The New Zealand Institute for Plant & Food Research Limited, Canterbury Agriculture and Science Centre, Christchurch Mail Centre, Christchurch, New Zealand.
Retired, Formerly AgResearch, Lincoln, New Zealand.
Glob Chang Biol. 2021 May;27(10):1998-2010. doi: 10.1111/gcb.15561. Epub 2021 Mar 6.
As soils under permanent pasture and grasslands have large topsoil carbon (C) stocks, the scope to sequester additional C may be limited. However, because C in pasture/grassland soils declines with depth, there may be potential to sequester additional C in the subsoil. Data from 247 continuous pasture sites in New Zealand (representing five major soil Orders and ~80% of the grassland area) showed that, on average, the 0.15-0.30 m layer contained 25-34 t ha less C than the top 0.15 m. High-production grazed pastures require periodic renewal (re-seeding) every 7-14 years to maintain productivity. Our objective was to assess whether a one-time pasture renewal, involving full inversion tillage (FIT) to a depth of 0.30 m, has potential to increase C storage by burying C-rich topsoil and bringing low-C subsoil to the surface where C inputs from pasture production are greatest. Data from the 247 pasture sites were used to model changes in C stocks following FIT pasture renewal by predicting (1) the C accumulation in the new 0-0.15 m layer and (2) the decomposition of buried-C in the new 0.15-0.30 m layer. In the 20 years following FIT pasture renewal, soil C was predicted to increase by an average of 7.3-10.3 (Sedimentary soils) and 9.6-12.7 t C ha (Allophanic soils), depending on the assumptions applied. Adoption of FIT for pasture renewal across all suitable soils (2.0-2.6 M ha) in New Zealand was predicted to sequester ~20-36 Mt C, sufficient to offset 9.6-17.5% of the country's cumulative greenhouse gas emissions from agriculture over 20 years at the current rate of emissions. Given that grasslands account for ~70% of global agricultural land, FIT renewal of pastures or grassland could offer a significant opportunity to sequester soil C and offset greenhouse gas emissions.
由于永久牧场和草原下的土壤具有较大的表土碳(C)储量,因此可能的碳封存范围可能有限。然而,由于牧场/草原土壤中的 C 随深度下降,因此在亚土层中可能有潜力封存额外的 C。来自新西兰 247 个连续牧场的资料(代表五种主要土壤类型和80%的草原面积)表明,平均而言,0.15-0.30 m 层的 C 含量比上层 0.15 m 少 25-34 t ha。高生产力的放牧牧场需要每隔 7-14 年进行一次周期性更新(重新播种),以维持生产力。我们的目标是评估一次性牧场更新(涉及到 0.30 m 深的全反转耕作(FIT))是否有潜力通过掩埋富碳表土和将低 C 亚土层带到牧场生产中 C 输入最大的地方来增加 C 储存。利用来自 247 个牧场的资料,通过预测(1)新的 0-0.15 m 层中的 C 积累和(2)新的 0.15-0.30 m 层中埋藏 C 的分解,来模拟 FIT 牧场更新后的 C 储量变化。在 FIT 牧场更新后的 20 年内,土壤 C 预计平均增加 7.3-10.3(沉积土壤)和 9.6-12.7 t C ha(含腐殖酸土壤),具体取决于应用的假设。假设在新西兰所有适宜土壤(2.0-2.6 M ha)上采用 FIT 进行牧场更新,预计可封存20-36 Mt C,足以抵消该国在当前排放速度下 20 年内农业累计温室气体排放的 9.6-17.5%。鉴于草原占全球农业用地的~70%,对牧场或草原进行 FIT 更新可能是封存土壤 C 和抵消温室气体排放的一个重要机会。