Biomass Gasification and Applied Intelligent Retrieval in Modeling
Abstract
:1. Introduction
2. Gasification Process
2.1. Basic Steps of Gasification Process
- Drying: In this step, heat is provided to the feedstock up to a significant temperature to reduce the moisture content in the given feedstock. The higher moisture content requires high energy to make it dry, so a prior drying process is necessary as a pretreatment of the feedstock before the gasification process. Naturally dried biomass may be an ideal feedstock for the gasification process [19]. It is a sophisticated process that entails simultaneous heat and mass transportation, as well as physicochemical changes. Heat can be transferred by direct (convection), radiant (radiation), and indirect (conduction) processes to the feedstock for drying purposes.
- Pyrolysis: Pyrolysis is the rapid thermal degradation of the carbonaceous material under an inert environment at high temperatures. Pyrolysis is the process of heating raw biomass, where heat is provided to the feedstock in the absence of oxygen, to break it into volatile gases and charcoal [20]. Pyrolysis is the initial phase of gasification or combustion, in which the biomass material begins to decompose with heat and breaks down into a combination of solids, liquids, and gases. While some hydrocarbons such as H2, CH4, and light carbon vapor (CO and CO2) are released into gaseous forms, high temperature leads to the thermal cracking process and releases condensable compounds such as topping atmospheric residue in vapor form and solid material into the pyrolysis process, known as char material. Pyrolysis has an essential role in gasification because it can improve the syngas output and, especially, hydrogen production [21].
- Combustion: Combustion is a process known as the direct burning of biomass at high temperatures with a limited amount of oxygen in a controlled manner to generate oxidized carbonaceous feedstock. Generally, atmospheric oxygen is used as an oxidant for the combustion process [22]. During the combustion process, various gases are produced from the biomass material in the form of smoke. Combustion is the only net exothermic process in all the processes of gasification and generates heat for the other processes of drying, pyrolysis, and reduction either directly, or it can be recovered indirectly from combustion by heat exchange processes in a gasifier [23]. In the combustion process, the carbon content reacts with oxygen and starts to convert into volatile products such as carbon dioxide, carbon monoxide, and char particles. The combustion process releases a large amount of heat and energy that can be used for subsequent gasification reactions, such as
- IV.
- Reduction: Reduction is a process to completely remove the oxygen from combusted hydrocarbons to restore them to a state where they may burn again. In reduction, heat is continuously provided to raw carbon to attract oxygen from water vapor and carbon dioxide, and it is redistributed into many single-bond sites. Now, no free oxygen can survive in its diatomic state because single-bond oxygen atoms are more attractive than the C bond. When all available oxygen is reallocated as single atoms, the reduction process is complete. In this process, oxygen atoms from CO2 will be reduced to make two CO molecules, whereas oxygen from H2O is also removed to produce H2 and CO. Both H2 and CO are combustible fuel gases that may be piped out to perform desired tasks elsewhere [24]. After the overall process, a cleaning process is required to provide efficient fuel. The cleaning of produced gas is also an important step in providing highly efficient fuel, which is a complex method after the gasification process [25].
2.2. Parameters of Gasification Process
2.3. Role of Different Gasifying Agents in the Gasification Process
2.4. Effects of Catalysts on Gasification
2.5. Fuel Characteristics
3. Artificial Intelligence in Biomass Gasification
3.1. Artificial Neural Network (ANN)
3.2. Physics-Informed Neural Network
3.3. Multiple Linear Regression (MLR)
3.4. Support Vector Machine (SVM)
3.5. Decision Tree
3.6. Random Forest
3.7. Gradient Boosting Algorithm
4. Evaluation Methods
4.1. Mean Impact Value (MIV)
4.2. Pearson Correlation Coefficient
4.3. Shapley Additive Explanation (SHAP)
4.4. Regression Evaluation Methods
5. Application of Artificial Intelligence in Gasification Process
5.1. AI in Prediction and Performance Evaluation
- ANN and particle swarm optimization (PSO)-based hybrid models were built to predict the product yield, which reduced the deviation of CO concentration from 13.93 to 8.39% [57].
- The GBR model is more convincing than the ANN model in predicting syngas compositions with real experimental data [88].
- A hybrid AI approach is remarkably satisfied, with a 0.134% mean prediction error to predict the hydrogen concentration in a downdraft fixed-bed gasifier [89].
- A stochastic GB (SGB) decision tree framework is proposed in [90] for modeling and quantifying the degradation kinetics of biomass, which shows high performance with a 0.993 determination coefficient.
- An AI-based hybrid model for solid fuel classification in energy harvesting from agricultural residue is discussed in [91].
- An ANN model is used to estimate the performance efficiency of a gasification system by using the back-propagation method. The study predicts the chemical exergy, and there are very few studies available in the context of chemical exergy analysis [85].
- Five different machine learning models are applied with an optimized ensemble model for predicting lower heating value (LHV) and syngas yield [80].
- Moreover, another study shows that the Gaussian-type kernel with a least-squares SVM can provide the best monitoring for biochar prediction [92].
5.2. Design of Integrated Gasification Systems
5.3. In Gasification of Municipal Solid Waste
5.4. For Environment Protection and Performance Analysis
6. Future Research Directions
6.1. Uncertainty in Machine Learning
6.2. Data-Driven Approaches to Manage Uncertainty
6.3. Response Surface Methodology as ML Techniques
6.4. Hybrid Machine Learning Models
6.5. Automated Machine Learning
7. Conclusions
Author Contributions
Funding
Data Availability Statement
Conflicts of Interest
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Parameter | Observation | ||||
---|---|---|---|---|---|
Equivalence ratio ↑ | ↓ | ↓ | ↑ | ↓ | ↑ |
Moisture content ↑ | ↓ | ↑ | ↑ | ↑ | ↓ |
Temperature ↑ | ↑ | ↑ | ↓ | - | - |
Steam-to-biomass ratio | ↓ | ↑ | ↑ | ↑ | ↓ |
Pressure ↑ | ↓ | ↑ | ↑ | ↑ | - |
CaO | ↓ | ↑ | ↓ | ↑ | - |
Dolomite | ↑ | ↑ | ↑ | - | - |
Air and oxygen | ↑ | ↑ | ↑ | ↓ | ↓ |
CO2 | ↑ | ↑ | ↑ | ↑ | ↓ |
Biomass type | Normally, a material with a higher (hemicellulose þ cellulose)/lignin ratio can provide a higher syngas yield. | ||||
Moisture content | 1. Moisture content 2. The higher moisture leads to a decrease in temperature. The optional moisture content is in the range of 10–20% for gasification, which can make bed temperatures more stable. However, updraft gasifiers can operate at 60% and downdraft at 25%, and plasma and supercritical reactors can operate at a high moisture content of biomass. | ||||
Ash content | Ash content should be lower than 2% for better results. | ||||
Particle size | 1. The small size of biomass increases the surface area and diffusion resistance, improving heat transfer and enhancing gasification. Generally, a particle size between 0.15 and 51 mm is recommended for gasification. 2. A particle size smaller than 0.15 mm is recommended for entrained-flow gasifiers, >6 mm for bubbling-bed reactors, and fixed-bed reactors can tolerate >51 mm 3. The effect of particle size is reduced with temperature. | ||||
Bed material | Bed material is inert and active. It is an energy transfer medium in gasification and can improve syngas quality and promote gas reforming and tar cracking. | ||||
Catalysts | 1. In the gasification process, the use of a catalyst can increase the surface area of the raw material and also increase the reaction rate of the process. 2. The catalyst in the gasification process is generally used to reduce the operating temperature and tar formation. | ||||
Steam-to-biomass (S/B) ratio | 1. The optimum S/B ratio varies in the range of 0.3–1.0 for gasification 2. The S/B capacity of gasifiers can be considered as follows: fixed-bed gasifiers > fluidized reactors > entrained-flow gasifiers. 3. A surplus of steam can decrease the gasification temperature and, as a result, lead to tar formation. | ||||
Gasifying agents | Gasification agents such as air, O2, steam, CO2, etc., can affect syngas quality, However, external heat is required during gasification. | ||||
Equivalence ratio | 1. The optimal equivalence ratio is between 0.2 and 0.3 for fixed-bed and fluidized-bed gasifiers, and entrained-flow gasifiers usually require a 20% equivalence ratio. 2. A high equivalence ratio can promote the tar cracking process. 3. The equivalence ratio can be affected by moisture and volatile contents. |
Statistical Methods | Mathematical Formulation |
---|---|
Actual error (AE) | |
Sum of squares error (SSE) | |
Standard deviation (SD) | |
Mean absolute error (MAE) | |
Mean standard error (MSE) | |
Relative absolute error (RAE) | |
Root mean square error (RMSE) | |
Normalized root mean squared error (NRMSE) | |
Average relative error (MeanRE) | |
Maximum relative error (MaxRE) | |
Mean absolute deviation (MAD) | |
Coefficient of determination ) | |
Adjusted coefficient of determination ) | |
Linear correlation coefficient ) | |
Regression correlation coefficient ) |
Work | Errors/Accuracy | Research Area | Refs. |
Linear regression and SVM applied in updraft gasifier | SVM classification | [75] | |
Automated sludge pyrolysis | RF, regression | [104] | |
Co-gasification of coal–biomass blend | Exergy = 34.19% | HHV prediction | [105] |
Environmental impact of palm kernel shell | Improved to 65.44 vol% | Steam gasification, Cao sorbent | [106] |
Experimental and AI-based study on catalytic reforming during pyrolysis | Structure modeling, pyrolysis | [107] | |
Emission control in reactors | Chemical looping | [108] | |
ML algorithms to determine heat capacity | R2 = 0.99347 | Oil reservoir | [109] |
Emission control in anaerobic digestion | Emission = 36.3% | H2 production | [100] |
GB-based electrochemical and thermal tri-generation process | Exergy efficiency = 34.6% | Multi-objective optimization | [110] |
Back-propagation (BP) neural network for microwave-assisted cracking | Efficiency = 95.7% | Catalytic pyrolysis | [111] |
Prediction of torrefaction severity index | Mean error = 0.9784 | Adaptive regression | [112] |
Economically feasible design of wind turbine integrated gasification process | Exergy increased by 7.3% | Thermodynamic analysis, | [113] |
100-year scaling of fluidized-bed and circulating fluidized-bed reactor. | fouling mitigation, clustering | [114] | |
Multi-objective optimization for flash cycling of SOFC system | Exegetic efficiency = 53.23% | Performance analysis | [115] |
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Meena, M.; Kumar, H.; Chaturvedi, N.D.; Kovalev, A.A.; Bolshev, V.; Kovalev, D.A.; Sarangi, P.K.; Chawade, A.; Rajput, M.S.; Vivekanand, V.; et al. Biomass Gasification and Applied Intelligent Retrieval in Modeling. Energies 2023, 16, 6524. https://doi.org/10.3390/en16186524
Meena M, Kumar H, Chaturvedi ND, Kovalev AA, Bolshev V, Kovalev DA, Sarangi PK, Chawade A, Rajput MS, Vivekanand V, et al. Biomass Gasification and Applied Intelligent Retrieval in Modeling. Energies. 2023; 16(18):6524. https://doi.org/10.3390/en16186524
Chicago/Turabian StyleMeena, Manish, Hrishikesh Kumar, Nitin Dutt Chaturvedi, Andrey A. Kovalev, Vadim Bolshev, Dmitriy A. Kovalev, Prakash Kumar Sarangi, Aakash Chawade, Manish Singh Rajput, Vivekanand Vivekanand, and et al. 2023. "Biomass Gasification and Applied Intelligent Retrieval in Modeling" Energies 16, no. 18: 6524. https://doi.org/10.3390/en16186524
APA StyleMeena, M., Kumar, H., Chaturvedi, N. D., Kovalev, A. A., Bolshev, V., Kovalev, D. A., Sarangi, P. K., Chawade, A., Rajput, M. S., Vivekanand, V., & Panchenko, V. (2023). Biomass Gasification and Applied Intelligent Retrieval in Modeling. Energies, 16(18), 6524. https://doi.org/10.3390/en16186524