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Journal articles on the topic 'Disinfection by-products'

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Published: 4 June 2021

Last updated: 31 January 2023

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1

McGuire, Michael J., Jennifer Orme, William H. Glaze, and Jennifer Orme. "Disinfection By-products." Journal - American Water Works Association 81, no. 8 (August 1989): 18–26. http://dx.doi.org/10.1002/j.1551-8833.1989.tb03254.x.

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2

Ilavský, J., D. Barloková, O. Kapusta, and M. Kunštek. "Water disinfection agents and disinfection by-products." IOP Conference Series: Earth and Environmental Science 92 (October 2017): 012022. http://dx.doi.org/10.1088/1755-1315/92/1/012022.

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3

Kriš, J., K. Munka, E. Büchlerová, M. Karácsonyová, and L. Gajdoš. "Chlorine dioxide disinfection by-products in the Nová Bystrica-Čadca-Žilina long distance water supply system." Water Supply 6, no. 2 (March 1, 2006): 209–14. http://dx.doi.org/10.2166/ws.2006.071.

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In a process of water disinfection it is necessary to distinguish between primary disinfection focused on removal or inactivation of microbiological contaminants from raw water, and secondary disinfection focused on maintenance of residual concentration of the disinfector in distribution system. Current practice related to disinfection follows two approaches. The paper presents results from a stage task solution “Research of physical-chemical changes in water quality during its distribution” at the Nová Bystrica-Čadca-Žilina long distance water supply system (LDWSS) focused on the presence of disinfection by-products by using chlorine dioxide.

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4

Zhang, Guichan, Binliang Lin, and Roger A. Falconer. "Modelling disinfection by-products in contact tanks." Journal of Hydroinformatics 2, no. 2 (March 1, 2000): 123–32. http://dx.doi.org/10.2166/hydro.2000.0010.

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Numerical modelling has been extensively used in the field of environmental engineering as an efficient method for predicting the fate of contaminants. For chlorine disinfection contact tanks, current numerical models predict the disinfection processes as well as first-order functions for chlorine demand. In recent years, the study of the formation of Disinfection By-Products (i.e. DBPs) in drinking water has been a cause for public concern. Since both chemical analyses and monitoring of DBPs are very expensive and not yet widely available, the establishment of an efficient numerical model has become a priori for the analysis of DBPs. This study includes a second-order kinetic representation for chlorine consumption in the disinfection processes and incorporates this representation in a numerical model to predict the formation of DBPs. The model has been refined to predict the chlorine demand in the disinfection process and the distribution of the main DBPs in contact tanks, including primarily total trihalomethanes (TTHMs), dichloroacetic acid (DCAA) and trichloroacetic acid (TCAA).

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5

Dell'Erba, Adele, Dario Falsanisi, Lorenzo Liberti, Michele Notarnicola, and Domenico Santoro. "Disinfection by-products formation during wastewater disinfection with peracetic acid." Desalination 215, no. 1-3 (September 2007): 177–86. http://dx.doi.org/10.1016/j.desal.2006.08.021.

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6

Sun, Xuefeng, Miao Chen, Dongbin Wei, and Yuguo Du. "Research progress of disinfection and disinfection by-products in China." Journal of Environmental Sciences 81 (July 2019): 52–67. http://dx.doi.org/10.1016/j.jes.2019.02.003.

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7

Johnson, Bruce A., Joseph C. Lin, John Chan, Mao Fang, Laura Jacobsen, David Rexing, and Patricia Sampson. "Localized Treatment for Disinfection By-Products." Proceedings of the Water Environment Federation 2009, no. 1 (January 1, 2009): 381–87. http://dx.doi.org/10.2175/193864709793848077.

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8

Cognet, L., Y. Courtois, and J. Mallevialle. "Mutagenic activity of disinfection by-products." Environmental Health Perspectives 69 (November 1986): 165–75. http://dx.doi.org/10.1289/ehp.8669165.

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9

Smith, M. K., H. Zenick, and E. L. George. "Reproductive toxicology of disinfection by-products." Environmental Health Perspectives 69 (November 1986): 177–82. http://dx.doi.org/10.1289/ehp.8669177.

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10

Voukkali, I., and A. A. Zorpas. "Disinfection methods and by-products formation." Desalination and Water Treatment 56, no. 5 (July 25, 2014): 1150–61. http://dx.doi.org/10.1080/19443994.2014.941010.

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11

Najm, Issam N., Nancy L. Patania, Joseph G. Jacangelo, and Stuart W. Krasner. "Evaluating surrogates for disinfection by-products." Journal - American Water Works Association 86, no. 6 (June 1994): 98–106. http://dx.doi.org/10.1002/j.1551-8833.1994.tb06213.x.

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12

Kobos, Lisa, Kim Anderson, Laura Kurth, Xiaoming Liang, Caroline P. Groth, Lucy England, A. Scott Laney, and M. Abbas Virji. "Characterization of Cleaning and Disinfection Product Use, Glove Use, and Skin Disorders by Healthcare Occupations in a Midwestern Healthcare Facility." Buildings 12, no. 12 (December 14, 2022): 2216. http://dx.doi.org/10.3390/buildings12122216.

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Healthcare facility staff use a wide variety of cleaning and disinfecting products during their daily operations, many of which are associated with respiratory or skin irritation or sensitization with repeated exposure. The objective of this study was to characterize the prevalence of cleaning and disinfection product use, glove use during cleaning and disinfection, and skin/allergy symptoms by occupation and identify the factors influencing glove use among the healthcare facility staff. A questionnaire was administered to the current employees at a midwestern Veterans Affairs healthcare facility that elicited information on cleaning and disinfection product use, glove use during cleaning and disinfection, skin/allergy symptoms, and other demographic characteristics, which were summarized by occupation. The central supply/environmental service (2% of the total survey population) and nursing occupations (licensed practical nurse: 3%, nurse: 26%, nursing assistant: 3%, other nurses: 10% of the total survey population, respectively) had the highest prevalence of using cleaning or disinfecting products, specifically quaternary ammonium compounds, bleach, and alcohol. Glove use while using products was common in both patient care and non-patient care occupations. The factors associated with glove use included using bleach or quaternary ammonium compounds and using cleaning products 2–3 or 4–5 days per week. A high frequency of glove use (≥75%) was reported by workers in most occupations when using quaternary ammonium compounds or bleach. The use of alcohol, bleach, and quaternary ammonium compounds was associated with skin disorders (p < 0.05). These research findings indicate that although the workers from most occupations report a high frequency of glove use when using cleaning and disinfection products, there is room for improvement, especially among administrative, maintenance, and nursing workers. These groups may represent populations which could benefit from the implementation of workplace interventions and further training regarding the use of personal protective equipment and the potential health hazards of exposure to cleaning and disinfecting chemicals.

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13

Buhl, Sebastian, Alexander Stich, Dario Clos, and Clemens Bulitta. "Cold plasma as a fast acting alternative disinfection method." Current Directions in Biomedical Engineering 8, no. 2 (August 1, 2022): 21–22. http://dx.doi.org/10.1515/cdbme-2022-1006.

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Abstract Cold plasma disinfection is a cost-efficient and, above all, fast way of disinfecting even complex products. There are already approaches where plasma disinfection is used for wound treatment or hand disinfection. The ionization of a gas results in a number of physical and chemical processes that have a damaging effect on microorganisms. Especially in the field of medical device reprocessing, a tool that can reliably disinfect even very complex products in a short time would be a great asset. In this work, the potential of a newly developed cold plasma disinfection device was tested for the reduction of microbiological contamination and thus the disinfecting effect. In order to examine this microbiological reduction 3D printed scaffolds with contaminated test plates were used. This was done with different concentrations of the bacteria in the cold plasma disinfection process to determine the maximum germ reduction effect. In a first test run, the maximum effect of germ reduction was achieved with log 3.6. By making further changes and increasing the disinfection cycles, it was possible to increase the germ reduction to log 4.7. If these values are confirmed and can be improved by further modifications (e.g. increasing the plasma concentration), cold plasma technology represents a very good alternative to conventional disinfection methods.

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14

Selcuk, Huseyin. "Disinfection and formation of disinfection by-products in a photoelectrocatalytic system." Water Research 44, no. 13 (July 2010): 3966–72. http://dx.doi.org/10.1016/j.watres.2010.04.034.

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15

Pfaff, John D., and Carol A. Brockhoff. "Determining Inorganic Disinfection By-products by Ion Chromatography." Journal - American Water Works Association 82, no. 4 (April 1990): 192–95. http://dx.doi.org/10.1002/j.1551-8833.1990.tb06951.x.

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16

TAKAHASHI, Yasuo, and Masatoshi MORITA. "Halogenated Disinfection By-Products in Tap Water." Journal of Environmental Chemistry 8, no. 3 (1998): 455–64. http://dx.doi.org/10.5985/jec.8.455.

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17

Klotz, J. B., and L. A. Pyrch. "NEURAL TUBE DEFECTS AND DISINFECTION BY-PRODUCTS." Epidemiology 9, Supplement (July 1998): S47. http://dx.doi.org/10.1097/00001648-199807001-00104.

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18

Smith, Rachel B., Mark J. Nieuwenhuijsen, James E. Bennett, John Wright, Pauline Raynor, and Mireille B. Toledano. "Exposure to Disinfection By-products During Pregnancy." Epidemiology 22 (January 2011): S122. http://dx.doi.org/10.1097/01.ede.0000392043.30688.93.

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19

Cardador, Maria Jose, Mercedes Gallego, Francisco Prados, and José Fernández-Salguero. "Origin of disinfection by-products in cheese." Food Additives & Contaminants: Part A 34, no. 6 (April 12, 2017): 928–38. http://dx.doi.org/10.1080/19440049.2017.1311421.

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20

Nissinen, T. K., I. T. Miettinen, P. J. Martikainen, and T. Vartiainen. "Disinfection by-products in Finnish drinking waters." Chemosphere 48, no. 1 (July 2002): 9–20. http://dx.doi.org/10.1016/s0045-6535(02)00034-6.

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21

Williams, David T., Guy L. LeBel, and Frank M. Benoit. "Disinfection by-products in Canadian drinking water." Chemosphere 34, no. 2 (January 1997): 299–316. http://dx.doi.org/10.1016/s0045-6535(96)00378-5.

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22

Wright, J. M., Z. Rivera-Núñez, and A. M. Evans. "Birth Defects and Disinfection By-Products (DBPS)." Annals of Epidemiology 23, no. 9 (September 2013): 597. http://dx.doi.org/10.1016/j.annepidem.2013.06.085.

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23

Pontius, Frederick W. "Small Systems to Tackle Disinfection By-products." Journal - American Water Works Association 90, no. 4 (April 1998): 14–176. http://dx.doi.org/10.1002/j.1551-8833.1998.tb08410.x.

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24

Pontius, Frederick W. "Disinfection By-products - A Regulatory Balancing Act." Opflow 19, no. 12 (December 1993): 1–5. http://dx.doi.org/10.1002/j.1551-8701.1993.tb01227.x.

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25

Williams, David T., Frank M. Benoit, and Guy L. Lebel. "Trends in levels of disinfection by-products." Environmetrics 9, no. 5 (September 1998): 555–63. http://dx.doi.org/10.1002/(sici)1099-095x(199809/10)9:5<555::aid-env323>3.0.co;2-w.

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26

Cho, J., H. Choi, I. S. Kim, and G. Amy. "Chemical aspects and by-products of electrolyser." Water Supply 1, no. 4 (June 1, 2001): 159–67. http://dx.doi.org/10.2166/ws.2001.0080.

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The electrolyser is a disinfection device consisting of a series of porous graphite plates through which water flows while low voltage and current are applied. This electrolyser had been demonstrated successfully for efficient microbial (coliform bacteria, bacteriophage, Giardia, and Cryptosporidium) inactivation before this study. In this study, chemical aspects were evaluated in terms of the formation of disinfectants and/or oxidants as well as disinfection by-products (DBPs) during the disinfection by the electrolyser. Experiments were performed under constant electrolyser conditions but variable water quality conditions (electrolyte type and concentration, dissolved organic carbon, bromide ion (Br-) and, to an extent, pH). It was shown that disinfectants and (chlorinated or ozonated) DBPs could be measured successfully for the effluent samples from the electrolyser. Chlorination by-products did not pose any problem in compliance to drinking water regulations, while bromate and chlorate (ozonation by-products) were shown to be formed at levels near their respective regulation levels, but only under extreme water quality conditions.

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27

Vieira, Adriano, Roger Hughes, Jimmy Helms, Aaron Archer, Mark Graves, and Joel Cantwell. "Treating Verdigris River Water - Disinfection Strategy for Minimal Disinfection By-Products Formation." Proceedings of the Water Environment Federation 2009, no. 1 (January 1, 2009): 388–417. http://dx.doi.org/10.2175/193864709793848130.

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28

Pilotto, Louis S. "Disinfection of drinking water, disinfection by-products and cancer: what about Australia?" Australian Journal of Public Health 19, no. 1 (February 12, 2010): 89–93. http://dx.doi.org/10.1111/j.1753-6405.1995.tb00304.x.

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29

Singer, P. C. "Disinfection by-products in US drinking waters: past, present and future." Water Supply 4, no. 1 (February 1, 2004): 151–57. http://dx.doi.org/10.2166/ws.2004.0018.

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Disinfection by-products have been regulated in finished drinking waters in the United States since 1979. The original regulations dealt only with trihalomethanes, but more recent rules also address haloacetic acids. Compliance with these regulations has traditionally been based on a running annual average of quarterly measurements of disinfection by-products in the distribution system and on concerns about adverse health effects associated with chronic exposure to these by-products. More recently, concerns have also been focused on short-term exposure and acute reproductive and developmental adverse health effects. Additionally, while compliance has previously been based on disinfection by-product levels in samples collected primarily at locations with average distribution system residence times, forthcoming regulations will base compliance on disinfection by-product levels in samples collected at locations with maximum trihalomethane and haloacetic acid concentrations. Moreover, instead of the maximum contaminant levels applying to the annual average of all distribution system samples, the new rules will require that the annual average of the regulated disinfection by-product concentrations at each monitoring location be less than their respective maximum contaminant levels. This paper reviews the evolution of disinfection by-product regulations in the United States and on the rationale behind these regulations.

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30

Lin, Yi-Li, Pen-Chi Chiang, and E.-E. Chang. "Reduction of disinfection by-products precursors by nanofiltration process." Journal of Hazardous Materials 137, no. 1 (September 2006): 324–31. http://dx.doi.org/10.1016/j.jhazmat.2006.02.016.

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31

Ghernaout, Djamel, and Noureddine Elboughdiri. "Foresight Look on the Disinfection By-Products Formation." OALib 07, no. 05 (2020): 1–17. http://dx.doi.org/10.4236/oalib.1106349.

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32

Ghernaout, Djamel, and Noureddine Elboughdiri. "Disinfection By-Products Regulation: Zero ng/L Target." OALib 07, no. 05 (2020): 1–9. http://dx.doi.org/10.4236/oalib.1106382.

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33

Ghernaout, Djamel, and Noureddine Elboughdiri. "Disinfection By-Products (DBPs) Control Strategies in Electrodisinfection." OALib 07, no. 05 (2020): 1–14. http://dx.doi.org/10.4236/oalib.1106396.

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34

Ghebremichael, K., A. Gebremeskel, N. Trifunovic, and G. Amy. "Modeling disinfection by-products: coupling hydraulicand chemical models." Water Supply 8, no. 3 (September 1, 2008): 289–95. http://dx.doi.org/10.2166/ws.2008.073.

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There are established chemical models that can predict disinfectant decay and DBPs formation with respect to various water quality parameters and reaction time (water age). While models such as EPANET are powerful tools in hydraulic simulations, they have limited use in simulating water quality, containing only a basic chlorine decay subroutine. This paper presents a study on the use of a link that was developed to couple the external water quality models and the hydraulic model of EPANET 2.The coupled model has been applied to a hypothetical distribution system under steady and non steady conditions. Simulations have taken the form of sensitivity analyses to probe operational strategies such as modified treatment as well as optimized secondary disinfection in order to maintain sufficient chlorine residual at critical points within the distribution system. Simulations have also been performed to compare the relative rates of formation of THMs vs HAAs as well as individual species. Of particular interest is optimization of chlorine dose to minimize residual chlorine under non-steady-state conditions.

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35

JANDA, Václav, Pavel PECH, and Martina PECHOVÁ. "Disinfection of water and its undesirable by-products." Kvasny Prumysl 50, no. 11-12 (November 1, 2004): 335–40. http://dx.doi.org/10.18832/kp2004022.

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36

Kogevinas*, Manolis, Esther Gracia-Lavedan, Beatriz Perez-Gomez, Jone M. Altzibar, Eva Ardanaz, Adonina Tardon, Antonio Jose Molina, et al. "Disinfection By-Products and Colorectal Cancer in Spain." ISEE Conference Abstracts 2014, no. 1 (October 20, 2014): 1867. http://dx.doi.org/10.1289/isee.2014.o-002.

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37

Do, Minh T., Nicholas J. Birkett, Kenneth C. Johnson, Daniel Krewski, and Paul Villeneuve. "Chlorination Disinfection By-products and Pancreatic Cancer Risk." Environmental Health Perspectives 113, no. 4 (April 2005): 418–24. http://dx.doi.org/10.1289/ehp.7403.

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38

Toledano, M. B., M. J. Nieuwenhuijsen, N. G. Best, H. Whitaker, C. De Hoogh, N. Cobley, J. Fawell, and P. Elliott. "CHLORINATION DISINFECTION BY-PRODUCTS AND ADVERSE BIRTH OUTCOMES." Epidemiology 14, Supplement (September 2003): S39. http://dx.doi.org/10.1097/00001648-200309001-00075.

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39

Simpson, Karen L., and Keith P. Hayes. "Drinking water disinfection by-products: an Australian perspective." Water Research 32, no. 5 (March 1998): 1522–28. http://dx.doi.org/10.1016/s0043-1354(97)00341-2.

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40

Barhorst, Jan Bernd, and Roland Kubiak. "Formation of chlorinated disinfection by-products in viticulture." Environmental Science and Pollution Research 16, no. 5 (May 29, 2009): 582–89. http://dx.doi.org/10.1007/s11356-009-0186-5.

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41

Hu, Chen-Yan, Yan-Guo Deng, Yi-Li Lin, and Yuan-Zhang Hou. "Chlorination of bromacil: Kinetics and disinfection by-products." Separation and Purification Technology 212 (April 2019): 913–19. http://dx.doi.org/10.1016/j.seppur.2018.12.002.

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42

Sohn, J., G. Amy, and Y. Yoon. "Bromide Ion Incorporation Into Brominated Disinfection By-Products." Water, Air, and Soil Pollution 174, no. 1-4 (May 23, 2006): 265–77. http://dx.doi.org/10.1007/s11270-006-9104-3.

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43

Mike Sudman, T., Todd E. Hone, and Cheryl L. Green. "Disinfection By-Products-Meeting the Challenges of Compliance." Opflow 38, no. 1 (January 2012): 18–21. http://dx.doi.org/10.5991/opf.2012.38.0003.

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44

Singer, Philip C. "Control of Disinfection By‐Products in Drinking Water." Journal of Environmental Engineering 120, no. 4 (July 1994): 727–44. http://dx.doi.org/10.1061/(asce)0733-9372(1994)120:4(727).

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45

Cardador, Maria Jose, Mercedes Gallego, Lourdes Cabezas, and Jose Fernández-Salguero. "Detection of regulated disinfection by-products in cheeses." Food Chemistry 204 (August 2016): 306–13. http://dx.doi.org/10.1016/j.foodchem.2016.02.146.

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46

Pontius, Frederick W. "Microbial/Disinfection By-Products Rules on Expedited Schedule." Journal - American Water Works Association 89, no. 5 (May 1997): 17–20. http://dx.doi.org/10.1002/j.1551-8833.1997.tb08223.x.

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47

Pontius, Frederick W. "Negotiating Regulations for Microorganisms and Disinfection By-products." Journal - American Water Works Association 91, no. 10 (October 1999): 14–28. http://dx.doi.org/10.1002/j.1551-8833.1999.tb08711.x.

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48

Badawy, Mohamed I., Tarek A. Gad-Allah, Mohamed E. M. Ali, and Yeoman Yoon. "Minimization of the formation of disinfection by-products." Chemosphere 89, no. 3 (September 2012): 235–40. http://dx.doi.org/10.1016/j.chemosphere.2012.04.025.

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49

Pontius, Frederick W. "Microbial-Disinfection By-products Rules on Expedited Schedule." Opflow 23, no. 6 (June 1997): 7–8. http://dx.doi.org/10.1002/j.1551-8701.1997.tb02055.x.

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50

Zhang, Jing, and Chen Yan Hu. "Review on Disinfection Pretreatment Processes to Remove Water N-Nitrosodimethylamine Disinfection By-Products." Advanced Materials Research 610-613 (December 2012): 1833–36. http://dx.doi.org/10.4028/www.scientific.net/amr.610-613.1833.

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As a new finding disinfection by-product (DBP), N-nitrosodimethylamine is becoming research focus for its high carcinogenicity. Some pretreatment technologies of drinking water such as activated carbon adsorption, enhanced coagulation, chemical oxidation, biological oxidation, advanced oxidation were summarized. As shown above, the control effect of process of NDMA and its precursors were analyzed.

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