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ANALYSIS OF TOTAL ORGANIC CARBON IN SOIL-BIOCHAR SYSTEMS

机译:土壤 - 生物炭系统总有机碳分析

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Amending agricultural soils with biochar can contribute to negative carbon strategies when the resistance to oxidation of soil carbon is improved (avoided CO_2 emission) and plant growth is promoted (increased CO_2 fixation). The environmental stability and sequestering capacity of biochar is dependent on the chemical form of carbon and its physical location in the carbonaceous matrix. The addition of biochar in soil increases noticeably the stable carbon pool, while the effect on labile carbon, including polyaromatic structures, is less marked. The fertilizing action can be lost if biochar is removed from the cultivated area due to physical processes (vertical transport, lateral export, slacking). Assessing the fate of carbon in the soil requires the use of suitable analytical methods that should be validated for the presence of biochar. While several studies have compared different methods (wet chemical, dry combustion, loss of ignition) for the determination of total organic carbon (TOC), comparative studies for biochar treated soils are scant.3 The principal aim of this study was to compare dry combustion methods with a TOC analyser (Shimadzu) and a HCN analyser (ThermoFisher scientific) to determine TC, TOC and IC (inorganic carbon) in model soils with and without biochar. Air dried agriculture soils with low and high content of IC were mixed with biochar at 1 % wt. level. Biochar produced from an up-draft gasifier utilized in the PSR project for application in cultivated soils was considered along with two reference biochars. The TOC analyser operated at 900 °C for TC, IC was determined at 200 °C after acidification with aq. H_3PO_4; quantitation was performed by infrared detection of evolved CO_2 using glucose and sodium carbonate as calibration standard for TC and IC, respectively; TOC was calculated by difference. The HCN analyser was applied to the samples directly (TC) and after aq. HCI treatment (TOC) using GC-TCD detection and calibration with 2,5-bis(5-tert-butyl-2-benzoxazol-2-yl)thiophene. Obtained results of TC and TOC were compared with the expected values. The effect of sample pretreatment, carbonate content and biochar type on carbon concentrations was investigated. In addition, thermogravimetric analysis (TGA) was evaluated as a method to discriminate labile (humic-like) and stable (black carbon-ile) components of soil organic matter.
机译:当对土壤碳氧化的抗性改善(避免CO_2发射)和促进植物生长(促进植物生长(增加CO_2固定)时,农业土壤可能导致负碳策略有助于负碳策略。生物炭的环境稳定性和螯合能力取决于碳质基质中的碳的化学形式及其物理位置。在土壤中添加BioChOr显着增加稳定的碳池,而对稳定碳的影响,包括多芳族结构的作用较小。如果由于物理过程(垂直运输,横向出口,松弛)从耕地面积中除去生物炭,施肥作用可能会丢失。评估土壤中的碳的命运需要使用应验证的合适的分析方法是否存在生物炭。虽然几项研究比较了不同的方法(湿化学,干燃烧,点火丧失),但用于测定总有机碳(TOC),但生物炭处理的土壤的比较研究是Scant.3本研究的主要目的是比较干燃烧方法采用TOC分析仪(Shimadzu)和HCN分析仪(Thermofisher Scientific),用于确定模型土壤中的TC,TOC和IC(无机碳),具有和不含生物炭。用低和高含量的IC的空气干燥的农业土壤与生物炭加1%wt。等级。考虑了由PSR工程中使用的加入气化器生产的Biochar,用于培养土壤中的应用,以及两种参考生物炸素。在用水溶液酸化后,在900℃下操作的TOC分析仪在900℃下操作,IC在200℃下测定。 h_3po_4;通过使用葡萄糖和碳酸钠作为TC和IC的校准标准,通过红外检测通过红外检测进行定量。 TOC通过差异计算。 HCN分析仪直接(TC)和AQ之后应用于样品。 HCI处理(TOC)使用GC-TCD检测和用2,5-双(5-叔丁基-2-苯并恶唑-2-基)校准校准。将TC和TOC的结果与预期值进行比较。研究了样品预处理,碳酸盐含量和生物炭型对碳浓度的影响。此外,评价热量分析(TGA)作为区分土壤有机物质的不稳定(蜂窝状)和稳定(黑碳-Ile)组分的方法。

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