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Greenhouse Gas Emissions from U.S. Agriculture and Forestry: A ...

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<strong>and</strong> Vitousek, 2009). For example, in a review by Snyder et al. (2007, 2009), N2O emissions <strong>from</strong><br />

pastures were reported to be reduced by 40‐92% when using nitrification inhibitors.<br />

Conversions <strong>from</strong> cropl<strong>and</strong> to natural grassl<strong>and</strong> (e.g., setting aside under the CRP program) will typically<br />

result in lower N2O emissions due to the elimination of fertilizer N use. A recent review by Swan et al. (in<br />

prep) reported decreased N2O emissions with conversion of cropl<strong>and</strong> to grassl<strong>and</strong>, by as much as 4.5 kg<br />

N (2.2 t CO2 eq.) ha ‐1 yr ‐1 if the amount of N fertilizer application was also reduced. In the case of no<br />

change in N fertilizer, N2O emission changes were estimated to be near zero, while N2O emissions were<br />

estimated to increase by as much as 6.9 kg N (3.4 t CO2 eq.) ha ‐1 yr ‐1 if fertilization rates were higher on<br />

the grassl<strong>and</strong>. Their analysis suggested that conversion of cropl<strong>and</strong> to grassl<strong>and</strong> can change soil N2O<br />

emissions, but the amount of change depends greatly on N fertilizer management. Planting herbaceous<br />

buffers within a field or along a riparian area can further reduce N2O emissions by capturing NO3 ‐ runoff<br />

<strong>from</strong> agricultural l<strong>and</strong> before it becomes denitrified off‐site (T‐AGG, 2010).<br />

Orchards, Agroforestry, Woody Crops<br />

N2O emissions tend to be reduced in agroforestry systems or in woody crop cultivations as these<br />

systems tend to rely less on N fertilization. However, results vary widely across studies. Machefert et al.<br />

(2002) found much lower N2O emissions in forested versus agricultural l<strong>and</strong> in Europe. Others have<br />

found little differences in N2O emissions between annual crops <strong>and</strong> woody crop plantations (e.g.,<br />

poplar) but much lower emissions <strong>from</strong> natural forests (Scheer et al., 2008). On the other h<strong>and</strong>,<br />

conventional horticulture systems tend to be heavily fertilized to maximize crop yields. Much higher<br />

fertilization rates were reported for example for lettuce compared to corn (T‐AGG, 2010) while N<br />

removal by lettuce is much smaller than for corn. Combined with irrigation practices, horticulture l<strong>and</strong><br />

may be a significant source of N2O emissions. N2O emissions <strong>from</strong> horticulture l<strong>and</strong> may be reduced by<br />

using the same mitigation strategies as promoted for annual cropl<strong>and</strong> (e.g., timing <strong>and</strong> placement of N<br />

fertilizer, enhanced‐efficiency fertilizers, etc.). Management practices such as cover crops or manure<br />

applications might reduce the need for N fertilizer <strong>and</strong> decrease N2O emissions (e.g., Wyl<strong>and</strong> et al.,<br />

1995). Further research needs include evaluating N2O mitigation strategies for the different types of<br />

horticulture crops, <strong>and</strong> quantifying N2O emissions <strong>from</strong> different management practices. In particular,<br />

research is lacking in orchard systems regarding both soil C sequestration <strong>and</strong> N2O <strong>and</strong> CH4 emissions.<br />

Contract # GS‐23F‐8182H, Project Technical Report 31

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