2016
DOI: 10.1007/s11368-016-1442-1
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The potential of using alternative pastures, forage crops and gibberellic acid to mitigate nitrous oxide emissions

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Cited by 29 publications
(11 citation statements)
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“…In contrast, 40% of the milking platform in the ‘improved(LOW)’ system consisted of diverse pasture containing chicory, plantain, ryegrass, and clover, with non-lactating cows wintered on forage kale and oat silage. Although the diverse pasture was modelled to produce lower N 2 O EF 3 values for deposited urine [30], the emission intensities associated with total N 2 O loss from dung and urine did not differ between the two systems (Table 4). This was partly due to the ‘improved(LOW)’ system including kale in the winter period, which had a higher EF 3 value than the fodder beet crop grazed in the ‘current’ and ‘improved(HIGH)’ systems.…”
Section: Resultsmentioning
confidence: 99%
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“…In contrast, 40% of the milking platform in the ‘improved(LOW)’ system consisted of diverse pasture containing chicory, plantain, ryegrass, and clover, with non-lactating cows wintered on forage kale and oat silage. Although the diverse pasture was modelled to produce lower N 2 O EF 3 values for deposited urine [30], the emission intensities associated with total N 2 O loss from dung and urine did not differ between the two systems (Table 4). This was partly due to the ‘improved(LOW)’ system including kale in the winter period, which had a higher EF 3 value than the fodder beet crop grazed in the ‘current’ and ‘improved(HIGH)’ systems.…”
Section: Resultsmentioning
confidence: 99%
“…In brief, this methodology uses estimates of dry matter intake (DMI), N inputs, and N leaching losses, in combination with CH 4 and N 2 O emission factors (EF). In this study a combination of NZAI emission factor values and CH 4 and N 2 O emissions factors were used that were measured for key components of the milking platform or the wintering period for each system [30,31,32]. We used these targeted measurements to provide us with emission factor results for key components in the farmlets that we otherwise would not able to assess as the NZAI emission factors are not sufficiently disaggregated.…”
Section: Methodsmentioning
confidence: 99%
“…There are currently no studies used by the IPCC to refine the EF 3PRP that use emissions reported from grazed herbs such as chicory. Although some studies did not report sward composition [181][182][183] , calculations were made from predominantly grass swards [184][185][186][187][188][189][190][191][192] , grass-clover [144,186,[193][194][195][196][197][198] or forage crops (e.g., barley, lucerne, or brassicas such as rape, Brassica napus, or kale, Brassica oleracea var. sabellica) [186,194,199] .…”
Section: Urine-patch N 2 O Emissionsmentioning
confidence: 99%
“…Although consistent observation of BNI is still lacking, the inclusion of pastures and forages that exhibit BNI potential in pastoral agricultural systems is being considered as a useful tool for reducing N 2 O emissions (Di et al, 2016; Gardiner et al, 2016; Balvert and Luo, 2017; Luo et al, 2018). In New Zealand pastoral agriculture, diverse pastures and forages are also being increasingly used for additional benefits such as drought tolerance or to meet feed deficits in winter or summer (Hoogendoorn et al, 2016).…”
mentioning
confidence: 99%