Nitrous oxide (N2O) is one of the most important greenhouse gases emitted mainly from biotic sources (Duxbury et al. 1993). Soil can remove atmospheric N2O under conditions favorable for N2O reduction (Letey et al., 1981; Smith at al., 1983; and Wlodarczyk et al., 2002, 2004). The main purpose of this study was to estimate the potential ability of soils to produce N2O under flooded conditions where NO3- content was a non-limiting factor (100 mg NO3--N per kg corresponding to 300 kg NO3--N per ha in 20 cm top soil layer) and a potential ability of soils to consume N2O. N2O evolution and consumption in Calcaric Regosols developed from sandy and silty loam (No 543 and 922) depending on nitrogen addition and kind of soil were studied. Soil samples from Ap horizons (5 g dry soil with 4.5 ml distilled water and 0.5 ml of solution of nitrogen like a KNO3, NaNO2 and (NH4)2SO4 in concentration 100 mg/kg) were incubated with addition of N2O (1% v/v) in tightly closed 60 cm3-glass flasks at 20oC for 26 days. Soils without N2O amendment were control variants. Gas concentrations (N2O, CO2, O2 by gas chromatograph) were measured during incubation in three replications.
Table 1. Maximum and daily N2O release and consumption
Treatment | N2O-N mg kg-1 | |||||||
Sandy loam (No 543) | Silty loam (No 922) | |||||||
Release | Consumption | Release | Consumption | |||||
max | daily | max | % | max | daily | max | % | |
Soil + H2O | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Soil + NO3- | 32.2 | 5.37 | 3.44 | 10.7 | 93.2 | 10.36 | 93.2 | 100 |
Soil + NO2- | 43.0 | 1.65 | 0 | 0 | 28.7 | 1.43 | 0.95 | 3.3 |
Soil + NH4+ | 1.99 | 0.33 | 0 | 0 | 0 | 0 | 0 | 0 |
Soil + N2O | 0 | 0 | 70.6# | 45.3 | 0 | 0 | 167.3## | 100 |
Soil + N2O + NO3- | 19.1 | 6.37 | 13.1 | 7.2 | 70.4 | 7.82 | 231.6 | 99.3 |
Soil + N2O + NO2- | 24.3 | 3.46 | 5.10 | 2.7 | 18.7 | 4.67 | 26.9 | 15.2 |
Soil + N2O + NH4+ | 2.45 | 0.61 | 77.1 | 47.5 | 1.46 | 0.24 | 162.0 | 100 |
# - 70.58 mg kg-1 /26 days = 2.72 mg kg-1 d-1
## - 167.32 mg kg-1/13 days =12.9 mg kg-1 d-1
In conclusion we can state that: (a) soil texture and kind of nitrogen addition affected significantly the N2O evolution and consumption, (b) two investigated soils showed an ability of nitrous oxide consumption by soils without nitrate amendment - 2.72 for sandy loam and 12.9 mg N2O-N kg-1day-1 for silty loam, (c) the ability of nitrous oxide consumption by the two investigated soils was higher than their capability of N2O evolution.
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