Table 3.
Source | PPc | (Range) | WCd | (Range) | HSe | (Range) |
---|---|---|---|---|---|---|
Enteric fermentation (CH4) | 7.09 | (6.16–8.02) | 7.7 | (6.43–9.70) | 7.52 | (5.24–9.61) |
Manure management (CH4)a | 1.36 | (0.73–1.78) | 1.83 | (1.11–2.56) | 1.68 | (1.27–2.59) |
Manure management (direct N2O) | 1.15 | (0.99–1.34) | 1.06 | (0.66–1.38) | 1.06 | (0.70–1.32) |
Manure management (indirect volatilisation N2O) | 0.2 | (0.17–0.22) | 0.18 | (0.11–0.23) | 0.18 | (0.12–0.23) |
Barley production | 0.56 | (0.44–0.69) | 0.62 | (0.46–0.90) | 0.61 | (0.50–0.87) |
Ammonium nitrate production | 3.56 | (2.78–4.39) | 0.53 | (0.39–0.76) | 3.32 | (2.73–4.72) |
Fertililser application (N2O) | 2.03 | (1.59–2.50) | 0.3 | (0.23–0.44) | 1.89 | (1.56–2.69) |
Urine and dung from ewes on pasture (N2O) | 0.6 | (0.47–0.74) | 0.67 | (0.50–0.97) | 0.66 | (0.54–0.94) |
Farmyard manure application (N2O) | 0.43 | (0.25–0.55) | 0.45 | (0.30–0.62) | 0.52 | (0.40–0.78) |
Crop residues (N2O) | – | – | 0.33 | (0.25–0.48) | 0.33 | (0.27–0.46) |
Indirect emissions from leaching (N2O) | 0.2 | (0.17–0.24) | 0.11 | (0.08–0.14) | 0.2 | (0.15–0.29) |
Urine and dung from cattle on pasture (N2O) | 0.25 | (0.19–0.31) | 0.21 | (0.13–0.29) | 0.19 | (0.11–0.27) |
Single superphosphate production | 0.03 | (0.02–0.04) | 0.18 | (0.14–0.27) | 0.03 | (0.03–0.05) |
Othersb |
1.03 |
(0.80–1.26) |
1.8 |
(1.34–2.58) |
1.97 |
(1.61–2.80) |
Total | 18.47 | (16.32–21.71) | 15.96 | (13.73–20.90) | 20.17 | (16.63–25.61) |
Methane arising from manure management was calculated under a deep bedding system assuming a methane conversion factor of 20% and an average annual temperature of 12 °C.
Includes processes which account for <1% of the total emissions intensity: lime production and decomposition, soybean production, pesticide production, transportation and diesel combustion for machinery.
PP: permanent pasture.
WC: white clover/high sugar grass mix.
HS: high sugar grass monoculture.