Abstract
A single-bed ion-exchange process for nitrate removal from water supplies has been studied extensively in the laboratory and in the field. In the conventional mode, nitrate removal is achieved by passing a portion of the feedwater through a fixed bed of chloride-form, strong-base anion resin, and blending the nitrate-free effluent with raw water to produce a blended product water with less than 10 mg/L NO3-N.
The theoretical and actual effects of sulfate concentration, sulfate/nitrate selectivity, resin type and empty bed contact time were studied during the exhaustion cycle. During pilot-scale field tests in Glendale, Arizona it was found that the end of a run could be reliably determined by bed volumes throughput or by the pH increase (0.6-1.0 pH) which accompanied nitrate breakthrough.
Regeneration was accomplished using NaCl but was not particularly efficient. In fact, for complete regeneration (3.5 eq Cl-/eq resin), 10 eq of Cl- were typically required for each eq of nitrate removed from the feedwater. It was discovered that substantial savings in NaCl could be achieved by using dilute (0.25-0.50 N NaCl) regenerants which minimize the effect of electroselectivity reversal on sulfate elution. Also, partial regeneration (1.0 eq Cl-/eq resin) followed by 7.0 mg/L NO3-N leakage during exhaustion (using a 20 mg/L NO3-N feedwater) was found to be feasible and less costly than complete regeneration with zero leakage and bypass blending.
A 4000 m3/day (blended product water) treatment plant to reduce nitrate from 21 mg/L to less than 10 mg/1 in a 600 mg/L TDS background containing 100 mg/L So 2-4 would cost about $300,000. Operating costs including capital recovery would be approximately 0.07 $/m3 of product water.
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References
World Health Organization, “European Standards for Drinking Water,” 2nd Ed., Geneva, 1970.
U.S. Environmental Protection Agency, “National Interim Primary Drinking Water Regulations,” EPA-570/9-76-003, 1972.
Green, L.A. Water Pollution Control, V. 77, No. 4, p. 478, 1978.
Holzmacher, R.G., Water and Sewage Works, p. 210, July 1971.
Holl, W. and B. Kiehling, Water Research, V. 15, p. 1027, 1981.
Clifford, D.A. and W.J. Weber, Jr., EPA Report No. EPA-600/2- 78 - 052, June 1978.
Clifford, D.A. and M.R. Bilimoria, Final EPA Report on Crant No. CR-806073, also University of Houston CE report UH CE 83XX.
Guter, G.A., USEPA Interim Report EPA-600/S2-81-029; also final EPA Report on Grant R-805900, 1982.
Gauntlett, R.B. Water Treatment and Examination, V. 24, Part III, p. 172, 1975.
Clifford, D.A. and W.J. Weber, Jr., Reactive Polymers, V. 1, p. 77, 1983.
Helfferich, F.G., Multicomponent Chromatography, Xerox Univ. Microfilms, Ann Arbor, originally Marcel Dekker, 1970.
Clifford, D.A. Ind. & Eng. Chem. Fundamentals, V. 21, P. 141, May 1982.
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© 1985 Martinus Nijhoff Publishers, Dordrecht
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Clifford, D., Horng, LL., Lin, CC. (1985). Salt Conservation, Selectivity Reversal and Breakthrough Detection in Ion Exchange for Nitrate Removal. In: Liberti, L., Millar, J.R. (eds) Fundamentals and Applications of Ion Exchange. Nato ASI Series, vol 98. Springer, Dordrecht. https://doi.org/10.1007/978-94-009-5161-7_10
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DOI: https://doi.org/10.1007/978-94-009-5161-7_10
Publisher Name: Springer, Dordrecht
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