Importance of flue gas cooling conditions in particulate matter formation during biomass combustion under conditions pertinent to pulverized fuel applications

Laboratory-scale experiments pertinent to pulverised fuel (PF) combustion are often carried out in droptube furnaces (DTFs) at air-fuel equivalence ratios and cooling rate for quenching flue gas that are much higher than those in PF boilers. This paper reports the effect of flue gas cooling conditions on the properties of PM with aerodynamic diameter of < 10 mu m (PM10 ) from biomass combustion. This study considers four cooling rates (1000, 2000, 6000 and 20,000 degrees C/s) and two biomass feeding rates (0.05 and 0.25 g/min) that represents flue gases with significantly-different concentrations of inorganic vapours. The PSDs of PM10 have a bimodal distribution with a fine mode within PM with aerodynamic diameter of < 1 mu m (PM1 ) and a coarse mode within PM with aerodynamic diameter of 1 10 mu m (PM1-10 ). All experimental conditions produce PM10 with similar PM1 and PM (1-10) yields ( similar to 0.8 and similar to 1.6 mg/g_biomass, respectively) and similar coarse mode diameters (i.e. 6.863 mu m). However, at a biomass feeding rate of 0.05 g/min, the fine mode diameter shifts from 0.022 to 0.077 mu m when the cooling rate decreases from 20,000 to 1000 degrees C/s, indicating more profound heterogeneous condensation at a lower cooling rate. As the biomass feeding rate increases to 0.25 g/min, the fine mode diameter further shifts to 0.043 mu m and at 20,000 degrees C/s but remained at 0.077 mu m at 1000 degrees C/s though a clear shift of PSD to larger diameters is evident. These are attributed to enhanced heterogeneous condensation and coagulation of small particulates resulting from increased particle population density in hot flue gas. Chemical analyses show PM1 contains dominantly volatile elements (i.e. Na, K and Cl) while PM (1-10) consists of mainly Ca. Similar trends are also observed for elemental PSDs and yields. It is also observed that slow cooling of hot flue gas leads to an increased yield of Cl in PM (1-10) due to enhanced chlorination of Ca species. (c) 2020 The Combustion Institute. Published by Elsevier Inc. All rights reserved.

Automated summary

Laboratory-scale experiments on PF combustion are usually conducted in droptube furnaces, investigating the effect of flue gas cooling conditions on PM10 properties from biomass combustion. The study found that cooling rate and biomass feeding rate have significant impacts on particle size and composition, showing different trends in particle diameter and component distribution.