%0 Articles
%T Use of wetland buffer areas to reduce nitrogen transport from forested catchments: Retention capacity, emissions of N<sub>2</sub>O and CH<sub>4</sub> and vegetation composition dynamics
%A Hynninen, Anu
%D 2011
%J Dissertationes Forestales
%V 2011
%N 129
%R doi:10.14214/df.129
%U http://dissertationesforestales.fi/article/1916
%X The use of buffer areas in forested catchments has been actively researched during the last 15 years; but until now, the research has mainly concentrated on the reduction of sediment and phosphorus loads, instead of nitrogen (N). The aim of this thesis was to examine the use of wetland buffer areas to reduce the nitrogen transport in forested catchments and to investigate the environmental impacts involved in their use. Besides the retention capacity, particular attention was paid to the main factors contributing to the N retention, the potential for increased N<sub>2</sub>O emissions after large N loading, the effects of peatland restoration for use as buffer areas on CH<sub>4</sub> emissions, as well as the vegetation composition dynamics induced by the use of peatlands as buffer areas. To study the capacity of buffer areas to reduce N transport in forested catchments, we first used large artificial loadings of N, and then studied the capacity of buffer areas to reduce ammonium (NH<sub>4<sup>-</sup></sub>N) export originating from ditch network maintenance areas in forested catchments. The potential for increased N<sub>2</sub>O emissions were studied using the closed chamber technique and a large artificial N loading at five buffer areas. Sampling for CH<sub>4</sub> emissions and methane-cycling microbial populations were done on three restored buffer areas and on three buffers constructed on natural peatlands. Vegetation composition dynamics was studied at three buffer areas between 1996 and 2009. Wetland buffer areas were efficient in retaining inorganic N from inflow. The key factors contributing to the retention were the size and the length of the buffer, the hydrological loading and the rate of nutrient loading. Our results show that although the N<sub>2</sub>O emissions may increase temporarily to very high levels after a large N loading into the buffer area, the buffer areas in forested catchments should be viewed as insignificant sources of N<sub>2</sub>O. CH<sub>4</sub> fluxes were substantially higher from buffers constructed on natural peatlands than from the restored buffer areas, probably because of the slow recovery of methanogens after restoration. The use of peatlands as buffer areas was followed by clear changes in plant species composition and the largest changes occurred in the upstream parts of the buffer areas and the wet lawn-level surfaces, where the contact between the vegetation and the through-flow waters was closer than for the downstream parts and dry hummock sites. The changes in the plant species composition may be an undesired phenomenon especially in the case of the mires representing endangered mire site types, and therefore the construction of new buffer areas should be primarily directed into drained peatland areas.