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Manure management facilities on farms and their relevance to efficient nutrient use Bernard Hyde & Owen, T. Carton Teagasc, Johnstown Castle The Fertilizer.

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Presentation on theme: "Manure management facilities on farms and their relevance to efficient nutrient use Bernard Hyde & Owen, T. Carton Teagasc, Johnstown Castle The Fertilizer."— Presentation transcript:

1 Manure management facilities on farms and their relevance to efficient nutrient use Bernard Hyde & Owen, T. Carton Teagasc, Johnstown Castle The Fertilizer Association of Ireland Winter Scientific Meeting 25 th November 2005 Faculty of Agriculture, University College Dublin

2 Manure 2003 - 6.3 million animals = 37 million tonnes Slurry = 29.3 million tonnes Solid = 7.7 million tonnes Dairy cows ~ 28% of slurry & ~ 7% of solid manure

3 Topic – facilities & utilisation Manure management facilities  Storage  Spreading date  Spreading method Nutrient efficiency  Manure type  N, P & K Cost vs. nutrient value

4 Requirements for efficient nutrient use NMP Changing slurry spreading date Changing slurry spreading method Storage vs. spreading date? Cost benefit?

5 Efficient manure nutrient use

6 NMP Soil Manure Crop demand Code of Practice  Rate  Date  Method

7 Current utilisation? Indicators? FUS (2002 & 2005)  Indications of N, P & K overuse Fert. input = Fert. required Slurry? Farm Facilities Survey (2003) – crop & timing of application

8 Topic – facilities & utilisation Manure management facilities  Storage  Spreading date  Spreading method

9 Timing of slurry application & % of total SpringSummerAutumnWinterTotal Conservation land0.260.430.110.030.83 Grazing land0.050.040.02 0.13 Maize0.020.010.00 0.03 Tillage0.010.00 0.02 Total0.330.480.140.05

10 Timing of slurry application & % of total SpringSummerAutumnWinterTotal Conservation land0.260.430.110.030.83 Grazing land0.050.040.02 0.13 Maize0.020.010.00 0.03 Tillage0.010.00 0.02 Total0.330.480.140.05

11 Timing of slurry application & % of total SpringSummerAutumnWinterTotal Conservation land0.260.430.110.030.83 Grazing land0.050.040.02 0.13 Maize0.020.010.00 0.03 Tillage0.010.00 0.02 Total0.330.480.140.05

12 Timing of slurry application SpringSummerAutumnWinter Conservation land3152134 Utilisation efficiency N25500 P100 K ?

13 Timing of slurry application SpringSummerAutumnWinter Conservation land3152134 Utilisation efficiency N25500 P100 K ? WHY ?

14 Efficient manure nutrient use

15

16

17 Storage Spreading date – 4% in winter Estimated storage deficits – national basis  21% for 16 week storage  31% for 22 week storage Action Programme  Ban on winter spreading  Required minimum slurry storage Reconcile deficit and date?

18 Landspreading - N efficiency N efficiency – key issue Spreading date & rate  Soil/weather conditions Contamination  Spreading date Spreader availability  Farmer owned  Contractor

19 Slurry spreading opportunities Distribution of the number of days on which soils have a soil moisture deficit in excess of 10 mm. (Schulte et al., in press)

20 Silage contamination ? End March/early April Crop – too far advanced Risk of poor fermentation

21 Spreader availability C.S.O. – Census of Ag. 2000 124, 108 livestock farms ( = 100 ha) 72, 368 livestock farms (20 to >= 100 ha) 31, 046 farms own or share slurry tankers 35, 281 farms hire or borrow slurry tankers Farm Facilities Survey

22 27% consist of 1 holding 31% have 4 + fragments Farm Fragmentation

23 Fragment Distance Farm Fragmentation – distance (km)

24 Topic – facilities & utilisation Nutrient efficiency

25 Nutrient availability Type of manure Dry matter(%) * N (kg/t) Total Spring Summer P (kg/t)K (kg/t) Cattle slurry 6.93.60.90.20.64.3 * Dry matter content varies widely and this determines the nutrient contents

26 N availability in slurry Organic - N (Ammonium – N) Inorganic - N

27 Ammonium - N Spring NH 3 Crop available Summer NH 3

28 Fertiliser N for silage compared to slurry N

29 ?

30 Current utilisation vs. available N Spreading method Spreading date Soil/weather conditions

31

32

33 =

34 = =

35 = = NH 3

36 = =

37 Efficient manure nutrient use

38 Advantages of trailing shoe application NH 3 emission reduced Recovery of total N ~ 40 - 50% Slurry can be applied to taller crops Slurry applied to soil surface – contamination ? Increased opportunity for spring application Heavier soils in wetter areas Teagasc research

39 Fertiliser N for silage compared to slurry N ?

40 Organic N Inorganic/organic = 50/50 Organic material/solid fraction Currently not considered as a reliable N source Mineralization 60 kg N/ha (33t/ha) for slurry Teagasc research

41 Topic – facilities & utilisation Cost vs. nutrient value

42 Economic value of slurry N (€ million)

43 6% 22% 44% 88%

44 Economic value of slurry N (€ million) € 67.2

45 Economic value of slurry N (€ million) € 67.2 € 3.8

46 Economic value of slurry N (€ million) € 67.2 € 3.8 € 14.8

47 Economic value of slurry N (€ million) € 67.2 € 3.8 € 14.8 € 29.5

48 Economic value of slurry N (€ million) € 67.2 € 3.8 € 14.8 € 29.5 € 59.1

49 Economic value (million €) of slurry

50 € 83.9 million

51 Economic value (million €) of slurry € 98.7 million

52 Economic value (million €) of slurry € 128.1 million

53 Summary 29.3 million tonnes slurry Current utilisation Key issues - storage & landspreading Nutrient availability – N efficiency Spreading methodology – conventional vs ts Economic value of slurry - €128 million

54 Conclusions Manure/slurry is a valuable resource Short-term  Change application timing from summer/autumn to spring  Change spreading method  Available N in slurry a/c’s ~ 45% of purchased fert. N Long-term  Increase nutrient efficiency  Organic N Research

55 Efficient manure nutrient use


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