Relevant bibliographies by topics / Water pH

Contents

  1. Journal articles
  2. Dissertations / Theses
  3. Books
  4. Book chapters
  5. Conference papers
  6. Reports

Academic literature on the topic 'Water pH'

Author: Grafiati
Published: 4 June 2021
Last updated: 25 July 2025

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Journal articles on the topic "Water pH"

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Hikmat, B. "Acidic pH of water." British Dental Journal 194, no. 11 (2003): 585. http://dx.doi.org/10.1038/sj.bdj.4810238.

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Nguyen, Bach T., Wenkai Wang, Brian R. Saunders, Lazhar Benyahia, and Taco Nicolai. "pH-Responsive Water-in-Water Pickering Emulsions." Langmuir 31, no. 12 (2015): 3605–11. http://dx.doi.org/10.1021/la5049024.

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Freedman, Arthur J. "Water Treatment Basics: Water Chemistry Revisited: pH." Materials Performance 44, no. 12 (2005): 44. https://doi.org/10.5006/mp2005_44_12-44.

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This article is first in a series on Water Treatment Basics written by water treatment expert Arthur J. Freedman. This issue's installment defines pH and discusses how it is measured and why. Future topics will include alkalinity, solubility, scaling, and other related subjects.
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Altland, J. "Irrigation water alkalinity, not pH, affects substrate pH©." Acta Horticulturae, no. 1212 (September 2018): 189–90. http://dx.doi.org/10.17660/actahortic.2018.1212.38.

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Wett, B., R. Rostek, W. Rauch, and K. Ingerle. "pH-controlled reject-water-treatment." Water Science and Technology 37, no. 12 (1998): 165–72. http://dx.doi.org/10.2166/wst.1998.0532.

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Dewatering of digested sludge causes significant internal nitrogen loading to a wastewater treatment plant. Due to the high concentration of nitrogen it is more effective to treat the reject-water not directly in the main purification process but to apply a separate biological treatment procedure. The intermittent operation of sludge-press facilities, the high initial pH-value of reject-water and the quick loss of alkalinity during nitrification makes a reliable control of the process necessary. A sequencing batch reactor (SBR) with an operational control based on on-line measurement of the pH
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Emond, Matthieu, Jing Sun, Jean Grégoire, Sylvie Maurin, Christophe Tribet, and Ludovic Jullien. "Photoinduced pH drops in water." Physical Chemistry Chemical Physics 13, no. 14 (2011): 6493. http://dx.doi.org/10.1039/c0cp02464c.

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Crans, Debbie C., and Nancy E. Levinger. "The Conundrum of pH in Water Nanodroplets: Sensing pH in Reverse Micelle Water Pools." Accounts of Chemical Research 45, no. 10 (2012): 1637–45. http://dx.doi.org/10.1021/ar200269g.

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Vilagines, Ph, B. Sarrette, G. Husson, and R. Vilagines. "Concentration à Ph neutre des virus hydriques dans des eaux de surface : étude quantitative et qualitative." Journal français d’hydrologie 20, no. 2 (1989): 193–201. http://dx.doi.org/10.1051/water/19892002193.

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Pratama, I. Putu Yoga pramesia, Kadek Suar Wibawa, and I. Made Agus Dwi Suarjaya. "Perancangan PH Meter Dengan Sensor PH Air Berbasis Arduino." JITTER : Jurnal Ilmiah Teknologi dan Komputer 3, no. 2 (2022): 1034. http://dx.doi.org/10.24843/jtrti.2022.v03.i02.p02.

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Kebutuhan akan air bersih sekarang ini semakin tinggi dengan lingkungan di era globalisasi yang sangat tinggi akan nilai pencemaran airnya. Salah satu hal yang patut diperhatikan dalam mengetahui tingkat kebersihan air adalah dengan mengukur kadar PH air tersebut, apakah tergolong ke dalam larutan asam, netral atau basa. Proses pengukuran kadar PH air tersebut dapat dilakukan dengan menggunakan sensor PH air yang merupakan sensor yang dapat mengecek tingkat keasaaman suatu larutan, sensor PH air dihubungkan dengan mikrokontroler Arduino mega sebagai pengolah data. Cara kerja dari sensor PH air
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Vikulin, Pavel Dmitrievich, and Vera Borisovna Vikulina. "EFFECT OF ULTRASOUND ON PH CHANGE IN WATER." Water and Ecology 24, no. 4 (2019): 3–8. http://dx.doi.org/10.23968/2305-3488.2019.24.4.3-8.

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Dissertations / Theses on the topic "Water pH"

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Botfield, Andrew Civil &amp Environmental Engineering Faculty of Engineering UNSW. "Kinetic modelling studies of As(III) oxidation in dark pH 3 and 8 Fenton - mediated and pH 8 Cu(II) - H2O2 systems." Awarded by:University of New South Wales. School of Civil and Environmental Engineering, 2006. http://handle.unsw.edu.au/1959.4/31969.

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In this thesis, a combination of laboratory experimentation under well defined conditions coupled with a kinetic modelling approach is used to verify the existence and respective kinetic rates of previously unconfirmed or postulated mechanisms that drive and limit dark Fenton (Fe(II)/H2O2) - mediated As(III) oxidation at pH 3 and 8 and dark Cu(II) - H2O2 - mediated As(III) oxidation at pH 8. Dark Fenton - mediated oxidation of As(III) at pH 3 is first examined and the effects of the variation in the concentration of reactants (As(III), Fe(II) and H2O2), oxygen, phosphate and organics (2 - prop
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Bohn, Hinrich L., Henry Schreiber, and Loel R. Cooper. "Rainfall pH in Tombstone, Arizona, 1968-81." Arizona-Nevada Academy of Science, 1986. http://hdl.handle.net/10150/296369.

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From the Proceedings of the 1986 Meetings of the Arizona Section - American Water Resources Association, Hydrology Section - Arizona-Nevada Academy of Science and the Arizona Hydrological Society - April 19, 1986, Glendale Community College, Glendale, Arizona<br>Rainfall pH was measured at the Tombstone, Arizona, USDA-ARS station from 1968 to 1981. The summer rains were more acidic than the winter rains. The pH of the summer rains was about pH 5, the winter rains about pH 6, with considerable variation. The summer rain pH increased gradually over this period, coinciding with a general decrease
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Baker, Paul B. "Influence of pH 11 Water on Termiticide Degradation in Arizona." College of Agriculture and Life Sciences, University of Arizona (Tucson, AZ), 2001. http://hdl.handle.net/10150/216349.

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Termites continue to be Arizona’s number one urban pest. Factors that influence the persistence of termiticides are constantly under investigation. High pH has been identified as a potential concern for persistence in termiticides. I studied the influence of pH 11 water on five termiticides applied to commercial ABC fill 10 months post-treatment. In general, the addition of pH 11 water had little influence on termiticide persistence under Arizona conditions. Initially plots treated with Ph 11 water had higher residues than those that did not receive the treated water; over time these differenc
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Gorshkova, M. Yr, I. V. Volkova, E. S. Grigorian, and V. A. Izumrudov. "Polyelectrolyte Nanocomplexes with pH-controlled Solubility." Thesis, Sumy State University, 2013. http://essuir.sumdu.edu.ua/handle/123456789/35468.

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The prepared polyelectrolyte complexes of anionic copolymer of divinyl ester and maleic anhydride and cationic water soluble chitosan proved to be able to undergo reversible phase transition, in particular at physiological pH and ionic strength. Formation of either soluble or insoluble complexes occurred depending on pH value, charge ratio and degree of polymerization of the polymers. The stability of positively or negatively charged complexes against destruction action of the added salt drastically increased in acidic media presumably owing to H-bonds formation. According to light-scatte
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de, la Haye Kate. "The behavioural consequences of reduced sea water pH in decapod crustaceans." Thesis, University of Plymouth, 2012. http://hdl.handle.net/10026.1/1028.

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The studies presented in this thesis were designed to investigate the effects of reduced sea water pH on the behaviour of intertidal decapod crustaceans, both within the context of the variations occurring naturally in the pH of rock pool habitats, and in relation to predicted changes to ocean pH resulting from ocean acidification and potential carbon dioxide (CO2) leaks from carbon capture storage (CCS) sites. Recent studies on marine fish have shown behavioural disruptions as a result of increased CO2 concentrations in sea water and reduced pH, but the effects on crustaceans are as yet unkno
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Watker, A. F. "A study into the alteration of pH through water distribution systems." Thesis, University of Glasgow, 1985. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.381109.

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Williams, N. L., L. W. Juranek, K. S. Johnson, et al. "Empirical algorithms to estimate water column pH in the Southern Ocean." AMER GEOPHYSICAL UNION, 2016. http://hdl.handle.net/10150/614732.

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Empirical algorithms are developed using high-quality GO-SHIP hydrographic measurements of commonly measured parameters (temperature, salinity, pressure, nitrate, and oxygen) that estimate pH in the Pacific sector of the Southern Ocean. The coefficients of determination, R-2, are 0.98 for pH from nitrate (pH(N)) and 0.97 for pH from oxygen (pH(Ox)) with RMS errors of 0.010 and 0.008, respectively. These algorithms are applied to Southern Ocean Carbon and Climate Observations and Modeling (SOCCOM) biogeochemical profiling floats, which include novel sensors (pH, nitrate, oxygen, fluorescence, a
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Fürtjes, Theresa Verfasser], and Stephan [Akademischer Betreuer] [Schreml. "Impact of a pH 5 Oil-in-Water (O/W) Emulsion on Skin Surface pH / Theresa Fürtjes ; Betreuer: Stephan Schreml." Regensburg : Universitätsbibliothek Regensburg, 2018. http://nbn-resolving.de/urn:nbn:de:bvb:355-epub-367214.

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Fürtjes, Theresa [Verfasser], and Stephan [Akademischer Betreuer] Schreml. "Impact of a pH 5 Oil-in-Water (O/W) Emulsion on Skin Surface pH / Theresa Fürtjes ; Betreuer: Stephan Schreml." Regensburg : Universitätsbibliothek Regensburg, 2018. http://d-nb.info/1152437542/34.

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Grant, Annie, and Ingrid Luffman. "IS WATER QUALITY IN BOONE LAKE A DAM PROBLEM? AN ASSESSMENT OF WATER QUALITY PRE- AND POST- DRAWDOWN." Digital Commons @ East Tennessee State University, 2018. https://dc.etsu.edu/asrf/2018/schedule/115.

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Boone Lake was formed in 1952 by the impoundment of the South Fork Holston River in Sullivan and Washington counties, TN. The “V” shaped lake spans 6.88 square miles; it consists of two primary tributaries of approximately equal-length which meet just above the dam. South Fork Holston River makes up the northern arm and Watauga River feeds the southern arm. In October 2014, the discovery of a sinkhole led to detection of sediment-laden seepage under the earthen part of the dam. As a safety precaution, the reservoir was immediately lowered to an elevation of 1,352.5 feet, 10 feet below operatio
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Books on the topic "Water pH"

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Russell, Stephen. pH: A guide to measurement in water applications. WRc, 1994.

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Emerson, A. G. D. Alkalinity, pH changes with temperature for waters in industrial systems. E. Horwood, 1986.

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Butkus, Steven R. Factors affecting waters with a high pH: Statewide analysis. Washington State Dept. of Ecology, Environmental Assessment Program, 2002.

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A, Lytle Darren, Clement Jonathan A, and National Risk Management Research Laboratory (U.S.), eds. Effect of pH, DIC, orthophosphate, and sulfate on drinking water cuprosolvency. National Risk Management Research Laboratory, Office of Research and Development, U.S. Environmental Protection Agency, 1995.

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Pogue, Ted R. Processes controlling dissolved oxygen and pH in the upper Willamette River basin, Oregon, 1994. U.S. Dept. of the Interior, U.S. Geological Survey, 1995.

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Pogue, Ted R. Processes controlling dissolved oxygen and pH in the upper Willamette River basin, Oregon, 1994. U.S. Dept. of the Interior, U.S. Geological Survey, 1995.

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Pogue, Ted R. Processes controlling dissolved oxygen and pH in the upper Willamette River basin, Oregon, 1994. U.S. Dept. of the Interior, U.S. Geological Survey, 1995.

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Limited, Boojum Research. pH history and potential pH development for 1996 and 1998 water samples from selected piezometers at South Bay. Boojum Research, 2000.

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Fiske, Steven. Macroinvertebrate survey of 25 soft water-pH sensitive lakes in Vermont. Special Studies & Surveillance Unit, Dept. of Environmental Conservation, 1987.

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Hall, David W. Temperature, pH, conductance, and dissolved oxygen in cross sections of 11 Lake Michigan tributaries, 1994-95. U.S. Dept. of the Interior, U.S. Geological Survey, 1998.

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Book chapters on the topic "Water pH"

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Boyd, Claude E. "pH, Carbon Dioxide, and Alkalinity." In Water Quality. Springer US, 2000. http://dx.doi.org/10.1007/978-1-4615-4485-2_7.

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Boyd, Claude E. "pH, Carbon Dioxide, and Alkalinity." In Water Quality. Springer International Publishing, 2015. http://dx.doi.org/10.1007/978-3-319-17446-4_8.

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Boyd, Claude E. "Carbon Dioxide, pH, and Alkalinity." In Water Quality. Springer International Publishing, 2019. http://dx.doi.org/10.1007/978-3-030-23335-8_9.

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Bonner, Philip L. R. "Water, pH and Buffers." In Protein Purification. Taylor & Francis, 2018. http://dx.doi.org/10.1201/9780429458187-1.

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Lung, Wu-Seng. "Modeling Analysis for pH." In Water Quality Modeling That Works. Springer International Publishing, 2022. http://dx.doi.org/10.1007/978-3-030-90483-8_5.

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Wesolowski, David J., Donald A. Palmer, and Robert E. Mesmer. "Measurement and control of pH in hydrothermal solutions." In Water-Rock Interaction. Routledge, 2021. http://dx.doi.org/10.1201/9780203734049-12.

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Grozdanov, Anita, Aleksandar Petrovski, Perica Paunovik, Aleksandar T. Dimitrov, and Maurizio Avella. "MWCNT/Polyaniline Nanocomposites Used for pH Nanosensors of Marine Waters." In Springer Water. Springer International Publishing, 2017. http://dx.doi.org/10.1007/978-3-319-71279-6_32.

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Gasse, F. "East african diatoms and water pH." In Diatoms and Lake Acidity. Springer Netherlands, 1986. http://dx.doi.org/10.1007/978-94-009-4808-2_12.

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Bertorino, G., A. M. Caredda, A. Ibba, and P. Zuddas. "Weathering of Pb-Zn mine tailings in pH buffered environment." In Water-Rock Interaction. Routledge, 2021. http://dx.doi.org/10.1201/9780203734049-214.

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Alekseyev, V. A., L. S. Medvedeva, N. I. Prisyagina, S. S. Meshalkin, V. G. Senin, and S. I. Andrianova. "Kinetics of feldspar dissolution at 300°C and pH 9." In Water-Rock Interaction. Routledge, 2021. http://dx.doi.org/10.1201/9780203734049-33.

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Conference papers on the topic "Water pH"

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Garber, James D., Vamshidhar R. Jangama, and Jeffery Willmon. "Parameters Affecting Downhole pH." In CORROSION 1997. NACE International, 1997. https://doi.org/10.5006/c1997-97606.

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Abstract The presence of acetic and formic acids in the produced water of gas condensate wells has been known for some time by the industry. In traditional water analysis, it has been titrated and reported as alkalinity. The calculation of accurate downhole pH values requires that these ions be analyzed separately in the water and that an organic acid material balance be performed on all three phases in the separator. In this manner, it is then possible to use phase distribution coefficients involving ionic equilibrium to determine how these acids distribute themselves between phases as the pH
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Amjad, Zahid, Libardo Perez, and Robert W. Zuhl. "Water Chemistry Impacts on Cooling Water System Iron Oxide Dispersants." In CORROSION 2015. NACE International, 2015. https://doi.org/10.5006/c2015-05996.

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Abstract The effects of water chemistry such as total dissolved solids, polyvalent metal ions, pH, and temperature on particulate iron oxide dispersion by a variety of polymeric additives have been investigated. The deposit control polymers (DCPs) evaluated include synthetic polymers (of varying composition and molecular weight). Results reveal that DCP iron oxide dispersant performance strongly depends on dosage and architecture (e.g., type and amount of monomers, monomer functional group ionic charge, molecular weight). Data show that pH changes cause varying but relatively small changes in
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Sherwood, Nancy S. "Inhibitor Performance in Process Water Containing Ammonia." In CORROSION 1998. NACE International, 1998. https://doi.org/10.5006/c1998-98572.

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Abstract Ammonia is a prevalent contaminant and issue in water reuse. Since ammonia exhibits decreasing dissociation with increasing pH, operation of cooling systems at high pH is effective in improving corrosion control, biocide demand and overall system performance. Polyamino polyether methylene phosphate based programs for high pH conditions provided scale and corrosion control at very high levels of ammonia contamination at a northern steel mill.
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Mouleeshuwarapprabu, R., K. Rajkumar, T. Kalavathidevi, S. Suganth, and P. Revathi. "Wireless Process Control For Monitoring Level and pH of Water." In 2024 15th International Conference on Computing Communication and Networking Technologies (ICCCNT). IEEE, 2024. http://dx.doi.org/10.1109/icccnt61001.2024.10724633.

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Olsen, Stein, and Anne Marie Koren Halvorsen. "Corrosion Control by pH Stabilization." In CORROSION 2015. NACE International, 2015. https://doi.org/10.5006/c2015-05733.

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Abstract The pH stabilization technique is a method for control of sweet corrosion in wet gas pipelines. The method is suited for systems with MEG for hydrate control as the pH stabilizer will remain in the lean MEG and do not need a continuous injection. Full pH stabilization is used when the risk for production of formation water is negligible as formation water will lead to calcium carbonate scaling. Partial pH stabilization combined with a film forming inhibitor may be an alternative when some formation water may be produced. This method has also been applied without MEG. The biggest chall
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Kunz, Robert G., and Donald W. Hines. "Corrosion of Zinc in Cooling Water." In CORROSION 1990. NACE International, 1990. https://doi.org/10.5006/c1990-90348.

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Abstract An effective corrosion inhibitor must protect all metallic components in a cooling system, including the zinc coating of a galvanized cooling tower. This is especially important with the current trend toward more alkaline cooling water treatments.1 Higher pH levels combined with newer deposit control agents may minimize corrosion, scaling, and fouling in the coolers but can simultaneously cause premature failure of a cooling tower made of galvanized steel. Too low a pH without proper corrosion inhibition can also pose a problem. Following a brief review of theory and previous work, th
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Alyaseen, Jafar, and Eid Albalawi. "A Fuzzy-Based System for Water pH and Conductivity Level Management." In 2025 4th International Conference on Computing and Information Technology (ICCIT). IEEE, 2025. https://doi.org/10.1109/iccit63348.2025.10989353.

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Roti, J. S., and M. M. Mullins. "Operating Experiences in Treating Alkaline, No pH Control Cooling Water Systems." In CORROSION 1989. NACE International, 1989. https://doi.org/10.5006/c1989-89158.

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Abstract Alkaline, no-pH control cooling water treatment applications represent a growing market in today's industrial environment. Many plants prefer to not feed acid to their open recirculating cooling systems to destroy alkalinity and lower pH because of the inherent handling and safety considerations of this material. Other plants view the use of acid as just another source of system upset should this material be over or under fed. This paper reviews the rationale of why more facilities are moving to this technology, outlines a number of treatment programs which are available to effectivel
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Lewandowski, Zbigniew, Whon Chee Lee, William G. Characklis, and Brenda Little. "Dissolved Oxygen and pH Microelectrode Measurements at Water Immersed Metal Surfaces." In CORROSION 1988. NACE International, 1988. https://doi.org/10.5006/c1988-88093.

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Abstract Dissolved oxygen and pH were measured at metal/artificial sea water interfaces using microelectrodes in biotic and abiotic systems. Measurements in a closed system suggested that presence of electrochemical and/or biological reaction products substantially influence the conditions at the metal surface. For long term studies, only open (e.g. continuous flow) reactors should be used. An open channel flow reactor suitable both for microbiological and electrochemical measurements has been constructed and successfully tested.
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Fuller, Ross K., and John W. McCarthy. "Recovery from Low pH Excursions in Cooling Water Systems Using All-Organic Treatment Programs." In CORROSION 1987. NACE International, 1987. https://doi.org/10.5006/c1987-87158.

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Abstract A low pH excursion can cause severe damage to an open recirculating cooling system which can cause a plant to shut down. With properplanning, the probability of having a pH excursion can be reduced but not eliminated entirely. Assuming that an accidental excursion has a finite probability of occurring, proper planning can minimize the effects of low pH. Once control of pH has been regained after a low pH excursion, a program of repassivation is necessary to minimize corrosion of active metal surfaces. Depending upon the severity of an excursion, repassivation using an all-organic corr
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Reports on the topic "Water pH"

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Daniel P. Molloy. IMPACT OF WATER PH ON ZEBRA MUSSEL MORTALITY. Office of Scientific and Technical Information (OSTI), 2002. http://dx.doi.org/10.2172/811450.

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Goldoni, Riccardo. Laboratory Tales: Check the pH of your water! ResearchHub Technologies, Inc., 2023. http://dx.doi.org/10.55277/researchhub.d7kk6e0n.

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Campobasso, Marissa, Musa Ibrahim, Amanda Chisholm, Julia Miazek, and Martin Page. pH pivoting for algae coagulation : bench-scale experimentation. Engineer Research and Development Center (U.S.), 2024. http://dx.doi.org/10.21079/11681/48611.

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Harmful algal blooms (HABs) threaten recreational waters and public supplies across the US, causing detrimental economic and environmental effects to communities. HABs can be mitigated with dissolved air flotation (DAF) treatment, which requires addition of pH-sensitive charged chemicals to neutralize algae, allowing them to attach to microbubbles and float to the surface. During HAB events and photosynthesis, algae raise the pH to levels that are not ideal for DAF. Traditionally, pH is reduced with a strong acid; however, this adds operational cost and permanently adjusts the water’s pH. This
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Wright, Wendy, M. Gregory, and Aaron Rinehart. Fixed-station water quality monitoring at Cumberland Island National Seashore: 2011 data summary. National Park Service, 2012. https://doi.org/10.36967/2190432.

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In 2006, the National Park Service (NPS) Southeast Coast Network (SECN) Inventory and Monitoring Program began collecting water-quality data in the estuarine waters near Cumberland Island National Seashore (CUIS) as part the NPS Vital Signs monitoring program. The CUIS station collected pH, dissolved oxygen, temperature, salinity, conductivity, turbidity and waterlevel data. Additional water-quality measurements were made by SECN staff and include monthly measurements of water clarity conditions, nutrients (total dissolved phosphorus [TDP] and total dissolved nitrogen [TDN]), and chlorophyll a
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Rinehart, Aaron, Wendy Wright, and M. Gregory. Fixed-station water-quality monitoring at Congaree National Park: Data Summary 2012. National Park Service, 2013. https://doi.org/10.36967/2195210.

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In 2006 Congaree National Park (CONG), in conjunction with the Southeast Coast Network (SECN) Inventory and Monitoring Program, began collecting water-quality data at Cedar Creek as part the NPS Vital Signs Monitoring Program. The continuous-monitoring data station is located approximately one mile south of the visitor center and collects water temperature, dissolved oxygen, pH, specific conductance, turbidity and water-level data every 30 minutes. This publication summarizes data collected from January 1, 2012 to December 31, 2012. The CONG fixed-station water-quality monitoring site is part
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Gregory, M., Wendy Wright, and Aaron Rinehart. Fixed-station water quality monitoring at Fort Matanzas National Monument: 2011 data summary. National Park Service, 2012. https://doi.org/10.36967/2190459.

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In 2010 the National Park Service (NPS) Southeast Coast Network (SECN) Inventory and Monitoring Program began collecting water-quality data in the estuarine waters near Fort Matanzas National Monument (FOMA) as part the NPS Vital Signs monitoring program. The continuous-monitoring data station is located at the visitors center dock. This station collects pH, dissolved oxygen, temperature, salinity, specific conductance, turbidity and water-level data every 30 minutes. Information collected by this monitoring program will be used to help managers make better-informed decisions by understanding
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Wright, Wendy, M. Gregory, and Aaron Rinehart. Fixed station water quality monitoring at Cape Hatteras National Seashore: 2010 data summary. National Park Service, 2012. https://doi.org/10.36967/2190306.

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In 2005 the National Park Service (NPS) Southeast Coast Network (SECN) Inventory and Monitoring Program began collecting water-quality data in the estuarine waters near Cape Hatteras National Seashore (CAHA) as part the NPS Vital Signs monitoring program. The continuous monitoring data station is located at a dock at the Ocracoke Village boat ramp. This station collects pH, dissolved oxygen, temperature, salinity, conductivity, turbidity and water level data every 30 minutes. Additional water quality measurements are made by SECN staff and include monthly measurements of water clarity conditio
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8

Mukerjee, Sanjeev, Ian Kendrick, Serge Pann, et al. Enabling Efficient Water Splitting with Advanced Materials Designed for High pH Membrane Interface. Office of Scientific and Technical Information (OSTI), 2021. http://dx.doi.org/10.2172/1963502.

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9

Hynds, Mark, Wendy Wright, Eric Starkey, and Wendy Wright. Fixed-station water-quality monitoring at Cumberland Island National Seashore: 2015–2016 data summary. National Park Service, 2018. https://doi.org/10.36967/2257646.

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In 2010 the National Park Service (NPS) Southeast Coast Network (SECN) Inventory and Monitoring Program began collecting water-quality data in the estuarine waters near Fort Matanzas National Monument (FOMA) as part of the NPS Vital Signs monitoring program. The continuous-monitoring station is located at the visitors center dock. This station collects pH, dissolved oxygen, temperature, salinity, specific conductance, turbidity, and water-level data every 30 minutes. The FOMA fixed-station water-quality monitoring site is part of the SECN estuarine water-quality monitoring program, which routi
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10

Hynds, Mark, Wendy Wright, Eric Starkey, and Wendy Wright. Fixed-station water-quality monitoring at Fort Matanzas National Monument: 2015–2016 data summary. National Park Service, 2018. https://doi.org/10.36967/2257645.

Full text
Abstract:
In 2010 the National Park Service (NPS) Southeast Coast Network (SECN) Inventory and Monitoring Program began collecting water-quality data in the estuarine waters near Fort Matanzas National Monument (FOMA) as part of the NPS Vital Signs monitoring program. The continuous-monitoring station is located at the visitors center dock. This station collects pH, dissolved oxygen, temperature, salinity, specific conductance, turbidity, and water-level data every 30 minutes. The FOMA fixed-station water-quality monitoring site is part of the SECN estuarine water-quality monitoring program, which routi
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