Please use this identifier to cite or link to this item:
https://hdl.handle.net/20.500.14279/1198
Title: | Long-term phosphorus immobilization by a drinking water treatment residual | Authors: | Agyin-Birikorang, Sampson O'Connor, George A. Jacobs, Lee W. Brinton, Scott R. Makris, Konstantinos C. |
metadata.dc.contributor.other: | Μακρής, Κωνσταντίνος X. | Major Field of Science: | Natural Sciences | Field Category: | Earth and Related Environmental Sciences | Keywords: | Computer simulation;Eutrophication;Leachate treatment;Phosphorus;Rain;Runoff;Soils;Water treatment;Phosphorus immobilization;Rainfall simulation techniques;Water treatment residuals (WTR) | Issue Date: | 1-Jan-2007 | Source: | Journal of Environmental Quality, 2007, vol. 36, no.1, pp. 316-323 | Volume: | 36 | Issue: | 1 | Start page: | 316 | End page: | 323 | Journal: | Journal of Environmental Quality | Abstract: | Excessive soluble P in runoff is a common cause of eutrophication in fresh waters. Evidence indicates that drinking water treatment residuals (WTRs) can reduce soluble P concentrations in P-impacted soils in the short term (days to weeks). The long-term (years) stability of WTR-immobilized P has been inferred, but validating field data are scarce. This research was undertaken at two Michigan field sites with a history of heavy manure applications to study the longevity of alum-based WTR (Al-WTR) effects on P solubility over time (7.5 yr). At both sites, amendment with Al-WTR reduced water-soluble P (WSP) concentration by ≥60% as compared to the control plots, and the Al-WTR-immobilized P (WTR-P) remained stable 7.5 yr after Al-WTR application. Rainfall simulation techniques were utilized to investigate P losses in runoff and leachate from surface soils of the field sites at 7.5 yr after Al-WTR application. At both sites, amendment with Al-WTR reduced dissolved P and bioavailable P (BAP) by >50% as compared to the control plots, showing that WTR-immobilized P remained nonlabile even 7.5 yr after Al-WTR amendment. Thus, WTR-immobilized P would not be expected to dissolve into runoff and leachate to contaminate surface waters or ground water. Even if WTR-P is lost via erosion to surface waters, the bioavailability of the immobilized P should be minimal and should have negligible effects on water quality. However, if the WTR particles are destroyed by extreme conditions, P loss to water could pose a eutrophication risk. | URI: | https://hdl.handle.net/20.500.14279/1198 | ISSN: | 15372537 | DOI: | 10.2134/jeq2006.0162 | Rights: | © American Society of Agronomy | Type: | Article | Affiliation : | University of Florida Michigan State University University of Texas |
Publication Type: | Peer Reviewed |
Appears in Collections: | Άρθρα/Articles |
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