Friday, 14 July 2006
89-5

Calcaric Regosols Ability of Nitrous Oxide Release and Sink–Model Experiment.

Jan Gliński, Teresa Włodarczyk, Małgorzata Brzezińska, and Paweł Szarlip. Institute of Agrophysics PAS, Doswiadczalna 4, Lublin, Poland

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.

  1. Duxbury J.M., Harper L.A., Mosier A.R. (1993) Contribution of agroecosystems to global climate change. In Rolston D.E., Duxbury J.M., Harper L.A., Mosier A.R. (eds) Agricultural ecosystem effects on trace gases and global climate change. ASA special publication 55, pp 1-18.
  2. Letey J., Valoras N., Focht D.D., Ryden J.C. (1981) Nitrous oxide production and reduction during denitrification as affected by redox potential. Soil Sci. Soc. Am. J. 45:727-730.
  3. Smith, C.J. Wright, M.F., Patrick, W.H. jr. (1983) The effect of soil redox potential and pH on the redaction and production of nitrous oxide. Journal Environmental Quality 12:186-188
  4. Wlodarczyk T., Stepniewski W., Brzezinska M.: (2002) Dehydrogenase activity, redox potential, and emission of carbon dioxide and nitrous oxide from Cambisols under flooding conditions. Biol. Fertil. Soils 36, 200-206.
  5. Wlodarczyk T. Stepniewski W. Brzezinska M. Stepniewska Z. (2004) Nitrate stability in loess soils under anaerobic conditions – laboratory studies. J. Plant Nutr. Soil Sci. 167, 1-8.


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