HOME HELP FEEDBACK SUBSCRIPTIONS ARCHIVE SEARCH TABLE OF CONTENTS		QUICK SEARCH:   [advanced] Author: Keyword(s): Year:  Vol:  Page:

This Article Full Text (PDF) Alert me when this article is cited Alert me if a correction is posted Services Similar articles in this journal Alert me to new issues of the journal Download to citation manager Citing Articles Citing Articles via HighWire Citing Articles via Google Scholar Google Scholar Articles by Chendorain, M. Articles by Villegas, F. Search for Related Content PubMed Articles by Chendorain, M. Articles by Villegas, F. Agricola Articles by Chendorain, M. Articles by Villegas, F.

The Fate and Transport of Viruses through Surface Water Constructed Wetlands

Dep. of E.S.P.M., Ecosystem Sciences Div., Univ. of California, Berkeley, CA, 94720-3110;

Marylynn Yates and Frank Villegas

Dep. of Soil & Environ. Sciences, Univ. of California, Riverside, CA. 92521.

^* Corresponding author (chendo{at}nature.berkeley.edu).

ABSTRACT

Coliphage removal efficiency and the effects of wetland hydrology on virus transport were determined for constructed wetlands in San Jacinto, CA. Mathematical models were used to further characterize virus transport. MS2, an F-specific RNA (FRNA) coliphage was used as a model for human enteric viral behavior. Two wetland types were studied, a one-phase cell and three-phase cell. These wetlands received unchlorinated secondary effluent at a constant rate. The mean residence time in the wetlands was 9 ± 3 d as determined using bromide as a conservative tracer. Assuming 100% porosity, a plug flow model predicts this mean residence time within the experimental standard deviation (8 d). This suggests that a negligible volume was occupied by vegetation and settled solids. The convection-dispersion equation adequately simulated the residence time distribution of the conservative tracer. MS2 removal in the wetlands was experimentally determined to be 97 ± 3%. There was no distinction between the two wetland types in terms of removal efficiency. The average coliphage decay rate was calculated to be 0.44 per day. However, the error involved with using the first order decay rate was high, 83 ± 12%. Therefore, first order decay does not adequately describe removal processes within the wetland. Most virus removal occurred within the first 3 m (k = 4.0 ± 1.8 d^–1) with a removal efficiency of 85.3 ± 0.6%. The remainder had a decay rate of 0.20 ± 0.17 d^–1 with a removal efficiency of 56 ± 33%.

Sponsoring Organization: U.S. Dep. of Interior, Bureau of Reclamation, Denver, CO 80225-0007.

Received for publication November 10, 1997.

This article has been cited by other articles:

				G. M. Huddleston III and J. H. Rodgers Jr. Design of a constructed wetland system for treatment of copper-contaminated wastewater Environmental Geosciences, March 1, 2008; 15(1): 9 - 19. [Abstract] [Full Text] [PDF]

				S. Xu and P. R. Jaffe Effects of Plants on the Removal of Hexavalent Chromium in Wetland Sediments J. Environ. Qual., January 5, 2006; 35(1): 334 - 341. [Abstract] [Full Text] [PDF]

				R. Collins Fecal Contamination of Pastoral Wetlands J. Environ. Qual., September 1, 2004; 33(5): 1912 - 1918. [Abstract] [Full Text] [PDF]

				Y. Q. Tian, P. Gong, J. D. Radke, and J. Scarborough Spatial and Temporal Modeling of Microbial Contaminants on Grazing Farmlands J. Environ. Qual., May 1, 2002; 31(3): 860 - 869. [Abstract] [Full Text] [PDF]