School of Biosciences, University of Nottingham, Loughborough, UK.
UK Centre for Ecology & Hydrology, Bangor, UK.
Glob Chang Biol. 2023 Aug;29(15):4279-4297. doi: 10.1111/gcb.16747. Epub 2023 May 15.
There are limited data for greenhouse gas (GHG) emissions from smallholder agricultural systems in tropical peatlands, with data for non-CO emissions from human-influenced tropical peatlands particularly scarce. The aim of this study was to quantify soil CH and N O fluxes from smallholder agricultural systems on tropical peatlands in Southeast Asia and assess their environmental controls. The study was carried out in four regions in Malaysia and Indonesia. CH and N O fluxes and environmental parameters were measured in cropland, oil palm plantation, tree plantation and forest. Annual CH emissions (in kg CH ha year ) were: 70.7 ± 29.5, 2.1 ± 1.2, 2.1 ± 0.6 and 6.2 ± 1.9 at the forest, tree plantation, oil palm and cropland land-use classes, respectively. Annual N O emissions (in kg N O ha year ) were: 6.5 ± 2.8, 3.2 ± 1.2, 21.9 ± 11.4 and 33.6 ± 7.3 in the same order as above, respectively. Annual CH emissions were strongly determined by water table depth (WTD) and increased exponentially when annual WTD was above -25 cm. In contrast, annual N O emissions were strongly correlated with mean total dissolved nitrogen (TDN) in soil water, following a sigmoidal relationship, up to an apparent threshold of 10 mg N L beyond which TDN seemingly ceased to be limiting for N O production. The new emissions data for CH and N O presented here should help to develop more robust country level 'emission factors' for the quantification of national GHG inventory reporting. The impact of TDN on N O emissions suggests that soil nutrient status strongly impacts emissions, and therefore, policies which reduce N-fertilisation inputs might contribute to emissions mitigation from agricultural peat landscapes. However, the most important policy intervention for reducing emissions is one that reduces the conversion of peat swamp forest to agriculture on peatlands in the first place.
农业温室气体排放(GHG)在热带泥炭地的小农系统中数据有限,而人类影响下的热带泥炭地的非 CO 排放数据尤其稀缺。本研究的目的是量化东南亚热带泥炭地小农系统的土壤 CH 和 N O 通量,并评估其环境控制因素。该研究在马来西亚和印度尼西亚的四个地区进行。在农田、油棕种植园、人工林和森林中测量了 CH 和 N O 通量和环境参数。森林、人工林、油棕和农田土地利用类型的年 CH 排放量(kg CH ha 年)分别为:70.7 ± 29.5、2.1 ± 1.2、2.1 ± 0.6 和 6.2 ± 1.9。年 N O 排放量(kg N O ha 年)分别为:6.5 ± 2.8、3.2 ± 1.2、21.9 ± 11.4 和 33.6 ± 7.3,顺序同上。年 CH 排放量主要由地下水位深度(WTD)决定,当年 WTD 高于-25cm 时,排放量呈指数增长。相比之下,年 N O 排放量与土壤水中的总溶解氮(TDN)呈强烈正相关,呈 S 型关系,直到 10mg/L 左右的明显阈值,此后 TDN 似乎不再是 N O 产生的限制因素。本文提出的新的 CH 和 N O 排放数据应有助于为国家温室气体清单报告的量化制定更稳健的国家“排放因子”。TDN 对 N O 排放的影响表明,土壤养分状况强烈影响排放,因此,减少氮肥投入的政策可能有助于减少农业泥炭地景观的排放。然而,减少排放的最重要政策干预措施是首先减少将泥炭沼泽森林转化为农业用地。