Gaseous and leaching nitrogen losses from no-tillage and conventional tillage systems following surface application of cattle manure |
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| Authors: | MS Mkhabela A Madani R Gordon D Burton D Cudmore A Elmi W Hart |
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| Institution: | aDepartment of Engineering, Nova Scotia Agricultural College, Truro, Nova Scotia, B2N 5E3, Canada;bDepartment of Environmental Sciences, Nova Scotia Agricultural College, Truro, Nova Scotia, B2N 5E3, Canada;cEnvironmental Technology Management Department, College for Women, University of Kuwait, Kuwait;dProcess Engineering and Applied Science, Sexton Campus, Dalhousie University, Halifax, Nova Scotia, B3J 2XA, Canada |
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| Abstract: | Previous studies have demonstrated inconsistent results on the impact of tillage systems on nitrogen (N) losses from field-applied manure. This study assessed the impact of no-tillage (NT) and conventional tillage (CT) systems on gaseous N losses, N2O:N2O + N2 ratios and NO3−-N leaching following surface application of cattle manure. The study was undertaken during the 2003/2004 and 2004/2005 seasons at two field sites in Nova Scotia namely, Streets Ridge (SR) in Cumberland County and the Bio-environmental Engineering Centre (BEEC) in Truro. Results showed that the NT system had higher (p < 0.05) NH3 losses than CT. Over the two seasons, manure incorporation in CT reduced NH3 losses on average by 86% at SR and 78% at BEEC relative to NT. At both sites and during both seasons, denitrification rates and N2O fluxes in NT were generally higher than in CT plots, presumably due to higher soil water and organic matter content in NT. Over the two seasons, mean denitrification rates at SR were 239 and 119 g N ha−1 d−1, while N2O fluxes were 120 and 64 g N ha−1 d−1 under NT and CT, respectively. At BEEC mean denitrification rates were 114 and 71 g N ha−1 d−1, while N2O fluxes were 52 and 27 g N ha−1 d−1 under NT and CT, respectively. Conversely, N2O:N2O + N2 ratios were lower in NT than CT suggesting more complete reduction of N2O to N2 under NT. When averaged across all soil depths, NO3−-N was higher (p < 0.05) in CT than NT. Nitrate-N decreased with depth at both sites regardless of tillage. In most cases, NO3−-N was higher under CT than NT at all soil depths. Similarly, flow-weighted average NO3−-N concentrations in drainage water were generally higher under CT. This may be partly attributed to higher denitrification rates under NT. Therefore, NT may be a viable strategy to remove NO3−-N from the soil, and thus, reduce NO3−-N contamination of groundwater. However, it should be noted that while the use of NT reduces NO3−-N leaching it may come with unintended environmental tradeoffs, including increased NH3 and N2O emissions. |
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| Keywords: | Tillage system Gaseous N losses Denitrification Drainage water quality NO3− -N leaching N2O:N2O + N2 ratios Cattle manure |
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