6,063 research outputs found

    Two-stage Bayesian model to evaluate the effect of air pollution on chronic respiratory diseases using drug prescriptions

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    Exposure to high levels of air pollutant concentration is known to be associated with respiratory problems which can translate into higher morbidity and mortality rates. The link between air pollution and population health has mainly been assessed considering air quality and hospitalisation or mortality data. However, this approach limits the analysis to individuals characterised by severe conditions. In this paper we evaluate the link between air pollution and respiratory diseases using general practice drug prescriptions for chronic respiratory diseases, which allow to draw conclusions based on the general population. We propose a two-stage statistical approach: in the first stage we specify a space-time model to estimate the monthly NO2 concentration integrating several data sources characterised by different spatio-temporal resolution; in the second stage we link the concentration to the ฮฒ2-agonists prescribed monthly by general practices in England and we model the prescription rates through a small area approach

    Air Quality Prediction in Smart Cities Using Machine Learning Technologies Based on Sensor Data: A Review

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    The influence of machine learning technologies is rapidly increasing and penetrating almost in every field, and air pollution prediction is not being excluded from those fields. This paper covers the revision of the studies related to air pollution prediction using machine learning algorithms based on sensor data in the context of smart cities. Using the most popular databases and executing the corresponding filtration, the most relevant papers were selected. After thorough reviewing those papers, the main features were extracted, which served as a base to link and compare them to each other. As a result, we can conclude that: (1) instead of using simple machine learning techniques, currently, the authors apply advanced and sophisticated techniques, (2) China was the leading country in terms of a case study, (3) Particulate matter with diameter equal to 2.5 micrometers was the main prediction target, (4) in 41% of the publications the authors carried out the prediction for the next day, (5) 66% of the studies used data had an hourly rate, (6) 49% of the papers used open data and since 2016 it had a tendency to increase, and (7) for efficient air quality prediction it is important to consider the external factors such as weather conditions, spatial characteristics, and temporal features

    A rigorous statistical framework for spatio-temporal pollution prediction and estimation of its long-term impact on health

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    In the United Kingdom, air pollution is linked to around 40000 premature deaths each year, but estimating its health effects is challenging in a spatio-temporal study. The challenges include spatial misalignment between the pollution and disease data; uncertainty in the estimated pollution surface; and complex residual spatio-temporal autocorrelation in the disease data. This article develops a two-stage model that addresses these issues. The first stage is a spatio-temporal fusion model linking modeled and measured pollution data, while the second stage links these predictions to the disease data. The methodology is motivated by a new five-year study investigating the effects of multiple pollutants on respiratory hospitalizations in England between 2007 and 2011, using pollution and disease data relating to local and unitary authorities on a monthly time scale

    Realtime Profiling of Fine-Grained Air Quality Index Distribution using UAV Sensing

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    Given significant air pollution problems, air quality index (AQI) monitoring has recently received increasing attention. In this paper, we design a mobile AQI monitoring system boarded on unmanned-aerial-vehicles (UAVs), called ARMS, to efficiently build fine-grained AQI maps in realtime. Specifically, we first propose the Gaussian plume model on basis of the neural network (GPM-NN), to physically characterize the particle dispersion in the air. Based on GPM-NN, we propose a battery efficient and adaptive monitoring algorithm to monitor AQI at the selected locations and construct an accurate AQI map with the sensed data. The proposed adaptive monitoring algorithm is evaluated in two typical scenarios, a two-dimensional open space like a roadside park, and a three-dimensional space like a courtyard inside a building. Experimental results demonstrate that our system can provide higher prediction accuracy of AQI with GPM-NN than other existing models, while greatly reducing the power consumption with the adaptive monitoring algorithm

    Spatial modelling of air pollution for open smart cities

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    A thesis submitted in partial fulfillment of the requirements for the degree of Doctor in Information Management, specialization in Geographic Information SystemsHalf of the worldโ€™s population already lives in cities, and by 2050 two-thirds of the worldโ€™s population are expected to further move into urban areas. This urban growth leads to various environmental, social and economic challenges in cities, hampering the Quality of Life (QoL). Although recent trends in technologies equip us with various tools and techniques that can help in improving quality of life, air pollution remains the โ€˜biggest environmental health riskโ€™ for decades, impacting individualsโ€™ quality of life and well-being according to World Health Organisation (WHO). Many efforts have been made to measure air quality, but the sparse arrangement of monitoring stations and the lack of data currently make it challenging to develop systems that can capture within-city air pollution variations. To solve this, flexible methods that allow air quality monitoring using easily accessible data sources at the city level are desirable. The present thesis seeks to widen the current knowledge concerning detailed air quality monitoring by developing approaches that can help in tackling existing gaps in the literature. The thesis presents five contributions which address the issues mentioned above. The first contribution is the choice of a statistical method which can help in utilising existing open data and overcoming challenges imposed by the bigness of data for detailed air pollution monitoring. The second contribution concerns the development of optimisation method which helps in identifying optimal locations for robust air pollution modelling in cities. The third contribution of the thesis is also an optimisation method which helps in initiating systematic volunteered geographic information (VGI) campaigns for detailed air pollution monitoring by addressing sparsity and scarcity challenges of air pollution data in cities. The fourth contribution is a study proposing the involvement of housing companies as a stakeholder in the participatory framework for air pollution data collection, which helps in overcoming certain gaps existing in VGI-based approaches. Finally, the fifth contribution is an open-hardware system that aids in collecting vehicular traffic data using WiFi signal strength. The developed hardware can help in overcoming traffic data scarcity in cities, which limits detailed air pollution monitoring. All the contributions are illustrated through case studies in Muenster and Stuttgart. Overall, the thesis demonstrates the applicability of the developed approaches for enabling air pollution monitoring at the city-scale under the broader framework of the open smart city and for urban health research

    ๋จธ์‹ ๋Ÿฌ๋‹ ๋ชจ๋ธ์„ ์‚ฌ์šฉํ•œ 2002~2020๋…„ ํ•œ๊ตญ์˜ O3, NO2, CO ๋†๋„์˜ ๊ณ ํ•ด์ƒ๋„ ์ถ”์ •

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    ํ•™์œ„๋…ผ๋ฌธ(์„์‚ฌ) -- ์„œ์šธ๋Œ€ํ•™๊ต๋Œ€ํ•™์› : ๋ณด๊ฑด๋Œ€ํ•™์› ๋ณด๊ฑดํ•™๊ณผ, 2023. 2. ๊น€ํ˜ธ.Backrgound : Long-term exposure to ozone (O3), nitrogen dioxide (NO2), and carbon monoxide (CO) is known to cause various diseases and increase mortality. For that reason, estimating ground-level O3, NO2, and CO concentrations with a high spatial resolution is crucial for assessing the health effects associated with these air pollutants. However, related studies are limited in South Korea. This study aimed to develop machine learning-based models to predict the monthly O3 (average of daily 8-hour maximums), NO2, and CO at a spatial resolution of 1 km ร— 1 km across South Korea from 2002 to 2020. Methods : Approximately 80% of the monitoring stations were used to train the three machine learning models (random forest, light gradient boosting, and neural network) with a 10-fold cross-validation, and 20% of the monitoring stations were used to test the model performance. The author also applied ensemble models to integrate the variation in predictions among the models. Multiple predictors with satellite-based remote sensing data, inverse distance weighted ground-level air pollutants, land use variables, reanalysis datasets for meteorological variables, and regional socioeconmoic variables collected from various databases were included in the prediction model. Results : For O3, the overall R2 of the ensemble model was 0.841 during the entire study period. Urban areas showed a better model performance (R2 = 0.845) than rural areas (R2 = 0.762). For NO2, the highest overall R2 was 0.756, which best fit in autumn (R2 = 0.768). For CO, the overall R2 value was 0.506. This study provides high spatial resolution monthly average O3 and NO2 estimates with excellent performance (R2 > 0.75). Conclusion : The authors predictions can be used to analyze the spatial patterns in pollutants in relation to population characteristics and studies on the health effects of long-term exposure to air pollution using geocode-based health information and local health data.์—ฐ๊ตฌ๋ฐฐ๊ฒฝ : ์˜ค์กด(O3), ์ด์‚ฐํ™”์งˆ์†Œ(NO2), ์ผ์‚ฐํ™”ํƒ„์†Œ(CO)์— ์žฅ๊ธฐ๊ฐ„ ๋…ธ์ถœ๋˜๋ฉด ๊ฐ์ข… ์งˆ๋ณ‘์„ ์œ ๋ฐœํ•˜๊ณ  ์‚ฌ๋ง๋ฅ ์„ ๋†’์ด๋Š” ๊ฒƒ์œผ๋กœ ์•Œ๋ ค์ ธ ์žˆ๋‹ค. ๊ทธ๋ ‡๊ธฐ์—, ๊ณ ํ•ด์ƒ๋„๋กœ ์ง€ํ‘œ๋ฉด O3, NO2, CO ๋†๋„๋ฅผ ์ถ”์ •ํ•˜๋Š” ๊ฒƒ์€ ์ด๋Ÿฌํ•œ ๋Œ€๊ธฐ์˜ค์—ผ๋ฌผ์งˆ๊ณผ ๊ด€๋ จ๋œ ๊ฑด๊ฐ• ์˜ํ–ฅ์„ ํ‰๊ฐ€ํ•˜๋Š” ๋ฐ ๋งค์šฐ ์ค‘์š”ํ•˜๋‹ค. ํ•˜์ง€๋งŒ, ์žฅ๊ธฐ๊ฐ„์— ๊ฑธ์ณ ๊ณ ํ•ด์ƒ๋„๋กœ ๊ฐ€์Šค์ƒ ๋Œ€๊ธฐ์˜ค์—ผ๋ฌผ์งˆ(O3, NO2, CO)๋ฅผ ์ถ”์ •ํ•œ ์—ฐ๊ตฌ๋Š” ๊ตญ๋‚ด์—์„œ ์•„์ง ์ง„ํ–‰๋œ ๋ฐ”๊ฐ€ ์—†๋‹ค. ๋”ฐ๋ผ์„œ, ๋ณธ ์—ฐ๊ตฌ๋Š” 2002๋…„๋ถ€ํ„ฐ 2020๋…„๊นŒ์ง€ ๋Œ€ํ•œ๋ฏผ๊ตญ ์ „์—ญ์—์„œ 1km ร— 1km์˜ ๊ณต๊ฐ„ํ•ด์ƒ๋„๋กœ ์›”๋ณ„ O3(์ผํ‰๊ท  8์‹œ๊ฐ„ ์ตœ๋Œ€์น˜), NO2, CO๋ฅผ ๋จธ์‹ ๋Ÿฌ๋‹ ๊ธฐ๋ฐ˜ ๋ชจ๋ธ ๋ฐ ๊ทธ๋“ค์˜ ์•™์ƒ๋ธ” ๋ชจํ˜•์„ ํ†ตํ•ด ์˜ˆ์ธกํ•˜๊ณ ์ž ํ•œ๋‹ค. ์—ฐ๊ตฌ๋ฐฉ๋ฒ• : 3๊ฐ€์ง€ ๋จธ์‹ ๋Ÿฌ๋‹ ๋ชจ๋ธ(๋žœ๋ค ํฌ๋ ˆ์ŠคํŠธ, ๋ผ์ดํŠธ ๊ทธ๋ž˜๋””์–ธํŠธ ๋ถ€์ŠคํŒ…, ์‹ ๊ฒฝ๋ง)์˜ ์ตœ์ ์˜ ํŒŒ๋ผ๋ฏธํ„ฐ๋ฅผ ์ฐพ๊ธฐ ์œ„ํ•ด ๋ชจ๋‹ˆํ„ฐ๋ง ์Šคํ…Œ์ด์…˜์˜ ์•ฝ 80%๋ฅผ ํ›ˆ๋ จ ๋ฐ์ดํ„ฐ๋กœ ์‚ฌ์šฉํ•˜์˜€๊ณ , 10-fold ๊ต์ฐจ๊ฒ€์ฆ์„ ํ†ตํ•ด ํ›ˆ๋ จ ๋ฐ์ดํ„ฐ ๋‚ด์—์„œ ํ›ˆ๋ จ/ํ‰๊ฐ€ ๋‹จ๊ณ„๋ฅผ ๊ฑฐ์ณค์œผ๋ฉฐ, ๋‚˜๋จธ์ง€ ๋ชจ๋‹ˆํ„ฐ๋ง ์Šคํ…Œ์ด์…˜์˜ 20%๋ฅผ ๋ชจ๋ธ ํ‰๊ฐ€์— ์‚ฌ์šฉํ•˜์˜€๋‹ค. ์—ฌ๊ธฐ์— ์ถ”๊ฐ€๋กœ ๋จธ์‹ ๋Ÿฌ๋‹ ๋ชจ๋ธ ๊ฐ„์˜ ์˜ˆ์ธก ๋ณ€๋™์„ ํ†ตํ•ฉํ•˜๊ธฐ ์œ„ํ•ด ์•™์ƒ๋ธ” ๋ชจ๋ธ์„ ์ ์šฉํ–ˆ๋‹ค. ๋ฐ์ดํ„ฐ์—๋Š” ์œ„์„ฑ ๊ธฐ๋ฐ˜ ์›๊ฒฉ ๊ฐ์ง€ ๋ฐ์ดํ„ฐ, ์—ญ๊ฑฐ๋ฆฌ ๊ฐ€์ค‘์น˜ ๊ธฐ๋ฐ˜ ๋Œ€๊ธฐ์˜ค์—ผ๋†๋„, ํ† ์ง€ ์ด์šฉ ๋ณ€์ˆ˜, ๊ธฐ์ƒ ์žฌ๋ถ„์„ ์ž๋ฃŒ, ๋‹ค์–‘ํ•œ ๋ฐ์ดํ„ฐ๋ฒ ์ด์Šค์—์„œ ์ˆ˜์ง‘๋œ ์ง€์—ญ ์‚ฌํšŒ๊ฒฝ์ œ์  ๋ณ€์ˆ˜ ๋“ฑ์ด ํฌํ•จ๋˜์—ˆ๋‹ค. ์—ฐ๊ตฌ๊ฒฐ๊ณผ : O3์˜ ๊ฒฝ์šฐ, ์ „์ฒด ์—ฐ๊ตฌ ๊ธฐ๊ฐ„ ๋™์•ˆ ์•™์ƒ๋ธ” ๋ชจ๋ธ์˜ R2๊ฐ€ 0.841์„ ๊ธฐ๋กํ–ˆ์œผ๋ฉฐ, ๋„์‹œ ์ง€์—ญ์ด ๋†์ดŒ ์ง€์—ญ(R2 = 0.762)๋ณด๋‹ค ์šฐ์ˆ˜ํ•œ ์˜ˆ์ธก ์„ฑ๋Šฅ(R2 = 0.845)์„ ๋ณด์˜€๋‹ค. NO2์˜ ๊ฒฝ์šฐ, ์•™์ƒ๋ธ”(ํ‰๊ท ) ๋ชจ๋ธ์˜ R2๊ฐ€ 0.756์œผ๋กœ ๊ฐ€์žฅ ๋†’์•˜์œผ๋ฉฐ, ๊ณ„์ ˆ๋กœ ๋ณด๋ฉด ๊ฐ€์„์— ์˜ˆ์ธก ์„ฑ๋Šฅ์ด ๊ฐ€์žฅ ๋†’์•˜๋‹ค(R2 = 0.768). CO์˜ ๊ฒฝ์šฐ, R2๊ฐ€ 0.506 ์„ ๊ธฐ๋กํ–ˆ๋‹ค. ๋ณธ ์—ฐ๊ตฌ๋Š” O3 ๋ฐ NO2 ์—์„œ R2 > 0.75 ์œผ๋กœ ๋†’์€ ์˜ˆ์ธก๋ ฅ์˜ ๊ณ ํ•ด์ƒ๋„ ์›”ํ‰๊ท  ์ถ”์ •์น˜๋ฅผ ์ œ๊ณตํ•œ๋‹ค. ๊ฒฐ๋ก  : ๋ณธ ์—ฐ๊ตฌ์—์„œ ์–ป์–ด์ง„ ๋Œ€๊ธฐ์˜ค์—ผ ์ถ”์ • ๊ฒฐ๊ณผ๋Š” ์ธ๊ตฌ ํŠน์„ฑ๊ณผ ๊ด€๋ จ๋œ ๊ฐ€์Šค์ƒ ๋Œ€๊ธฐ์˜ค์—ผ๋ฌผ์งˆ์˜ ๊ณต๊ฐ„ ํŒจํ„ด์„ ๋ถ„์„ํ•˜๊ฑฐ๋‚˜, ์œ„์น˜ ๊ธฐ๋ฐ˜ ๊ฑด๊ฐ• ์ •๋ณด์™€ ํ–‰์ •๊ตฌ์—ญ ๋‹จ์œ„ ๊ฑด๊ฐ• ๋ฐ์ดํ„ฐ์™€ ์—ฎ์—ฌ์„œ ์žฅ๊ธฐ๊ฐ„ ๋Œ€๊ธฐ์˜ค์—ผ ๋…ธ์ถœ์˜ ๊ฑด๊ฐ• ์˜ํ–ฅ์„ ํ‰๊ฐ€ํ•˜๋Š” ์—ฐ๊ตฌ์— ์‚ฌ์šฉ๋  ์ˆ˜ ์žˆ์„ ๊ฒƒ์œผ๋กœ ๊ธฐ๋Œ€๋œ๋‹ค.Chapter 1. Introduction 1 Chapter 2. Materials and Methods 6 2.1. Study area 6 2.2. Air pollution monitoring data 6 2.3. Satellite-based remote sensing data 7 2.3.1. Meteorological data 7 2.3.2. Land-use data 10 2.3.3. Surface reflectance 11 2.4. Regional socioeconomic predictors 12 2.5. Modeling procedures 13 2.5.1. Data Preprocessing 14 2.5.2. Machine learning-based model 15 2.5.3. Ensemble Model 16 2.5.4. Model Prediction 17 Chapter 3. Results 19 Chapter 4. Discussion 29 Chapter 5. Conclusion 34 Supplementary materials 47 ๊ตญ๋ฌธ ์ดˆ๋ก 82 Tables Table 1. Model performance for O3, NO2, and CO overall and in three- and four-year periods 21 Table S1. Detailed information about data sources 61 Table S2. Variables sorted by % missing values 65 Table S3. Results of parameter grid search using 10-fold cross-validation for O3, NO2 and CO 68 Table S4. Yearly ensemble (GAM) performance for O3, NO2, and CO 70 Table S5. Model performances for O3, NO2, and CO by season and urbanity 71 Table S6. Number of monitoring stations by year for O3, NO2 and CO in urban and rural areas 73 Figures Fig. 1. Flowchart of the modeling process. GEE: Google Earth Engine, SEDAC: Socioeconomic Data and Applications Center, RSD: Regional Socioeconomic Database from Korean Disease Control and Prevention Agency 18 Fig. 2. Density scatter plot for monthly averages of the monitored and predicted concentrations of O3, NO2, and CO 26 Fig. 3. Maps of monitored and predicted O3, NO2 and CO during 2002~2020 27 Fig. 4. Percentage decrease in R2 when excluding grouped variables from each machine learning model of O3, NO2, and CO. The closer the color is to red, the greater the effect of the variables on the model performance 28 Fig. S1. Urban/Rural and Metropolitan (Metro) area for entire contiguous regions of South Korea 74 Fig. S2. Distribution maps of predicted O3 (ppb) by year and season for contiguous South Korea 75 Fig. S3. Distribution maps of predicted NO2 (ppb) by year and season for contiguous South Korea 76 Fig. S4. Distribution maps of predicted CO (ppm) by year and season for contiguous South Korea 77 Fig. S5. Monthly fluctuations in the number of monitoring stations for O3, NO2, and CO between 2002 and 2020 78 Fig. S6. Density scatter plot for monthly averages of the monitored and predicted concentrations of O3, NO2, and CO with seasonal discrimination 79์„
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