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Article

Characteristics of Smoldering on Moist Rice Husk for Silica Production

by
Shengtai Yan
1,
Dezheng Yin
1,
Fang He
1,*,
Junmeng Cai
2,
Thomas Schliermann
3 and
Frank Behrendt
1,4
1
School of Transportation and Vehicle Engineering, Shandong University of Technology, Zibo 255049, China
2
School of Agriculture and Biology, Shanghai Jiao Tong University, Shanghai 200240, China
3
DBFZ Deutsches Biomasseforschungszentrum Gemeinnützige GmbH, 04347 Leipzig, Germany
4
Institute of Energy Engineering, Technische Universität Berlin, 10623 Berlin, Germany
*
Author to whom correspondence should be addressed.
Sustainability 2022, 14(1), 317; https://doi.org/10.3390/su14010317
Submission received: 2 December 2021 / Revised: 19 December 2021 / Accepted: 24 December 2021 / Published: 29 December 2021
(This article belongs to the Special Issue Valorization of Residues from Energy Conversion of Biomass for Advanced and Sustainable Material Applications)
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Versions Notes

Abstract

:
In order to assess the possibility of silica production via smoldering of moist rice husk, experiments of washed (moist) rice husk (7 kg with moisture content of 51%) in a newly designed smoldering apparatus was performed. The temperature inside the fuel bed during smoldering was recorded, and characteristics of ash were analyzed. Results showed that the highest temperature in the middle of the naturally piled fuel bed was about 560.0 °C, lower than those in most of combustors. Some volatiles from the lower part of the fuel bed adhere to its upper ash during piled smoldering. Silica content and specific surface area of ash from smoldering of washed (moist) rice husk were 86.4% and 84.9 m2/g, respectively. Compared to our experiments, they are close to smoldering of unwashed rice husk (89.0%, 67.7 m2/g); different from muffle furnace burning (600 °C, 2 h) of washed (93.4%, 164.9 m2/g) and un-washed (90.2%, 45.7 m2/g) rice husk. The specific surface area is higher than those from most industrial methods (from 11.4 to 39.3 m2/g). After some improvements, the smoldering process has great potential in mass product of high quality silica directly from moist rice husk.

1. Introduction

Smoldering is slow, low-temperature, and flameless burning of porous fuels, which is an important and complex phenomenon [1,2]. The application of it in the field of waste-to-energy conversion such as sludge treatment [3], recovery of resources from waste streams [4], and biomass energy conversion [5] has attracted lots of attention in recent years. The main advantages are its low temperature of the solid phase [6] and self-sustainability in a fuel bed with high moisture content (75–80 wt.%) [7]. From an environmental point of view, these characteristics avoid the ash-related slagging/corrosion [8], making nutrients recovery easy via recycling of ash directly to farms [9] and reducing the pollution of solid waste. As to energy consumption, it makes the complete burning of moist solid waste possible [10], reducing the energy consumption for drying fuel.
Rice husk is a typical biomass waste [11], accounting for 14–25% of the grain’s overall mass [12]. In 2021, approximately 150 million tons of rice husk were produced around the world, with China contributing approximately 40 million tons. Nowadays most rice husk is directly buried or open burned [13] due to its low nutritive value for humans compared with rice grain and rice bran [14]. Direct burying results in soil pollution, because of its slow decomposition owing to its hard surface resulting from its high silicon and high lignin content [15]. Open burning leads to air pollution because of the release of fine dust and incomplete combustion gases of CO, NOx, CH4, poly-cyclic hydrocarbons (PAH) and soot [16].
There is great potential in producing silica from rice husk due to its high content of amorphous silica (around 18–23% [17]) and ash (around 85–95% [18]). Silica is an important inorganic material and is widely used in various fields such as fertilizer, insulator, adsorbent and catalyst [19]. It is characterized by high mechanical strength, good chemical stability, high-temperature resistance, easy dispersion in solvents, etc [20,21]. With the widespread application of silica, a variety of methods have been adopted to produce it, such as precipitation, plasma synthesis, chemical vapor deposition, micro emulsion processing, combustion synthesis and hydrothermal technique [22,23]. At present, most popular mass producing methods are precipitation from alkaline silicates and hydrothermal treatment of sand with lye [24]. However, both methods are expensive, intensive energy input, and environmentally harmful due to the production of dust, nitrogen and sulfur oxides, etc in the process of obtaining silica [25,26].
Producing silica from thermochemical conversion of rice husk has received considerable attention due to its economic and environmental advantages [27]. As to lab-scale production, Dizaji et al. [28] prepared silica by burning raw rice husk and pretreated rice husk (water washing at 50 °C for 2 h) in a muffle furnace at 600 °C for 4 h. The specific surface area was around 45.0 and 240.0 m2/g, respectively. Abu Bakar et al. [29] prepared silica by burning rice husk (unleached/acid-leached) in a muffle furnace (600 °C for 2 h). The purity of silica from unleached and acid-leached rice husk was 95.8 and 99.6 wt.% (XRF results), respectively, and specific surface area was 116.0 and 218.0 m2/g, respectively. Almeida et al. [30] prepared a mixture of silica and carbon by pyrolysis of raw rice husk in a tubular furnace. The obtained silica was black, in a mixture of amorphous and crystalline, with purity of 81.6 wt.% and specific surface area of 114.0 m2/g. Schliermann et al. [31] obtained ashes produced from water washed (50 °C for 2 h) rice husk using ÖKOTHERM® furnaces. The ashes are post-treated with acid and then thermally treated at 650 °C using a muffle furnace. The specific surface area of silica is about 150–200 m2/g. As to industrial production, Fernandes et al. [32] investigated characteristics of ash from burning rice husk in a grate furnace, a fluidized bed, and a suspension/entrained combustor. The silica content in these three types of ash was 90.0, 96.7, 93.6 wt.%, and the specific surface area was 39.3, 11.4, 26.7 m2/g, respectively. The specific surface area of silica from mass production tends to be lower than that prepared in a laboratory, which may be related to none pretreatment of rice husk and the high burning temperature in industrial combustors. It is recorded that high combustion temperature results in the transformation of amorphous silica to crystalline material [33].
Pretreatment of rice husk is an effective way to increase the purity and specific surface area of silica and typical pretreatments for rice husk are acid-leaching and water-washing [29,34,35]. Moisture content of the treated rice husk is normally high. According to our pre-experiments, moisture content of rice husk is around 50% after washing. The moist rice husk is not suitable to be burned directly in a normal combustor (the moisture content in a fluidized bed combustor needs to be <35% [36], for a suspension burner <15% [37]). Smoldering might be a good choice for thermochemical conversion of moist rice husk directly to silica. Yet, to the best of our knowledge there are no experiments using smoldering in literature.
The objective of this study is to assess the possibility of silica production via smoldering of rice husk with high moisture content omitting a drying step before thermochemical conversion. A smoldering apparatus was designed and smoldering experiment of rice husk with high moisture content was performed. Temperature inside a fuel bed was recorded and characteristics of ash (silica content, specific surface area and mass loss characteristic) were analyzed.

2. Materials and Methods

2.1. Material

Rice husk was collected from rural southern China in 2021. Two types of rice husk (washed/unwashed) were chosen as raw material in the experiment. The washing process is the following: 3.5 kg of rice husk was put into a bucket (Ф42 cm diameter × 40 cm height), then the bucket was filled with tap water (mass ration of water to rice husk: 10:1). The mixture was stirred for 10 min at ambient temperature. After being immersed for 12 h, rice husk was taken out and leaked above a screen in air for 1 h. The proximate and ultimate analysis of washed and unwashed rice husk were performed three times and the results were shown in Table 1.

2.2. Experimental Set-Up

A batch smoldering apparatus consisting of three parts (a smoldering chamber, a gas burning chamber and a heat exchanger) was designed, as shown in Figure 1. The smoldering chamber is rectangular (inner size 60 × 30 × 30 cm) with an insulation layer (4 cm) outside of its inner wall. An air inlet (Ф5 cm) and a flue gas outlet (Ф5 cm) are on the left and the right wall, respectively. A hole (Ф30 cm) with door on the top wall is used for material feeding and ash removal. The gas burning chamber is a square cavity (30 × 30 × 30 cm) with an insulation layer (4 cm) outside of its inner wall. Its inlet (Ф5 cm) on the left wall is connected with the flue gas outlet of the smoldering chamber. A quartz glass tube inside the burner is used to introduce the incomplete combustion flue gas from the smoldering chamber to the bottom of the burner, then the gas is ignited using an igniter. The heat exchanger is a cylinder with a diameter of 30 and a height of 100 cm. The heat is transferred from high temperature flue gas through three tubes (diameter of 5 and a height of 40 cm) to the water outside them. Rice husk is smoldered in the smoldering chamber, smoke is burned out in the gas burning chamber, and flue gas is discharged into the air after cooled in the heat exchanger.

2.3. Ash Preparation and Treatment

2.3.1. Ash Preparation from Rice Husk

For comparison, four types of ash―from washed/unwashed rice husk via smoldering and muffle furnace burning―were prepared. The washed and unwashed rice husk (3.5 kg of raw materials) were put naturally piled into the smoldering chamber. The height of the fuel beds was around 24 and 20 cm, and the bulk density were about 160 and 100 kg/m3, respectively. Then, it was ignited with a block of solid alcohol at the air inlet. Two thermocouples (Ф1 mm, KMTXL-040-G) were put into the bottom and middle (10 cm from the bottom) layer of the fuel bed to monitor the change of temperature inside the fuel bed, and data were recorded every 60 s. It was found that a thin layer of upper ash was black due to the low temperature and the other part of ash was homogeneous after extinguishing and cooling of the fuel bed. A vacuum cleaner was used to remove the black ash on the upper layer and 200 g rice husk ash was taken out from the center of the piled residue every time.
About 3 g of washed and unwashed rice husk were put into an ash tray (6 × 3 × 2 cm) respectively, heated in a muffle furnace from ambient temperature to 600 °C at 10 °C /min and holding for 2 h. Air entered the muffle furnace through a 2–3 cm gap between the furnace door and the wall. Then the ash was taken out and cooled to ambient temperature in a desiccator for later use.

2.3.2. Grinding and Drying of Ash

For homogeneity in the subsequent measurements, the four types of ash were separately crushed to powder with a particle size <120 mesh using an agate mortar. After that, these powders were dried in an oven at 105 °C for 24 h.

2.4. Thermal and Physical Characterization of Ash

Mass loss characteristic was analyzed using a simultaneous thermogravimetric analysis (TGA DSC1, Mettler TOLEDO). To avoid corrosion to the instrument, a pair of crucibles (inner: alumina 50 µL, outer: platinum 70 µL) were used in experiments. About 8 mg of ash was put into the inner crucible and heated from 50 to 950 °C at a heating rate of 10 °C /min. An air flow rate of 200 mL/min was used as reactive gas and 20 mL/min of N2 was used as protective gas. Each experiment was repeated three times to check reproducibility.
The contents of silica and other elements in ash were triplicate and measured by Wavelength Dispersive X-Ray Fluorescence Spectrometer (ZXS100e, Rigaku Corporation) at room temperature. It should be noted that contents are only reliable for elements with atomic weight ≥23 [38]. Because of the data overflow of the results of carbon and boron, the results of them were deleted before calculation of the oxides’ content.
Specific surface area was evaluated according to the Brunnauer, Emmett and Teller (BET) method and based on the nitrogen adsorption of the material at 77K. It was determined in the pressure range of p/p0 = 0.05–0.3 [28], where p is the system pressure, and p0 is the initial pressure (1 bar in this experiment). The measurement was conducted in a surface area analyzer (ASAP 2460, Micromeritics).

3. Results and Discussion

3.1. Characteristics of Smoldering Process

3.1.1. Temperature inside Fuel Bed

Temperature inside the washed (moist) and unwashed fuel bed is shown in Figure 2. The temperature history at one spot of the batch fuel bed can be divided into two stages―drying and oxidation. At the drying stage, the temperature first increases and then stabilizes at a temperature of about 60 °C. This is similar to the temperature of smoldering pine bark particle [39] and sewage sludge [4], which is different from the temperature (around 100 °C) of smoldering corn stalk powder [40] and corn flour [6]. Supplement experiments show this temperature is always around 60 °C in natural piled rice husk. In our experiments of smoldering branches, there is even no obvious plat temperature at the preheating period, which is similar to smoldering of unwashed rice husk. It implies temperature in the fuel bed at drying stage might be related to the porosity inside the fuel bed, materials, particle size, air flow, etc. The detailed analysis of this will be left for future work. At the oxidation stage, the temperature first increases rapidly and then increases at a stable rate. It drops quickly at the end stage of oxidation. For both cases the highest temperatures are around 560.0 °C, being much lower than those in most combustors (>700 °C) [41,42]. The low temperature is favorable to maintain the amorphous state of the silica [43].
Comparing the temperature development of the washed (moist) fuel bed with the unwashed fuel bed, the former has a longer duration of drying stage. The lower the part of the zone in the fuel bed, the longer the drying stage lasts. At oxidation stage, the duration of temperature > 400 °C of the moist fuel bed is shorter than for the unwashed fuel bed. This happens due to more heat generated in the process of smoldering is used to dry the moist rice husk and heat transfer rate to dry fuel is bigger than those for unwashed rice husk. The oxidation duration is also affected by bulk density of the fuel bed. In our supplementary experiments, smoldering of unwashed rice husk with bulk density of 170 kg/m3 was performed in a small apparatus. It was found that the maximum temperature becomes higher (around 600 °C) than for naturally piled rice husk. The bigger bulk density decreases the porosity inside the fuel bed, reducing thermal dispersions [39]. Besides, another possible reason is that the dwell time of gaseous species is extended resulting in longer duration.

3.1.2. Absorption of Volatiles by the Upper Ash

A one-dimensional simplified illustration on temperature field of the whole fuel bed after formation of a thin layer of ash at top surface is shown in Figure 3. It was drawn according to the history of temperature inside the fuel bed, our previous experiments [40] and the characteristic temperature profile in a forward smoldering system in the literature [4]. Due to the longer drying time of the moist fuel bed than an unwashed one shown in Figure 2, the former has a thinner layer of high temperature area (reaction zone) than the latter after a short time, as illustrated in the curve of Figure 3. The amount of the unreacted rice husk (without pyrolysis) is proportional to the marked area of the left side. During their devolatilization, part of the volatiles can be absorbed by the upper ash due to its low temperature. As a result, the ash of the moist fuel bed has a higher tendency to absorb volatiles from its lower part than the ash of fuel with less moisture.

3.2. Physical Properties and Mass Loss Characteristic of Rice Husk Ash

3.2.1. Physical Properties of Ash

Photos of ash before and after grinding from washed and unwashed smoldering as well as washed and unwashed burning are shown in Figure 4. These ashes are gray, soft, and almost retains the shape of rice husk itself. The whitest ash stems from washed burning, followed by unwashed burning. As for the other two ashes, the difference in the whiteness is negligible. The main reason is that temperature in smoldering (560 °C) is significantly lower than in muffle furnace (600 °C) and the duration of this temperature in smoldering is shorter. Other possible reasons are the removal of impurities like dust by washing or absorption of volatiles by the upper ash. The higher the whiteness, the higher silica content in ash [44]. It is worth mentioning that there are always some black particles in the ash. These might be the rice husk with incomplete combustion. Bridge forming in the fuel bed that makes the cooling of the related particle faster than the dense piled should be the reason.

3.2.2. Mass Loss Characteristic of Rice Husk Ash

Thermogravimetric (TG) and derivative thermogravimetric (DTG) curves of four types of ash (washed and unwashed smoldering, washed and unwashed burning) are shown in Figure 5. It is seen from TG data that total mass-loss of four ashes is <5%. The mass loss from 50 to 950 °C for the above four types of ash are 4.2 wt.%, 3.1 wt.%, 2.5 wt.%, and 2.3 wt.%, respectively. The lower the combustion temperature and oxidation duration, the higher total mass loss.
As shown in the DTG curves, there are three stages of mass loss: drying, oxidation, and combustion of residual carbon. Mass loss at each stage is shown in Table 2. At the drying stage (<200 °C), more water and longer drying time are there for burning ash than those for smoldering ash. This implies that the absorption of condensed materials stated in Section 3.1.2 decreases the capability of moisture absorption of ash. At the oxidation stage (200–700 °C), more mass is lost at lower temperatures for the two smoldering ashes than those for the burning ashes. For smoldering ashes, especially for smoldering of moist rice husk, mass loss occurs in the range 400–560 °C. In theory, the mass in this range is burned out during smoldering due to the maximum temperature inside the fuel bed is around 560 °C. The mass loss in this range indicates the oxidation of volatiles and carbon. At the stage of combustion of residual carbon (>700 °C), the mass loss of ash from smoldering is higher compared with burning ash due to more carbon in ash. The reason for the formation of residual carbon is that the melted silica obstructs the transport of oxygen to carbon [45]. At a higher temperature, the residual carbon can be burned out. Besides, the mass loss at this stage might also relate to the evaporation of KCl [38], the decomposition of carbonates [42].

3.3. Silica Content in Rice Husk Ash

3.3.1. Reproducibility and Reliability of XRF Measurement

Main compositions (>0.5%) from triplicate XRF measurements of ash produced by smoldering of washed rice husk are shown in Table 3. It is seen that the reproducibility is good (relative error < 10%). As to reliability, if there are elements with atomic weights <23, the absolute contents of element are not reliable as pointed in Section 2.4. For smoldering ash, residue carbon and absorbed volatiles affect this measured elemental content.

3.3.2. Content of Silica and Other Main Compositions in Rice Husk Ash

The contents of SiO2 and others main compositions in the four types of ash are listed in Table 4. The main component is SiO2 and the contents of it in all ashes is >85%. The SiO2 content in descending order is washed burning (93.4%), unwashed burning (90.2%), unwashed smoldering (89.0%), and washed smoldering (86.4%). Contents of other compositions in descending order of the content are K2O, CaO, SO3, P2O5, MgO, Cl, Fe2O3, Al2O3 in smoldering ash, and this order holds for most elements in other ashes.

3.3.3. Effect of Production Method on Silica Content

The purity of silica in ash is affected by three main factors: absorption of volatiles by upper ash, combustion temperature and pretreatment of rice husk. Volatiles adhering to the surface of upper-ash smoldering decreases the SiO2 content. Incomplete burn out of solid organics at low combustion temperature also decreases SiO2 content in ash. The pretreatment way of washing can remove some water soluble inorganics, such as K, Cl and dust [46,47]. The removal of water soluble inorganics can increase the silica content [35]. According to Table 4, the measured silica content in ash of washed smoldering is similar to or lower than that in unwashed smoldering, while the content of water-soluble ions (Ca, S, P, Mg, Cl, Fe, Al) is higher than that in unwashed smoldering. The lower silica content for washed smoldering is related to the shorter oxidation duration in the moist fuel bed, which results in incomplete combustion of rice husk. The higher content of water-soluble ions might relate to the inaccuracy of XRF measurement as mentioned in Section 3.3.1. The removing of carbon results in an increase of those water-soluble ions contents as a percentage of the whole ash.

3.4. BET Specific Surface Area

3.4.1. Specific Surface Area of the Four Types of Rice Husk Ash

The BET specific surface area of ash produced in this study (washed and unwashed smoldering, washed and unwashed burning) and in literature is shown from Figure 6. Two characteristics can be seen from this data of this study: (1) The specific surface area of ash prepared from washed rice husk is higher than that from unwashed rice husk; (2) for the ash of prepared from washed rice husk, the specific surface area is lower when smoldering is used compared with burning in the muffle furnace. However, the situation is opposite for the ash prepared from unwashed rice husk.

3.4.2. Factors of Specific Surface Area

It can be seen from the above characteristics that the specific surface area is affected by pretreatment conditions and combustion temperature. Pretreatment, such as washing, removes part of potassium. This decreases the formation of eutectic from interaction of K and Si. The decrease in amount of the eutectic partly avoids the transformation from amorphous silica to crystalline via melting in eutectic and condensing in cooling stage, and consequently increases the specific surface area [49]. Pretreatment of washing also removes soil particles which normally have lower specific surface area than amorphous silica.
As to temperature, low temperature avoids sintering/eutectic melting of the mixed components in ash of rice husk and is beneficial for silica to maintain its amorphous state and high specific surface area [50]. There is a combination effect of the two factors. It is very hard to get high-specific-surface-area ash from burning original rice husk at a high temperature (>700 °C).

3.4.3. Comparison of Specific Surface Area in This Study with Those of Silica Prepared Using Methods in Literature

The specific surface area of ash produced by smoldering of washed rice husk is 84.9 m2/g, which is lower than those prepared in the laboratory (99.2–293.9 m2/g) [13,29,51], but higher than those produced in the industry (11.4–39.3 m2/g) [32,52], as shown in Figure 6. In the laboratory, rice husk is normally washed or leached using water and acid to remove alkali and alkaline earth metals, such as the experiments performed by Dizaji [28] and Huang [48]. In the industry, no-pretreatment rice husk is burned directly in combustors. The high temperature (>700 ℃) of most combustor is not suitable to produce silica with high specific surface area.

3.5. Supplementary Experiment of Smoldering Air-Dried Rice Husk after Washing

To decrease the absorption of volatiles by upper ash, a supplementary smoldering experiment using air dried rice husk after washing was performed in the experimental set-up. It was found that the silica content is 93.5%, and specific surface area is 145.9 m2/g. Both the purity and specific surface are significantly higher than those (86.4%, 84.9 m2/g) from moist rice husk. It shows that drying before smoldering does increase both silica content and specific surface area.

4. Potential of Mass Product of Silica from Smoldering of Rice Husk

4.1. Measures to Increase Silica Content and Specific Surface Area

As mentioned before, the purity and specific surface area of silica produced from smoldering of rice husk are affected by pretreatment of the raw material, the volatile absorption of ash in reactor, and the solid temperature and dwell time in the fuel bed. According to the above experience in smoldering, two measures are proposed here to improve silica properties. The first is to develop a lateral continuously smoldering involving a dry stage apparatus. The second is to supply a little amount of air to improve fuel bed temperature slightly.

4.1.1. Lateral Continuously Smoldering Involving a Dry Stage of Rice Husk

A continuously lateral propagation smoldering is proposed here as shown in Figure 7. The smoldering of rice husk can be divided into three stages using a grate: drying, pyrolysis and oxidation. Due to its lateral propagation, the volatiles generated in the pyrolysis stage are discharged into the gas burning chamber directly and burned out, which cannot adhere to the ash in oxidation stage. The heat generated by oxidation can be used for the drying of rice husk. The condensate water generated in the process of drying can be collected and used for the washing of rice husk.

4.1.2. The Supply of Air at the Oxidation Stage

To increase the combustion temperature, a small amount of air can be provided in the stage of oxidation. As mentioned before, temperature of 700 °C can increase the purity and specific surface area. The highest temperature of the current piled smoldering is around 600 °C, which can be increased by supplying a small amount of air.

4.2. Feasibility of Mass Product of Silica from Smoldering of Rice Husk

Although silica prepared in the laboratory from pretreated rice husk has a high silica content and high specific surface area, considerable energy is necessary for removal of the water from moist rice husk. Besides, a lot of waste acid and lye is produced during pretreatment and post-treatment, which is harmful to the environment. As to a traditional combustor, the high temperature of the solid during combustion is disadvantageous in maintaining a high specific surface area of silica. Besides, most combustors are not suitable for burning rice husk with high moisture content.
Smoldering is characterized by a low temperature in the fuel bed and is self-sustained with moist content. Our experiments show that the highest silica content and specific surface area of ash is from smoldering of air-dried-washed rice husk. It indicates that after some improvement of our experimental set-up, it has great potential in the mass production of high-quality silica directly from moist rice husk.

5. Conclusions

Smoldering experiments with moist rice husk were performed in a self-designed apparatus to check its possibility for silica production. Temperature inside the fuel bed and silica content/specific surface area/mass-loss-characteristics of ash were analyzed. The main conclusions are:
  • Smoldering is a novel method for producing silica from rice husk. In our experimental set-up with a smoldering chamber, a gas burning chamber and a heat exchanger, the smoldering was self-sustained for naturally-piled rice husk with moisture content of 51.0%. Incomplete-combustion smoldering gas can be burned out in a gas burning chamber, and the heat generated during smoldering can be used for heating.
  • The highest temperature inside the fuel bed is around 560 °C, which was lower than those in many combustors. In the piled smoldering process of rice husk, part of the volatiles will be absorbed by the upper ash, which can decrease the silica content and specific surface area of ash. It should be avoided in the future.
  • Specific surface area of ash prepared from washed (moist) rice husk by smoldering was lower than those prepared in the laboratory, but it is higher than those produced from most industrial methods. It was greatly improved by air drying of moist rice husk before smoldering.
  • In future, a lateral continuously smoldering scheme involving a drying stage and small amount of air supply can be used for silica production. Smoldering of rice husk shows great potential for the industrial production of high-quality silica.

Author Contributions

Conceptualization, F.H.; methodology, F.H. and J.C.; software, S.Y. and F.H.; investigation, T.S.; data curation, T.S.; writing—original draft preparation, T.S.; writing—review and editing, D.Y., F.H., J.C., T.S. and F.B.; supervision, F.H.; funding acquisition, F.H. and F.B. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by [National Natural Science Foundation of China] grant number [51676115] and [Sino-German Center for Research Promotion] grant number [M-0183].

Institutional Review Board Statement

Exclude this statement.

Informed Consent Statement

Not applicable.

Data Availability Statement

Data are available upon request.

Conflicts of Interest

The authors declare no conflict of interest.

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Figure 1. Photo and schematic of the smoldering apparatus.
Figure 1. Photo and schematic of the smoldering apparatus.
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Figure 2. History of temperature of middle and bottom layer of washed (a) and unwashed (b) fuel bed (red and green pentacles for the maximum temperatures of middle and bottom layers, respectively).
Figure 2. History of temperature of middle and bottom layer of washed (a) and unwashed (b) fuel bed (red and green pentacles for the maximum temperatures of middle and bottom layers, respectively).
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Figure 3. Schematic of spatial temperature distributions of washed (a) and unwashed (b) fuel bed.
Figure 3. Schematic of spatial temperature distributions of washed (a) and unwashed (b) fuel bed.
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Figure 4. Photos of four types of rice husk ash (circles show black particles in ash).
Figure 4. Photos of four types of rice husk ash (circles show black particles in ash).
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Figure 5. TG & DTG curves of four types of ash.
Figure 5. TG & DTG curves of four types of ash.
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Figure 6. Specific surface area of silica produced by different methods. ([32]: no-pretreatment rice husk burned in a fluidized bed combustor; [28]: washed rice husk (50 °C tap water for 2 h) burned in a muffle furnace (600 °C for 4 h); [48]: citric acid-leached rice husk (1 wt.% at 80 °C for 3 h) burned in a muffle furnace (700 °C for 2 h)).
Figure 6. Specific surface area of silica produced by different methods. ([32]: no-pretreatment rice husk burned in a fluidized bed combustor; [28]: washed rice husk (50 °C tap water for 2 h) burned in a muffle furnace (600 °C for 4 h); [48]: citric acid-leached rice husk (1 wt.% at 80 °C for 3 h) burned in a muffle furnace (700 °C for 2 h)).
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Figure 7. Schematic diagram of lateral continuously smoldering.
Figure 7. Schematic diagram of lateral continuously smoldering.
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Table
Table 1. Proximate and elemental analysis of the rice husk. Oxygen is calculated by difference (C + H + O + N + S + Ash = 100 wt.%, dry basis).
Table 1. Proximate and elemental analysis of the rice husk. Oxygen is calculated by difference (C + H + O + N + S + Ash = 100 wt.%, dry basis).
Proximate Analysis (Arrival Basis, wt.%)Elemental Analysis (Dry Basis, wt.%)
MoistureVolatileAshFixed CarbonCHONS
Washed51.0 ± 0.232.0 ± 1.59.3 ± 0.37.7 ± 0.840.2 ± 0.35.5 ± 0.135.0 ± 0.20.3 ± 0.1<0.1
Unwashed8.1 ± 0.159.0 ± 1.418.4 ± 0.114.5 ± 0.738.7 ± 0.35.4 ± 0.135.5 ± 0.20.2 ± 0.1<0.1
Table
Table 2. Mass loss of different stages (wt.%).
Table 2. Mass loss of different stages (wt.%).
DryingOxidationCombustion of Resdiual Carbon
Washed smoldering0.6 ± 0.12.4 ± 0.21.2 ± 0.1
Unwashed smoldering0.7 ± 0.11.4 ± 0.11.0 ± 0.1
Washed burning0.9 ± 0.11.3 ± 0.10.3 ± 0.1
Unwashed burning0.8 ± 0.21.3 ± 0.10.2 ± 0.1
Table
Table 3. Contents of main elements in ash from triplicate measurements (wt.%).
Table 3. Contents of main elements in ash from triplicate measurements (wt.%).
NO.SiO2K2OCaOSO3P2O5MgOClFe2O3Al2O3
186.64.162.611.251.151.080.780.730.72
286.44.202.701.261.231.140.810.710.70
386.24.202.761.261.221.150.900.700.69
Ave86.4 ± 0.204.19 ± 0.032.69 ± 0.081.26 ± 0.011.20 ± 0.051.12 ± 0.040.83 ± 0.070.71 ± 0.020.70 ± 0.02
Table
Table 4. Main compositions in 4 types of ash.
Table 4. Main compositions in 4 types of ash.
TypesSiO2K2OCaOSO3P2O5MgOClFe2O3Al2O3
Washed smoldering86.44.192.691.261.201.120.830.710.70
Unwashed smoldering89.04.461.340.751.170.910.750.490.41
Washed burning93.41.072.080.580.500.700.300.390.21
Unwashed burning90.24.121.220.820.940.830.610.360.19
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Yan, S.; Yin, D.; He, F.; Cai, J.; Schliermann, T.; Behrendt, F. Characteristics of Smoldering on Moist Rice Husk for Silica Production. Sustainability 2022, 14, 317. https://doi.org/10.3390/su14010317

AMA Style

Yan S, Yin D, He F, Cai J, Schliermann T, Behrendt F. Characteristics of Smoldering on Moist Rice Husk for Silica Production. Sustainability. 2022; 14(1):317. https://doi.org/10.3390/su14010317

Chicago/Turabian Style

Yan, Shengtai, Dezheng Yin, Fang He, Junmeng Cai, Thomas Schliermann, and Frank Behrendt. 2022. "Characteristics of Smoldering on Moist Rice Husk for Silica Production" Sustainability 14, no. 1: 317. https://doi.org/10.3390/su14010317

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