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首页> 外文期刊>European Journal of Soil Science >Reducing capacity of water extracts of biochars and their solubilization of soil Mn and Fe.
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Reducing capacity of water extracts of biochars and their solubilization of soil Mn and Fe.

机译:生物炭水提物的还原能力及其对土壤锰和铁的溶解作用。

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摘要

Biochar, being produced in an oxygen-restricted environment, is chemically more reduced than the original feedstock. Consequently, it was hypothesized that reduced biochar components could participate in redox-mediated reactions in the soil. This hypothesis was tested by measuring the reducing capacities of aqueous extracts of biochars and the reduction and solubilization of soil Mn and Fe oxides by the extracts. The reduction capacity of extracts from biochars produced from three feedstocks (eucalyptus wood, EUC; olive pomace, OP; and greenhouse waste, GHW) at different highest pyrolysis treatment temperatures (HTT; 350, 450, 600 and 800 degrees C) was less for the EUC feedstock than the others, and was greater for biochars produced at lower HTTs. The organic fraction of the extracts apparently was responsible for the major part of the reducing capacity. Extracts of smaller-HTT biochars, having greater dissolved organic carbon (DOC) contents, had greater reducing capacities than extracts of larger-HTT biochars from the same feedstock. Extracts of two GHW biochars (GHW-450 and GHW-600) solubilized Mn and Fe from soils at pH values below 8. The extract with the greater reducing capacity (GHW-450) solubilized both metals to a significantly greater extent. Smaller-HTT biochars produced from agricultural wastes, having a greater variety and concentration of soluble reducing agents, are expected to have more impact on soil redox reactions than larger-HTT biochars. By participating in chemical and biological redox-mediated reactions in the soil, biochar could influence microbial electron shuttling, nutrient cycling, pollutant degradation, contaminant mobilization and abiotic formation of humic structures.
机译:在氧气受限的环境中生产的生物碳在化学上比原始原料还原得更多。因此,据推测,减少的生物炭成分可以参与土壤中氧化还原介导的反应。通过测量生物炭水提取物的还原能力以及提取物对土壤锰和铁氧化物的还原和增溶作用来检验该假设。在三种不同的最高热解处理温度(HTT; 350、450、600和800摄氏度)下,由三种原料(桉木,EUC;橄榄渣,OP和温室废物,GHW)产生的生物炭提取物的还原能力较低。 EUC原料要比其他原料高,并且在较低HTT下产生的生物炭含量更高。提取物中的有机部分显然是还原能力的主要部分。与来自相同原料的较大HTT生物炭的提取物相比,具有更高的溶解有机碳(DOC)含量的较小HTT生物炭的提取物具有更大的还原能力。两种GHW生物炭(GHW-450和GHW-600)的提取物可在pH值低于8的情况下从土壤中溶解锰和铁。还原能力更大的提取物(GHW-450)在很大程度上溶解了两种金属。从农业废弃物中产生的较小的HTT生物炭,具有较大的可溶性还原剂种类和浓度,预计比较大的HTT生物炭对土壤氧化还原反应的影响更大。通过参与土壤中化学和生物氧化还原介导的反应,生物炭可影响微生物电子穿梭,养分循环,污染物降解,污染物迁移和腐殖质结构的非生物形成。

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