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Priming of soil organic carbon induced by sugarcane residues and its biochar control the source of nitrogen for plant uptake: A dual C-13 and N-15 isotope three-source-partitioning study

机译:甘蔗残基诱导的土壤有机碳的启动及其生物炭控制植物氮素源:双C-13和N-15同位素三源分区研究

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Sugarcane (Saccharum spp.) farming systems globally have largely transitioned away from burning the crop prior to harvest. Harvesting the sugarcane crop 'green' results in large volumes of biomass residues being left on the soil. Despite this, there is little evidence for increased soil organic carbon stocks. We investigated the role of surface application or incorporation (0-200 mm soil layer) of harvest residues (15 t dry weight residues ha(-1)) and its biochar (5.4 t ha(-1) based on the quantity of resource recovered after pyrolysis) on the priming of native soil organic carbon (SOC), the mineralisation of the organic amendments and the source of crop nitrogen (N) uptake (soil, organic amendment or urea). All treatments received urea at 180 kg N ha(-1). To achieve the separation of C and N sources, dual C-13 and N-15-enriched sugarcane residues and corresponding biochar (350 degrees C) were used in an 84-d controlled environment study. A three-pool isotope mixing model, utilising two levels of C-13 enrichment in residue (16.6 parts per thousand and 23.8 parts per thousand) and biochar (16.8 parts per thousand and 24.1 parts per thousand), was also applied to partition the C from three sources: 1) root respiration, 2) organic amendment mineralisation, and 3) SOC priming. The SOC mineralisation was increased following both surface-applied and incorporated residues, over the nil organic amendment (control) by 72.3 and 78.3 CO2-C m(-2) respectively over 84 days. In contrast, biochar lowered the mineralisation of SOC by 62.9 g CO2-C m(-2) compared to the control. The cumulative mineralisation of sugarcane residue biochar (18.9 g CO2-C m(-2)) was lower (P = 0.03) than surface applied residue (50.1 g CO2-C m(-2)) and incorporated residue (71.9 g CO2-C m(-2)) over the study period. While there were no differences in total crop N uptake between the organic-amended soils and the control, the source of N was significantly different. The sugarcane plants utilised 31.0% and 29.4% of the supplied urea N in the nil organic-amended control and biochar treatment, respectively. This was significantly reduced to 24.8% and 20.6% in the surface residue and incorporated residue treatments, respectively. In comparison, the plant uptake of N derived from the organic amendments was 27.8%, 15.4% and 6.4% from incorporated residues, surface-applied residues and biochar, respectively (P < 0.001). Results suggest that the increased mineralisation of SOC, partly driven by the high C:N ratio (73:1) and the unbalanced nutrient stoichiometry may lead to low SOC accumulation from surface residue application and that sugarcane residue biochar results in SOC stabilisation and an increase in the use efficiency of fertiliser N in sugarcane systems.
机译:甘蔗(Saccharum SPP。)在收获之前,全球的农业系统在很大程度上过渡到烧毁作物。收获甘蔗作物“绿色”导致大量的生物质残留物留在土壤上。尽管如此,土壤有机碳股增加几乎没有证据。我们调查了收获残余物的表面施用或掺入(0-200mm土壤层)的作用(15t干重残留物Ha(-1))及其生物炭(5.4 t ha(-1),基于所回收的资源量热解后)对天然土壤有机碳(SoC)的启动,有机修正的矿化和作物氮气源(N)摄取(土壤,有机修正或尿素)。所有治疗均为180千克(-1)尿素。为了实现C和N来源的分离,在84-D受控环境研究中使用双C-13和富含富含富含富含富含甘蔗残基和相应的生物炭(350℃)。三个池同位素混合模型,利用两种水平的残留物(16.6份每千份每千份)和BioChar(每千份16.8份/份每千份),用于分区C.从三个来源:1)根呼吸,2)有机修正矿化,3)SOC引发。在82.3和78.3 CO 2 -C m(-2)上,在含量有机修正(对照)在84.3天内,将表面施加和掺入的残基掺入Soc矿化。相比之下,Biochar与对照相比将SoC的矿化降低62.9g CO 2-C m(-2)。甘蔗残基生物炭的累积矿化(18.9g CO 2-C m(-2))低(p = 0.03),比表面施加的残余物(50.1g CO 2-C m(-2))和掺入残余物(71.9g CO2-研究期间C m(-2))。虽然在有机修正的土壤和对照之间的总作用N产生没有差异,但n的源极明显不同。甘蔗植物分别在无机有机修正的对照和生物炭治疗中使用31.0%和29.4%的供应尿素N.在表面残留物中,这显着降至24.8%和20.6%,并分别掺入残留物处理。相比之下,衍生自有机修正的植物的植物摄取为掺入残基,表面施加的残基和生物炭的27.8%,15.4%和6.4%(P <0.001)。结果表明,SOC的矿化增加,部分由高C:N比(73:1)和不平衡的营养化学计量和不平衡的营养化学计量可能导致表面残留物施用的低SoC积累,并且甘蔗残留生物炭导致SoC稳定和增加在甘蔗系统中肥料N的使用效率。

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