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Data from: Carbon dioxide and methane fluxes from different surface types in a created urban wetland

<p><span>Many wetlands have been drained due to urbanization, agriculture, forestry or other purposes, which has resulted in losing their ecosystem services. To protect receiving waters and to achieve services such as flood control and stormwater quality mitigation, new wetlands are created in urbanized areas. However, our knowledge of greenhouse gas exchange in newly created wetlands in urban areas is currently limited. In this paper we present measurements carried out at a created urban wetland in boreal climate.</span></p> <p><span>We conducted measurements of ecosystem CO<sub>2 </sub>flux (NEE) and CH<sub>4</sub> flux (F<sub>CH4</sub>) at the constructed stormwater wetland Gateway in Nummela, Vihti, Southern Finland using eddy covariance (EC) technique. The measurements were commenced the fourth year after construction and lasted for one full year and two subsequent growing seasons. Besides ecosystem scale fluxes measured by EC tower, the diffusive CO<sub>2 </sub>and<sub> </sub>CH<sub>4</sub> fluxes from the open-water area (F<sub>w</sub>_CO<sub>2</sub> and F<sub>w</sub>_CH<sub>4, </sub>respectively) were modelled based on measurements of CO<sub>2 </sub>and<sub> </sub>CH<sub>4 </sub>concentration in the water. Fluxes from vegetated area were estimated by applying a simple mixing model using above-mentioned fluxes and footprint-weighted fractional area. The half-hourly footprint-weighted contribution of diffusive fluxes from open water ranged from 0 to 25.5 % in year 2013.</span></p> <p><span>The annual NEE of the studied wetland was 8.0 g C-CO<sub>2 </sub>m<sup>-2</sup> yr<sup>-1 </sup>with the 95 % confidence interval between<sup> </sup>-18.9 and 34.9 g C-CO<sub>2 </sub>m<sup>-2</sup> yr<sup>-1 </sup>and F<sub>CH4 </sub>was 3.9 g C-CH<sub>4</sub> m<sup>-2</sup> yr<sup>-1</sup> with the 95 % confidence interval between 3.75 and 4.07 g C-CH<sub>4</sub> m<sup>-2</sup> yr<sup>-1</sup>. The ecosystem sequestered CO<sub>2 </sub>during summer months (June-August), while the rest of the year it was a CO<sub>2</sub> source. CH<sub>4</sub> displayed strong seasonal dynamics, higher in summer and lower in winter, with a sporadic emission episode in the end of May 2013. Both CH<sub>4 </sub>and CO<sub>2 </sub>fluxes<sub>, </sub>especially those obtained from vegetated area, exhibited strong diurnal<sub> </sub>cycle during summer with synchronized peaks around noon. The annual F<sub>w</sub>_CO<sub>2 </sub>was 297.5 g C-CO<sub>2 </sub>m<sup>-2</sup> yr<sup>-1 </sup>and F<sub>w</sub>_CH<sub>4 </sub>was 1.73 g C-CH<sub>4 </sub>m<sup>-2</sup> yr<sup>-1</sup>. The peak diffusive CH<sub>4</sub> flux was 137.6 nmol C-CH<sub>4</sub> m<sup>-2</sup> s<sup>-1</sup>, which was<sup> </sup>synchronized with the F<sub>CH4</sub>.</span></p> <p><span>Overall, during the monitored time period, the established stormwater wetland had a climate warming effect with 0.263 kg CO<sub>2</sub>-eq m<sup>-2</sup> yr<sup>-1 </sup>of<sup> </sup>which 89 % was contributed by CH<sub>4</sub>. The radiative forcing of the open-water exceeded the vegetation area (1.194 kg CO<sub>2</sub>-eq m<sup>-2</sup> yr<sup>-1</sup> and<sup> </sup>0.111 kg CO<sub>2</sub>-eq m<sup>-2</sup> yr<sup>-1</sup>, respectively), which implies that, when considering solely the climate impact of a created wetland over a 100-year horizon, it would be more beneficial to design and establish wetlands with large patches of emergent vegetation, and to limit the areas of open-water to the minimum necessitated by other desired ecosystem services.</span></p>

ShareScore

36/100

Overall dataset sharing score

Score breakdown

These five areas show where the dataset supports — or may limit — practical reuse.

Stewardship
4
Harmonization
12
Access
12
Reuse readiness
0
Engagement
8

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