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The main purpose of this study was to investigate the removal of ammonia, orthophosphate, and COD present in landfill leachate using vertical subsurface flow constructed wetland systems (VFCW). The effect of different types of plants (

Treatment performance of horizontal flow (HF) and vertical flow (VF) constructed wetland planted with Rhynchospora corymbosa were compared. The average porosity of the CW beds were 0.55, hydraulic retention time (HRT) of 3 days, hydraulic loading rate (HLR) and Organic Loading rate were 0.058 m/day and 3.96 (g·BOD/m

This six-month study aimed to evaluate the removal of total nitrogen (TN) in two duplicated partially saturated (PS) vertical flow (VF) wetlands added with corncob in two different heights of the free-drainage zone (FDZ) after two years in operation. Both PS VF wetlands efficiently removed organic matter measured as biochemical oxygen demand (BOD

The aim of this study is to evaluate the influence of Agapanthus africanus (A. africanus) on nitrification in a vertical subsurface flow constructed wetlands (VSSFs) system. Two lab-scale VSSFs were operated: a) one was planted with A. africanus (vertical flow planted, VFP), and b) the other was unplanted (vertical flow control, VFC). The operation strategy was divided into three phases and consisted of increasing the ammoniacal nitrogen loading rate (ALR) (Phase I: 1.4; Phase II: 2.4; Phase III: 4.4 g NH4+-N·m-2·d-1). Nitrification was evaluated in the system at two different depths in the VSSFs (30.5 cm and 60.3 cm, from the top of the system). The removal efficiencies of COD, BOD5, TP, and PO4-3-P were above 40% in the VFP and VFC during all operation. The mean removal efficiencies of NH4+-N were above 70%. Nitrification was the principal NH4+-N removal mechanism in both systems and transformed more than 50% of the NH4+-N to NO3--N. In terms of the effect of A. africanus on NH4+-N removal during the three operational phases, nonsignificant differences between the two VSSFs were noted (p > 0.05). Thus, A. africanus did not influence nitrification. Finally, the analysis at different depths showed that nitrification occurred in the upper 30.5 cm.

This study aims to remove the macro-sized nutrients that are present in the cheese whey powder solution through the use of constructed wetland systems. For this purpose, 70% and 40% demineralized solutions of cheese whey powder were used. For both concentrations, control reactors are run in parallel with Typha angustifolia planted reactors for the duration of a 92 day period. Zeolite and gravel were used as the filling material. The planted reactor, which was fed with the 70% solution, was named as Cheese Whey Powder Solution (CWPS) 1 and its unplanted control was named CWPS 2 while the reactor, which was fed with the 40% solution, was named as CWPS 3 and its unplanted control was named CWPS 4. The removal of COD, PO4-P and NH4-N were obtained as 37.47%, 45.62%, and 68.88% in CWPS 1; 24.89%, 35.74%, and 63.15% in CWPS 2; 51.15%, 54.96%, and 64.13% in CWPS 3; and 28.35%, 23.99%, and 65.92% in CWPS 4, respectively.