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Waste disposal by ridge and furrow irrigationSchraufnagel, F. H. January 1962 (has links)
Thesis (M.S.)--University of Wisconsin--Madison, 1962. / Typescript. eContent provider-neutral record in process. Description based on print version record. Includes bibliographical references (leaves 51-55).
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The utilization of treated municipal wastewater for crop production in Buckeye, ArizonaMcFadyen, John Alexander, January 1976 (has links) (PDF)
Thesis (M.S. - Plant Sciences)--University of Arizona. / Includes bibliographical references.
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The physical and chemical properties of soils and growth of plants as affected by irrigation with sewage effluentSessing, John Roy, January 1961 (has links)
Thesis (Ph. D.)--University of Wisconsin--Madison, 1961. / Typescript. Vita. eContent provider-neutral record in process. Description based on print version record. Includes bibliographical references.
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Some effects of treated municipal wastewater on oats (Avena sativa L.)Kirkpatrick, Richard Michael, January 1972 (has links) (PDF)
Thesis (M.S. - Agronomy and Plant Genetics)--University of Arizona. / Includes bibliographical references.
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Numerical modelling of nitorogen leaching from effluent irrigation on Great Barrier Reef islands /Gallagher, Mark Robert. January 2002 (has links) (PDF)
Thesis (M.Eng.Sc.) - University of Queensland, 2003. / Includes bibliography.
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DEVELOPMENT OF A METHOD FOR THE RECOVERY OF ROTAVIRUSES FROM VEGETABLES AND ITS APPLICATION FOR ROTAVIRUS SURVIVAL ON CROPS.BADAWY, AMIN SOLIMAN. January 1986 (has links)
As the shortage of fresh water becomes more and more critical, alternative sources are being sought. The reuse of wastewater has become a viable option, particularly for agriculture and landscaping. However, the possible presence of the enteric pathogens, especially viruses, in wastewater has created concern about potential health risks associated with this practice. If wastewater is used for irrigation it may contaminate vegetable crops which are commonly eaten raw. Also, it may contaminate grass used for golf courses, school yards, and playgrounds where more people may be exposed. Rotaviruses may be of particular concern since they are a cause of infantile diarrhea and gastroenteritis in adults and have been a cause of waterborne disease outbreaks. No information, however, is available about the dissemination and survival of rotaviruses on uncooked food and landscaped areas. This information is necessary in developing criteria for determining safe uses of wastewater for crop irrigation. A method was developed for recovery of rotavirus from the surface of vegetables. The simian rotavirus SA-11, adsorbed onto the vegetable surfaces and effects of various eluents, pH, and exposure time, was evaluated to optimize recovery. The maximum recovery of rotavirus occurred with a solution of 3% beef extract at pH 8.0 after 5 minutes of exposure. Survival of rotavirus SA-11 on lettuce, radishes, and carrots stored at 4°C and room temperature was evaluated. Rotavirus SA-11 was able to survive up to 30 days at refrigeration temperatures and up to 25 days at room temperatures. Rotavirus survived longest on lettuce. The survival of coliphage and enteric viruses on grass was studied during winter and summer outdoors. Coliphage, poliovirus, and rotavirus SA-11 survived on two types of grass during winter and summer from 8 to 40 hours. Human rotavirus survived longer than the other enteric viruses, however, coliphage was more sensitive to inactivation. The occurrence of rotaviruses and enteroviruses in the secondarily treated sewage (activated sludge) was evaluated over a one year period. Total coliforms, pH, and turbidity were also determined. Rotavirus concentrations peaked during Spring and Winter while concentrations of enteroviruses peaked during May, September, and December. No correlation was found between the concentrations of total coliforms, rotaviruses and enteroviruses.
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Extended Use of Treated Municipal Wastewater by the Buckeye Irrigation Company: A Documentation of EffectsCluff, C. B., Tucker, T. C., Day, A. D., McFadyen, John A., Sebenik, Paul G. 09 1900 (has links)
Project Completion Report, OWRT Project No. A-050-ARIZ. / Agreement No. 14-31-0001-5003 / Project Dates: July 1974 - June 1976. / The work upon which this publication was based was supported in part by funds provided by the Office of Water Research and Technology (A-050-ARIZ), U.S. Department of the Interior, Washington, D.C., as authorized by the Water Research and Development Act of 1978. / INTRODUCTION: The use of treated sewage effluent by the Buckeye Irrigation Company began
with 800 acre -feet in 1962 and had increased to 40,000 a.f. by 1968. The effluent was diverted by the Buckeye Irrigation Company from the Gila River approximately seven miles below the City of Phoenix 91st Avenue treatment plant, as it
became available at their diversion point. Natural streamflow, used in earlier years, had virtually stopped due to upstream development except in heavy runoff years such as 1941. The ground water in the district of the Buckeye Irrigation Company is relatively high in dissolved solids. The quality of the treated effluent is better. In 1971 the company signed a 40 -year contract with Phoenix to assure its use of 30,000 a.f. of effluent per year. The effluent is mixed with native ground water to bring the total water applied on the 18,000-acre
district up to approximately 90,000 a.f. (Halpenny, 1973). The treated effluent use by the Buckeye Irrigation Company is the largest in the State of Arizona and one of the largest land applications of treated effluent in the United States. It is unique in that it is being utilized by an irrigation district. Most other uses have been by city operated farms or
private farms under a single ownership. In spite of its uniqueness the effects of effluent use by the Buckeye Irrigation District had not, prior to this research, been well documented. This documentation was made in order to improve the general knowledge needed to extend this type of use to other areas in the state and nation. "Widespread consideration and utilization of land application cannot be made until such time as adequate information concerning the technique involved is made available. The experience gained by those who have successfully utilized this wastewater management should be used... specific evaluation of established systems in the various climatic zones would appear to be more fruitful than new research installations for determining long term effects on soils, vegetation, ground water and the indigenous ecology..." (Sullivan, et al., 1973). During the two year research period most of the initial objectives were achieved. The original specific objectives were: 1. To identify changes during an extended period of application of treated wastewater to irrigated fields in: a. irrigation practices
b. cropping patterns
c. fertilization practices
d. crop yield response and quality
e. quality of irrigation water, and
f. soil properties. 2. To make a preliminary evaluation of the effects of the use of
effluent on ground-water conditions.
3. To make a preliminary evaluation of changes in water costs and
farm profits.
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Using the submergent Triglochin huegelii for domestic greywater treatment /Mars, Ross. January 2001 (has links)
Thesis (Ph.D.)--Murdoch University, 2001. / Thesis submitted to the Division of Science and Engineering. Bibliography: leaves 201-228.
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Reuse of domestic greywater for the irrigation of food cropsFinley, Sara. January 1900 (has links)
Thesis (M.Sc.). / Written for the Dept. of Bioresource Engineering. Title from title page of PDF (viewed 2009/06/23). Includes bibliographical references.
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Nitrogen losses in gaseous form from soils [I.] II. Sewage and sewage effluent disposal through usage for fertilization and irrigation /Hedlin, R. A. January 1950 (has links)
Thesis (Ph. D.)--University of Wisconsin--Madison, 1950. / Typescript. Vita. eContent provider-neutral record in process. Description based on print version record. Bibliographies: leaves 43-47, 66-67.
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