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Artykuły w czasopismach na temat "Sewage farming"
Dwivedi, Avinash, Mr Anupam Mehrotra i Mr Kamal Nabh Tripathi. "Comparative Study of Different Sewage Farming on Soil Quality". International Journal of Trend in Scientific Research and Development Volume-3, Issue-4 (30.06.2019): 235–38. http://dx.doi.org/10.31142/ijtsrd23701.
Pełny tekst źródłaBalengayabo, Jonas G., Gabriel R. Kassenga, Shabaan M. Mgana i Fredrick Salukele. "Effect of Recurrent Irrigation with Treated Sewage from Anaerobic Digester Coupled with Anaerobic Baffled Reactor on Soil Fertility". International Journal of Environment 11, nr 2 (7.10.2022): 105–23. http://dx.doi.org/10.3126/ije.v11i2.46898.
Pełny tekst źródłaSaber, M. S. M. "Prolonged Effect of Land Disposal of Human Wastes on Soil Conditions". Water Science and Technology 18, nr 7-8 (1.07.1986): 371–74. http://dx.doi.org/10.2166/wst.1986.0310.
Pełny tekst źródłaTiwari, Soni, Prabhash Kumar Pandey, Ranjan Singh, Ajad Patel, Laxmi Kant Pandey, Femina Sobin, Neeraj Khare i in. "Detoxification of Sewage Sludge by Natural Attenuation and its Application as a Fertilizer-A Review". International Journal of Current Microbiology and Applied Sciences 12, nr 4 (10.04.2023): 71–85. http://dx.doi.org/10.20546/ijcmas.2023.1204.008.
Pełny tekst źródłaDwivedi, Avinash, Mr Anupam Mehrotra i Mr Kamal Nabh Tripathi. "Comparative Study of Different Sewage Farming on Soil Quality: A Review". International Journal of Trend in Scientific Research and Development Volume-3, Issue-3 (30.04.2019): 1849–52. http://dx.doi.org/10.31142/ijtsrd21594.
Pełny tekst źródłaRobinson, K. "Volatile emissions from livestock farming and sewage operations". Biological Wastes 28, nr 3 (styczeń 1989): 237. http://dx.doi.org/10.1016/0269-7483(89)90088-8.
Pełny tekst źródłaMoriarty, F. "Volatile emissions from Livestock farming and sewage operations". Environmental Pollution 57, nr 2 (1989): 179. http://dx.doi.org/10.1016/0269-7491(89)90009-2.
Pełny tekst źródłaSheail, John. "Town wastes, agricultural sustainability and Victorian sewage". Urban History 23, nr 2 (sierpień 1996): 189–210. http://dx.doi.org/10.1017/s0963926800011925.
Pełny tekst źródłaKaware, Samrudhi. "A Review of Sensor Application in E-Farming". Turkish Journal of Computer and Mathematics Education (TURCOMAT) 12, nr 11 (10.05.2021): 102–5. http://dx.doi.org/10.17762/turcomat.v12i11.5842.
Pełny tekst źródłaWilliams, Adrian. "Book Review: Volatile Emissions from Livestock Farming and Sewage Operations." Outlook on Agriculture 18, nr 2 (czerwiec 1989): 93. http://dx.doi.org/10.1177/003072708901800213.
Pełny tekst źródłaRozprawy doktorskie na temat "Sewage farming"
Tidåker, Pernilla. "Integrating farming and wastewater management : a system perspective /". Uppsala : Dept. of Biometry and Engineering, Swedish University of Agricultural Sciences, 2007. http://epsilon.slu.se/200785.pdf.
Pełny tekst źródłaRibeiro, Maycon Diego 1988. "Projeto de uma mesa de subirrigação para ambientes protegidos". [s.n.], 2013. http://repositorio.unicamp.br/jspui/handle/REPOSIP/256797.
Pełny tekst źródłaDissertação (mestrado) - Universidade Estadual de Campinas, Faculdade de Engenharia Agrícola
Made available in DSpace on 2018-08-22T21:34:01Z (GMT). No. of bitstreams: 1 Ribeiro_MayconDiego_M.pdf: 3280137 bytes, checksum: 9c253671fd642a329f3232738ee0af37 (MD5) Previous issue date: 2013
Resumo: No cultivo em ambientes protegidos, o uso da irrigação é necessário, requerendo alta frequência e gerando dependência tecnológica do produtor na aplicação de água e fertilizantes. Irrigações inadequadas potencializam problemas, trazendo prejuízos financeiros pela baixa produtividade e desperdício de solução nutritiva (SN) e energia. Adicionalmente, o descarte inadequado desses insumos pode contaminar o solo e, consequentemente, o lençol freático. Estudos mostram que os sistemas de subirrigação têm potencial para obter altas eficiências na irrigação nesses ambientes, principalmente, quando há a recirculação da solução nutritiva. Porém, os equipamentos existentes atualmente no mercado foram desenvolvidos sem critérios de engenharia e produzidos em pequena escala para atender condições específicas de produção resultando em elevado custo inicial. Adicionalmente, a falta de conhecimentos sobre a sua aplicabilidade para diferentes sistemas de produção e sobre recomendações do manejo hídrico e nutricional para culturas distintas, proporciona outra limitação na sua aplicação, desencoraja sua adoção pelos produtores. O projeto e construção de uma mesa de subirrigação utilizando critérios de engenharia, que permitam o reuso da SN e o controle automático do manejo hídrico nutricional para diferentes culturas, disponibilizará um equipamento com potencial para ser inserido no mercado nacional de produção em ambientes protegidos. O objetivo desse trabalho foi projetar uma mesa de subirrigação automatizada com reuso da SN, a partir da aplicação de critérios de projeto de engenharia. Essa pesquisa foi dividida nas seguintes etapas: levantamento de informações sobre sistemas de subirrigação existentes no mercado, avaliação de campo de um sistema em operação, estabelecimento de parâmetros de dimensionamento por simulação, e a construção e avaliação de protótipo de equipamento. Os levantamentos realizados não localizaram fabricantes nacionais de equipamentos de subirrigação, e mostraram que os equipamentos em operação apresentavam projetos desenvolvidos empiricamente e construídos a partir de demanda específica do produtor. O sistema de subirrigação em operação avaliado apresentou baixa eficiência de irrigação e aplicação de água devido a perdas e ao descarte de SN. Os critérios adotados para o projeto da mesa de subirrigação foram ergonômicos e de segurança, funcionalidade e aplicabilidade, a escolha do material construtivo. A aplicação dos critérios adotados possibilitou o estabelecimento das seguintes características da mesa de subirrigação: largura de 1,58 m, comprimento variável, altura da borda de 0,06 m, chapa de poliestireno de alto impacto para a mesa e perfis de alumínio para a estrutura. A variação da combinação da vazão e do diâmetro do orifício de dreno associado ao controle automático do nível da lâmina na mesa de subirrigação atendem as exigências de manejo hídrico de diferentes culturas possibilitam a redução do uso de mão de obra e evita descartes com a recirculação da SN. Os resultados de avaliação da mesa de subirrigação construída permitiram identificar diferentes combinações de manejo associada à variação da altura e tempo de permanência da SN no interior da mesa. Concluiu-se que a mesa de subirrigação construída a partir de critérios de projeto de engenharia, com controle automático da reutilização da SN, tem potencial para ser inserido no mercado de ambiente protegido, tendo a opção de ser empregada em diferentes recipientes de produção, cultura e manejo
Abstract: Irrigation is a mandatory practice in greenhouse production, requiring high frequency and generating farmer technological dependency in water and fertilizers application. Low irrigation efficiencies increase production problems, bringing financial losses due to low yield and nutrient solution (NS) waste and energy cost. Additionally, the unsuitable disposal of these inputs can contaminate the soil and hence, the water resources. Studies showed that subirrigation systems have the potential for high efficiencies in greenhouse irrigation, especially when the recirculation of the nutrient solution is employed. However, subirrigation equipments currently available on the Brazilian market were designed without engineering criteria and produced on a small scale to meet specific production conditions, determining high initial investment cost. Furthermore, the lack of knowledge about its applicability to different production systems and water and nutritional management for distinct crops, provides another restriction in its application, and discourages producers in adopting this system. The design and construction of a subirrigation bench based on engineering criteria, enabling the NS reuse and the automatic control of water and nutrient management for different crops will provide a device with the potential to be introduced in the domestic market of greenhouse production. The objective of this work was to design an automated subirrigation bench with NS reuse, applying the fundamentals of engineering design criteria. This research was divided into the following steps: an information survey on commercial subirrigation systems, a subirrigation system field evaluation, and establishment of parameters for sizing simulation and the construction and evaluation of prototype equipment. The survey results do not tracked national companies that manufacture detailed subirrigation equipment, and shown that equipment found in farm operations was designed and developed empirically and constructed from specific producer demands. The evaluated subirrigation system revealed low values of irrigation and water application efficiencies due to NS losses and frequent disposal. The criteria adopted for the subirrigation bench design were based on ergonomic and safety, functionality and applicability issues, and the manufacture material selection. The implemented design criteria enabled the establishment of the following subirrigation bench features: width 1.58 m, length adjustable, edge height of 0.06 m, high impact polystyrene sheets for the bench frame and aluminum sheets for the supporting structure. The combinations of operation flow rate and drain orifice diameters, associated to the automated level control, allowed to establish water and nutrient management for different crops, reducing manpower needs and avoiding NS disposal due to the recirculated practice. The evaluation results of the assembled subirrigation bench showed that different management combinations can be performed by varying the NS depth and its residence time inside the equipment. It was concluded that the subirrigation bench constructed based on engineering design criteria, with automated management system and NS reuse, has the potential to be introduced in the greenhouse production market, with the option to be implemented to various crops and containers
Mestrado
Agua e Solo
Mestre em Engenharia Agrícola
Mofokeng, Dikonketso Shirley-may. "Analyses of the impacts of bacteriological seepage emanating from pig farming on the natural environment". Diss., 2014. http://hdl.handle.net/10500/19820.
Pełny tekst źródłaEnvironmental Sciences
M. Sc. (Environmental Sciences)
Gardiner, Sharen M. "Risk factors for potentially toxic blue-green cyanobacterial blooms of Microcystis aeruginosa in recycled wastewater intended for agricultural irrigation". Thesis, 2019. http://hdl.handle.net/1959.7/uws:51477.
Pełny tekst źródłaKsiążki na temat "Sewage farming"
C, Nielsen V., Voorburg J. H i L'Hermite P. 1936-, red. Volatile emissions from livestock farming and sewage operations. London: Elsevier Applied Science, 1988.
Znajdź pełny tekst źródłaStevens, Daryl, Jim Kelly, Mike McLaughlin i Murray Unkovich. Growing crops with reclaimed wastewater. Collingwood, Vic: CSIRO Pub., 2006.
Znajdź pełny tekst źródłaYi, Tong-bŏm. Chayon ŭl kkum kkunŭn twikkan. Wyd. 8. Soul-si: Tŭllyŏk, 2000.
Znajdź pełny tekst źródłaOdour prevention and control of organic sludge and livestock farming. London: Elsevier Applied Science Publishers, 1986.
Znajdź pełny tekst źródłaNielsen, V. C., i J. H. Voorburg. Odour Prevention and Control of Organic Sludge and Livestock Farming. Taylor & Francis Group, 1986.
Znajdź pełny tekst źródłaNielsen, V. C., i J. H. Voorburg. Odour Prevention and Control of Organic Sludge and Livestock Farming. Taylor & Francis Group, 1986.
Znajdź pełny tekst źródłaNielsen, V. C., i J. H. Voorburg. Odour Prevention and Control of Organic Sludge and Livestock Farming. Taylor & Francis Group, 2011.
Znajdź pełny tekst źródłaNielsen, V. C., i J. H. Voorburg. Odour Prevention and Control of Organic Sludge and Livestock Farming. Taylor & Francis Group, 1986.
Znajdź pełny tekst źródłaKajitvichyanukul, Puangrat, i Brian D'Arcy, red. Land Use and Water Quality: The Impacts of Diffuse Pollution. IWA Publishing, 2022. http://dx.doi.org/10.2166/9781789061123.
Pełny tekst źródłaCzęści książek na temat "Sewage farming"
Mundoli, Seema, C. S. Dechamma, Madhureema Auddy, Abhiri Sanfui i Harini Nagendra. "A New Imagination for Waste and Water in India’s Peri-Urban Interface". W Water Security, Conflict and Cooperation in Peri-Urban South Asia, 27–43. Cham: Springer International Publishing, 2021. http://dx.doi.org/10.1007/978-3-030-79035-6_2.
Pełny tekst źródłaShenoy, Rashmi S., Prathibha Narayanan i Savithri Bhat. "Emerging Technologies for Separation and Recycle of Phosphorous from Sewage Sludge for Hydroponic Farming System". W Biorefinery for Water and Wastewater Treatment, 249–69. Cham: Springer International Publishing, 2023. http://dx.doi.org/10.1007/978-3-031-20822-5_12.
Pełny tekst źródła"Box 3.3 Sewage and farming in Hubli-Dharwad". W Rural-Urban Interaction in the Developing World, 93–107. Routledge, 2004. http://dx.doi.org/10.4324/9780203646274-20.
Pełny tekst źródła"(3) Commission of the European Communities. COST project 68 ter. Final Reports of the Community COST Concertation Committee. 1983. (4) Department of the Environment/National Water Council Standing Committee on the Disposal of Sewage Sludge. Sewage Sludge Survey 1980 Data. Department of the Environment 1983. (5) Anaerobic digestion of Sewage Sludge and Organic Agricultural Waste. Proceedings of a COST 681 Workshop held in Athens May 1984. (In the Press). (6) EIKUM, A.S., and BERG, N. Odour characterisation and removal of odours from facilities receiving septage. To be published in Review Papers on Sewage Sludge Processing, 1985. Commission of the European Communities, Brussels." W Odour Prevention and Control of Organic Sludge and Livestock Farming, 21–49. CRC Press, 1986. http://dx.doi.org/10.1201/9781482286311-15.
Pełny tekst źródła"COST 68 bis was more extensive in scope than the initial project since it covered both treatment and use of sewage sludge. This meant that the topics included both the engineering and economics aspects of sludge processing at sewage works and the environmental aspects of sludge disposal particularly in regard to its utilisation as a fertilizer in agriculture. The use of sewage sludge in this way is important in most countries and it was recognised that co-ordinated research was desirable into both the possible adverse environmental effects of heavy metals and pathogens in sludges and the beneficial effects of plant nutrients in sludge. The problem of odour nuisance arising from the handling and spreading of sewage sludge was also recognised as an important subject-area for research. Under COST 68 bis, five Working Parties were established to co-ordinate the various areas of research. As a 'Concerted Action1, no direct funding was available from the European Commission to finance research projects on sewage sludge, each country being expected to contribute its own publicly-funded projects to the common ’pool*. COST 68 bis ran from 1977 to 1980(2) and was followed by an extension programme - COST 68 ter - which ran from 1981 to 1983(3). In 1983, it was decided to further extend this Concerted Action but to widen the range of research topics in the scientific programme to include animal manures. The renewed programme was designated COST Project 681 'Treatment and Use of Organic Sludges and Liquid Agricultural Wastes'. It is obvious that sewage sludges and farm manures have many aspects in common particularly with regard to handling and treatment techniques and to the environmental impact (e.g. odour) which can occur from their utilisation on land. On the other hand, from the administrative point of view, sewage sludge and farm manures are in two different 'worlds'. Sewage sludge is the general responsibility of public authorities while responsibility for disposing of animal manures belong mainly to the private farming sector. Funding for research on the two types of waste, even if from Government sources, is usually from different Departments and there is little cross-involvement of research scientists in the two sectors. Nonetheless, the COST 681 activity is attempting to promote some co-ordination of effort between the two research areas and, hopefully, this will result in mutual benefit to both those authorities responsible for sewage sludge treatment and those concerned with farm manures and their disposal. This joint Workshop on 'odours' is a good example of the type of co-operation, and sharing of information on a common problem, which can be of great mutual benefit to both sectors. PARTICIPATING COUNTRIES". W Odour Prevention and Control of Organic Sludge and Livestock Farming, 17. CRC Press, 1986. http://dx.doi.org/10.1201/9781482286311-11.
Pełny tekst źródła"different aspects of slurry disposal, for example, spreading, and odour from land after spreading. Correlation work to establish which fractions are best remains to be done, and will probably involve chemical analysis. It is clear then, that the concept of Odour Potential of a sludge or slurry can be a useful tool not only to the odour specialist but also to the operators of sewage treatment works and agricultural slurry handling facilities in minimising the nuisance from the disposal of sludges. (1 j GILLARD, F. ’Measurements of odours by dynamic olfactometry; application to the steel and carbonisation industries." Paper presented at internation symposium: Characterisation and control of odoriferous pollutants in process industries, Belgian Filtration Society, Louvain-La-Neuve, April 1984. (2) TOOGOOD, S. J., and HOBSON, J.A. ’The Discharge of Volatile M rials to Sewers", Water Research Centre, Technical Report TR142, England, 1979. (5) Commission of European Communities, ’The use of Sewage Sludge in Agriculture’, Draft Directive, November 1981. (6) HURLEY, B. J., and RACHWAL, A. J. "Reducing Sludge Volune" Effluent and Water Treatment Journal, 21» 292-296, 1981." W Odour Prevention and Control of Organic Sludge and Livestock Farming, 154. CRC Press, 1986. http://dx.doi.org/10.1201/9781482286311-66.
Pełny tekst źródłavan Santen, Rutger, Djan Khoe i Bram Vermeer. "Water for Life". W 2030. Oxford University Press, 2010. http://dx.doi.org/10.1093/oso/9780195377170.003.0008.
Pełny tekst źródła"In any case, covering may be impracticable for other reasons. Many processes as they are currently designed depend upon at least visual access by operators for process control, and in other instances the production of odorous chemicals such as hydrogen sulphide can be accompanied by the formation of methane, giving a potential fire or explosion hazard. 1.1.1. Odours .from the Spreading of Sludge and Slurries on Land The chimney, originally devised to increase draught through fires and to provide smoke extraction, has found extensive use in many industries to aid the dispersion of odour. The extra height gained by the point of emission is frequently enough to give the extra dilution required to reduce the risk of odour nuisance at even relatively nearby properties. This is an option that is not open to the farmer or the sewage works operator. The cost and practicability of enclosing the processes used in sewage treatment varies considerably, but in the disposal of sludge or animal slurries to land there is never a realistic option that the dispersion of odours once transferred to the gas phase might be effectively controlled. For the prevention of nuisance therefore there are two possibili ties. First, the formation or release of odorous chemical species can be discouraged. In practice this usually means the prevention of reducing conditions (negative redox potential) and possibly the prior removal of certain key compounds. Second, the time of contact between the sludge/ slurry and the air can be reduced, for example by ploughing in or sub-surface injection, and the act of spreading can be timed to coincide with favourable atmospheric conditions. These two approaches can of course be used in combination. Both approaches naturally add to the cost of sludge disposal, and for the sewage works manager add to the risk that farmers might be less willing to accept sludge to land, causing a greater problem still. For the fanner, sewage sludge can be a useful source of cheap nitrogen, though of unspecified strength, and also of much needed soil structure, but the imposition of no-grazing periods after application can add to the cost taken as a whole. A further problem, especially for farmers with arable crops is that the demand for soil nutrients and the practicability of spreading and ploughing in are seasonal, whereas a sludge and slurry are produced at a more or less constant rate. In the case of slurries, seme form of storage is inevitable, and commonly takes place in open pits. Scxne digestion and therefore stabilisation takes place during storage, reducing the capacity of the slurry to cause odour nuisance, and as long as the surface crust is not disturbed, little odour results. It is the emptying of slurry pits that gives rise to the release of odour. 2. P rin ciple, Sources, of Odour at .^ weg e .lreatment Works". W Odour Prevention and Control of Organic Sludge and Livestock Farming, 146. CRC Press, 1986. http://dx.doi.org/10.1201/9781482286311-58.
Pełny tekst źródła"the panel leader on a panel of light in a separate signal box. The panel leader records the judgements and calculates by Beans of a statistical procedure, the averaged panel value termed E D . This term denotes Effective £osage at the 50 percent level, i.e. thlt dilution level at which 50 percent of the panel would and 50 percent would not detect odour of the diluted sample. The dilution is denoted by the dilution factor. For instance: ED = 1000 means that one litre of the odorous air must be diluted with 1000 litres of non-dodrous air to reach the panel threshold termed ED . With the olfactometer in use it is possible to measure dilutions between approximately 10x up to approximately 30.000x. 3. APPLICATIONS In general the main sources of odour emission in Norway are fish meal plants, pulp and paper mills, and plants for the treatment of sewage sludge and waste water. Investigations have been carried out in these and other branches of the industry, i.e. the food industry. Each case may provide features which influence the olfactometric measurements, often demanding special sampling techniques and inter pretations. In the following some of the problems and experiences will be pointed out by means of examples from sewage treatment and fish meal plants, showing the use of olfactometry for obtaining satisfactory odour reducing results. A couple of years ago an investigation was carried out to evaluate the efficiency of odour reducing processes based on different principles, such as chemical scrubbers, soil bed filters, activated carbon filters, iron oxide filters, and combustion. Samples for the olfactometric measurements were taken in different positions in the installations and the odour reducing efficiency was calculated as the ratio between the recorded ED value at the outlet and inlet of the purification steps: nfilter:". W Odour Prevention and Control of Organic Sludge and Livestock Farming, 96. CRC Press, 1986. http://dx.doi.org/10.1201/9781482286311-32.
Pełny tekst źródła"parameters, efforts can be made to improve odour reducing processes within their limitations. Better odour reducing efficiency can be obtained by appropriate management of the process, and energy costs may be reduced by discriminative venting of process operations contributing with high concentrations of odorous compounds. However, attention must be paid to the sampling procedures in processes involving high temperatures and high degrees of humidity. Measurements indicate that such conditions may influence on ED values to some extent. REFFERENCES (1) DRAVNIEKS, A. and PROKOP, W.H. (1973). Source emission odour measurement by a dynamic forced choice triangle olfactometer. Air Poll. Control Assoc. Paper, 73-276. (2) PETTIT, C.G. (1959). 20 years of sewage sludge burning at Barberton, Ohio. J. San. Eng. Div. Amer. Soc. Civil Engr. 85SA6, 17. (3) LABOON, J.F. (1961). Construction and operation of the Pittsburgh project. J. Water. Poll. Control Fed. 33, 758." W Odour Prevention and Control of Organic Sludge and Livestock Farming, 99–111. CRC Press, 1986. http://dx.doi.org/10.1201/9781482286311-35.
Pełny tekst źródłaStreszczenia konferencji na temat "Sewage farming"
Kuusik, Argo, Karin Pachel, Aare Kuusik i Enn Loigu. "Anaerobic co-digestion of sewage sludge with fish farming waste". W The 9th International Conference "Environmental Engineering 2014". Vilnius, Lithuania: Vilnius Gediminas Technical University Press “Technika” 2014, 2014. http://dx.doi.org/10.3846/enviro.2014.084.
Pełny tekst źródłaKEMESIUS, Martynas, Gerda SILINGIENE, Regina VASINAUSKIENE i Remigijus ZALKAUSKAS. "THE INFLUENCE OF SEWAGE SLUDGE ON NORWAY SPRUCE (PICEA ABIES (L.) H. KARST.) SEEDLINGS GROWTH". W Rural Development 2015. Aleksandras Stulginskis University, 2015. http://dx.doi.org/10.15544/rd.2015.079.
Pełny tekst źródłaHuppmann, Gerhard. "The MTU Carbonate Fuel Cell HotModule®: Utilization of Biomass and Waste Originated Fuels for Polygeneration in Fuel Cells". W ASME 2006 4th International Conference on Fuel Cell Science, Engineering and Technology. ASMEDC, 2006. http://dx.doi.org/10.1115/fuelcell2006-97120.
Pełny tekst źródłaCauduro, Ma´rcia. "Plan of Communications and Relationship With Third Parties for the Bolivia-Brazil Pipeline Right-of-Way". W 2010 8th International Pipeline Conference. ASMEDC, 2010. http://dx.doi.org/10.1115/ipc2010-31603.
Pełny tekst źródłaBonchkovskyi, Andrii. "Assessment of anthropogenic pressure by nutrients and organic substances in the Sula river basin". W International Conference of Young Scientists on Meteorology, Hydrology and Environmental Monitoring. Ukrainian Hydrometeorological Institute, 2023. http://dx.doi.org/10.15407/icys-mhem.2023.029.
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