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首页> 外文期刊>Biogeosciences Discussions >Carbon budgets for an irrigated intensively grazed dairy pasture and an unirrigated winter-grazed pasture
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Carbon budgets for an irrigated intensively grazed dairy pasture and an unirrigated winter-grazed pasture

机译:灌溉密集放牧的奶牛牧场和未灌溉的冬季放牧的牧场的碳预算

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摘要

pstrongAbstract./strong Intensification of pastoral agriculture is occurring rapidly across New Zealand, including increasing use of irrigation and fertiliser application in some regions. While this enables greater gross primary production (GPP) and livestock grazing intensity, the consequences for the net ecosystem carbon budget (NECB) of the pastures are poorly known. Here, we determined the NECB over one year for an irrigated, fertilised and rotationally grazed dairy pasture and a neighbouring unirrigated, unfertilised, winter-grazed pasture. Primary terms in the NECB calculation were net ecosystem production (NEP), biomass carbon removed by grazing cows and carbon (C) input from their excreta. Annual NEP was measured using the eddy-covariance method. Carbon removal was estimated with plate-meter measurements calibrated against biomass collections, pre- and post-grazing. Excreta deposition was calculated from animal feed intake. The intensively managed pasture gained C (NECBspan class="thinspace"/spana??=a??span class="thinspace"/span103span class="thinspace"/span?±span class="thinspace"/span42span class="thinspace"/spang??Cspan class="thinspace"/spanmsupa??2/supspan class="thinspace"/spanyrsupa??1/sup) but would have been subject to a non-significant C loss if cattle excreta had not been returned to the pasture. The unirrigated pasture was C-neutral (NECBspan class="thinspace"/spana??=a??span class="thinspace"/spana??13span class="thinspace"/span?±span class="thinspace"/span23span class="thinspace"/spang??Cspan class="thinspace"/spanmsupa??2/supspan class="thinspace"/spanyrsupa??1/sup). While annual GPP of the former was almost twice that of the latter (2679 vs. 1372span class="thinspace"/spang??Cspan class="thinspace"/spanmsupa??2/supspan class="thinspace"/spanyrsupa??1/sup), ecosystem respiration differed by only 68span class="thinspace"/span% between the two pastures (2271 vs. 1352span class="thinspace"/spang??Cspan class="thinspace"/spanmsupa??2/supspan class="thinspace"/spanyrsupa??1/sup). The ratio of GPP to the total annual water input of the irrigated pasture was 37span class="thinspace"/span% greater than that of the unirrigated pasture, i.e. the former used the water input more efficiently than the latter to produce biomass. The NECB results agree qualitatively with those from many other eddy-covariance studies of grazed grasslands, but they seem to be at odds with long-term carbon-stock studies of other New Zealand pastures./p.
机译:> >摘要。新西兰各地的牧业集约化活动正在迅速发生,包括某些地区灌溉和化肥用量的增加。虽然这可以提高初级生产总值(GPP)和牲畜放牧强度,但对牧场的净生态系统碳预算(NECB)的后果知之甚少。在这里,我们确定了灌溉,施肥和轮转放牧的奶牛牧场和附近的未灌溉,未施肥的冬季放牧的牧场在一年内的NECB。 NECB计算中的主要术语是生态系统净产量(NEP),奶牛放牧除去的生物量碳和粪便排泄的碳(C)输入。使用涡度协方差法测量年度NEP。用针对生物量收集,放牧前和放牧后校准的平板仪表测量值估算除碳量。从动物采食量计算排泄物沉积。在集约化管理的牧场上获得C(NECB class =“ thinspace”> a ?? = a ?? class =“ thinspace”> 103 class =“ thinspace”> ?± class =“ thinspace”> 42 class =“ thinspace”> g ?? C class =“ thinspace”> m a ?? 2 class =“ thinspace”> yr a ?? 1 ),但如果没有牛排泄物,本来会造成非重大的C损失。回到牧场。未灌溉的牧场是C中性的(NECB class =“ thinspace”> a ?? = a ?? class =“ thinspace”> a ?? 13 class =“ thinspace “> ?± class =” thinspace“> 23 class =” thinspace“> g ?? C class =” thinspace“> m a ?? 2 class =“ thinspace”> yr a ?? 1 )。前者的年度GPP几乎是后者的两倍(2679与1372的对比) class =“ thinspace”> g ?? C class =“ thinspace”> m a ?? 2 class =“ thinspace”> yr a ?? 1 ),生态系统呼吸仅相差68 class =“ thinspace”> %(2271与1352之间。 class =“ thinspace”> g ?? C class =“ thinspace”> m a ?? 2 class =“ thinspace”> yr a ?? 1 )。 GPP与灌溉草场年总水输入量的比率比未灌溉草场高37 class =“ thinspace”> %,即前者比后者更有效地利用了水输入生产生物质。 NECB的结果与许多其他放牧草地的涡度-协方差研究的结果在质量上吻合,但似乎与其他新西兰牧场的长期碳储量研究不一致。

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