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Table 1: Broadc<strong>as</strong>t and trailing shoe slurry application details (March 2004)<br />

Application<br />

rate (m3/ha)<br />

N applied<br />

(kg/ha)<br />

Surface area occupied<br />

by band spread slurry<br />

(%)<br />

Hydraulic loading rate (mm)<br />

Broadc<strong>as</strong>t Trailing shoe<br />

20 91 18 2.0 11<br />

35 159 22 3.5 16<br />

50 227 26 5.0 19<br />

65 295 30 6.5 22<br />

80 363 27 8.0 30<br />

CONCLUSIONS<br />

Shallow injection of slurry into the clay loam gr<strong>as</strong>sland soil (at application rates<br />

between 20 and 80 m 3 /ha) reduced NH 3<br />

emissions by c. 60% compared with<br />

surface broadc<strong>as</strong>t application, largely <strong>as</strong> a result of the smaller emitting surface area.<br />

Although there w<strong>as</strong> some ‘overspill’ from the injection slots at the higher application<br />

rates, the majority of the slurry remained within the slot and this did not affect NH3<br />

emissions <strong>as</strong> a % of the total N applied.<br />

Slurry application using a trailing shoe did not reduce NH 3<br />

emissions compared with<br />

surface broadc<strong>as</strong>t application. Although the slurry remained within a band (surface<br />

area occupied 18–30%), the combination of a high hydraulic loading rate (11–30 mm)<br />

and wet soil conditions restricted the rate of slurry infiltration into the soil, which<br />

resulted in similar NH 3<br />

losses to the broadc<strong>as</strong>t application.<br />

These data indicate that for slurry shallow injection and bandspreading techniques to<br />

successfully reduce NH 3<br />

emissions, slurry needs to be retained in a band/slot (to give<br />

a smaller emitting surface area) and to rapidly infiltrate into the soil. If both conditions<br />

are not satisfied, the NH 3<br />

reduction benefit of bandspread/shallow injection spreading<br />

techniques will not be realised.<br />

ACKNOWLEDGEMENTS<br />

Funding of this work by Defra is gratefully acknowledged.<br />

REFERENCES<br />

B<strong>as</strong>ford WD, Briggs W, Jackson DR and Smith KA (1996). Equipment for the improved<br />

precision application of animal w<strong>as</strong>te slurries and liquid effluents to field plots. In:<br />

Proceedings of the International Conference on Mechanisation of Field Experiments<br />

(IAMFE ‘96), IAMFE, Paris/Versailles, France, pp. 161-166.<br />

Defra (2002). Ammonia in the UK. Defra Publications, London.<br />

Lockyer DR (1984) A system for the me<strong>as</strong>urement in the field of losses of ammonia<br />

through volatilisation. Journal of the Science of Food and Agriculture 35, 837–848.<br />

Smith KA, Jackson DR, Misselbrook TH, Pain BF and Johnson RA (2000). Reduction<br />

of ammonia emissions by slurry application techniques. Journal of Agricultural<br />

Engineering Research 77, 277–287.<br />

243

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