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Books on the topic 'Water Quality Parameters'

Author: Grafiati

Published: 4 June 2021

Last updated: 11 September 2023

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1

Flanagan, P. J. Parameters of water quality: Interpretation and standards. Dublin: Foras Forbartha, 1986.

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2

Flanagan, P. J. Parameters of water quality: Interpretation and standards. 2nd ed. Dublin: Environmental Research Unit, 1990.

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3

Agency, Ireland Environmental Protection. Parameters of water quality: Interpretation and standards. Johnstown Castle, Wexford: Environmental Protection Agency, 2001.

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4

LeChevallier, Mark W. Profiling water quality parameters: From source water to the household tap. Denver, CO: Awwa Research Foundation, 2004.

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5

Arizona. Department of Environmental Quality. Lakeside Lake TMDL: Nutrients & associated parameters. Phoenix, Ariz.]: Arizona Dept. of Environmental Quality, 2005.

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6

Kalin, Margarete A. Water quality concerns and treatment parameters for Armanda Lake. Toronto, Ont: Boojum Research, 2001.

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7

J, Gilliom Robert, and Geological Survey (U.S.), eds. Estimation of distributional parameters for censored trace-level water-quality data. Reston, Va: U.S. Dept. of the Interior, Geological Survey, 1985.

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8

Helsel, Dennis R. Estimation of distributional parameters for censored trace-level water-quality data. Reston, Va: U.S. Dept. of the Interior, Geological Survey, 1985.

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9

Helsel, Dennis R. Estimation of distributional parameters for censored trace-level water-quality data. Reston, Va: U.S. Dept. of the Interior, Geological Survey, 1985.

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10

Bourbonniere, Richard A. Depositional history of sediments in Legend and Weekes Lakes: Geochronology and bulk parameters. Edmonton, Alta: Northern River Basins Study, 1996.

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11

Bourbonniere, Richard A. paul Depositional history of sediments in Lake Athabasca: Geochronology, bulk parameters, contaminants and biogeochemical markers. Edmonton, Alta: Northern River Basins Study, 1996.

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12

Bukata, R. P. Application of direct measurements of optical parameters to the estimation of lake water quality indicators. Burlington, Ont: Inland Waters Directorate, 1985.

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13

Caskey, B. J. Relations of stream fish communities to physical and chemical parameters and land use in the Mississippi Alluvial Plain Ecoregion. Jackson, Miss: U.S. Dept. of the Interior, U.S. Geological Survey, 2003.

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14

Directorate, Canada Environment Canada Inland Waters. Application of Direct Measurements of Optical Parameters to the Estimation of Lake Water Quality Indicators. S.l: s.n, 1985.

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15

1944-, Scott H. Don, and Arkansas Agricultural Experiment Station, eds. Geographical and statistical relationships between landscape parameters and water quality indices in an Arkansas watershed. Fayetteville, Ark: Arkansas Experiment Station, 1992.

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16

Harwood-Matthews, Simon. The chemistry of the LoosdrechtLakes and its relationship with remotely sensed optical water quality parameters. Wolverhampton: University of Wolverhampton 1993., 1993.

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17

Lee, K. E. Water-quality parameters and benthic algal communities at selected streams in Minnesota, August 2000: Study design, methods, and data. Mounds View, MN: U.S. Dept. of the Interior, U.S. Geological Survey, 2002.

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18

Chen, Kai. Set membership estimation of state and parameters and operational control of integrated quantity and quality models of water supply and distribution systems. Birmingham: University of Birmingham, 1997.

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19

Rossknecht, Henno. Langjährige Entwicklung chemischer Parameter im Bodensee-Obersee. [Reichenau]: Internationale Gewässerschutzkommission für den Bodensee, 1998.

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20

Groschen, G. E. Evaluation of measurements collected with multi-parameter continuous water-quality monitors in selected Illinois streams, 2001-03. Reston, Va: U.S. Geological Survey, 2005.

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21

Holmes, K. John. Field application of parameter identification in groundwater contaminant transport modeling: A case study. Seattle: University of Washington, Dept. of Civil Engineering, 1987.

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22

New York (State). Division of Water. Bureau of Monitoring and Assessment, ed. Report of the fixed station conventional parameter water quality surveillance network, 1985. [Albany, N.Y.?]: New York State/Dept. of Environmental Conservation, 1986.

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23

Amatya, Devendra. Lumped parameter models for predicting nitrogen loading from lower coastal plain watersheds. Raleigh, NC: Water Resources Research Institute of the University of North Carolina, 2003.

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24

Scalamera, Robert. Proposal of a total maximum daily load for Tonto Creek (headwaters to Haigler Creek): Salt River Watershed, Tonto National Forest near Payson, Gila County, Arizona : parameter, total nitrogen. Phoenix, AZ]: Arizona Dept. of Environmental Quality, 2005.

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25

Guyer, J. Paul. Introduction to Reservoir Water Quality Parameters. Independently Published, 2017.

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26

Keith, Lawrence H. Epa's Sampling and Analysis Methods Database: Elements and Water Quality Parameters. CRC, 1990.

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27

Profiling Water Quality Parameters: From Source Water to the Household Tap (Awwa Research Foundation Reports). Awwarf, 2005.

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28

U.S. Department of the Interior. Sediment Loads and Yield, and Selected Water-Quality Parameters in Clear Creek, Carson City and Douglas County, Nevada, Water Years 2004-07. CreateSpace Independent Publishing Platform, 2014.

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29

Ess, Erica Van. Investigation of the presence and change over time of water quality parameters in selected natural swimming areas in Oregon. 1997.

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30

Chiou, Wen-An, Helmut Coutelle, Andreas Decher, Michael Dörschug, Reiner Dohrmann, Albert Gilg, Stephan Kaufhold, et al. Bentonites -. Edited by Stephan Kaufhold. E. Schweizerbart Science Publishers, 2021. http://dx.doi.org/10.1127/bentonites/9783510968596.

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<p><b>Bentonites</b> are rocks mostly consisting of swelling clay minerals. They were first described from the Cretaceous Benton Shale near Rock River, Wyoming, USA. </p> <p> Because of their useful properties (e.g. highly adsorbent, cation exchanging, swelling), bentonites have many uses, in industry (among them as drilling mud, purification agent, binder, adsorbent, paper production), culture (for e.g. pottery) and medicine/cosmetics/cat litter, civil engineering, and in the future even in the disposal of high-level nuclear waste. </p> <p> Particular chemical characteristics of bentonite clay minerals are rather variable but critically determine their suitability for a particular application. </p> <p> The 15 specialist authors discuss bentonite terminology, classification and genesis and use in eight chapters. Individual chapters deal with the methods bentonites are analysed with, their properties and performance in terms of parameters such as cation exchange capactiy, rheology, coagulation concentraion, water uptake capacity, free swelling, and electrical resistivity (amongst others). </p> <p> A chapter is dedicated to the sources of bentonites, the technology employed to produce them, and how quality control is carried out both in the mine and the laboratory. A further chapter is dedicated to methods of processing the mined material, different activation methods, drying, grinding, and purification. </p> <P> Use cases for bentonites are discussed in a chapter of its own. References, a section on norms and standards, and a list of abbreviations complete the text. </p> <p> The volume addresses students, researchers, and professionals in the mineral industry dealing with bentonite and their clay-mineral constituents, quality assessement and control, and persons that use bentonites in their products. </p>

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31

Marshall, Mark R. Intermittent acute renal replacement therapy. Edited by Norbert Lameire. Oxford University Press, 2018. http://dx.doi.org/10.1093/med/9780199592548.003.0233_update_001.

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This chapter summarizes current best practice with respect to intermittent haemodialysis and sustained low-efficiency dialysis (SLED) for those with acute kidney injury. These modalities can be delivered using a variety of technology platforms. These platforms for the most part use online dialysate, and water quality needs to be monitored and maintained to current standards. Intermittent haemodialysis and SLED provide reasonable outcomes in experienced hands, and ameliorate morbidity and mortality resulting from the ‘acute uraemic syndrome’: that is, intractable infection, non-resolving shock, and haemorrhage.Careful consideration needs to be given to appropriate modality selection for patients. Lower-efficiency modalities such as continuous therapies or SLED are more appropriate for patients at risk from dialysis disequilibrium syndrome, those with abdominal compartment syndrome, and those who are haemodynamically unstable (including cardiogenic shock). Care should be taken to avoid complications related to rapid fluid and solute removal, anticoagulation, and vascular access. Intradialytic hypotension is detrimental for both general and renal recovery of critically ill patients, and can be mitigated by sodium and ultrafiltration profiling, and frequent treatments and prolonged treatment time to minimize ultrafiltration goals and rates.Irrespective of the modality applied, an adequate dialysis dose must be achieved. This is facilitated through the use of optimally placed and technically superior central venous catheters, and well-considered prescription of haemodialysis and SLED operating parameters. Dose should be monitored regularly through urea kinetic modelling, either using Kt/V for thrice-weekly schedules or the corrected equivalent renal urea clearance (EKRc) for more frequent ones.

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