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Carbon stability and mitigation of fertilizer induced N_2O emissions in soil amended with biochar

机译:生物炭对土壤中碳的稳定性和化肥诱导的N_2O排放的缓解作用

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Biochar is a promising tool for an efficient and low environmental impact agriculture since can offer both soil carbon (C) sequestration and mitigation of nitrous oxide (N2O) emissions. The extent of biochar C stability after soil amendment and efficiency in reducing N2O emissions from an external nitrogen (N) source were accessed through laboratory incubations. A clay loam soil was amended with chicken manure (CM), sewage sludge (SS), eucalyptus sawdust (ES) and filter cake (FC) feedstocks and corresponding slow-pyrolysis (400°C) biochars at 5gCkg−1soil in combination with two N fertilizer rates (0 and 140mgNkg−1soil). Carbon dioxide (CO2) and N2O emissions were measured during 60days. Biochars and feedstocks CO2emissions were described by an exponential first order kinetics model. For C mineralization an interaction effect was observed for feedstock source and organic amendment. Lower values of mineralizable C was found for biochars than corresponding feedstocks, except for ES. Carbon losses in 60days of incubation totaled between 0.8 and 9.4% and 2.4 and 32% for biochars and feedstocks, respectively. Regarding to N2O emissions, only CM-biochar impacted emissions with a two-fold increase in non-fertilized soil. When NH4NO3was co-applied, biochars reduced fertilizer induced N2O emissions, reaching a seven-fold reduction in SS-biochar treatment. The fertilizer emission factor (EF) decreased with biochar amendments as well, varying between 0.01 and 0.08% of the fertilizer N emitted as N2O, which shows the biochar potential to reduce fertilizer induced N2O emissions, with major reduction by SS-biochar mitigating 87% of the soil-fertilizer emissions. Such potential could be explored by designing biochars based on feedstock chemical and structural properties, including a mixed feedstock source biochar that promotes C sequestration and mitigates N2O emissions.
机译:生物炭是高效且对环境影响小的农业的有前途的工具,因为它既可以隔离土壤碳(C),又可以减少一氧化二氮(N2O)的排放。土壤改良后的生物炭C稳定性的程度以及减少外部氮(N)来源的N2O排放的效率可通过实验室培养来获得。用鸡粪(CM),污水污泥(SS),桉木锯末(ES)和滤饼(FC)原料以及相应的慢热解(400°C)生物炭在5gCkg-1土壤中结合两种对土壤肥沃的土壤进行改良氮肥用量(0和140mgNkg-1土壤)。在60天内测量了二氧化碳(CO2)和N2O排放。生物炭和原料的CO2排放通过指数一级动力学模型进行描述。对于碳矿化,观察到了原料来源和有机改性剂的相互作用。发现生物炭的可矿化碳值低于相应的原料(ES除外)。孵化60天的碳损失分别为生物炭和原料的0.8%至9.4%,2.4%至32%。关于N2O排放,只有CM生物炭影响了排放,未施肥的土壤增加了两倍。当共同使用NH4NO3时,生物炭减少了肥料诱导的N2O排放,SS-生物炭处理减少了七倍。肥料排放因子(EF)也随着生物炭的添加而降低,在以N2O排放的肥料氮中的0.01%至0.08%之间变化,这表明生物炭具有减少肥料诱导的N2O排放的潜力,其中SS-生物炭的主要减排量减少了87%土壤肥料的排放量。可以通过基于原料化学和结构特性设计生物炭来探索这种潜力,其中包括可促进碳固存并减轻N2O排放的混合原料源生物炭。

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