Potential of Soybean Straw in Ukraine and Solid Biofuel Production

Khomina, Veronika; Trach, Ivan; Semenyshyna, Iryna; Koberniuk, Olena; Mudryk, Krzysztof; Jewiarz, Marcin; Wróbel, Marek; Styks, Jakub

doi:10.1007/978-3-030-13888-2_15

Cited by 2 publications

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“…Products in the form of torrefied Miscanthus will also be able to serve the farmers who produce them, as biochar in the form of an additive (carrier of the carbon element) to organic fertilizer, suitable for agriculture and greenhouses, improving soil properties and increasing productivity. Pomades, fruit stones, kernel shells, and other residuals are also used, such as waste cooking oil [ 8 , 9 , 10 , 11 , 12 , 13 ]. Recently, so-called water biomass, such as hyacinths or algae, has also become popular [ 14 , 15 , 16 ].…”

Section: Introductionmentioning

confidence: 99%

Sustainable Drying and Torrefaction Processes of Miscanthus for Use as a Pelletized Solid Biofuel and Biocarbon-Carrier for Fertilizers

et al. 2021

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Miscanthus is resistant to dry, frosty winters in Poland and most European Union countries. Miscanthus gives higher yields compared to native species. Farmers can produce Miscanthus pellets after drying it for their own heating purposes. From the third year, the most efficient plant development begins, resulting in a yield of 25–30 tons of dry matter from an area of 1 hectare. Laboratory scale tests were carried out on the processes of drying, compacting, and torrefaction of this biomass type. The analysis of the drying process was conducted at three temperature levels of the drying agent (60, 100, and 140 °C). Compaction on a hydraulic press was carried out in the pressure range characteristic of a pressure agglomeration (130.8–457.8 MPa) at different moisture contents of the raw material (0.5% and 10%). The main interest in this part was to assess the influence of drying temperature, moisture content, and compaction pressure on the specific densities (DE) and the mechanical durability of the pellets (DU). In the next step, laboratory analyses of the torrefaction process were carried out, initially using the Thermogravimetric Analysis TGA and Differential Scaning Calorimeter DSC techniques (to assess activation energy (EA)), followed by a flow reactor operating at five temperature levels (225, 250, 275, 300, and 525 °C). A SEM analysis of Miscanthus after torrefaction processes at three different temperatures was performed. Both the parameters of biochar (proximate and ultimate analysis) and the quality of the torgas (volatile organic content (VOC)) were analyzed. The results show that both drying temperature and moisture level will affect the quality of the pellets. Analysis of the torrefaction process shows clearly that the optimum process temperature would be around 300–340 °C from a mass loss ratio and economical perspective.

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