A b s t r a c t. Flooded organic soils are potentially important sources of greenhouse gases. The effect of soil temperature and moisture on the concentration of N 2 O and CO 2 at two depths of organic soil flooded with two doses of purified wastewater was studied. Nitrous oxide concentrations at the 10-30 cm depth range were generally increased with an increase in soil moisture, showing dependence on the aeration status of soil. The maximum values of N 2 O concentrations were higher at the 50-100 than 10-30 cm depth range, but a similar pattern of increasing maximum values of N 2 O concentration with an increasing input of nitrogen in treatments at both depth ranges was observed. The maximum concentrations of carbon dioxide within the 50-100 cm depth range remained at a similar level in all treatments reaching 7.1-7.7%, which indicated weak relations with the input of water and nitrogen at this depth range. We conclude that the N 2 O and CO 2 concentrations at 10-30 cm depths in the examined organic soil flooded with 600 mm year -1 of purified wastewater exhibited a similar level as the concentrations in soil watered only by precipitation.K e y w o r d s: nitrous oxide, soil temperature, soil moisture, carbon dioxide, wastewater
INTRODUCTIONUnder anaerobic conditions, organic soils are important sources of a number of greenhouse gases (GHGs) such as N 2 O and CO 2 (Koponen et al., 2006;Maljanen et al., 2003). Accurate quantification of nitrous oxide emission is difficult and uncertain (van den Heuvel et al., 2009;Stehfest and Bouwman, 2006). The emission of N 2 O from soil may be dominated by emission from hotspots characterized by favourable conditions for production of N 2 O. McClain et al. (2003) defined biogeochemical hotspots as patches that show disproportionately high reaction rates relative to the surrounding matrix. The high temporal and spatial variability of gas emissions from soil makes measurements at small scales impractical (Giltrap et al., 2010). According to this, analyses that will help in more robust estimation of N 2 O production and emission from soil at large scales that can be based on general relations between N 2 O production in the soil profile and soil properties are needed.Irrigation of soil with treated municipal wastewater can be treated as a last step of purification thereof. Soils irrigated with substantial doses of wastewater can induce anoxic conditions in which nitrate (NO 3 -) and nitrite (NO 2 -) are converted to dinitrogen gas (N 2 ) (Nosalewicz et al., 2005). N 2 O, which is mainly emitted from wastewater treatment systems, is an intermediate in the process of denitrification (Schalk-Otte et al., 2000); additionally, N 2 O can also be produced from nitrification in aerobic conditions (Szarlip et al., 2010).The relations between production of two gases ie N 2 O and CO 2, and soil moisture and temperature are dependent on their effect on overall soil microbial activity. Various enzymatically catalyzed transformations have different optimum temperature and moisture (Müller, 2...