Download as a PDF - CiteSeerX
Download as a PDF - CiteSeerX
Download as a PDF - CiteSeerX
Create successful ePaper yourself
Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.
RAPID INCORPORATION OF SOLID MANURE AS A BEST<br />
MANAGEMENT PRACTICE?<br />
RE Thorman 1 , J Webb 2 and S Yamulki 3<br />
1<br />
ADAS Boxworth, Battlegate Road, Boxworth, Cambridge, CB3 8NN, UK, E-mail:<br />
rachel.thorman@ad<strong>as</strong>.co.uk; 2 ADAS Wolverhampton, Wergs Road, Wolverhampton,<br />
WV6 8TQ, UK; 3 IGER North Wyke, Okehampton, Devon, EX20 2SB, UK<br />
SUMMARY<br />
After solid manure spreading, rapid incorporation by ploughing h<strong>as</strong> been recognised<br />
<strong>as</strong> a successful technique to reduce ammonia (NH 3<br />
) emissions. However, the reduced<br />
NH 3<br />
loss conserves nitrogen which may subsequently be emitted from the soil <strong>as</strong> the<br />
greenhouse g<strong>as</strong>, nitrous oxide (N 2<br />
O). Emissions of N 2<br />
O were monitored at two UK<br />
sites (central and south west England) after application of cattle manure, pig manure,<br />
layer manure and broiler litter to arable land. At both sites, ploughing reduced NH 3<br />
emissions compared with those from plots where manure remained on the soil surface<br />
(P < 0.001). However, the effect of incorporation on N 2<br />
O loss w<strong>as</strong> inconsistent. In the<br />
warm and wet south west, incorporation had no effect on N 2<br />
O emissions (P > 0.05),<br />
but at the cooler and drier central site, N 2<br />
O losses incre<strong>as</strong>ed (P < 0.001), suggesting<br />
that rapid incorporation may be considered <strong>as</strong> a best management practice (BMP)<br />
for both N 2<br />
O and NH 3<br />
abatement only under site-specific conditions.<br />
INTRODUCTION<br />
Around 43 million tonnes of solid manure are handled annually in the UK (Williams et al.,<br />
2000), with 36% of agricultural ammonia (NH 3<br />
) emissions (82 kt N) estimated to arise<br />
from the management of solid manures (Misselbrook et al., 2000). After land spreading,<br />
ammonia emissions of manures represent both a large loss of potential crop available<br />
nitrogen and a considerable environmental risk. Deposition of NH 3<br />
can lead to soil<br />
acidification and nitrogen (N) enrichment of sensitive habitats, consequently the UK<br />
h<strong>as</strong> signed a number of international agreements [UNECE Gothenburg Protocol, EC<br />
Integrated Pollution Prevention and Control (IPPC) Directive, EC National Emission<br />
Ceilings Directive] to reduce NH 3<br />
emissions. After the application of solid manures<br />
to arable land, rapid incorporation h<strong>as</strong> been identified <strong>as</strong> an effective me<strong>as</strong>ure to<br />
abate NH 3<br />
emissions (Webb et al., 2005). However, the reduced NH 3<br />
loss conserves<br />
N incre<strong>as</strong>ing the mineral N pool in the soil, which may subsequently be available<br />
for microbial nitrification and denitrification and the production of the greenhouse<br />
g<strong>as</strong>, nitrous oxide (N 2<br />
O). Nitrous oxide is a potent greenhouse g<strong>as</strong> with a global<br />
warming potential 310 times that of carbon dioxide (IPCC, 1996). The current UK<br />
emissions inventory (2003) shows that 67% of N 2<br />
O is produced from agriculture with<br />
the majority emitted from agricultural soils (Baggott et al., 2005). As a result of the<br />
Kyoto protocol, the UK h<strong>as</strong> agreed to a legally binding reduction of greenhouse g<strong>as</strong><br />
emissions of 12.5% of 1990 levels by the period 2008–12. It is, therefore, important<br />
that me<strong>as</strong>ures implemented <strong>as</strong> a BMP to reduce NH 3<br />
emissions do not result in an<br />
incre<strong>as</strong>ed loss of N 2<br />
O.<br />
249