A platform for research: civil engineering, architecture and urbanism
Oxygen transfer in marsh-pond-marsh constructed wetlands treating swine wastewater
Oxygen transfer efficiencies of various components of the marsh-pond-marsh (M-P-M) and marsh-floating bed-marsh (M-FB-M) wetlands treating swine wastewater were determined by performing oxygen mass balance around the wetlands. Biological oxygen demand (BOD) and total nitrogen (TN) loading and escaping rates from each wetland were used to calculate carbonaceous and nitrogenous oxygen demands. Ammonia emissions were measured using a wind tunnel. Oxygen transfer efficiencies of the aerated ponds were estimated by conducting the ASCE standard oxygen transfer test in a tank using the same aeration device. Covering pond water surface with the floating bed slightly decreased oxygen transfer efficiency. The diffused membrane aeration (26.7 kg O2 ha-1 d-1) of M-P-M was surprisingly not as effective as plant aeration in the marsh (38.9 to 42.0 kg O2 ha-1 d-1). This unusually low oxygen transfer efficiency of the diffused aeration was attributed to its low submergence depth of 0.8 m compared to typical depth of 4.5 m. The wetlands consisting entirely of marsh removed similar amounts of C and N without investing additional equipment and energy costs of aerating ponds in the middle of wetlands.
Oxygen transfer in marsh-pond-marsh constructed wetlands treating swine wastewater
Oxygen transfer efficiencies of various components of the marsh-pond-marsh (M-P-M) and marsh-floating bed-marsh (M-FB-M) wetlands treating swine wastewater were determined by performing oxygen mass balance around the wetlands. Biological oxygen demand (BOD) and total nitrogen (TN) loading and escaping rates from each wetland were used to calculate carbonaceous and nitrogenous oxygen demands. Ammonia emissions were measured using a wind tunnel. Oxygen transfer efficiencies of the aerated ponds were estimated by conducting the ASCE standard oxygen transfer test in a tank using the same aeration device. Covering pond water surface with the floating bed slightly decreased oxygen transfer efficiency. The diffused membrane aeration (26.7 kg O2 ha-1 d-1) of M-P-M was surprisingly not as effective as plant aeration in the marsh (38.9 to 42.0 kg O2 ha-1 d-1). This unusually low oxygen transfer efficiency of the diffused aeration was attributed to its low submergence depth of 0.8 m compared to typical depth of 4.5 m. The wetlands consisting entirely of marsh removed similar amounts of C and N without investing additional equipment and energy costs of aerating ponds in the middle of wetlands.
Oxygen transfer in marsh-pond-marsh constructed wetlands treating swine wastewater
Ro, Kyoung S. (author) / Hunt, Patrick G. (author) / Johnson, Melvin H. (author) / Matheny, Terry A. (author) / Forbes, Dean (author) / Reddy, Gudigopuram B. (author)
Journal of Environmental Science and Health, Part A ; 45 ; 377-382
2010-01-01
6 pages
Article (Journal)
Electronic Resource
English
Oxygen transfer in marsh-pond-marsh constructed wetlands treating swine wastewater
Online Contents | 2010
|Taylor & Francis Verlag | 2010
|Treating swine wastewater by integrating earthworms into constructed wetlands
Taylor & Francis Verlag | 2011
|Treating swine wastewater by integrating earthworms into constructed wetlands
Online Contents | 2011
|