Department of Radiochemistry and Environmental Chemistry, Institute of Chemical Sciences, Faculty of Chemistry, Maria Curie-Sklodowska University, 3 Maria Curie-Sklodowska Square, 20-031 Lublin, Poland.
Department of Agricultural Ecology, Faculty of Agrobioengineering, University of Life Sciences, 13 Akademicka Street, 20-950 Lublin, Poland.
Sci Total Environ. 2021 Oct 1;789:147458. doi: 10.1016/j.scitotenv.2021.147458. Epub 2021 May 1.
The aim of this study was to determine the effect of abiotic aging of biochars under controlled laboratory conditions on its physicochemical properties and in consequence on their stability. Biochars (BCs) produced at 500 and 700 °C from willow or sewage sludge were incubated at different temperatures (-20, 4, 20, 60, or 90 °C) for 6 and 12 months. Pristine (i.e. immediately after their production) and aged BCs were characterized using a range of complementary methods. As a result of simulated temperature aging, there was a change in all biochar properties studied, with the direction of these changes being determined by both the type of feedstock and biochar production temperature. At all temperatures, aging was the most intense during the first 6 months and led to oxidation of the biochars and removal of the most labile components from them. The intensity of these processes increased with increasing aging temperature. Incubation of the biochars for another 6 months did not have such a significant effect on the biochar properties as that observed during the first months of incubation, which is evidence that the biochars had reached stability. The sewage sludge-derived biochars with a higher mineral content than the willow-derived biochars were less stable. The low-temperature biochars (BC-500) with lower aromaticity were more prone to abiotic oxidation than the high-temperature biochars (BC-700) with higher aromaticity and structurally ordered C. Based on this study, it can be concluded that aging induced changes will be specific for each biochar, i.e. they will depend on both the type of feedstock and pyrolysis temperature. Nonetheless, all biochars will be oxidized to a smaller or greater extent, which will result in an increase in the number of surface oxygen functional groups, an increased degree of their hydrophilicity and polarity, and a decrease in pH.
本研究旨在确定在控制的实验室条件下生物炭的非生物老化对其物理化学性质的影响,进而对其稳定性产生影响。本研究使用柳树或污水污泥在 500 和 700°C 下制备生物炭,并在不同温度(-20、4、20、60 或 90°C)下孵育 6 和 12 个月。使用一系列互补方法对原始(即刚生产后)和老化的生物炭进行了表征。模拟温度老化后,所有研究的生物炭特性均发生变化,这些变化的方向取决于原料类型和生物炭生产温度。在所有温度下,老化在最初的 6 个月最为剧烈,导致生物炭氧化和最不稳定的成分从生物炭中去除。这些过程的强度随老化温度的升高而增加。将生物炭再孵育 6 个月对生物炭性质的影响不如在孵育的最初几个月观察到的那么显著,这表明生物炭已经达到了稳定状态。与柳树衍生的生物炭相比,矿物含量较高的污水污泥衍生的生物炭稳定性较差。芳香度较低的低温生物炭(BC-500)比芳香度较高且结构有序的 C 含量较高的高温生物炭(BC-700)更容易发生非生物氧化。基于这项研究,可以得出结论,老化引起的变化将是特定于每个生物炭的,即它们将取决于原料类型和热解温度。尽管如此,所有生物炭都将在不同程度上被氧化,这将导致表面氧官能团数量增加、亲水性和极性增加以及 pH 值降低。