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Nitrogen Transformation in Horizontal Subsurface Flow Constructed Wetlands I: Model Development

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dc.creator Mayo, Aloyce W.
dc.creator Bigambo, T.
dc.date 2016-05-24T10:39:56Z
dc.date 2016-05-24T10:39:56Z
dc.date 2005
dc.date.accessioned 2018-03-27T08:40:48Z
dc.date.available 2018-03-27T08:40:48Z
dc.identifier Mayo, A.W. and Bigambo, T., 2005. Nitrogen transformation in horizontal subsurface flow constructed wetlands I: Model development. Physics and Chemistry of the Earth, Parts A/B/C, 30(11), pp.658-667.
dc.identifier http://hdl.handle.net/20.500.11810/2225
dc.identifier 10.1016/j.pce.2005.08.005
dc.identifier.uri http://hdl.handle.net/20.500.11810/2225
dc.description In this paper a mathematical model for prediction of nitrogen transformation in horizontal subsurface flow constructed wetlands was developed. Two horizontal subsurface flow constructed wetlands were designed to receive organic loading rate below 50 kg/ha/d and hydraulic loading rate of 480 m3 /ha/d from a primary facultative pond. Two rectangular shaped units each 11.0 m long,3.7 m wide and 1.0 m deep and bottom slope of 1% were constructed and filled with 6–25 mm diameter gravel pack to a depth of 0.75 m. Each unit was planted with Phragmites mauritianus with an initial plant density of 29,000 plants/ha. The plants were allowed to grow for about four months before sampling for water quality parameters commenced. Samples were collected daily for about three months. Dissolved oxygen,pH and temperature were measured in situ and ammonia,total Kjeldahl nitrogen,nitrates,nitrite and Chemical Oxygen Demand were measured in the laboratory in accordance with Standard Methods. The mathematical model took into account activities of biomass suspended in the water body and biofilm on aggregates and plant roots. The state variables modelled include organic,ammonia,and nitrate–nitrogen,which were sectored in water,plant and aggregates. The major nitrogen transformation processes considered in this study were mineralization,nitrification,denitrification,plant uptake, plant decaying,and sedimentation. The forcing functions,which were considered in the model,are temperature,pH and dissolved oxygen. Stella II software was used to simulate the nitrogen processes influencing the removal of nitrogen in the constructed wetland. One of the two-wetland units was used for model calibration and the second unit for model validation. The model results indicated that 0.872 gN/m2 d was settled at the bottom of the wetland and on gravel bed and roots of the plants. However,0.752 gN/m2 d (86.2%) of the settled nitrogen was regenerated back to the water body,which means that only 13.8% of the settled nitrogen was permanently removed. Denitrification and nitrification were responsible for transformation of 0.436 gN/m2 d and 0.425 gN/m2 d,respectively. Uptake of nitrogen by plants was 0.297 gN/m2 d out of which 0.140 gN/m2 d was returned to the water body as plants decay. It was found that the major pathways leading to permanent removal of nitrogen in a horizontal subsurface flow constructed wetland system in descending order are denitrification (29.9%),plant uptake (10.2%) and net sedimentation (8.2%). A total nitrogen removal of 48.9% was achieved in this study.
dc.language en
dc.publisher Elsevier
dc.subject Constructed wetlands
dc.subject Nitrogen transformation
dc.subject Nitrification
dc.subject Denitrification
dc.subject Biofilm
dc.title Nitrogen Transformation in Horizontal Subsurface Flow Constructed Wetlands I: Model Development
dc.type Journal Article, Peer Reviewed


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