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Artykuły w czasopismach na temat "ODOUR PROBLEM"
Calafat, Consuelo, i Aurea Gallego-Salguero. "Livestock odour dispersion and its implications for rural tourism: case study of Valencian Community (Spain)". Spanish Journal of Agricultural Research 18, nr 2 (10.06.2020): e0106. http://dx.doi.org/10.5424/sjar/2020182-15819.
Pełny tekst źródłaGrzelka, Agnieszka, Elżbieta Romanik i Urszula Miller. "Odour nuisance assessment of the food industry wastewater treatment plant". E3S Web of Conferences 100 (2019): 00024. http://dx.doi.org/10.1051/e3sconf/201910000024.
Pełny tekst źródłaBoth, R. "Directive on odour in ambient air: an established system of odour measurement and odour regulation in Germany". Water Science and Technology 44, nr 9 (1.11.2001): 119–26. http://dx.doi.org/10.2166/wst.2001.0521.
Pełny tekst źródładu Toit, A. J. "Quantification of Odour Problems Associated with Liquid and Solid Feedlot and Poultry Wastes". Water Science and Technology 19, nr 1-2 (1.01.1987): 31–41. http://dx.doi.org/10.2166/wst.1987.0186.
Pełny tekst źródłaMužniece-Treija, Evita. "ODOUR STUDY WITH QUALITATIVE AND QUANTITATIVE RESEARCH METHODS IN VARIOUS DISTRICTS OF RIGA". Environment. Technology. Resources. Proceedings of the International Scientific and Practical Conference 1 (15.06.2017): 192. http://dx.doi.org/10.17770/etr2017vol1.2643.
Pełny tekst źródłaHanková, M., K. Maturová i H. Čížková. "GC-MS/O for the characterization of odours from cheese-production wastewater: A case study". Water Science and Technology 82, nr 11 (27.10.2020): 2482–90. http://dx.doi.org/10.2166/wst.2020.513.
Pełny tekst źródłaWaldrop, Lindsay D., Laura A. Miller i Shilpa Khatri. "A tale of two antennules: the performance of crab odour-capture organs in air and water". Journal of The Royal Society Interface 13, nr 125 (grudzień 2016): 20160615. http://dx.doi.org/10.1098/rsif.2016.0615.
Pełny tekst źródłaVasarevičius, Saulius, i Tadas Batavičius. "Experimental Tests on the Influence of Waste Covering Layer on Odour Reduction". Ecological Chemistry and Engineering S 20, nr 3 (1.09.2013): 543–54. http://dx.doi.org/10.2478/eces-2013-0032.
Pełny tekst źródłaSzulczyński, Bartosz, i Jacek Gębicki. "Electronic nose – an instrument for odour nuisances monitoring". E3S Web of Conferences 100 (2019): 00079. http://dx.doi.org/10.1051/e3sconf/201910000079.
Pełny tekst źródłaGostelow, P., S. A. Parsons i M. Lovell. "Integrated odour modelling for sewage treatment works". Water Science and Technology 50, nr 4 (1.08.2004): 169–76. http://dx.doi.org/10.2166/wst.2004.0253.
Pełny tekst źródłaRozprawy doktorskie na temat "ODOUR PROBLEM"
Dawes, C. A. "Odour pollution problems within the district of the Wrekin Council". Thesis, Aston University, 1987. http://publications.aston.ac.uk/9699/.
Pełny tekst źródłaWoodfield, Ria. "Management and control of taste and odour problems associated with geosmin and 2-methylisoborneol in drinking water supplies". Thesis, University of Bristol, 2014. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.685972.
Pełny tekst źródłaWiesenthal, Karina Edwardovna. "The effect of pipe materials on taste and odor problems in drinking water distribution systems". Diss., Restricted to subscribing institutions, 2006. http://proquest.umi.com/pqdweb?did=1273124431&sid=1&Fmt=2&clientId=1564&RQT=309&VName=PQD.
Pełny tekst źródłaSilva, Alcione Batista da. "Avaliação da produção de odor na estação de tratamento de esgoto Paranoá e seus problemas associados". reponame:Repositório Institucional da UnB, 2007. http://repositorio.unb.br/handle/10482/2290.
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No Distrito Federal vêm ocorrendo problemas de emanações de odores provenientes de estações de tratamento de esgotos (ETE). Por essa razão, este trabalho tem por objetivo avaliar a produção de odor na ETE Paranoá (composta de reatores anaeróbios e lagoas de estabilizações), Distrito Federal, e os seus problemas associados, analisando o sulfeto de hidrogênio (H2S) como indicador do mau cheiro. Para isso, utilizou-se um procedimento composto pelas seguintes ações: (1) determinações analíticas na fase líquida (pH, temperatura, condutividade elétrica, sulfeto total, sulfeto de hidrogênio, sulfato, enxofre elementar, oxigênio dissolvido, DQO e DBO); (2) determinação na fase gasosa do H2S através de um sensor específico; (3) determinação da carga de emissão de H2S utilizando como ferramenta um modelo matemático de emissão de odor; e (4) aplicação de questionários na área circunvizinha à ETE Paranoá. A concentração de H2S variou com relação aos horários de coleta, apresentando os valores máximos de 9,30, 14,87 e 5,81 mg/L (manhã, tarde e noite) no efluente do reator anaeróbio. Essa variabilidade na concentração de H2S é creditada, principalmente, às variáveis externas (temperatura, pH, teor de enxofre, potencial redox, etc.) e ao próprio processo de tratamento. No que diz respeito à concentração de H2S emitido para a atmosfera, próxima ao local da saída do efluente do reator anaeróbio, ficou sempre acima do limiar de odor de 0,0005 mg/L. As cargas emitidas de H2S para a atmosfera no tratamento preliminar, no reator anaeróbio, e na lagoa foram de 0,03 g/s; 0,30 g/s e 0,45 g/s (observadas) e de 0,05 g/s, 0,04 g/s e 0,38 g/s (preditas pelo modelo de emissão), respectivamente. Os parâmetros sulfato e DQO revelaram-se bons indicadores da redução do sulfato a sulfeto. Verificou-se a formação de sulfeto via redução dissimilatória de sulfato nas lagoas durante a noite, pois, na maioria do tempo, obteve-se baixa concentração de oxigênio dissolvido nessas lagoas (0,1 a 1,0 mg/L). Observou-se que ocorreu percepção de odor pelos habitantes circunvizinhos à ETE, com decorrente insatisfação, uma vez que 78% das pessoas entrevistadas sentem o mau cheiro proveniente da ETE e 60% disseram que a intensidade do odor é muito forte. Concluiu-se que houve formação de H2S no reator anaeróbio e redução de H2S no tratamento preliminar e na lagoa. __________________________________________________________________________________________ ABSTRACT
The Federal District of Brazil has been suffering problems of emanations of odors proceeding from sewage treatment plants (STP). For this reason, this work has the objective of evaluating the production of odor in the Paranoá sewage treatment plant (Paranoá STP), in Federal District, and its associated problems, employing hydrogen sulfide (H2S) as an indicator of mal odor. In order to doing this, we used a procedure composed of the following actions: (1) analytical determinations in the liquid phase (pH, temperature, electric conductivity, total sulfide, hydrogen of sulfide, sulfate, elementary sulphur, DO, COD and BOD); (2) determination of the H2S concentrations in the gaseous phase through a specific sensor; (3) determination of the H2S emission rates using a mathematical model for odor emission and (4) application of questionnaires in the surrounding area of the Paranoá STP. The H2S concentration presented variability with regard to the collection schedules, presenting maximum values of 9,30, 14,87 and 5.81 mg/L (morning, late and night) in the anaerobic reactor effluent. This variability in the H2S concentration is credited, mainly, to the external variable (temperature, pH, sulphur concentration, potential redox, etc.) and to the proper process of treatment. The concentration of H2S emitted for the atmosphere next to the place of the exit of the anaerobic reactor effluent was always above of the threshold of odor of 0,0005 mg/L. The emitted loads of H2S for the atmosphere in the preliminary treatment, in the anaerobic reactor, and in the lagoon had been of 0,03 g/s; 0,30 g/s and 0,45 g/s (observed) and of 0,05 g/s, 0,04 g/s and 0,38 g/s (predicted by the emission model), respectively. Sulphate and DQO had shown to be good pointers of the reduction of sulphate to sulfide. Sulfide formation by dissimilatory sulphate reduction was verified in the lagoons during the night, since concentrations of oxygen dissolved in these lagoons were low along the majority of the time, (0.1 to 1,0 mg/L). It was observed that perception of odor for the surrounding inhabitants to the STP occurred, with consequent non-satisfaction, since 78% of the interviewed people felt the bad smell proceeding from the STP and 60% had said that the odor intensity was very strong. It was possible to conclude that H2S was formed in the anaerobic reactor and that H2S reduction occurred in the preliminary treatment and in the lagoon.
Anselme, Christophe. "Etude et caracterisation des problemes de mauvais gout de l'eau potable". Paris 7, 1987. http://www.theses.fr/1987PA077178.
Pełny tekst źródłaMALLERET, LAURE. "Developpement d'outils analytiques pour l'analyse de traces des composes responsables des problemes de gout et odeur de terre/moisi de l'eau potable". Paris 6, 2001. http://www.theses.fr/2001PA066156.
Pełny tekst źródłaSINGH, RAJENDRA PRATAP. "ODOUR PROBLEM IN FLEXIBLE PACKAGING MATERIALS". Thesis, 2012. http://dspace.dtu.ac.in:8080/jspui/handle/repository/14167.
Pełny tekst źródłaSun, Chih-Yuan, i 孫至遠. "A study on improving odor problem in a solar cell factory". Thesis, 2016. http://ndltd.ncl.edu.tw/handle/33104366272311381864.
Pełny tekst źródła國立交通大學
工學院產業安全與防災學程
104
The purpose of this study is to investigate how to resolve the odor generated from solar cell manufacturing process. From the air sampling analysis result, it was known beforehand that the concentrations of Acetaldehyde and Isopropyl Alcohol are among the highest of all volatile organic compounds utilized in the factory. Based on this finding we observed, measured and designed experiments on how they were used in the manufacturing flow and how the odor was released. Firstly, the environmental airborne Volatile Organic Compound was measured using a Photo Ionization Detector (PID) at the printing area and at the Fast Firing Furnace area. Next, we measured air flow in the exhaust duct with a wind speed anemometer. Finally a survey was carried out in the factory to try to locate odor source. The wind speed anemometer measurement matched well with the specification of the original exhaust duct design. The PID detected 0 ppm of airborne VOC concentration inside the printing station and the surrounding area, 1.5 ppm at the Fast Firing Furnace and 5 ppm in the surrounding area. This measurement result consists with what the survey reported of strong odor found near the Fast Firing Furnace area. We concluded this is where the odor was released. The following experiments were designed in order to resolve the odor releasing issue at Fast Firing Furnace including (1) Extend the opened exhaust duct to the platform exhaust outlet. (2) Set up a PVC curtain to enable environment exhaust. (3) Replace the opened exhaust duct by a closed exhaust system. The experiment results showed that "(3) closed exhaust system" is the most effective method for which the airborne VOC concentrations were reduced from 5 ppm to 0.5 ppm. A follow-up survey also confirmed that the odor smell was reduced to a detectable level.
"Problems of industrial odours in western Enfield - towards an effective response by Enfield Council". Title page, contents and abstract only, 1995. http://web4.library.adelaide.edu.au/theses/09ENV/09envr863.pdf.
Pełny tekst źródłaKsiążki na temat "ODOUR PROBLEM"
Dawes, Christopher Allan. Odour pollution problems within the district of the Wrekin council. Birmingham: Aston University. Department of Chemical Engineering and Applied Chemistry, 1987.
Znajdź pełny tekst źródłaDietrich, Andrea M. Taste-and-odor problems associated with chlorine dioxide. Denver, CO: The Foundation, 1991.
Znajdź pełny tekst źródłaAssociation, American Water Works, red. Diagnosing taste and odor problems: Source water and treatment field guide. Denver, CO: American Water Works Association, 2011.
Znajdź pełny tekst źródłaMueller, David K. Limnological characteristics, nutrient loading and limitation, and potential sources of taste and odor problems in Standley Lake Colorado. Denver, Colo: U.S. Dept. of the Interior, U.S. Geological Survey, 1993.
Znajdź pełny tekst źródłaColor, taste and odor problems in drinking water. [Olympia, Wash.]: Washington State Dept. of Health, Environmental Health Programs, Division of Drinking Water, 2005.
Znajdź pełny tekst źródłaGrocott, Patricia, Georgina Gethin i Sebastian Probst. Skin problems in palliative care. Oxford University Press, 2015. http://dx.doi.org/10.1093/med/9780199656097.003.0111.
Pełny tekst źródłaCraufurd, David, i Julie S. Snowden. Neuropsychiatry and Neuropsychology. Oxford University Press, 2014. http://dx.doi.org/10.1093/med/9780199929146.003.0003.
Pełny tekst źródłaand, Bruno. Object Perception and Recognition. Oxford University Press, 2018. http://dx.doi.org/10.1093/oso/9780198725022.003.0004.
Pełny tekst źródłaCzęści książek na temat "ODOUR PROBLEM"
Olsson, Liselott Mariett. "The Odour of a False Problem". W Becoming Pedagogue, 31–57. London: Routledge, 2023. http://dx.doi.org/10.4324/9781315461779-3.
Pełny tekst źródłaSuffet, I. H., D. Khiari i J. Mallevialle. "Taste and odor problems in drinking water". W Food Taints and Off-Flavours, 107–38. Boston, MA: Springer US, 1996. http://dx.doi.org/10.1007/978-1-4615-2151-8_4.
Pełny tekst źródłaKüppers, Stephan, Tim aus der Beek, Wenhai Chu, Bingzhi Dong, Anna Dahlhaus, Henner Hollert, Jianliang Hua i in. "Fostering Water Treatment in Eutrophic Areas: Innovative Water Quality Monitoring, and Technologies Mitigating Taste & Odor Problems Demonstrated at Tai Hu". W Future City, 91–110. Cham: Springer International Publishing, 2019. http://dx.doi.org/10.1007/978-3-030-01488-9_5.
Pełny tekst źródłaMahat, Nor Idayu, Maz Jamilah Masnan, Ali Yeon Md Shakaff, Ammar Zakaria i Muhd Khairulzaman Abdul Kadir. "Artificial Odour Classification System". W Electronic Nose Technologies and Advances in Machine Olfaction, 25–37. IGI Global, 2018. http://dx.doi.org/10.4018/978-1-5225-3862-2.ch002.
Pełny tekst źródła"complaints or problems relating to disposal of sewage sludge to land were related to odour nuisance. Table 1. Summary of complaints or problems relating to disposal of sewage sludge to land in the UK (1980 data)(^) Type of problem Per cent occurrence Environmental nuisance (smell) 60 Transport 19 Water Pollution 10 Agricultural 5 Metals 4 Veterinary 1 Planning consent 1 100 It is clear from this that odour nuisance is an important problem and it follows that standard methods of scientifically measuring odours are desirable. ACHYHX Iff QQ2I M l . SUBdGTOUP .r.OBMBS' This sub group was established in 1984 as part of the activity of Working Party 1 but drawing on experts from outside the Working Party. The Chairman is Mr J H Voorburg of the Netherlands and other experts in odours include Dr M Hangartner (QD, Dr J Hartung (D), Dr A Eikun (No) and Mr V C Nielsen (UK). Mr H M Scheltinga (NL) and A M Bruce (UK) are also members of the group. The sub-group is hoping to complete its tasks quickly, the main ones being (a) To develop proposals for a harmonised and standardised odour measurement technique (b) To exchange information about research on odour measurement and control. On (a) good progress has been made in collecting information on the existing guidelines in different countries for sampling and transportation of samples for odour measurement, for dilution techniques and for panel selection etc. The question of acceptable levels of odour intensity is net being considered. All these matters will be discussed at this joint Workshop and it is hoped that clear recommendations will emerge from the experts so that a formal report can be presented for discussion at the COST 681 4th Symposium to be held in Rome in October 1985. In regard to objective (b), one of the major tasks of the sub-group has been to compile an inventory of organisations and scientists in Europe who are actively involved in research on the measurement and/or". W Odour Prevention and Control of Organic Sludge and Livestock Farming, 19. CRC Press, 1986. http://dx.doi.org/10.1201/9781482286311-13.
Pełny tekst źródła"The physical condition is checked by the panel leader using a question naire or simply by asking the test persons according to the guidelines of Germany and the United Kingdom. Only the German guideline tests reli ability of panel members by repeated measurements with the same odorant. Problems of honesty are minimized by forced choice technique (France, Netherlands). In the German guideline persons with more than 20% of errors in more than three test series are excluded. 5.2 Panel size The extent to which a panel constitutes a representative sample of the population depends directly on the numbers of panel members. For practical reasons a cxxrpromise must be sought between costs and the representative ness of the result, and this depends on the question to be answered: basic measurement e.g. emission standards or only comparative measurements, e.g. odor abatement efficiency. Nether Germany United France lands Kingdom basic measure 8-15 10 6-86-8 ments comparative measurements > 4 Table 5: Panel size. 6. CCECLUSICNS - There is more or less agreement in all guidelines about general back ground conditions. - The limit method is proposed as detection method in all guidelines. The indication of response is either yes/no or correct/incorrect. The latter, forced choice technique, may certainly give lower odor thres holds. - The mathematical treatment of data will produce only slight differences in the threshold values. - For the panel size different members are given. 8 people appears the right size for the panel. - Selection of panelists is the most difficult question and large varia tions of threshold data are expected due to this problem. No generally accepted procedure exists and only vague recanmendations are given in the guidelines. A possible solution will be the evaluation of the sensi tivity distribution of a large panel (>25) of the actual odor to be tested, and screening the panel members according to their position in the distribution. However, this procedure might not be suitable in practice." W Odour Prevention and Control of Organic Sludge and Livestock Farming, 74. CRC Press, 1986. http://dx.doi.org/10.1201/9781482286311-28.
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"DISPERSION MODELS FOR EMISSIONS FROM AGRICULTURAL SOURCES G.-J. MEJER and K.-H. KRAUSE Institut fiir landtechnische Grundlagenforschung der Bundesforschungsanstalt fiir Landwirtschaft Summary The aim of dispersion models is the prediction of atmospheric dilution of pollutants in order to prevent or avoid nuisance. Established dispersion models, designed for the large scale of industrial air pol lution have to be modified to the small scale of agricultural pol lutions. An experimental setup is described to measure atmospheric dilution of tracer gas under agricultural conditions. The experimental results deliver the data base to identify the parameters of the models. For undisturbed airflow modified Gaussian models are applicable. For the consideration of obstacles more sophisticated models are necessary. 1. INTRODUCTION The aim of dispersion models is to develop reliable methods for calcu lating the atmospheric dilution of airborne pollutants under practical conditions. One application in agriculture is the determination of that distance, at which i.g. odouriferous pollutants of an animal farm are diluted in the atmosphere to a concentration below a certain threshold, in order to allow the farmer a profitable production and likewise to prevent odour nuisance from the neighbourhood. Another application is the prediction of the effectiveness of changes in the emission source configuration, in order to reduce the odour nuisance in the existent vicinity. That could help to avoid expensive misinvestments. In air pollution control it is useful! to subdivide this large problem into three main divisions /1/, fig. 1:". W Odour Prevention and Control of Organic Sludge and Livestock Farming, 113. CRC Press, 1986. http://dx.doi.org/10.1201/9781482286311-37.
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"be detected specifically, which is possible for sane groups of odorants (thiols or mercaptans, sulphides, amines) with specific GC-detectors. Spe cific detectors are available for haloganted compounds, sulphur-, phosphor-and nitrogen compounds. Figure 4 shews the analysis of the sulphur-ccmpounds produced by the acidic decomposition of phosphate-rock and causing the typi cal smell of fertilizer plants. Another approach is to aim at selective concentration methods. Indeed odour problems are caused by a limited number of compounds, on rather a li mited number of classes of compounds, mentioned in figure 5. For most odour nuisance problems, chemical plants, refineries, live stock production, food processing, rendering, water purification plants etc., the compounds responsible for the odour are known. So chemical analysis of the odour can be limited to these odorants, and selective concentrating techniques can be used. Selective concentrating methods are based on speci fic absorption techniques, using particular chemical reactions of odorant classes. Semet imes several absorption methods have to be used in order to describe the odour problem, thus increasing the labor cost of the analysis. On the other hand absorption methods allow better quantitative results. Se lective absorption of odorants from air produces a far less complex mixture. We developed or are developing several of these methods for aldehydes, amines, acids, thiols etc. Carbonyl ccnpounds for instance can be trapped by absorption in a rea gent solution containing 2,4-dinitrcphenylhydrazine and hydrogen chloride. Details of this method are extensively described elsewhere (8). The prin ciple of the method is that the carbonyl ccnpounds, in case of rendering plant emission the aldehydes, react with the 2,4-dinitrophenylhydrazine and form 2,4-dinitrophenylhydrazones (2,4-DNPH's) according to the scheme. These 2,4-dinitrophenylhydrazones have seme interesting properties. It are cristalline caipounds so that after extract of the 2,4-DNPH's fran the reagens, they can be concentrated by evaporation of the solvent without losing product. Besides these caipounds shown intense absorption of UV-light (X 356 nm) and so they can easily be detected with an UV-detec-tor. These properties make the 2,4-DNPH's particularly suitable for HPDC-analyse. This methods is used since seme time. A chranatogram is given in figure 6 and results of the quantitative determination of carbonyl com pounds in different situations are given in table 2. For amines absorption in an acid solution, or preferably adsorption onto an acid ion exchange column (acidified divinylbenzene-styrenesulfo-nic acid copolymer) is used. 10-50 1 of ambient air is sent over*a wet 100nnix3irmI.D. column; the ion exchange polymer is put into a vial, made alkaline and the water solution is analysed on packed Carbowax-KDH GC-column with a thermionic selective detector (TSD), which is specific for nitrogen- and phosphorus-catpounds. Trimethylamine is detected easi ly at 1 ppb. Aibids can be absorbed specifically in an alkaline impringer, which is extracted with ether after acidification to pH 2. This method was used for rendering plant emissions, shewing a series of linear and branched". W Odour Prevention and Control of Organic Sludge and Livestock Farming, 170. CRC Press, 1986. http://dx.doi.org/10.1201/9781482286311-76.
Pełny tekst źródłaStreszczenia konferencji na temat "ODOUR PROBLEM"
Ale, B. J. M., i M. A. Piers. "The Use of Risk Information for the Development of a Safety Policy Around an Airport". W ASME 2000 International Mechanical Engineering Congress and Exposition. American Society of Mechanical Engineers, 2000. http://dx.doi.org/10.1115/imece2000-1022.
Pełny tekst źródłaHou, Linzao, Jun Zhang, Mian Li i Ruixiang Zheng. "Modeling Odor Optimization of Vehicles Based on Data-Driven Goal Programming". W ASME 2020 International Mechanical Engineering Congress and Exposition. American Society of Mechanical Engineers, 2020. http://dx.doi.org/10.1115/imece2020-23519.
Pełny tekst źródłaRamkumar, S. "A Research on Partial Replacement of Fine Aggregate by Waste Foundry Sand". W Sustainable Materials and Smart Practices. Materials Research Forum LLC, 2022. http://dx.doi.org/10.21741/9781644901953-20.
Pełny tekst źródłaAyhan, T., M. K. Muezzinoglu, A. Vergara i M. E. Yalcin. "Using a cellular neural network based olfactory bulb model for choosing the best sensor temperature for an odor classification problem". W 2010 IEEE 18th Signal Processing and Communications Applications Conference (SIU). IEEE, 2010. http://dx.doi.org/10.1109/siu.2010.5653934.
Pełny tekst źródłaShih, Chien-Jen, Keith E. Forrester i Wen-Bin Fan. "Application of Dry Chemical Stabilization Technology in Taiwan Kobin Bottom Ash Processing and Recycle Plant". W 14th Annual North American Waste-to-Energy Conference. ASMEDC, 2006. http://dx.doi.org/10.1115/nawtec14-3191.
Pełny tekst źródłaMeiren, Thomas, Christian van Husen i Reuven Karni. "Laboratory Support for Service Engineering and Design". W ASME 2008 9th Biennial Conference on Engineering Systems Design and Analysis. ASMEDC, 2008. http://dx.doi.org/10.1115/esda2008-59155.
Pełny tekst źródłaAndreev, Nadejda, Peter Matuku Mawioo, Elena Zubcov, Nina Bagrin, Anastasia Ivanova i Antoaneta Ene. "Application of vermifiltration for sustainable management of septage". W Xth International Conference of Zoologists. Institute of Zoology, Republic of Moldova, 2021. http://dx.doi.org/10.53937/icz10.2021.22.
Pełny tekst źródłaReis, Mariana Tavares dos, Gabriela Marques De Oliveira i Sarah Aparecida Ludwig. "GIARDÍASE CANINA". W I Congresso On-line Nacional de Clínica Veterinária de Pequenos Animais. Revista Multidisciplinar em Saúde, 2021. http://dx.doi.org/10.51161/rems/1848.
Pełny tekst źródłaWright, Natasha C., i Amos G. Winter. "Energetic and Socioeconomic Justification for Solar-Powered Desalination Technology for Rural Indian Villages". W ASME 2014 International Design Engineering Technical Conferences and Computers and Information in Engineering Conference. American Society of Mechanical Engineers, 2014. http://dx.doi.org/10.1115/detc2014-35176.
Pełny tekst źródłaLille, Simon, Wlodzimierz Blasiak, Magnus Mo¨rtberg, Tomasz Dobski i Weihong Yang. "Heat Flux Evaluation in a Test Furnace Equipped With High Temperature Air Combustion (HTAC) Technique". W 2002 International Joint Power Generation Conference. ASMEDC, 2002. http://dx.doi.org/10.1115/ijpgc2002-26031.
Pełny tekst źródłaRaporty organizacyjne na temat "ODOUR PROBLEM"
Limnological characteristics, nutrient loading and limitation, and potential sources of taste and odor problems in Standley Lake Colorado. US Geological Survey, 1993. http://dx.doi.org/10.3133/wri924053.
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