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Готові списки джерел за темами / Drinking water

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Добірка наукової літератури з теми "Drinking water"

Автор: Grafiati

Опубліковано: 4 червня 2021

Оновлено: 9 листопада 2024

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Статті в журналах з теми "Drinking water"

1

Kiran. A, Kiran A., Nikhil T. R. Nikhil. T. R, and Harish J. Kulkarni. "Harvested Rain Water for Drinking." Indian Journal of Applied Research 2, no. 1 (October 1, 2011): 71–72. http://dx.doi.org/10.15373/2249555x/oct2012/24.

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2

Horth, Helene. "Identification of mutagens in drinking water." Journal français d’hydrologie 21, no. 1 (1990): 135–45. http://dx.doi.org/10.1051/water/19902101135.

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3

Moosa, Merfat Ebrahim Al, Munawwar Ali Khan, Usama Alalami, and Arif Hussain. "Microbiological Quality of Drinking Water from Water Dispenser Machines." International Journal of Environmental Science and Development 6, no. 9 (2015): 710–13. http://dx.doi.org/10.7763/ijesd.2015.v6.685.

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4

Imran, Abubakar, Tariq Manzoor, Muhammad Ibrahim, and Wasif Munaf. "DRINKING WATER." Professional Medical Journal 23, no. 03 (March 10, 2016): 339–42. http://dx.doi.org/10.29309/tpmj/2016.23.03.1485.

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Introduction: World Health Organization, (WHO) estimates that more than 80%of poor health conditions in developing countries, is related to water and sanitation condition.The supply water and sanitary lines often overlap in our water supply system and watercontaminated by fecal contents and become a major cause of GIT infections and outbreaksin human populations. Objective: The Objective of the study was to determine the fecalcontamination level in tube well water across the distributing supply lines. Study Design: Thestudy design was observational. Settings: Fatima Memorial Hospital, College of Medicine andDentistry Shadman Lahore. Period: February 01, 2012 to May 29, 2012. Method: The studydid not engage any ethical issues and conducted in five specific regions of Lahore. A 100 mlof water sample was collected in sterile container, from the tube well and after every 100 meterdistance till 500 meters. The sample size was 250 from 45 tube wells and their distributingsupply lines. It was then observed for fecal coliforms using prescribed scientific methods.Result: The results indicated that bacterial growth at baseline was 42.2%, and at extremity was73.3%. The A Category water obtained at baseline is 60.0% and at the extreme level it is 26.7%.So by increasing distance from source of water the risk of fecal contamination and low qualityof drinking water increases. Conclusion: It is concluded that as the distance increased fromthe main source

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5

Alpert, Patricia T. "Drinking Water." Home Health Care Management & Practice 25, no. 4 (March 28, 2013): 179–81. http://dx.doi.org/10.1177/1084822313481784.

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6

Fessenden, Marissa. "Drinking Water." Scientific American 307, no. 5 (October 16, 2012): 84. http://dx.doi.org/10.1038/scientificamerican1112-84b.

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7

Říhová Ambrožová, J., J. Říha, J. Hubáčková, and I. Čiháková. "Risk analysis in drinking water accumulation." Czech Journal of Food Sciences 28, No. 6 (December 13, 2010): 557–63. http://dx.doi.org/10.17221/98/2010-cjfs.

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Drinking water is safe water, from the perspective of long-term use is does not cause any disease, pathogenic and hygienically unsafe microorganisms do not spread in it and customers enjoy its consumption. Drinking water is regarded as a foodstuff, therefore the known HACCP system can be used in the control system which can be applied not only directly to the final product, but also to the whole system of drinking water production, distribution, and accumulation. Even if there is no problem concerning the water processing and the technological line is well adjusted, the quality of drinking water is subsequently deteriorated by its transportation and accumulation. The condition and character of the operated distribution network and reservoirs are significantly and substantially related to the maintenance of the biological stability and quality of drinking water. This is well confirmed by biological audits of the distribution networks and water reservoirs. A significant fact is the negative influence of the secondary contamination by air in the reservoir facilities and the occurrence of microorganisms (fungi, bacteria) in free water and in biofilms. The findings obtained in the framework of biological audits were so alarming that the outputs of biological audits contributed to the reconsideration of the efficiency of the standard for the construction and design of water reservoirs and pointed out the necessity of its review.

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8

Ray, L. Bryan. "How drinking (alcohol) affects drinking (water)." Science 360, no. 6391 (May 24, 2018): 871.5–872. http://dx.doi.org/10.1126/science.360.6391.871-e.

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9

Říhová Ambrožová, J., J. Hubáčková, and I. Čiháková. "Drinking water quality in the Czech Republic." Czech Journal of Food Sciences 27, No. 2 (May 25, 2009): 80–87. http://dx.doi.org/10.17221/155/2008-cjfs.

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The quality of water has to be controlled and monitored by drinking water suppliers during all stages of the treatment process from the water sources to the end of distribution systems. The research, performed in Czech Republic from 2006 to 2008, deals with the assessment of the affect of water tanks on the quality of water supplied to consumers, specifically from various points of view: microbiological, biological and physic-chemical changes in water accumulation. Also studied was the influence of the air on the quality of accumulated water (secondary contamination), the influence of the structural layout and hydraulic ratios. In the project quick screening methods (paddle testers and BART<sup>TM</sup> tests) were applied in the collection of water samples and scrapings from wetted surfaces of water tanks. The results of the contamination degree discovered in the course of the project solution will serve as basic data for a scale that should evaluate the degree of water tank pollution as well as for resulting corrective measures or optimisation of water tank cleaning. The recommendations of limits for a scraping sample are based especially on the microbiological parameters. Secondary air contamination plays an important role in maintains of biologically stable water. Based on the number of microbial contamination discovered water tanks will be categorised and methods of suitable measures to be taken will be stipulated, operation optimisation as well as cleaning (schedule, methods and frequency of cleaning). The water quality in a storage tanks depends on their maintenance, e.g., to prevent the plaster falling on water surface, the use of antifungal surface coatings (prevention the growth of fungi on walls), the use of ceramics surface of reservoir walls, dark conditions (no windows or blue sheets) in all technological units, the prevention of dust fall out, the selection of suitable air condition and special air filters.

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10

Watson, Charles R. R. "Safe drinking water." Medical Journal of Australia 166, no. 6 (March 1997): 285–86. http://dx.doi.org/10.5694/j.1326-5377.1997.tb122312.x.

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Дисертації з теми "Drinking water"

1

Velie, Ted. "Drinking the Water." Connect to online resource, 2008. http://gateway.proquest.com/openurl?url_ver=Z39.88-2004&rft_val_fmt=info:ofi/fmt:kev:mtx:dissertation&res_dat=xri:pqdiss&rft_dat=xri:pqdiss:1453528.

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2

Hassinger, Elaine, and Jack Watson. "Drinking Water Standards." College of Agriculture and Life Sciences, University of Arizona (Tucson, AZ), 1998. http://hdl.handle.net/10150/146411.

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4 pp.
Gasses, minerals, bacteria, metals and chemicals suspended or dissolved in water can influence the quality of the water and hence affect our health. Therefore, EPA, the U.S. Environmental Protection Agency, has established limits on the concentration of certain drinking water contaminants allowed in public water supplies. This publication discusses drinking water standards and how these standards are set.

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3

Li, Hongjie. "Optimizing drinking water filtration." Thesis, National Library of Canada = Bibliothèque nationale du Canada, 2000. http://www.collectionscanada.ca/obj/s4/f2/dsk1/tape4/PQDD_0011/MQ60148.pdf.

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4

Kilungo, Aminata Peter. "Drinking Water Quality Monitoring." Diss., The University of Arizona, 2013. http://hdl.handle.net/10150/306073.

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This dissertation involves two different studies. The first concerns the real-time detection of microbial contamination in drinking water using intrinsic fluorescence of the microorganisms. The prototype, “Blinky”, uses LEDs that emit light at 365nm, 590nm, and 635nm for ultraviolet, amber, and red light, respectively. At 365 nm, the cellular components excited include reduced pyridine nucleotides (RPNs), flavins, and cytochromes to distinguish viable bacteria; at 590 nm, the cellular components excited include cytochromes for non-viable bacteria; at 635 nm, the cellular components excited include calcium dipicolinic acid (DPA) for spores. By using these three different wavelengths, the prototype can differentiate between viable and non-viable organisms and also has the potential to detect spores. The aim of this study was to improve the detection limit by modifying the design of the instrument and to establish the detection limit of viable and non-viable bacteria and spores. The instrument was modified by replacing existing LEDs with LEDs that had 50% more intensity. Two additional LEDs were added for amber and red light, bringing the total to four LEDs for each. The LEDs were also positioned closer to the photomultiplier tube so as to increase sensitivity. For UV, only two LEDs were used as previous. The detection limit of the viable bacteria was ~50 live bacteria/L. No change in the intrinsic fluorescence below the concentration of ~10⁸ dead bacteria/L was observed. The results for spore measurements suggested that most of the spores had germinated before or during the measurements and could not be detected. The instrument was successful in detection of viable bacteria and also differentiating viable and non-viable bacteria. The instrument was not successful in detection of spores. The second study was designed to assess the water quality of well construction in southeastern Tanzania. Three designs were tested: Msabi rope pump (lined borehole and covered), an open well converted into a closed well (uncovered well into a covered and lined well), and an open well (uncovered and may or may not be lined). The study looked at the microbial and chemical water quality, as well as turbidity. The survey included 97 water collection points, 94 wells and three rivers. For microbial analysis, heterotrophic plate count (HPC), total coliforms and E. coli tests were performed. Fifteen of these wells were further analyzed for microflora and diversity for wells comparison purposes, using culture methods, followed by polymerase chain reaction (PCR) and genome sequencing. Ten wells out of the fifteen were analyzed for calcium (water hardiness), potassium, nitrates, nitrites, chloride, fluoride, bromide, sulfate, iron, and arsenic. Two water collection points were also selected for organic compound analysis (gasoline components). All samples tested positive for coliforms. Two samples tested positive for Escherichia coli for the lined borehole (Msabi rope pump) and four samples from closed wells. All open wells tested positive for E. coli. There was more microbial diversity in open wells than the closed wells and Msabi rope pumps. Potential bacterial pathogens were detected in seven wells out of the fifteen examined. The wells that tested positive were one Msabi rope pump, one closed well; the rest were from open water sources. Open wells had high turbidity followed by closed wells. Msabi rope pumps had low turbidity comparing to the two wells designs. No traces of gasoline components were detected in any of the water sources. One well out of ten had high amounts of nitrates-nitrogen (> 10 mg/L). The results of this study showed that the Msabi rope pumps performed comparably to the closed wells in terms of microbial quality but performed better with regard to turbidity. The open wells performed poorly in terms of microbial water quality as well and turbidity. There was a statistical difference in HPC, total coliforms, E.coli numbers and turbidity between open wells, closed wells and the Msabi rope pumps. However, there was no statistical difference in HPC, total coliforms and E.coli numbers between the closed wells and Msabi rope pumps. Msabi rope pumps performed better in turbidity

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5

Schalau, Jeff. "Arsenic in Drinking Water." College of Agriculture and Life Sciences, University of Arizona (Tucson, AZ), 2005. http://hdl.handle.net/10150/147004.

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2 pp.
Arsenic is the twentieth most abundant element in the earth's crust and frequently occurs in rock formations of the Southwestern United States. Arsenic remains in the environment over long periods and when it occurs in high concentrations, it can be toxic to many life forms, but it also has been shown to be an essential nutrient for many animal species and may be to humans, too. This publication provides information about the impact arsenic in drinking water has over human and plant health and the ways to remove it.

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6

Kavcar, Pınar Sofuoğlu Sait C. "Assessmanet of exposure and risk associated with trihalomethanes and other volatile organic compounds in drinking water/." [s.l.]: [s.n.], 2005. http://library.iyte.edu.tr/tezler/master/cevremuh/T000375.pdf.

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Thesis (Master)--İzmir Institute Of Technology, İzmir, 2005.
Keywords:Trihalomethane, volatile organic compounds, drinking water, risk assessment, exposure. Includes bibliographical references (leaves. 64-70).

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7

Rojko, Christine. "Solar disinfection of drinking water." Link to electronic thesis, 2003. http://www.wpi.edu/Pubs/ETD/Available/etd-0423103-124244.

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8

Van, der Leer Daniel. "Modelling lead in drinking water." Thesis, Swansea University, 2003. https://cronfa.swan.ac.uk/Record/cronfa42919.

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In light of substantial medical evidence of the detrimental effect of lead on the body, the use of lead in pipe networks, and the subsequent lead emissions into drinking water is now a major concern. As a result, the new European Union 'drinking water' directive requires the standard for lead in drinking water to be tightened from 50pg/l to 25pg/l by December 2003 and to 10pg/l by December 2013. It is anticipated that these standards will be achieved by a combination of water treatment, which must be optimised, and selective lead pipe replacement where necessary. In order to optimise corrective treatment, accurate monitoring of lead emissions across a water supply zone must be achieved. The severe limitations of traditional monitoring methods have provided the motivation to develop a computational model to facilitate the optimisation of corrective treatment as well as to investigate lead emissions at individual houses. The development of a model to assess lead emissions in drinking water at a single house and across a water supply zone is described. The model has been used to investigate the daily variation of lead emissions at a single house and to determine the influence of factors, such as pipework geometry and water usage, on the daily average concentration of lead in drinking water. The ability to simulate traditional sampling methodologies on simulated water supply zones has enabled the model to be validated for a wide range of real water supply zones. This has allowed the model to be used successfully for the purposes of assessing zonal compliance and facilitating the optimisation of corrective treatment. Additionally, the model has enabled a detailed assessment of the use of the Random Day Time sampling method, for the optimisation of plumbosolvency control.

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9

Sá, Jacinto de Paiva. "Catalytic denitration of drinking water." Thesis, University of Aberdeen, 2007. http://digitool.abdn.ac.uk/R?func=search-advanced-go&find_code1=WSN&request1=AAIU602323.

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Human demand for clean water has increase drastically in the past centuries, mainly due its demographic growth. The sources of clean drinking water have been continuously reduced due to depletion or contamination with one example being the extensive use of fertilizers in agriculture, which can lead to leaching of nitrates into groundwater and hence into surface water. The gravity of the situation was expressed by European Environmental Agency in 1998, revealing that, 87% of agricultural areas in the European Union (EU) have nitrate concentrations in groundwater above the guide level (25 ppm). Catalytic hydrogenation is one potential solution if an appropriate active, selective catalyst could be identified. One of the major drawbacks of the hydrogenation approach is the absence of robust studies which clearly describe what happens during reaction, essential for full understanding of the process. It was decided to use FTIR under operando conditions to try to disclose what happens in the catalyst surface during reaction. Pd/TiO2 catalysts were selected one. Upon adsorption at Lewis acid sites (oxygen vacancies), the nitrates are reduced by the electron enriched titania species, most likely Ti4O7 as identified by electron microscopy, which lead to the formation of nitrites, generally detected in solution during the hydrogenation tests and expected assuming a stepwise mechanism exists. The rather weak adsorption of nitrate onto the catalysts surface allied to their stability might be the reasons for their low reactivity, i.e., limiting step of the hydrogenation process. The nitrite reduction occurs essentially on Pd sites however their adsorption site is Lewis acid sites. NO is adsorbed and reduced exclusively on the noble metal. The order of reactivity of the surface species decreases with the decrease in the oxidation state of the nitrogen, i.e., NO3- NO2- NO. High surface concentration of nitrite leads to the formation of N2O, while ammonia is formed via consecutive hydrogenation of Nads. originating from the dissociation of NO. Ammonia formation takes place over Pd and is dependent on the hydrogen availability and presence of water. Ever since Becquerel discovered the photoelectric effect back 1839, researchers and engineers have been infatuated with the idea of converting light into electric power or chemical fuels. Photocatalysis is also particularly suitable for the abatement of contaminants since it offers potentially high conversions at low cost. Two aspects have dominated the research of photocatalysts, namely improvement of catalytic performances under visible light and the minimization of charge recombination. The latter can be improved by a decrease in the particle size and/or by the addition of small metal clusters of elements such as Cu that operate as electrons sinks thus allowing the system to be employed in processes such as N03- reduction. The addition of metal to TiO2 P25, led to a significant enhancement in the photocatalytic activity of the catalyst. The overall process was found to be dependent on the temperature of reaction media, and the nature and concentration of the hole scavenger, and on the metal loaded. In the case of Hombikat, the metal-free support appeared to operate better possibly as a consequence of its greater surface area as this would hinder, to a certain extent, the charge recombination process. EPR and FTIR experiments under UV irradiation carried out using the metal clusters (Au, Ag and Cu) supported on TiO2, revealed that the presence of the metal leads to the loss of signal related to the stabilized electrons on the pure TiO2 when a hole scavenger such as hydrogen is present. The Fermi level equilibration process, in a semiconductor - metal nanocomposite system, is a clear indication of the presence of electron transfer process between support and metal. Addition of the metal did not, however, modify the band gap energy of the studied semiconductor. In the generality of the cases studied, the photocatalytic approach was found to have much higher activities when compared to the hydrogenation process.

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10

Blain, Heather Ann. "Drinking water out of streams." College Park, Md. : University of Maryland, 2008. http://hdl.handle.net/1903/8212.

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Thesis (M.F.A.) -- University of Maryland, College Park, 2008.
Thesis research directed by: Dept. of English. Title from t.p. of PDF. Includes bibliographical references. Published by UMI Dissertation Services, Ann Arbor, Mich. Also available in paper.

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Книги з теми "Drinking water"

1

Hrubec, Jiri. Water pollution: Drinking water and drinking water treatment. Berlin: Springer, 1995.

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2

Goncharuk, Vladyslav V. Drinking Water. Cham: Springer International Publishing, 2014. http://dx.doi.org/10.1007/978-3-319-04334-0.

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3

Great Britain. Drinking Water Inspectorate. Drinking water. London: Stationery Office, 1999.

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4

McFeters, Gordon A., ed. Drinking Water Microbiology. New York, NY: Springer New York, 1990. http://dx.doi.org/10.1007/978-1-4612-4464-6.

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5

Ray, Chittaranjan, and Ravi Jain, eds. Drinking Water Treatment. Dordrecht: Springer Netherlands, 2011. http://dx.doi.org/10.1007/978-94-007-1104-4.

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6

O, Cliver Dean, Newman Ruth A, and North Atlantic Treaty Organization. Committee on the Challenges of Modern Society., eds. Drinking water microbiology. Park Forest, Il: Journal of Environmental Pathology, Toxicology, andOncology, 1987.

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7

Washington (State). State Board of Health. Drinking water regulations. Olympia, WA (Mail Stop LD-11, Olympia 98504): Dept. of Health, 1989.

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8

Ontario. Ministry of the Environment., ed. Drinking water treatment. [Toronto, Ont: Ministry of the Environment], 2001.

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9

United States. Environmental Protection Agency. and International Symposium on Health Effects of Drinking Water Disinfectants and Disinfection By-products (2nd : 1985 : Cincinnati, Ohio), eds. Drinking water disinfectants. Research Triangle Park, N.C: U.S. Dept. of Health and Human Services, Public Health Service, National Institutes of Health, National Institute of Environmental Health Sciences, 1986.

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10

Adams, Jill U. Drinking Water Safety. 2455 Teller Road, Thousand Oaks California 91320 United States: CQ Press, 2016. http://dx.doi.org/10.4135/cqresrre20160715.

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Частини книг з теми "Drinking water"

1

Kot, Megan. "Drinking Water." In Encyclopedia of Quality of Life and Well-Being Research, 1696–99. Dordrecht: Springer Netherlands, 2014. http://dx.doi.org/10.1007/978-94-007-0753-5_779.

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2

Zolnikov, Tara Rava. "Drinking Water." In Autoethnographies on the Environment and Human Health, 53–66. Cham: Springer International Publishing, 2017. http://dx.doi.org/10.1007/978-3-319-69026-1_5.

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3

Dutta, Suparna, and Arabinda K. Das. "Drinking water." In Handbook of Mineral Elements in Food, 455–71. Chichester, UK: John Wiley & Sons, Ltd, 2015. http://dx.doi.org/10.1002/9781118654316.ch19.

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4

Szálkai, Kinga. "Drinking Water." In The Palgrave Encyclopedia of Global Security Studies, 1–8. Cham: Springer International Publishing, 2019. http://dx.doi.org/10.1007/978-3-319-74336-3_529-1.

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5

Moore, James W. "Drinking Water." In Balancing the Needs of Water Use, 217–43. New York, NY: Springer New York, 1989. http://dx.doi.org/10.1007/978-1-4612-3496-8_9.

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6

Unnerstall, Thomas. "Drinking Water." In Factfulness Sustainability, 83–94. Berlin, Heidelberg: Springer Berlin Heidelberg, 2022. http://dx.doi.org/10.1007/978-3-662-65558-0_8.

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7

Kayser, Olivier, and Valeria Budinich. "Drinking water." In Scaling up Business Solutions to Social Problems, 66–74. London: Palgrave Macmillan UK, 2015. http://dx.doi.org/10.1057/9781137466549_8.

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Birkenholtz, Trevor. "Drinking Water." In Eating, Drinking: Surviving, 23–30. Cham: Springer International Publishing, 2016. http://dx.doi.org/10.1007/978-3-319-42468-2_3.

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9

Arnold, Ellen F. "Drinking Water." In Water in World History, 92–114. New York: Routledge, 2024. http://dx.doi.org/10.4324/9781003127390-5.

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10

Kot, Megan. "Drinking Water." In Encyclopedia of Quality of Life and Well-Being Research, 1879–82. Cham: Springer International Publishing, 2023. http://dx.doi.org/10.1007/978-3-031-17299-1_779.

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Тези доповідей конференцій з теми "Drinking water"

1

Chudzicki, J., M. Kwietniewski, M. Iwanek, and P. Suchorab. "Secondary contamination in Polish drinking water." In URBAN WATER 2014. Southampton, UK: WIT Press, 2014. http://dx.doi.org/10.2495/uw140021.

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SOLÍS-ALVARADO, YOLANDA, ARMANDO MENDIOLA-MORA, HÉCTOR SANVICENTE-SÁNCHEZ, ROBERTO GALVÁN-BENITEZ, JENNY ROMÁN-BRITO, and RENÉ MENDOZA-BETANZOS. "DRINKING WATER: AN OVERVIEW OF THE HUMAN RIGHT TO SAFE DRINKING WATER IN MEXICO." In WATER AND SOCIETY 2019. Southampton UK: WIT Press, 2019. http://dx.doi.org/10.2495/ws190021.

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3

Prochazka, J., and D. Prochazkova. "Drinking water supply failure." In The 2nd International Conference on Engineering Sciences and Technologies. CRC Press Taylor & Francis Group 6000 Broken Sound Parkway NW, Suite 300 Boca Raton, FL 33487-2742: CRC Press, 2017. http://dx.doi.org/10.1201/9781315210469-282.

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4

Goel, Isha, Swarnima Shishodia, Hari Om Upadhyay, and Rohit Rastogi. "Drinking Water Management System." In 2022 4th International Conference on Advances in Computing, Communication Control and Networking (ICAC3N). IEEE, 2022. http://dx.doi.org/10.1109/icac3n56670.2022.10074535.

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5

Blatchley, III, Ernest R., Nimrata K. Hunt, and James E. Smith, Jr. "Ozone Disinfection in Drinking Water." In World Water and Environmental Resources Congress 2001. Reston, VA: American Society of Civil Engineers, 2001. http://dx.doi.org/10.1061/40569(2001)468.

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6

Ahmeti, Muhamet, and Ilira Abdullahu. "Climate Change and Drinking Water." In University for Business and Technology International Conference. Pristina, Kosovo: University for Business and Technology, 2015. http://dx.doi.org/10.33107/ubt-ic.2015.80.

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Babu, C. Ganesh, S. Arun Jayakar, R. Dhanasekar, and M. Kalaiyarasi. "Quality drinking water distribution system." In SECOND INTERNATIONAL CONFERENCE ON CIRCUITS, SIGNALS, SYSTEMS AND SECURITIES (ICCSSS - 2022). AIP Publishing, 2023. http://dx.doi.org/10.1063/5.0125231.

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8

Bagalkar, N. W., and M. G. Ingale. "Evaluation of drinking water pollution by bacteriological analysis of water used for drinking purpose." In INTERNATIONAL CONFERENCE ON “MULTIDIMENSIONAL ROLE OF BASIC SCIENCE IN ADVANCED TECHNOLOGY” ICMBAT 2018. Author(s), 2019. http://dx.doi.org/10.1063/1.5100429.

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9

Jayadipraja, Erwin Azizi, Dedeh Nurhayati, and Muhammad Chaerul. "The Quality of Drinking Water Preparation in Drinking Water Refill Depots in Kendari, Indonesia." In The Health Science International Conference. SCITEPRESS - Science and Technology Publications, 2019. http://dx.doi.org/10.5220/0009123000920095.

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Souza, Roseane Maria Garcia Lopes de, and Cassiana Maria Reganhan Coneglian. "Pioneirismo da Câmara Técnica de Saúde Ambiental do Comitê PCJ na segurança da água." In International Workshop for Innovation in Safe Drinking Water. Universidade Estadual de Campinas, 2022. http://dx.doi.org/10.20396/iwisdw.n1.2022.4802.

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Анотація:

Sanitation is an essential human right for quality of life and health guarantee for every citizen, regardless of their socioeconomic condition. Everyone has the right to have access to an adequate supply of safe and drinking water. Safe water cannot be sustained only by monitoring its quality, it is necessary to guarantee the supply of water on a continuous basis. The Water Safety Plan carries out a systematic assessment that identifies and characterizes the hazards and risks of water supply systems for human consumption, from the source to the point of delivery, aiming at a preventive risk approach to help guarantee the security of water served to the population, establishing control measures and thereby reducing the burden of diseases related to water supply. The Water Safety Plan is an important instrument for identifying possible deficiencies in the water supply system, organizing and structuring it to minimize the chance of incidents. The Environmental Health Technical Chamber (CT-SAM) of the Piracicaba, Capivari and Jundiaí River Basin Committee (PCJ) has been a pioneer in water security, carrying out actions in the municipalities in order to encourage the implementation of Water Safety Plans to ensure the implementation of the Environmental Health Policy, approved within the scope of the PCJ Committee's area of ??activity.

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Звіти організацій з теми "Drinking water"

1

Andersen, B. D., and L. J. Peterson-Wright. Drinking Water Program 1992 annual report. Office of Scientific and Technical Information (OSTI), August 1993. http://dx.doi.org/10.2172/10193876.

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2

Putnam, Mike. Measurement of Lead in Drinking Water. Fort Belvoir, VA: Defense Technical Information Center, November 1998. http://dx.doi.org/10.21236/ada607341.

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3

Brady, Robert F., Adkins Jr., and James D. Control of Lead in Drinking Water. Fort Belvoir, VA: Defense Technical Information Center, July 1997. http://dx.doi.org/10.21236/ada327758.

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4

Putnam, Mike. Measurement of Lead In Drinking Water. Fort Belvoir, VA: Defense Technical Information Center, July 1996. http://dx.doi.org/10.21236/ada631329.

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5

Shapsugova, M. D. PROBLEMS OF DRINKING WATER RESOURCES MANAGING. Агропродовольственная экономика, 2020. http://dx.doi.org/10.18411/0131-5226-2020-60013.

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6

Brennan, Greg, and Jason Vogelgesang. Drinking Water Protection in Decorah, Iowa. Iowa City, Iowa, USA: Iowa Geological Society, The University of Iowa, January 2023. http://dx.doi.org/10.17077/rep.006596.

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7

Dilparic, Daria. PFAS forensics of drinking water sources. Ames (Iowa): Iowa State University, December 2023. http://dx.doi.org/10.31274/cc-20240624-1115.

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8

Pasqualini, Donatella. Drinking Water Consequences Tools. A Literature Review. Office of Scientific and Technical Information (OSTI), May 2016. http://dx.doi.org/10.2172/1253514.

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9

Lowry, Thomas Stephen, Vincent C. Tidwell, William John Peplinski, Roger Mitchell, David Binning, and Jenny Meszaros. Framework for Shared Drinking Water Risk Assessment. Office of Scientific and Technical Information (OSTI), January 2017. http://dx.doi.org/10.2172/1339494.

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10

Hill, Elaine, and Richard DiSalvo. Drinking Water Contaminant Concentrations and Birth Outcomes. Cambridge, MA: National Bureau of Economic Research, August 2023. http://dx.doi.org/10.3386/w31567.

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