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Soil moisture affects the degradation of organic fertilizers in soils considerably, but less is known about the importance of rainfall pattern on the turnover of C and N. The objective of this study was to determine the effects of different rainfall patterns on C and N dynamics in soil amended with either biogas slurry (BS) or composted cattle manure (CM). Undisturbed soil cores without (control) or with BS or CM, which were incorporated at a rate of 100 kg N ha –1 , were incubated for 140 d at 13.5°C. Irrigation treatments were (1) continuous irrigation (cont_irr; 3 mm d –1 ); (2) partial drying and stronger irrigation (part_dry; no irrigation for 3 weeks, 1 week with 13.5 mm d –1 ), and (3) periodic heavy rainfall (hvy_rain; 24 mm d –1 every 3 weeks for 1 d and 2 mm d –1 for the other days). The average irrigation was 3 mm d –1 in each treatment. Cumulative emissions of CO 2 and N 2 O from soils amended with BS were 92.8 g CO 2 ‐C m –2 and 162.4 mg N 2 O‐N m –2 , respectively, whereas emissions from soils amended with CM were 87.8 g CO 2 ‐C m –2 and only 38.9 mg N 2 O‐N m –2 . While both organic fertilizers significantly increased CO 2 production compared to the control, N 2 O emissions were only significantly increased in the BS‐amended soil. Under the conditions of the experiment, the rainfall pattern affected the temporal production of CO 2 and N 2 O, but not the cumulative emissions. Cumulative NO ₃⁻ leaching was highest in the BS‐amended soils (9.2 g NO ₃⁻ ‐N m –2 ) followed by the CM‐amended soil (6.1 g NO ₃⁻ ‐N m –2 ) and lowest in the control (4.7 g NO ₃⁻ ‐N m –2 ). Nitrate leaching was also independent of the rainfall pattern. Our study shows that rainfall pattern may not affect CO 2 and N 2 O emissions and NO ₃⁻ leaching markedly provided that the soil does not completely dry out.
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Sänger et al. (2010) studied this question.
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