems mean that the aerobic sludge is recirculated in the aerobic circuit, and the anaerobic sludge is recirculated in the anaerobic circuit. The second configuration was conducted in a contact stabilization and denitrification processes in a one sludge system. The one sludge system meant that there are no separation between aerobic and anaerobic sludge; the aerobic and anaerobic processes are in the same circuit and all sludge are recirculated in the same circuit. The third configuration was performed in anaerobic-aerobic-anaerobic reactors and ended by the clarifier to clarify the biosludge before recirculated to the head of the circuit. This configuration was also using a one sludge system. In those three configurations, the hydraulic detention time in the reactors were varied from 2 to 6 hours, and the sludge age from 2 to 15 days. The results showed that the first configuration gave a very high performance in carbon and nitrogen removal. In terms of TOC [total oxygen concentration], the carbon removal achieved up to 92 percent or in terms of total COD [carbon oxygen demand] up to 80 percent, and 97 percent for total nitrogen removal. On the other hand, the phosphorus removal was only limited to the amount required for cells metabolism. More carbon removal were observed in the second configuration (94 percent of total COD) but less total nitrogen were removed (93), however, phosphorus were removed significantly (up to five times of the cells metabolism requirement). The best results in those three nutrients removal was achieved in the third configuration. No less than 95 percent of total COD and 96 percent of nitrogen removal were noticed, and phosphorus were removed at the level of more than six times of the cells metabolism requirement. The experiments concluded that the phosphorus removal was conducted by the aerobic microorganisms which are alternately treated in aerobic-anaerobic conditions. The degree of removal depended on how long the microorganisms were put in the aerobic and anerobic conditions. If the anaerobic condition was too long, the microorganisms would die, and no phosphorus removal took place. If it was too short, the removal would be less. For carbon and nitrogen removals in the system, the hydraulic detention time in the reactors and sludge appeared as the essential parameters in the process
Show more [+] Less [-][Interest and limits of the use of sludges from wastewater treatment in agriculture]
1993
Perrin, D. (Faculte des Sciences Agronomiques de Gembloux (Belgium). Unite de Biologie Vegetale)
Obstacles to the implementation of anaerobic treatment technology for industrial wastewater treatment
1994
Switzenbaum, M.S. (Massachusetts Univ., Amherst (USA). Dept. of Civil and Environmental Engineering)
Filamentous bacteria in Subotica [Serbia] wastewater treatment plant activated sludge
2007
Burger, B.,JKP Vodovod i kanalizacija, Subotica (Serbia) | Reh, Z.,JKP Vodovod i kanalizacija, Subotica (Serbia)
Filamentous bacteria are commonly found in activated sludge. If numerous, they can cause bulking problems. In order to control their number in a system detailed identification of filaments is necessary. In Subotica Wastewater Treatment Plant (WWTP) daily analyses of filamentous bacteria were performed from January 2006 till March 2007. The dominant and constantly abundant was Thiothrix sp. The filaments of Haliscomenobacter hydrosis and Type 1863 were also common (moderately numerous with periods when develop massively). Nostocoida limicola was frequent, but not numerous. Sphaerotilus natans was numerous in some periods when even dominant. Type 1701, Beggiatoa sp. and nocardioform actinomycetes were rarely found and were not abundant.
Show more [+] Less [-]Diagnóstico de la situación actual de la planta de tratamiento de agua residual de la Universidad Autónoma de Occidente
2018
Giraldo García, Katherin | Vásquez Sarria, Nancy
Las plantas de tratamiento de agua residual (PTARs) generan diversos impactos en la sociedad y en el ambiente, mejorando la calidad de vida y la disminución del riesgo sanitario al tener una correcta gestión del agua residual; en este sentido, el conocimiento de las condiciones operacionales del sistema, juega un papel fundamental en los proyectos de mejoramiento y optimización de los sistemas de tratamiento existente. Teniendo en cuenta estos apectos, en este proyecto se realizó un diagnóstico de la situación actual de la planta de tratamiento del agua residual de la Universidad Autónoma de Occidente, con el fin de identificar elementos clave orientados a visualizar oportunidades de mejora en la planta o factores a resaltar en la gestión del agua residual en la Universidad. El estudio consistió en un análisis técnico del sistema de tratamiento en términos de las unidades diseñadas y construidas y las variables de control y operación del sistema de lodos activados. Este análisis permitió establecer, que en términos de condiciones operacionales el sistema es operado como un sistema de lodos activados en la modalidad convencional y en términos de condiciones hidráulicas es operado como un sistema de lodos activados bajo la modalidad de aireación extendida. Del mismo modo se pudo identificar que el sistema se ha venido operando bajo condiciones de sobrecarga hidráulica y orgánica, lo que se ha reflejado en un TRH de 19h en el tanque de aireación y presentando eventos de flotación de lodos; no obstante, se resalta que el sistema ha alcanzado eficiencias de reducción de DBO5, SST y grasas y aceites de 96.6% ± 4.1%, 98.4% ± 3.3% y 95.1% ± 5.2% respectivamente, permitiendo alcanzar los objetivos de calidad en términos de cumplimiento de la normativa para el vertimiento del agua residual sobre una fuente superficial. En términos de las condiciones biológicas del sistema, se realizó un análisis exploratorio de la microbiota presente y se encontró que la biomasa encontrada en el sistema presenta una microbiota típica de sistemas de lodos activados principalmente de protozoos, de los cuales se destaca la presencia de ciliados libres reptantes como Euplotes sp., y ciliados libres nadadores como Paramecium sp. Adicionalmente, se evidenció la presencia de bacterias filamentosas que podrán estar relacionadas con algunos de los eventos de mala sedimentabilidad en el sedimentador secundario | The wastewater treatment plants (WWTP) generate impacts on society and the environment, improving the quality of life and reducing the health risk by having a correct wastewater management; In this sense, the knowledge of the operational conditions of the system plays a fundamental role in the improvement and optimization projects of the existing treatment systems. Taking into account these aspects, in this project a diagnosis was made of the current situation of the Wastewater Treatment Plant of the Autonomous University of the West, in order to identify key elements oriented to the possibility of improving the plant or factors to highlight in the wastewater management in the University. The study consisted of a technical analysis of the treatment system in terms of the units and constructions and the variables of control and operation of the activated sludge system. This analysis is established, that in terms of operational conditions, the system is operated as a sludge system, activated in the conventional mode, and in the terms of the conditions, technical, operational, such as a mud system, activated, in the aeration mode, extended. In the same way, it was identified that the system was operated under the conditions of hydraulic and organic overload, which was reflected in a HRT of 19 hours in the aeration tank and presenting sludge flotation events; nevertheless, it is highlighted that the system has achieved on average efficiency reduction of BOD5, TSS and fats and oils of 96.6% ± 4.1%, 98.4% ± 3.3% and 95.1% ± 5.2% respectively, allowing toreach the quality objectives in terms of compliance with regulations for the discharge of wastewater on a surface source. In terms of the biological conditions of the system, an exploratory analysis of the present microbiota was carried out and it was found that the biomass found in the system presents a typical microbiota of activated sludge systems mainly of protozoa, of which the presence of ciliates stands out free crawlers such as Euplotes sp., and free swimming ciliates such as Paramecium sp. Additionally, the presence of filamentous bacteria that can be found with the events of bad sedimentation in the secondary sedimenter is evidenced. | Pasantía de investigación (Ingeniero Ambiental)- Universidad Autónoma de Occidente, 2018 | Pregrado | Ingeniero(a) Ambiental
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