Supervised Machine Learning Approaches for Predicting Key Pollutants and for the Sustainable Enhancement of Urban Air Quality: A Systematic Review
Abstract
:1. Introduction
2. Related Works
2.1. Qualitative Approaches in the Air Quality Field
2.2. Air Quality Analysis and Forecasting
2.3. Machine Learning in Urban and Industrial Planning
2.4. Machine Learning in Climate Change Context
3. Method
3.1. Database Collection
3.2. Initial Selection
3.3. Preliminary Screening
3.4. Assessment and Retrieval
3.5. Synthesis and Presentation
4. Air Quality Monitoring with Supervised Learning
4.1. Air Quality Field
4.1.1. Air Quality Landscape
4.1.2. Pollutants and Air Quality Indices
- PMs, including PM1, PM2.5, and PM10, which refers to particles with a diameter less than 1 µm, 2.5 µm, and 10 µm, respectively, are linked to illnesses and fatalities. Reducing PM2.5 levels from 35 µg/m3 to 10 µg/m3 could potentially decrease air pollution-related deaths by 15% [43,45]. PM2.5 was the fifth-ranked mortality risk factor in the world and was responsible for 7.6% of all fatalities [46].
- Ozone (O3) is produced through photochemical reactions and plays a dual role in greenhouse gas emissions and its impact on human health and the environment. High concentrations of ground-level ozone can be particularly harmful. O3 exists as a gas both in the upper atmosphere (stratosphere) and at ground level. Stratospheric ozone is beneficial as it acts as a protective shield against ultraviolet rays. However, at the ground level and in the troposphere, ozone becomes a secondary air pollutant. It is formed through a series of intricate photochemical reactions involving solar radiation and ozone precursors [47].
- Nitrogen dioxide (NO2) and sulfur dioxide (SO2), produced from fuel burning [48], particularly in power plants and vehicles, are associated with respiratory issues and were responsible for 39% of NOx emissions in Europe’s road transportation industry in 2017 [49]. These gasses are the primary acidic gases released by human activities. they not only contribute to the creation of acid rain and photochemical smog but also have detrimental effects on human health, vegetation, and materials [50].
- Carbon dioxide (CO2), produced by burning fossil fuels, respiration, and natural processes, is a greenhouse gas contributing to global warming and pollution concentration, accounting for a significant percentage of emissions [35,51]. CO2, as one of the greenhouse gasses (GHGs), plays a significant role in the global warming issue intertwined with industrial development in the globalized world. According to the current literature, the adoption of low-carbon practices is considered the most effective strategy for mitigating global warming. The combustion of fossil fuels by human activities is the primary source of CO2 emissions, which greatly contributes to the creation of an environment conducive to global warming [52].
- Carbon monoxide (CO) is a hazardous gas emitted from various sources such as incineration, power plants, and urban road traffic. Inhalation of this gas can be fatal, as it converts to CO2 in the atmosphere. CO poisoning is a prevalent form of toxicity in the modern world and is the leading cause of poisoning-related deaths in the United States. It is a highly toxic gas that lacks taste, odor, and irritants. Detecting CO is challenging due to these properties and the absence of a distinctive clinical signature, often mimicking other common disorders. CO is produced when hydrocarbons undergo incomplete combustion. Sources of CO include poorly ventilated garages with motor vehicle exhaust, as well as areas near garages. Combustion appliances can also generate CO when there is partial combustion of fuels like oils, coal, wood, kerosene, and others. A common scenario involves infrequently used and poorly maintained heating units [53].
- Methane (CH4), mainly from natural gas and human activities like landfills and livestock, is another potent greenhouse gas. Methane contributes to the enhanced greenhouse effect. Methane production is a microbiological process, which is predominantly controlled by the absence of oxygen and the amount of easily [54]. CH4 plays a significant role in intensifying the greenhouse effect, as it is approximately 20 times more potent than CO2 on a molar basis. It is the second most influential greenhouse gas, following CO2, and its overall impact, considering both direct and indirect effects on tropospheric ozone and stratospheric water vapor, is equivalent to about half of CO2 [55].
- Volatile organic compounds (VOC), are considered significant contributors to air pollution, affecting the environment through both indirect and direct means. Indirectly, they act as precursors to the formation of ozone and smog. Directly, they pose toxicity risks to the environment. The rise of industrialization and urbanization has resulted in an increase in VOC emissions from various sources, both indoors and outdoors. These sources include the chemical industry, paper manufacturing, food processing, transportation, petroleum refineries, vehicle manufacturing, textiles, electronics, solvents, and cleaning products [56].
4.2. Supervised Learning Field
4.3. Supervised Learning Approaches for Air Quality Analysis
4.3.1. PM and Beyond: Exploring Pollutant Prediction in Air Quality Analysis
4.3.2. Regression Techniques for Air Pollution Prediction
4.3.3. Enhancing Air Quality Classification Methods
4.3.4. Deep Learning’s Role in Reliable Air Pollution Forecasting
4.3.5. Enhancing Air Pollution Forecasting with Hybrid Models
5. Challenges and Future Directions
5.1. Findings, Limitations, and Challenges in Air Quality Research
5.2. The Role of ML Models in Mitigating Climate Change and Air Pollution: A Sustainable Development
5.3. Future Directions and Open Perspectives in Urban Planning for Air Quality Research
6. Conclusions
Supplementary Materials
Author Contributions
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Acknowledgments
Conflicts of Interest
References
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Source | ML Method | Predicted Value | |
---|---|---|---|
01 | Ravindra et al. [86] | RF, K-NN, LASSO, Decision Tree(DT), SVR Xgboost, DNN | Hospital admissions related to Acute Respiratory Infections |
02 | Dutta and Pal [87] | stacked-bidirectional long short-term memory (stacked-BDLSTM) | PM2.5, PM10 |
03 | Van et al. [88] | DT, RF, XGBoost | AQI |
04 | Eren et al. [89] | LSTM, RNN, GRU | PM2.5 |
05 | Barthwal [90] | Markov chain (DTMC) models | AQI |
06 | Wang et al. [91] | EML | Ozone |
07 | Persis and Amar [92] | NNs, SVM, DT, RF, XGboost. | AQI |
08 | Koo et al. [93] | DNN, RNN, Convolutional Neural Network (CNN), | PM2.5 |
09 | Natsagdorj et al. [94] | Bayesian optimized LSTM, CNN-LSTM | PM2.5 |
10 | Falah et al. [95] | RF, XGboost | PM2.5 |
11 | Xie et al. [96] | Deep Learning-based Complex Trait Estimation Model(DL-CTEM) | NH3, CO2, H2S |
12 | Muthukumar et al. [97] | Convolutional Long Short-Term Memory (ConvLSTM), Graph Convolutional Network (GCN) | PM2.5 |
13 | Abu El-Magd et al. [98] | RF | PM10 |
14 | Huang et al. [99] | LR, RF, SVM, GPR, NN, ensemble tree | PM2.5, PM10 |
15 | Gilik et al. [100] | CNN, LSTM | PM, NOx, SO2 |
16 | Kumar and Pande [101] | Gaussian naive bayes (GNB), SVM XGBoost | AQI |
17 | Sethi and Mittal [102] | weighted naive bayes(WNB) | AQI |
18 | Abirami et al. [103] | SVR, Decision Tree Regression (DTR) RFR, MLR | AQI |
19 | Chen et al. [104] | DNN, LSTM | Ozone |
20 | Cheng et al. [105] | ResNet-LSTM | PM2.5 |
21 | Cho and Moon [106] | ANN | CO2, PM10, PM2.5 |
22 | Geetha et al. [107] | LSTM, RNN | SO2, CO2, NO2, CO, CFCs |
23 | Liu et al. [108] | SVM | AQI |
24 | Martín-Baos et al. [109] | LR, GPR, RF | AQI |
25 | Asha et al. [110] | Edited Nearest Neighbor (ENN) | NH3, CO, NO2, CH4, CO2, PM2.5 |
26 | Ferreira et al. [111] | fuzzy ARTMAP | PMs |
27 | Choudhury et al. [112] | KNN, SVR, Hidden Markov Model(HMM) CNN,LSTM | NO2, O3 |
28 | Qader et al. [113] | NNs, GPR | CO2 |
29 | Magazzino et al. [38] | NNs, DT | Deaths |
30 | Mokhtari et al. [81] | CNN, LSTM | Propylene |
31 | De Mattos Neto et al. [73] | ANN, MLP | PM10, PM2.5 |
32 | Wei et al. [114] | EMD-FUSION | SO2 |
33 | Cihan et al. [37] | ANFIS, SVR, CART, RF, KNN, ELM | PM10, PM2.5 |
34 | Taheri and Razban [67] | SVM, AdaBoost, RF, GBM, LR, MLP | CO2 |
35 | K et al. [115] | LR | PM2.5 |
36 | Cole et al. [39] | RF | PM2.5 |
37 | Shahriar et al. [74] | L-SVM, GPR, RFR | PM2.5 |
38 | Chang et al. [116] | Gradient Boosting Trees (GBT), SVR LSTM, LSTM2 | PM2.5 |
39 | Bozdag et al. [65] | LASSO, SVR, RF, kNN, xGBoost, ANN | PM10 |
40 | Chang et al. [117] | LSTM, SVR, GBT | PM2.5 |
41 | Magazzino et al. [118] | ANNs | Deaths |
42 | AlOmar et al. [84] | W-ANN | Ozone |
43 | Cazzolla Gatti et al. [40] | RF | Deaths |
44 | Han et al. [83] | LSTM | PM2.5 |
45 | Shams et al. [75] | MLR, ANN | CO |
46 | Zeinalnezhad et al. [119] | ANFIS | SO2, O3, NO2, CO |
47 | Alyousifi et al. [120] | Multi-Wave Fuzzy Time Series (MWFTS) | API |
48 | Lu et al. [121] | Density-Based Spatial Clustering of Applications with Noise (DBSCAN), DNN | PM2.5 |
49 | Tao et al. [82] | CBGRU | PM2.5 |
50 | Chen et al. [66] | 16 methods | NO2 |
51 | Araujo et al. [72] | ELM, MLR, Radial Basis Function(RBF) Echo State Network(ESN),ENN | Hospitalizations |
52 | Murillo-Escobar et al. [70] | SVR–PSO | NO, NO2, O3, PM10, PM2.5 |
53 | Zhou et al. [122] | GPM | NO2, HC |
54 | Yadav et al. [123] | CTSPD Algorithm | CO, Ozone, NO2, PM2.5, PM10 |
55 | Jiang et al. [85] | ICEEMDAN-BPNN-ICA | PM2.5, SO2, NO2, CO, O3 |
56 | Yuchi et al. [69] | MLR, RFR | PM2.5 |
57 | Son et al. [71] | LASSO | PM2.5, PM10, O3, NO2, CO, SO2 |
58 | Ketu et al. [76] | Adjusting Kernel Scaling (AKS)Adaboost, Multi-Layer Perceptron, GaussianNB, and SVM | AQI |
59 | Zhang, Lei, et al. [77] | hybrid SVM (HSVM)Euclidean distance to centroids (EDC), simplified fuzzy ARTMAP network (SFAM), multilayer perceptron neural network (MLP), individual FLDA, and single SVM | SO2, NO2, CO, CO2, NH3, O3, formaldehyde, benzene, toluene, inhalable particle, and VOCs |
60 | Singh et al. [78] | PCA, Single Decision Tree (SDT), Decision Tree Forest (DTF), Decision Tree Boost (DTB)SVM | AQI |
61 | Tella, Abdulwaheed, et al. [79] | Naïve Bayes, Random Forest, and K-Nearest Neighbor | PM10 |
62 | Velásquez et al. [80] | Reduced-Space Gaussian Process Regression | NO2, PM10 |
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Essamlali, I.; Nhaila, H.; El Khaili, M. Supervised Machine Learning Approaches for Predicting Key Pollutants and for the Sustainable Enhancement of Urban Air Quality: A Systematic Review. Sustainability 2024, 16, 976. https://doi.org/10.3390/su16030976
Essamlali I, Nhaila H, El Khaili M. Supervised Machine Learning Approaches for Predicting Key Pollutants and for the Sustainable Enhancement of Urban Air Quality: A Systematic Review. Sustainability. 2024; 16(3):976. https://doi.org/10.3390/su16030976
Chicago/Turabian StyleEssamlali, Ismail, Hasna Nhaila, and Mohamed El Khaili. 2024. "Supervised Machine Learning Approaches for Predicting Key Pollutants and for the Sustainable Enhancement of Urban Air Quality: A Systematic Review" Sustainability 16, no. 3: 976. https://doi.org/10.3390/su16030976
APA StyleEssamlali, I., Nhaila, H., & El Khaili, M. (2024). Supervised Machine Learning Approaches for Predicting Key Pollutants and for the Sustainable Enhancement of Urban Air Quality: A Systematic Review. Sustainability, 16(3), 976. https://doi.org/10.3390/su16030976