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In Situ Persistence and Migration of Biochar Carbon and Its Impact on Native Carbon Emission in Contrasting Soils under Managed Temperate Pastures

机译:温带草场下不同土壤中生物碳的原位持久性和迁移及其对天然碳排放的影响

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摘要

Pyrogenic carbon (PyC) is an important component of the global soil carbon (C) pool, but its fate, persistence, and loss dynamics in contrasting soils and environments under planted field conditions are poorly understood. To fill this knowledge gap, a 13C-labelled biochar, as a surrogate material for PyC, produced from Eucalyptus saligna by slow pyrolysis (450°C; δ13C -36.7‰) was surface (0−10 cm) applied in C3 dominated temperate pasture systems across Arenosol, Cambisol and Ferralsol. The results show a low proportion of the applied biochar-C mineralised over 12 months in a relatively clay- and C-poor Arenosol (i.e., 2.0% loss via mineralisation), followed by a clay- and C-rich Cambisol (4.6%), and clay-, C- and earthworm-rich Ferralsol (7.0%). The biochar-C mean residence time (MRT), estimated by different models, varied between 44−1079 (Arenosol), 18−172 (Cambisol), and 11−29 (Ferralsol) years, with the shorter MRT estimated by a one-pool exponential and the longer MRT by an infinite-pool power or a two-pool exponential model. The two-pool model was best fitted to biochar-C mineralisation. The biochar-C recovery in the 12−30 cm soil layer varied from between 1.2% (Arenosol), 2.5−2.7% (Cambisol) and 13.8−15.7% (Ferralsol) of the applied biochar-C after 8−12 months. There was a further migration of biochar-C below the 50-cm depth in the Arenosol, as the combined biochar-C recovery in the mineralised pool and soil profile (up to 30 or 50 cm) was 82%, in contrast to 101% in the Cambisol and 104% in the Ferralsol after 12 months. These results indicate that the downward migration of biochar-C was greatest in the Arenosol (cf. Cambisol and Ferralsol). Cumulative CO2-C emission from native soil-plant sources was lower (p <0.10) in the biochar-amended vs. non-amended Ferralsol. This field-based study shows that the downward migration of biochar-C exceeded its loss via mineralisation in the Arenosol and Ferralsol, but not in the Cambisol. It is thus important to understand biochar-soil interactions to maximise long-term biochar C sequestration potential in planted soil systems.
机译:热解碳(PyC)是全球土壤碳(C)库的重要组成部分,但是人们对在种植田间条件下土壤和环境形成对比的命运,持久性和损失动态知之甚少。为了填补这一知识空白,通过缓慢热解(450°C;δ 13 C-在Arenosol,Cambisol和Ferralsol的C3为主的温带牧草系统中施用了36.7‰(0-10 cm)的表面。结果表明,在相对贫瘠和贫C的槟榔中,在12个月内矿化的生物炭C的比例很低(即,因矿化而损失2.0%),其次是富粘土和富C的坎比索(4.6%) ,以及富含粘土,碳和and的Ferralsol(7.0%)。通过不同模型估算的生物炭C平均停留时间(MRT)在44-1079(Arenosol),18-172(Cambisol)和11-29(Ferralsol)年之间变化,MRT较短的时间为一个通过无限池功率或两池指数模型计算池指数和更长的MRT。两池模型最适合生物炭C矿化。 8-12个月后,在12-30 cm土层中生物碳的回收率介于所施用生物碳的1.2%(Arenosol),2.5-2.7%(Cambisol)和13.8-15.7%(Ferralsol)之间。砂岩中低于50厘米深度的生物炭进一步迁移,因为矿化池和土壤剖面(高达30或50厘米)中生物炭C的总回收率为82%,而101% 12个月后,在Cambisol和Ferralsol中为104%。这些结果表明,生物炭-C的向下迁移在槟榔中最大(参见Cambisol和Ferralsol)。经过生物炭改良的Ferralsol与未经土壤改良的Ferralsol相比,来自天然土壤植物来源的累积CO2-C排放较低(p <0.10)。这项基于野外的研究表明,生物炭-C的向下迁移超过了其在槟榔和Ferralsol中矿化的损失,但在Cambisol中却没有。因此,重要的是要了解生物炭与土壤的相互作用,以使种植土壤系统中的长期生物炭固碳潜力最大化。

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