Background N2O
emissions are defined as N2O emission from soils that received no
nitrogen (N) fertilizer and soil management (e.g., Bouwan, 1996; Lu et al.,
2006; Neftel et al., 2007; Gu et al. 2009; van Beek et al., 2011). Gu et al. (2009)
noted that BNE in agricultural lands originates from residual N that has
remained in the soil from N addition in previous years or seasons, and other N
sources, such as biological N fixation, that are present in the soil. Crop
residues can provide substrate for microbial activities such as nitrification and
denitrification which produce N2O (Aulakh et al., 1991; Huang et
al., 2004; Miller et al., 2008). Also soil disturbance for agricultural
activities can enhance N2O emission through changing soil
microclimate (i.e., soil temperature and moisture) and soil properties (i.e.,
bulk density, porosity and diffusivity) (Dobbie and Smith, 2001; Saggar et al.,
2011). Kim et al. (2009) observed that soil temperature and soil moisture in
crop fields were significantly different from adjacent grass lands and soils in
crop fields had severe soil drought and frozen which caused peak N2O
emissions following rewetting and thawing events (Kim et al., 2012). In animal grazing grassland, treading and
trampling by the animals cause soil compaction, making the soil more anaerobic
and stimulating denitrification activity, thus facilitating N2O
production (van Groenigen et al., 2005; Bhandral et al., 2007; Uchida et al.,
2008). In agricultural land, magnitude of BNE may be influenced by the
fertilization and soil management during previous years (Bouwan, 1996).
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