It is hard to know how this summer will
turn out. An exceptionally wet autumn
and winter completely prevented the establishment of autumn-sown crops at
Loddington and other local farms. There
was just about time to drill spring varieties in those fields where we needed
to do so for research, or considered that it would still be economically viable
to do so for our farm business. Then the drought hit.
By June, livestock farmers were
searching around for additional grazing as pasture and leys withered, recalling
memories of the prolonged drought just two years ago. Social media were scattered with posts from normally
successful arable farmers sharing images of drought stressed crops and professing
that the continuing weather uncertainties and extremes were now making it
impossible to maintain a viable business. Recent rain has provided a reprieve by increasing surface soil moisture, at least for now.
Loddington soil moiture deficit to June 2020, including the 2018 drought and exceptionally wet autumn/winter of 2019/20 |
Global warming potential of CO2 and N2O in compacted SoilCare project plots |
Monitoring of greenhouse gas flux in
compacted soils as part of our contribution to the EU-funded SoilCare project reveals
that carbon dioxide flux is higher in ploughed plots than in direct drilled
plots. In these compacted conditions, nitrous
oxide flux is higher in direct drilled plots.
The amounts involved are very low, but because nitrous oxide has a global
warming potential that is nearly 300 times that of carbon dioxide, the
implications for climate change are that much greater. Looked at together, the global warming
potential of greenhouse gases associated with ploughed and direct drilled
plots is roughly equivalent. The
additional emissions associated with multiple field operations in the ploughed
plots mean that direct drilling has the lower impact.
Mean Soil Organic Carbon from ten Water Friendly Farming project fields |
As a Direct driller who has reduced to 90kg of Urea @46% in his operation to produce 6 tonnes per Ha of Spring Barley and places the Urea under the surface next to the seed and only in the coulter lines to minimise losses can you please clarify the metrics upon which you measure the increase in Nitrous Oxide flux compared to tillage because it just doesnt stack up with our model? Our Nitrous Oxide emissions per Ha or tonne of product are far lower using a complete 5 year Regen Ag rotation. Thank you
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