
不同方法提取的生物质炭可溶性有机物性质研究
Biochar-derived Dissolved Organic Matter Extracted by Different Methods: Property Study
为了揭示不同提取方法对生物质炭来源可溶性有机物(DOM)性质的影响,以生物质炭为研究对象,采用多种提取剂、提取方式提取生物质炭DOM,分析其碳含量及化学组成特征。结果表明:低温生物质炭中碱提取物DOC含量较高(15.6~40.0 g/kg),而高温生物质炭中盐提取物较高(0.27~7.04 g/kg)。酸提取物DOM化学组成较为简单,表现为SUVA254、SUVA280值较低,且玉米秆生物质炭中酸提取物亲水性DOM比例(44.6%~73.6%)显著高于水和碱提取物(11.0%~53.2%、0.30%~31.4%)。碱提取物DOM化学组成较复杂,其SUVA254、SUVA280值较高,同时玉米秆生物质炭中碱提取物疏水性DOM比例(68.6%~99.7%)显著高于酸和盐提取物(26.4%~55.4%、0%~46.9%)。该研究揭示了提取剂在生物质炭DOM提取方法中的重要性,而提取方式对其性质影响不显著,可为生物质炭DOM提取方法的选择提供参考。
This study aims at investigating the impact of different extraction methods on the properties of dissolved organic matter (DOM) derived from biochar. Biochar was used as material, DOM was extracted with various extracting agents and extraction patterns, and the carbon content and chemical composition of the extracts were analyzed. The results showed that the DOC content of alkali extract in low-temperature biochar was relatively high (15.6-40.0 g/kg), so was the DOC content of salt extract in high-temperature biochar (0.27-7.04 g/kg). The chemical composition of DOM in the acid extract remained relatively simple, showing that SUVA254 and SUVA280 were low. A higher proportion of hydrophilic DOM was found in the acid extract from cornstalk-derived biochar (44.6%-73.6%) compared with that in the water and alkali extracts (11.0%-53.2% and 0.30%-31.4%), respectively (P<0.05). Correspondingly, the chemical composition of DOM in the alkali extract was relatively complex, showing that SUVA254 and SUVA280 were high. A higher proportion of hydrophobic DOM was found in the alkali extract from cornstalk-derived biochar (68.6%-99.7%) compared with that in the acid and salt extracts (26.4%-55.4% and 0%-46.9%), respectively (P<0.05). The study indicates that extracting agents have certain significance in biochar DOM extraction, while extraction patterns exhibit a minor effect on the properties of biochar DOM. It could provide reference for selecting biochar DOM extraction method.
生物质炭 / 可溶性有机物 / 提取方法 / 化学组成 / 土壤重金属污染修复 {{custom_keyword}} /
biochar / dissolved organic matter / extraction method / chemical composition / soil heavy metal contamination remediation {{custom_keyword}} /
表1 生物质炭基本性质 |
生物质炭类型 | 表面积/(m2/g) | 孔直径/nm | N/% | C/% | H/% | H/C | O/C |
---|---|---|---|---|---|---|---|
玉米秆-低温 | 3.33 | 1.36 | 2.75 | 53.7 | 3.70 | 0.07 | 0.74 |
玉米秆-高温 | 3.05 | 4.72 | 1.59 | 65.2 | 2.02 | 0.03 | 0.48 |
猪粪-低温 | 16.2 | 1.18 | 2.23 | 19.4 | 1.75 | 0.09 | 3.92 |
猪粪-高温 | 52.5 | 1.19 | 0.33 | 9.59 | 0.92 | 0.10 | 9.20 |
表2 不同提取剂及提取方法下生物质炭Hi-DOM和Ho-DOM组分比例 |
Hi-DOM组分/% | |||||
---|---|---|---|---|---|
生物质炭原料 | 编号 | 水 | 酸 | 碱 | 盐 |
玉米秆 | 1 | 53.2 | 73.6 | 31.4 | 46.6 |
2 | 25.4 | 44.6 | 0.3 | 82.4 | |
3 | 35.1 | 60.5 | 17.3 | 57.5 | |
4 | 11 | 63.2 | 20.2 | 100 | |
猪粪 | 1 | 57.1 | 53.4 | 80.8 | 67.2 |
2 | 90.6 | 62 | 93.8 | 100 | |
3 | 81.1 | 78.7 | 75.4 | 87.4 | |
4 | 100 | 81 | 100 | 89 | |
玉米秆 | 1 | 46.7 | 26.4 | 68.6 | 46.9 |
2 | 74.6 | 55.4 | 99.7 | 17.6 | |
3 | 64.9 | 38.7 | 82.7 | 42.5 | |
4 | 89 | 36.8 | 79.8 | 0 | |
猪粪 | 1 | 42.9 | 46.6 | 19.2 | 32.8 |
2 | 9.4 | 38 | 6.2 | 0 | |
3 | 18.9 | 21.3 | 24.6 | 12.6 | |
4 | 0 | 19 | 0 | 11 |
注:编号1~4分别代表提取方法+裂解温度分别为超声+低温、超声+高温、震荡+低温、震荡+高温生物质炭提取的DOM。每种原料制备的生物质炭对应组分(Hi或者Ho-DOM组分)中,不同提取剂处理分别采用配对t检验进行显著性检验,其差异显著性已在文中提及但表中未标出。 |
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Biochar, as a soil amendment, can increase concentrations of soil organic matter, especially water-extractable organic carbon (WEOC). This can affect the adsorption-desorption equilibrium between the dissolved solid phases in soil organic matter. Dissolved organic carbon (DOC) represents a small proportion of soil organic matter, but is of significant importance in the soil ecosystem due to its mobility and reactivity. Here, water extracts obtained from twelve non-herbaceous biochars (before, and after, chemical treatment with either H(3)PO(4) or KOH), were tested by Liquid Chromatography - Organic Carbon Detection (LC-OCD) to identify the effects of both pyrolysis conditions and chemical treatments on WEOC content. LC-OCD has the capacity to provide a fingerprint of WEOC, which allows analysis of the various fractions present. WEOC content was affected by both the pyrolysis temperature and the feedstock used. High mineral ash contents deriving from the feedstock can prompt thermochemical reactions of lignocelluloses to produce a relatively high WEOC content, which includes low molecular weight neutrals and humic acids as dominant components. A significant change in WEOC occurred during pyrolysis due to secondary reactions which resulted in a much lower WEOC in the high temperature biochars where fractions of low molecular weight acids and neutrals are dominant. Chemical treatments with H(3)PO(4) or KOH increased WEOC concentration, possibly by promoting hydrolysis reactions on biochar surfaces. These observations assist in assessing the contribution of biochar additions to the soil ecosystem and demonstrate the utility of LC-OCD in providing an understanding of how biochar additions to soil can alter DOC.Copyright © 2011 Elsevier Ltd. All rights reserved.
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Biochars derived from wetland biomass have been extensively applied in water and wastewater treatments. This study investigated the quantity and chemical quality of dissolved organic matter (DOM) released from the biochar prepared from the typical wetland plant (Typha orientalis) at different pyrolysis temperatures (300-700 °C) by using fluorescence excitation-emission (EEM) spectrophotometry with parallel factor analysis (PARAFAC) and UV-Visible spectroscopy. The results showed that the content of DOM released from biochars at low pyrolysis temperatures (300-500 °C) was higher than that observed at high pyrolysis temperatures (600-700 °C). The distribution of DOM components (mainly including three humic acid-like substances, one fulvic acid-like substance and one tyrosine-like substance) varied significantly due to the increase of pyrolysis temperatures. The fulvic acid-like material was the key DOM component at the low pyrolysis temperature while the humic acid-like material became dominant at the high temperature. DOM quality indices also indicated that the percentage of the low molecular-weight DOM increased with the decreasing DOC concentration due to the higher temperatures. The results obtained in this study would be beneficial to guide the rational application of biochars in waste treatments.Copyright © 2019 Elsevier Ltd. All rights reserved.
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The capacity of biochar to take up heavy metals from contaminated soil and water is influenced by the pyrolysis temperature. We have prepared three biochar samples from Jerusalem artichoke stalks (JAS) by pyrolysis at 300, 500 and 700 °C, denoted as JAS300, JAS500, and JAS700, respectively. A variety of synchrotron-based techniques were used to assess the effect of pyrolysis temperature on the molecular properties and copper (Cu) sorption capacity of the samples. The content of oxygen-containing functional groups in the biochar samples decreased, while that of aromatic structures and alkaline mineral components increased, with a rise in pyrolysis temperature. Scanning transmission X-ray microscopy indicated that sorbed Cu(II) was partially reduced to Cu(I), but this process was more evident with JAS300 and JAS700 than with JAS500. Carbon K-edge X-ray absorption near edge structure spectroscopy indicated that Cu(II) cations were sorbed to biochar via complexation and Cu-π bonding. With rising pyrolysis temperature, Cu(II)-complexation weakened while Cu-π bonding was enhanced. In addition, the relatively high ash content and pH of JAS500 and JAS700 facilitated Cu precipitation and the formation of langite on the surface of biochar. The results of this investigation will aid the conversion of halophyte waste to useable biochar for the effective remediation of Cu-contaminated soil and water.Copyright © 2019 Elsevier Ltd. All rights reserved.
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The dissolved organic matter (DOM) samples from biochars produced from Jerusalem artichoke stalks by pyrolysis at 300, 500, and 700 °C were characterized using a combination of spectroscopic techniques. Additionally, the binding affinities (long K) and the complexation capacities (C) of the DOM samples with Cu(II) were calculated to assess their Cu binding properties. The biochar-borne DOM contained mainly humic-like components (C1-C3) with a small amount of a protein-like component (C4). As the charring temperature increased, the concentrations of released DOM decreased. The low temperature biochar-borne DOM was found to have more carboxyl groups than its high temperature counterparts, and thus it had larger C values. In contrast, the high temperature biochar-borne DOM had larger long K values. Low temperature biochars, if applied in a large quantity, would alter copper mobility in the environment because of their high DOM contents and large copper binding capacities.
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