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Effects of temperature and processing conditions on biochar chemical properties and their influence on soil C and N transformations

机译:温度和加工条件对生物炭化学性质的影响及其对土壤碳氮转化的影响

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There have been limited studies of how the pyrolysis process and activation conditions affect the chemical properties of biochar and how these properties alter soil carbon (C) and nitrogen (N) transformations when used as an amendment. This study compared the chemical properties of biochars produced through slow pyrolysis at 200, 400 and 600 degrees C, in the presence or absence of steam and CO2 activation at 800 degrees C. Quantitative solid-state C-13 nuclear magnetic resonance spectroscopy and elemental analysis were used to evaluate processing condition effects on biochar chemical properties. Biochars were added at a rate of 0.75% by weight and soils were incubated for 28 d, during which soil inorganic N and CO2 and N2O emissions were determined. Thereafter, adsorption of ammonium (NH4+) and nitrate (NO3-) - N were investigated further. While constituents of biochar feedstock were not altered at pyrolysis temperature of 200 degrees C, NMR data showed that biochars produced at 400 and 600 degrees C converted >82% of labile C constituents to aromatic C structures, which increased their recalcitrance. Also the later pyrolysis temperatures increased biochar cation exchange capacity (CEC) and pH, however, exposure to steam and CO2 activation decreased their CEC. Compared to unamended soil, amendment with biochar produced at 200 degrees C significantly increased cumulative CO2 and N2O emissions by more than 3 fold, whereas those produced at 400 degrees C had no effect on CO2 emissions but had a similar effect on cumulative N2O emissions. Biochar produced at 600 degrees C had no effect on either CO2 or N2O emissions. In contrast, activation of biochar significantly decreased cumulative CO2 emissions by 18%. Amendment with biochars produced at 400 and 600 degrees C and activated biochars significantly decreased soil inorganic N, which was attributed to their increased adsorptive capacity for NH4+ by 62-81%. This study highlights the importance of production conditions for designing biochars for use as amendments to sequester soil C and N, by promoting the formation of stable soil organic matter and by increasing retention of soil inorganic N. From a soil amendment perspective, this study suggests that activation of biochar did not benefit soil C and N transformations. Crown Copyright (C) 2015 Published by Elsevier Ltd. All rights reserved.
机译:关于热解过程和活化条件如何影响生物炭的化学性质以及当用作改良剂时这些性质如何改变土壤碳(C)和氮(N)转化的研究有限。这项研究比较了在有或没有蒸汽和800°C的CO2活化下在200、400和600°C缓慢热解所产生的生物炭的化学性质。定量固态C-13核磁共振波谱和元素分析被用来评估加工条件对生物炭化学性质的影响。以0.75%(重量)的比例添加生物炭,将土壤保温28天,在此期间测定土壤中的无机氮和CO2和N2O排放量。此后,进一步研究了铵(NH4 +)和硝酸盐(NO3-)-N的吸附。虽然生物炭原料的成分在200摄氏度的热解温度下没有改变,但NMR数据显示,在400摄氏度和600摄氏度下产生的生物炭将超过82%的不稳定C成分转化为芳族C结构,从而增加了其顽固性。同样,后来的热解温度增加了生物碳交换量(CEC)和pH,但是,暴露于蒸汽和CO2活化会降低其CEC。与未改良的土壤相比,用200摄氏度下产生的生物炭进行改良可显着增加累积CO2和N2O排放量的3倍以上,而在400摄氏度下产生的生物炭对CO2排放量没有影响,但对累积N2O排放量具有类似的影响。在600摄氏度下产生的生物炭对CO2或N2O排放均无影响。相比之下,生物炭的活化显着降低了累计CO2排放量18%。分别在400和600摄氏度下生产的生物炭和活化的生物炭的修正显着降低了土壤无机氮,这归因于它们对NH4 +的吸附能力提高了62-81%。这项研究强调了生产条件对于设计生物碳以改良螯合土壤碳和氮,通过促进稳定的土壤有机质的形成以及增加土壤无机氮的保留的重要性。从土壤改良的角度来看,该研究表明生物炭的活化并没有使土壤碳和氮转化受益。 Crown版权所有(C)2015,由Elsevier Ltd.发行。保留所有权利。

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