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Air Pollution in Cities

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Abstract

Air quality in cities is the result of a complex interaction between natural and anthropogenic environmental conditions. Air pollution in cities is a serious environmental problem – especially in the developing countries. The air pollution path of the urban atmosphere consists of emission and transmission of air pollutants resulting in the ambient air pollution. Each part of the path is influenced by different factors. Emissions from motor traffic are a very important source group throughout the world. During transmission, air pollutants are dispersed, diluted and subjected to photochemical reactions. Ambient air pollution shows temporal and spatial variability. As an example of the temporal variability of urban air pollutants caused by motor traffic, typical average annual, weekly and diurnal cycles of NO, NO2, O3 and Ox are presented for an official urban air-quality station in Stuttgart, southern Germany. They are supplemented by weekly and diurnal cycles of selected percentile values of NO, NO2, and O3. Time series of these air pollutants give information on their trends. Results are discussed with regard to air pollution conditions in other cities. Possibilities for the assessment of air pollution in cities are shown. In addition, a qualitative overview of the air quality of the world's megacities is given.

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Preprint
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Article
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... Atmospheric aerosols negatively affect visibility (Watson, 2002), human health (Pope et al., 2002;Laden et al., 2006;Beelen et al., 2014), and urban air quality (Fenger, 1999;Mayer, 1999) on local and regional scales. Aerosols also provide the largest uncertainties for global radiation balance and climate change (Lohmann and Feichter, 2005;Forster et al., 2007;Penner et al., 2011;Myhre et al., 2013). ...
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Source apportionment studies have struggled to quantitatively link secondary organic aerosols (SOAs) to their precursor sources due largely to instrument limitations. For example, aerosol mass spectrometer (AMS) provides quantitative measurements of the total SOA fraction but lacks the chemical resolution to resolve most SOA sources. In contrast, instruments based on soft ionisation techniques, such as extractive electrospray ionisation mass spectrometry (EESI, e.g. the EESI time-of-flight mass spectrometer, EESI-TOF), have demonstrated the resolution to identify specific SOA sources but provide only a semi-quantitative apportionment due to uncertainties in the dependence of instrument sensitivity on molecular identity. We address this challenge by presenting a method for positive matrix factorisation (PMF) analysis on a single dataset which includes measurements from both AMS and EESI-TOF instruments, denoted “combined PMF” (cPMF). Because each factor profile includes both AMS and EESI-TOF components, the cPMF analysis maintains the source resolution capability of the EESI-TOF while also providing quantitative factor mass concentrations. Therefore, the bulk EESI-TOF sensitivity to each factor can also be directly determined from the analysis. We present metrics for ensuring that both instruments are well represented in the solution, a method for optionally constraining the profiles of factors that are detectable by one or both instruments, and a protocol for uncertainty analysis. As a proof of concept, the cPMF analysis was applied to summer and winter measurements in Zurich, Switzerland. Factors related to biogenic and wood-burning-derived SOAs are quantified, as well as POA sources such as wood burning, cigarette smoke, cooking, and traffic. The retrieved EESI-TOF factor-dependent sensitivities are consistent with both laboratory measurements of SOA from model precursors and bulk sensitivity parameterisations based on ion chemical formulae. The cPMF analysis shows that, with the standalone EESI-TOF PMF, in which factor-dependent sensitivities are not accounted for, some factors are significantly under- or overestimated. For example, when factor-dependent sensitivities are not considered in the winter dataset, the SOA fraction is underestimated by ∼25 % due to the high EESI-TOF sensitivity to components of primary biomass burning such as levoglucosan. In the summer dataset, where both SOA and total OA are dominated by monoterpene oxidation products, the uncorrected EESI-TOF underestimates the fraction of daytime SOA relative to nighttime SOA (in which organonitrates and less oxygenated CxHyOz molecules are enhanced). Although applied here to an AMS and EESI-TOF pairing, cPMF is suitable for the general case of a multi-instrument dataset, thereby providing a framework for exploiting semi-quantitative, high-resolution instrumentation for quantitative source apportionment.
... Samples 3, 4, and 5 showed two fluorophores, in which both 3 and 5 showed identical fluorophores at Ex/Em = 270-290/340-355 nm (peak T) and Ex/Em = 225-245/330-370 nm (peak T uv ) ( Figure S2). Fluorophore peaks A and C indicate fulvic acid (humic substance) or hydrophilic DOM in the river water that might originate from industrial activities and sewage pollution (Mayer, 1999;Niloy et al., 2021a). On the other hand, peaks T and T uv indicate the presence of protein substances in urban industrial river water that might originate from anthropogenic sources (Haque et al., 2020;Niloy et al., 2022b). ...
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This study aims to identify continuous water quality changes and identify fluorescence properties from urban rivers to marine zones. Various types of natural and anthropogenic sources derived dissolved organic matter (DOM) have been identified in this study. These include soil‐derived DOM, plant remnants, and soluble particles produced when organic material partially decomposes and is released by microorganisms, such as bacteria, algae, and plants. DOM was characterized using a three‐dimensional excitation–emission matrix (3DEEM), parallel factor analysis (PARAFAC), and water quality parameters from the Buriganga River, Dhaka to Patenga Seaport, Chittagong, along with the Shitalakshya River, a small portion of the Padma River, and the Meghna River. To better understand the data analysis, the study area was divided into three central regions: urban industrial rivers, industrial estuarine rivers, and marine zones. In the urban industrial river, 3DEEM and PARAFAC identified five fluorophores (peaks: A, C, M, T, and T uv ) with five components: detergent‐like, fulvic‐like, tryptophan or protein‐like, fulvic‐like (C‐type), and protein‐like, which might originate from the industrial activities and sewage pollution. In the industrial estuarine river zone, three fluorophores have been identified (peaks: A, C, T uv ) with two known components, namely, fulvic acid (A‐type) and fulvic acid (C‐type), with an unknown photoproduct at Ex/Em = 295/368 (peak T uv ). Components in the industrial river zone may originate from terrestrial sources, indicating vegetation along the river. In the marine zone, four fluorophores have been identified (peaks: T uv , A, T, C) with two components, that is, protein‐ or tryptophan‐like and humic acid‐like from coral origin. The intensities of both fulvic‐like and protein‐like substances were high in urban industrial river water owing to industrial activity and sewage pollution. SUVA 254 suggests high aromaticity in all three regions, whereas the optical properties suggest that terrestrial and microbial components are present in the urban industrial and estuarine rivers. This further indicates that urban industrial river water quality is highly polluted. The lowest degradation potential index (DPI) in the marine zone might result from the presence of the highest number of dissolved solids in the water, and the highest DPI of industrial estuarine rivers explains the comparatively high presence of terrestrial‐derived humic (A)‐ and humic (C)‐like components in the ratio to the unknown photoproduct of mid‐wavelength. Practitioner Points This study's uniqueness is a 220‐km cruise from an urban river to a coastal seaport to analyze fluorescence properties. The study found that most water parameters were within the DoE standards, except for DO, which was consistently low. 3DEEM‐PARAFAC identified five fluorophores linked to detergent, fulvic, and protein‐like substances from sewage and industrial sources. Our study concludes that microbial and terrestrial sources dominate dissolved organic matter in urban, estuarine, and marine regions.
... In addition to its effects on human health, these pollutants can also be a serious hazard to monuments and artwork, particularly those located in city centers (Samet, 2000). PM, SO 2 , CO, O 3 , nitrogen oxides (NO X ), and volatile organic compounds (VOCs) are the major air pollutants in cities (Mayer 1999). Various factors influence air quality in big cities, including meteorological conditions, topography, urban morphology, and socioeconomic factors, (Liang, 2020). ...
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In urban settings, a significant issue revolves around poor air quality, characterized by elevated levels of particulate matter (PM) and diverse pollutants (CO and NO2) detrimental to both human health and the global environment. Consequently, there exists an immediate imperative to mitigate air pollution through the adoption of a spectrum of short and long-term strategies. This study examines different factors that influence air quality in Skopje, North Macedonia, focusing on the impact of meteorological parameters, the implementation of policy measures as waste burning ban, the impact of green infrastructure as well as the effects of measures against COVID-19 spread. To analyze the impact of these factors, the data analysis spans various periods: pre-COVID-19 lockdown restrictions (with emphasis on 2018), the lockdown period (2020), and subsequent years (2021 and 2022) as life gradually returns to normal. Additionally, it evaluates the effects of meteorological parameters such as wind speed, relative humidity, and temperature on air quality and their impact on particulate matter reduction, Furthermore, the paper establishes a significant correlation between the most common types of particulate matter, namely those with diameters of 10 µm or less (PM10) and 2.5 µm or less (PM2.5). Our statistical analyses unveil significant correlations between the collected data, confirming a negative correlation between PM and higher air temperatures/wind speed. Furthermore, the investigation highlights elevated pollutant concentrations during nighttime hours. Notably, the study identifies positive outcomes associated with reduced traffic and decreased use of fossil fuels for heating during winter months, as evidenced by the acquired data. Graphical abstract
... Many people move to cities to improve their quality of life in terms of infrastructure, jobs, education, and other factors (economic growth and social development) [1,3,4]. Urbanization, however, can also generate many issues, and among those issues are environmental (ecological) aspects, such as air quality degradation (air pollution) and increases in thermal discomfort, energy use, and greenhouse gas emissions [5][6][7]. ...
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Urban heat island (UHI) and thermal comfort conditions are among the impacts of urbanization, which have been extensively studied in most cities around the world. However, the comprehensive studies in Indonesia in the context of urbanization is still lacking. This study aimed to classify land use and land cover (LULC) and analyse urban growth and its effects on surface urban heat islands (SUHIs) and urban thermal conditions as well as contributing factors to SUHI intensity (SUHII) using remote sensing in the western part of Java Island and three focused urban areas: the Jakarta metropolitan area (JMA), the Bandung and Cimahi Municipalities (BC), and the Sukabumi Municipality (SKB). Landsat imagery from three years was used: 2000, 2009, and 2019. Three types of daytime SUHII were quantified, namely the SUHII of urban central area and two SUHIIs of urban sprawl area. In the last two decades, urban areas have grown by more than twice in JMA and SKB and nearly 1.5 times in BC. Along with the growth of the three cities, the SUHII in the urban central area has almost reached a magnitude of 6 °C in the last decade. Rates of land surface temperature change of the unchanged urban pixels have magnitudes of 0.25, 0.15, and 0.14 °C/year in JMA, SKB, and BC, respectively. The urban thermal field variance index (UTFVI) and discomfort index (DI) showed that the strongest SUHI effect was most prevalent in urban pixels and the regions were mostly in the very hot and hot categories. Anthropogenic heat flux and urban ratio have positive contributions to SUHII variation, while vegetation and water ratios are negative contributors to SUHII variation. For each city, the contributing factors have a unique magnitude that can be used to evaluate SUHII mitigation options.
... Various environmental monitoring sensors for air, (1) soil, (2) water, (3) and marine (4) pollutions are required to address diverse environmental issues. Since these different environmental factors are closely interrelated, comprehensive and systematic management measures are necessary. ...
... (H. Mayer 1999). ...
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In 2023, it was declared that the Bangladesh at the first place and then Pakistan, after which the most polluted country is India at the third place. Polluted air is becoming a very considerate issue all over the world. This study is all about comparing the air quality of two metro cities, Lucknow and Kanpur during (November 2022- October,2023) buy monitoring and assessment of few selective basic AQI air pollutants namely Particulate Matter (PM10) , Sulphur dioxide (SO2), Nitrogen dioxide (NO2) concentrations and also AQI of Lucknow and Kanpur at 5 representative locations categorized as residential, commercial and industrial areas. Residential area in Lucknow (Mahanagar and Aliganj) and in Kanpur (Kidwai Nagar and Shastri Nagar), Commercial areas in Lucknow (Hazarat Ganj and Ansal T.C.) and in Kanpur (Zareeb Chauki and Ramadevi), Industrial area Talkatora in Lucknow and Panki in Kanpur have been taken under consideration. The result found that 24 hours concentration of PM10 were in the range of 76.40 to 261.19 µg/m3 in Lucknow and 74.68 to 400.67 µg/m3 in Kanpur with an average of 174.34 and 160.36 µg/m3, respectively. The average value of PM10 was above as per the guideline of WHO and permissible limit prescribed by NAAQ in both the cities. Similarly, 24 hours average concentration of SO2 was below the prescribed level of NAAQ in Lucknow and Kanpur which was in the range of 5.33 to 12.70 µg/m3 in Lucknow and 2.00 to 9.53 µg/m3 in Kanpur with an average of 8.71 and 7.19 µg/m3, respectively. The 24 hours average concentration of Nitrogen dioxide (NO2) was below prescribed level of NAAQ in Lucknow and Kanpur. In Lucknow it was in the range of 13.83 to 48.01 µg/m3 and in Kanpur 21.45 to 64.02 µg/m3 with an average of 29.45 and 50.14 µg/m3, respectively. The 24 hours AQI was reported in the range of 76 to 211 in Lucknow and 75 to 363 in Kanpur with an average of 150.84 and 142.76 respectively which is greater moderate to severe by NAAQ and WHO guideline throughout the year. Ultimately, this entire study is related to human health because polluted air gives rise to various hazardous diseases such as asthma cancer, premature death cardiovascular diseases, respiratory tract diseases etc.
... Parameters such as wind speed and direction, temperature, or relative humidity can change the process of pollutant dispersion, deposition mechanisms, and the formation of atmospheric particles and thus influence the concentration of air pollutants in a region . Rapid urbanization and the existence of UHI has been observed in Accra, the capital city of Ghana , and are among the key driving force of poor air quality (Mayer, 1999) and are known to exacerbate the effects of air pollutants in urban areas . Again, the annual reported PM 2.5 mean concentration in Ghana in 2016 was 31.1 μg/m 3 which exceeded the recommended standard level of 10 μg/m 3 (World Health Organization, 2016). ...
... En las ciudades densamente pobladas, las emisiones de Material Particulado (PM por sus siglas en inglés) hacia la atmósfera se originan principalmente a causa del flujo vehicular (UNICEF, 2020). Mayer (1999) indica que los niveles de contaminación en el aire de las ciudades aumentan por la combinación entre el incremento de la población y los cambios del uso del suelo para aumentar áreas urbanas. Así también, Rojas (2007) sostiene que uno de los aspectos determinantes en la calidad de vida de un centro urbano, es la calidad de aire que los pobladores respiran y Pérez (2017) reafirma que la existencia de PM en el aire afecta directamente en la salud de los seres humanos, animales e incluso plantas. ...
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... So far haze-fog incidents are still an environmental issue of great concern in developing countries, continuing despite temporary abatement during the COVID-19 pandemic. Haze-fog not only commonly leads to extremely low visibility (Fu & Chen, 2017;Yang et al., 2015) but may also cause a series of disruptions in people's daily lives, public safety, human health, and ecosystems (Cao et al., 2012;Mayer, 1999;Sun & Zhou, 2017;Wang et al., 2015;Zheng, Pozzer, et al., 2015). Severe haze-fog events, characterized by lasting for a long time, high particle concentration, and extensive spatial coverage, have occurred frequently over the past few decades in China (Chen & Wang, 2015;Fu & Chen, 2017). ...
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An extreme haze‐fog event occurred during October 20–22, 2013, in Harbin, Northeast China, which lasted for nearly 60 h with local visibility as low as 20 m. However, causes of the extreme haze‐fog formation remain unclear. Through the analysis of in situ data and objective weather circulation classification, it is revealed that high pollutant emissions from biomass burning played a very important role in the extreme event. Stable weather conditions under the circulation type 8 (CT8), marked by weak high‐pressure control, strong inversion (6.55°C), shallow boundary layer depth (<300 m), and high relative humidity (>90%), aided in the accumulation of pollutants and hygroscopic aerosol growth. All of these factors collectively contributed to the extreme haze‐fog formation. The insights derived from this study can improve the predictability of extreme haze‐fog events, and indicate that pollution emissions should be tightly controlled in the adverse meteorological circulation type in Northeast China.
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Despite significant advances in knowledge about the spatial distribution of potentially toxic elements (PTEs), the accurate determination them in urban areas remains a challenge due to multiple sources. We investigated concentrations and spatial patterns for six PTEs, namely Pb, Cu, Ni, Zn, Cd and As in the top layer of urban and peri-urban soils. The study was conducted on the territory of the Ufa city (Russia), with a population of more than 1 million people and an area of more than 700 km². For these purposes, a total of 250 soil samples were collected at 0–20 cm depth. Random Forest algorithm, in combination with environmental and anthropogenic variables, was applied for the spatial prediction of PTEs. The covariates were represented by distance from river, topographic attributes, remote sensing data, geology and soil properties, distance from highways and railroads, their density, distance from combined heat and power, and refineries. Results showed that Pb, Cu, Ni, Zn, Cd and As contents ranged from 1 to 98.1 mg/kg, 1.5 to 360 mg/kg, 1.7 to 110 mg/kg, 1 to 336 mg/kg, 0.2 to 1 mg/kg, and 0.1 to 7.4 mg/kg, respectively. The average values of elements did not exceed the maximum and approximate permissible concentrations (MPC, APC). Terrain and anthropogenic-related covariates were estimated as the most important predictors. The generated maps revealed geographic trends and hotspot concentrations of Pb, Cu, Ni and Zn. Our findings and generated maps can provide useful information for future digital soil mapping of PTEs in urban areas.
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Air pollution in urban environments is a complex, multidimensional issue that significantly impacts public health and people’s well-being. Previous studies have tended to focus on general public awareness in metropolitan urban areas. The novelty of this study lies in examining whether perceptions regarding air pollution and the urban environment differ based on specific demographic characteristics such as age and dwelling place in a provincial city of Greece. Thus, a quantitative cross-sectional research approach was employed, resulting in the collection of 659 valid questionnaires from residents in the wider area of Volos city. To analyze the data, one-way ANOVA was applied to reveal differences in perceptions of air pollution and its effects on urban well-being. The results indicate that perceptions vary by age, particularly concerning the effects of air pollution on the natural environment. Participants acknowledge that air pollution levels differ across cities of various sizes and recognize the adverse effects of pollution on the overall well-being of urban areas. Furthermore, our analysis reveals significant differences in perceptions between urban and rural residents. Particularly, people living in the city tend to report higher awareness of air pollution levels compared to those in the countryside, highlighting the need for targeted interventions tailored to specific communities. Overall, this study underscores the importance of understanding demographic influences on perceptions of air quality, which can inform policymaking and public health initiatives aimed at improving air quality and mitigating health risks in urban settings.
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Purpose: The survey aims to identify current trends in the green marketing of the provincial Polish cities. The trend analysis will provide an understanding of how cities' authorities promote ecology, what activities and solutions are currently being implemented by them to promote cities from an environmental perspective. The purpose of the analysis is to examine whether the cities' ecological marketing contribute to reducing air pollution? Design/methodology/approach: The study will use content analysis, and trend analysis. Content analysis will identify elements of green marketing in ongoing projects of the provincial Polish cities. Trend analysis will answer the question of the relationship between green marketing and the level of city pollution. Findings: Considering that the EU Green Deal guidelines impose air pollution reduction targets on cities and countries, it can be hypothesized that cities should focus their activities on green marketing. It can be assumed that there is a positive (positive) relationship between the marketing activities implemented by the city and the decreasing level of air pollution. Originality/value: The article makes a significant contribution to the field of urban ecology and municipal marketing research. It combines two key issues: the marketing strategies used by cities to promote ecological activities and the analysis of PM10 air pollution trends. This two-pronged analysis allows for a comprehensive understanding of whether the marketing efforts undertaken have a real impact on improving air quality in Polish cities.
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Air pollution caused by motor vehicles is harmful to public health. Managing the cause of this type of pollution is very difficult. Effective prediction and management of pollution can be attained only by computing air pollution. It is difficult to measure emissions directly, so it is estimated using a variety of models developed worldwide. The current study made an attempt to integrate the emission model COPERT with the traffic assignment model in CUBE software for predicting the traffic-related emissions of pollutants SO2, NO2 & PM2.5 in mixed traffic conditions by considering passenger car and light duty vehicles (LDVS), two-wheeler, auto and bus. The study also aimed to include fuel variables and meteorological variable humidity along with fleet composition, average speed and average monthly temperature as inputs. This would enable us to control the rising vehicular emission, by assessing current and future air quality and thereby implementing policy decisions.
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Processing of data obtained using lidar technologies was carried out to identify the vertical variability of the distribution of aerosols in the atmospheric column by month. The results of 227 lidar measurements from 2014 to 2023 were processed in total. It has been established that the concentration and height of compacted aerosol layers begin to increase in spring time, reaches a maximum in July, and from October there is a visible decline in aerosol concentrations in the atmospheric air. It has been established that in the warm season the height of compacted aerosol layers reaches 1200–1800 m, while in the cold season it reaches only heights of 600–1100 m. It was concluded that fine aerosol predominates over the city, based on the calculated Angstrom parameter in the range from 1.95 to 2.91.
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Книга адресована як дослідникам, які професійно займаються проблемами охорони середовища і атмосфери, так і науковцям, зацікавлених парадигмою інтелектуальних обчислень, що є універсальними методами розв’язування широкого класу задач моделювання й аналізу великих множин даних
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Introduction: Assessing atmospheric changes is crucial as population density increases and countries industrialize to meet growing demands. Pakistan is listed among the countries with the most deteriorating air quality globally. Novelty Statement: This research investigates tropospheric NO₂ patterns in Pakistan from 2005 to 2022 using OMI data. It reveals seasonal variations and anthropogenic impacts, offering valuable insights for air quality policies in developing regions. Material and Methods: This study analyzed tropospheric nitrogen dioxide (NO₂) patterns using data from the Ozone Monitoring Instrument (OMI) and examined their relationship with meteorological parameters such as rainfall, wind speed, and temperature. The analysis focused on NO₂ pollution patterns at the district level in Pakistan from 2005 to 2022, including major urban centers like Lahore, Faisalabad, and Peshawar. Results and Discussion: An increasing trend in NO₂ concentrations was observed, with a rise of 9.028 x 10¹⁵molecules/cm²in winter. Summer values were lower, around 1.9 x 10¹⁵molecules/cm². A notable decrease in NO₂ concentrations occurred in the pre-monsoon months, except in Peshawar, where concentrations fell during spring. The study revealed varied patterns in NO₂ levels in relation to temperature, wind speed, and rainfall over the years. Industrial cities with heavy traffic, large populations, agricultural fires, and fossil fuel combustion exhibited high anthropogenic emission levels in the lower atmosphere. Conclusion: This study provides regulators with a deeper understanding of anthropogenic emission levels in major cities, helping to identify sources and develop effective air quality management strategies.
Chapter
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Chapter
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This study consists of three main sections. The first section delves into a performance analysis centered around modeling PM10, NOx, and CO emissions from a cement factory. It examines the effectiveness of various factors, including meteorological data, physics models, and air quality dispersion models, in producing accurate results for atmospheric simulations. The second section covers the dispersion direction and concentrations obtained by visualizing the dispersion maps. The third section covers an analysis of heavy metals emitted from the facility, taking into account potential risks in the region such as cancer, acute and chronic effects, and long-term respiratory risks. This study made use of meteorological models (WRF, AERMET, and CALMET), air quality dispersion models (AERMOD and CALPUFF), a health risk analysis model (HARP), and various sub-models (MMIF and CALWRF). Satellite meteorological data were obtained from NCEP and ERA, with the majority of meteorological data based on the Global Data Assimilation System (GDAS)/Final Operational Global Analysis (FNL) from Global Tropospheric Analyses and Forecast Grids used for the WRF model. In the daily results, AERMOD showed the highest concentration values, but CALPUFF had greater concentrations throughout the annual period. The winter season had the highest concentrations of pollutants. Although there are differences among the physics models used in this research, the conclusions produced are consistent. Analysis of the data from the HARP model suggested that cancer risk levels exceeded the threshold of one person per million. However, the proportion of exceedance instances is rather small in comparison to the receptor points.
Chapter
Formation of ozone in the boundary layer during photochemical pollution episodes gives rise to an ozone concentration ranging from 100 to, more than 400 ppb, with monthly averages showing a maximum in summer. The frequency of such episodes is controlled by meteorology and varies widely in place and time. There is, however, a general tendency for ozone concentrations to be lower in urban areas than in downwind rural areas, because in urban areas some ozone is removed by reaction with other pollutants, mostly nitric oxide. In polluted atmospheres these reactions constitute a major sink for ozone. Conversion rates of NOx range from about 1% per hour in winter to over 15% per hour during photochemical pollution episodes. Some NO2 is removed from the boundary layer by dry deposition, up to more than 50% of NO2 in Europe may be converted into peroxyacetyl nitrate (PAN), and the remainder into nitrates and some other peroxy nitrates. In the Netherlands PAN levels have been increasing by more than 10% annually over the last decade. Dry and wet deposition remove HNO3 and PAN. Some PAN decomposes into NO2 and peroxy radicals. This would suggest that the effect of anthropogenic NOx emissions are felt only on a regional scale, i.e. several hundreds of kilometres. However, the decomposition rate of PAN depends on temperature. At lower temperatures it is slow enough for PAN to be transported over very large distances away from its source. We argue that transport of PAN, and therefore of NOx plus anthropogenic carbon monoxide, methane and less reactive hydrocarbons are responsible for the observed ozone increase in the troposphere in the northern hemisphere, and for the observed PAN and ozone maximum in spring (May) in the northern background (free) troposphere and at remote sites away from man-made pollution sources.
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Exposure to elevated concentrations of ambient air pollutants causes adverse human health effects. Two modes or methods of study are generally relied on to quantify the relationships between pollutants and specific effects. These are: human clinical experiments and epidemiological (or community exposure) studies. (Animal toxicological studies can be used to indicate the existence of an effect, but not the rate of the effect in humans.) Each method has limitations as a basis for quantifying the level of adverse effects anticipated in a given human population as a result of exposure. Consequently, care must be taken in deciding which studies are appropriate for assessment of health impacts in a population. Some limitations are inherent in the method. Epidemiological studies, for example, depend on adequate community monitoring and the ability to associate a cohort with ambient data. Clinical studies often do not represent the complex mix of pollutants in the atmosphere. Consequently, construction of dose/exposure-response functions is challenging. Another common complication in quantifying expected health impacts of a pollutant mix is lack of adequate ambient monitoring data coupled with little or no knowledge of a population's time and activity profiles. This paper summarizes the difficulties inherent in constructing estimates of health effects in populationsliving in densely populated and polluted areas and suggests approaches to making initial limited estimates. An example of the level of effort required to conduct a sophisticated study, using relatively rich databases, is given based on work done in the Southern California region.
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The synoptic climatology of ozone (O3) for S Ontario has shown that, over the 1976–1981 period, average summer O3 concentrations follow a relationship similar to that reported for event analysis during periods of high O3 concentration. Highest average concentrations, 36 parts per billion (ppb), occur with ‘back of the high’ situations while lowest average concentrations (20 ppb) occur with ‘front of the high’ situations.With similar weather events in the winter, the pattern is reversed with highest average O3 concentrations on the ‘front of the high’ (19 ppb) and lowest average concentrations on the ‘back of the high’ (13 ppb). Concentration of O3 in the ‘front of the high’ sector is due in part to the intrusion of O3 in the vicinity of storms from the stratosphere. The seasonal variation of average concentrations in these situations is low, ranging from 14 to 26 ppb.The very low average concentration during the winter and fall for the ‘back of the high’ situation may be the result of scavenging by NOx from the urban/industrial areas around the Great Lakes. During the spring and summer, solar energy and warm temperatures cause the photochemical production of O3 from NOx and HCs precursors. In the fall and winter, photochemical production of O3 is either very low or absent, and the NOx consume O3 rather than produce it. Thus, average O3 concentrations for winter ‘back of the high’ situations are one-third of those in the summer months.The synoptic climatology of events during the months from May to September with maximum O3 concentrations in excess of 80 ppb indicates that 78 % of these events occur under synoptic weather classes generally indicative of back or centre of the high situations.
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Photochemical air pollution is still a serious environmental issue in Tokyo and Osaka areas. To clarify the past trend and present status of photochemical air pollution, the annual trends of daily maximum oxidant concentration covering Kanto (Tokyo and surrounding prefectures) and Kansai (Osaka and surrounding prefectures) areas were analyzed. Trends in the photochemical air pollution and NOx and VOC precursors showed identical characteristics both in Tokyo and Osaka areas. Trends in volatile organic hydrocarbons and NOx were analyzed; NOx is incresing and NMHC/NOx ratio is decreasing in the long term over both Kanto and Kansai areas, indicating an increase in ozone forming potential and a decrease in photochemical reactivity, which may be responsible for the air pollution patterns observed in the Tokyo and Osaka areas. The location of the daily maximum oxidant concentration has moved further from the emission areas.
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In the frame of the APSIS project simulations of the dispersion of air pollutants over the Attica Peninsula are carried out for May 25, 1990. This day is characterized by clear sky conditions and a general flow from Northwest. Such conditions support the development of a sea breeze around the Peninsula, which is especially pronounced in the basin of Athens and the neighbouring coastal zone. The flow and turbulence fields are simulated with the the non hydrostatic model KAMM (Adrian and Fiedler, 1991). Based on these fields the dispersion of the air pollutants are calculated with the DRAIS model (Nester and Fiedler, 1992). The simpler chemical mechanism RADM1 was selected because only measurements of NO, NO 2, SO 2,CO and O 3 are available, which are well predicted by the RADM1 mechanism.
Article
Hintergrund Benetzungsstörungen zählen zu den häufigsten Erkrankungen des äußeren Auges. Die symptomatische Therapie ist oftmals unzureichend, so dass die Patienten über subjektive Beschwerden und Beeinträchtigung ihrer Befindlichkeit klagen. Die Verträglichkeit des Substitutionsmittels spielt eine wichtige Rolle. Sie kann durch unkonservierte Präparate verbessert werden. Methode In eine offene, multizentrische Prüfung von acht Wochen Dauer wurden 59 Patienten mit den klinischen Symptomen des „trockenen Auges” unterschiedlicher Ätiologie aufgenommen, die unter Therapie mit handelsüblichen Tränenersatzmitteln keine ausreichende Besserung der Symptomatik erzielten. Sie wurden mit einem neuen unkonservierten Polyvidonhaltigen Tränensubstitutionsmittel, dessen Zusammensetzung dem Elektrolytgehalt der natürlichen Tränenflüssigkeit angepaßt war, behandelt. Der therapeutische Effekt wurde durch Auswertung von subjektivem Beschwerdebild. Tränenfilmaufreiß-zeit (BUT), Schirmer-I-Tesl, Visus, Biomikroskopie und ärztliche Beurteilung des Therapieerfolges bewertet. Ergebnisse Es konnte gezeigt werden, dass die symptomatische Therapie mit dem neuen Tränenersatzmittel (Oculotect® fluid sine) die wichtigsten Kriterien Befindlichkeit und BUT im Vergleich zur unbefriedigenden Vorbehandlung signifikant besserte (t-Test, verbundene Stichproben, zweiseitig, Signifikanzniveau p < 0,05). Alle weiteren Befunde bestätigten die Verbesserung ebenfalls. Schlußfolgerungen Bei einer für Augenarztpraxen typischen Patientengruppe mit Benetzungsstörungen und unzureichendem therapeutischen Effekt der Vorbehandlung ließen sich bei 4/5 der Patienten Befunde und Beschwerden durch Behandlung mit dem neuen unkonservierten Präparat deutlich bessern. Die Konservierungsmittelfreiheit trägt zur besseren Verträglichkeit der Tränensubstitution bei. Summary Background Diseases of the ocular surface very frequently seen are related to irregularities of wetting. Patients often have complaints and feeling of ill-health, although under symptomatic therapy. Tolerability of the tear substitutes plays a key role in these cases. It is improved with unpreserved medication. Method 59 patients with ,dry eye condition' of various etiology were enrolled in an open multicentre study and treated 8 weeks with a new preservative-free tear substitute. All patients had a history of previous ineffective treatment with artificial tears. The product was formulated with polyvidone and electrolytes in a composition which resembles natural tears. The therapeutic effect was evaluated by ratings of patients' self assessment of their complaints, tear film break up time (BUT), Schirmer I test, visual acuity, biomicroscopic examination and physicians' assessment. Results Based on the key criteria patients's self assessment and BUT, the new agent (Oculotect® fluid sine) improved symptoms and reduced discomfort significantly compared with the previous treatment (paired t test, two-sided, level of significance p < 0.05). The improved condition was confirmed by the other findings taken. Conclusion In 4/5 of patients, as typically met in ophthalmologists' offices, whose complaints were insufficiently relieved by previously applied tear substitutes, treatment with the new preservative-free product resulted in a distinct improvement of their condition. The lack of preservatives contributed to better tolerability and acceptance of tear substitution.
Book
This book is divided into the following chapters: the atmospheric boundary layer; atmospheric diffusion; pollutants and their properties; and environmental monitoring and impact.
Article
Los Alamos National Laboratory and Instituto Mexicano del Petróleo are completing a joint study of options for improving air quality in Mexico City. We have modified a three-dimensional, prognostic, higher-order turbulence model for atmospheric circulation (HOTMAC) and a Monte Carlo dispersion and transport model (RAPTAD) to treat domains that include an urbanized area. We used the meteorological model to drive models which describe the photochemistry and air transport and dispersion. The photochemistry modeling is described in a separate paper. We tested the model against routine measurements and those of a major field program. During the field program, measurements included: (1) lidar measurements of aerosol transport and dispersion, (2) aircraft measurements of winds, turbulence, and chemical species aloft, (3) aircraft measurements of skin temperatures, and (4) Tethersonde measurements of winds and ozone. We modified the meteorological model to include provisions for time-varying synoptic-scale winds, adjustments for local wind effects, and detailed surface-coverage descriptions. We developed a new method to define mixing-layer heights based on model outputs. The meteorology and dispersion models were able to provide reasonable representations of the measurements and to define the sources of some of the major uncertainties in the model-measurement comparisons.
Article
Observed ozone concentrations are valuable indicators of possible health and environmental impacts. However, they are also used to monitor changes and trends in the sources of ozone and of its precursors, and for this purpose the influence of meteorological variables is a confounding factor. This paper examines ozone concentrations and meteorology in the Chicago area. The data are described using least absolute deviations and local regression. The key relationships observed in these analyses are then used to construct a nonlinear regression model relating ozone to meteorology. The model can be used to estimate that part of the trend in ozone levels that cannot be accounted for by trends in meteorology, and to ‘adjust’ observed ozone concentrations for anomalous weather conditions.
Article
The high concentration of NO2 in the Tokyo Metropolitan area was investigated by means of air quality monitoring station data analysis and two numerical models: a photochemical box model and a photochemical grid model. Based on monitoring data, the typical variation with time of NO, NO2 and O3 for days with high NO2 concentrations is presented. The application of the photochemical box and photochemical grid models successfully reproduced these variations when using typical emission intensities for NOx and NMHC from the Tokyo downtown area. Model results revealed that the high concentrations of NO2 in winter (exceeding the Japan environmental quality standard) mainly result from photochemical oxidation of NO to NO2.
Article
The main objective of this paper is to present analytical models relating maximum pollutant concentrations in urban areas with meteorological and other variables. The analysis is based on measurements from Greater Athens Area and is restricted in only one pollutant of special interest, namely N02. The meteorological variables, used in analytical modeling for forecasting pollution concentrations, cover the most important atmospheric processes favoring pollution episodes. The selection of the variables was based both on extensive correlation analysis and on the existing knowledge from the scientific literature. The evaluation of the developed forecasting models showed that their degree of success is promising. The final model equations derived are simple and they can be used easily for operational forecasts from the air quality management authorities.
Article
Urban air pollution is a major environmental problem in the developing countries of the world. WHO and UNEP created an air pollution monitoring network as part of the Global Environment Monitoring System. This network now covers over 50 cities in 35 developing and developed countries throughout the world. The analyses of the data reported by the network over the past 15–20 yr indicate that the lessons of the prior experiences in the developed countries (U.S.A., U.K.) have not been learned. A study of air pollution in 20 of the 24 megacities of the world (over 10 million people by year 2000) shows that ambient air pollution concentrations are at levels where serious health effects are reported. The expected rise of population in the next century, mainly in the developing countries with a lack of capital for air pollution control, means that there is a great potential that conditions will worsen in many more cities that will reach megacity status. This paper maps the potential for air pollution that cities will experience in the future unless control strategies are developed and implemented during the next several decades.
Article
This article deals with the part of urban climatology which is of particular relevance to human beings. Presented first is a summary of all human biometerologically effective complexes, as well as other factors which are relevant to urban planning and which depend on atmospheric conditions in urban structures in a direct or indirect manner. Later, methods for human biometerologically significant assessment of thermal and air pollution components of the urban climate are discussed in detail, because these components can be strongly influenced by urban planning. The application of these methods is illustrated by some results of appropriate investigations in urban areas.
Ozone on an urban and regional scale } with special reference to the situation in the Netherlands Tropospheric Ozone
  • R Guicherit
Guicherit, R., 1988. Ozone on an urban and regional scale } with special reference to the situation in the Netherlands. In: Isaksen, I.S.A. (Ed.), Tropospheric Ozone. Reidel Publ.
Principles of Air Pollution Met-eorology Urban air pollution in megacities of the world Atmospheric Environment 30 Human-biometeorologische Probleme des Stadtklimas Air pollution caused by motor-tra$c in urban spaces Analyse der Ozonkonzentrationen an Sonn-und Werktagen
  • W Kuttler
  • T J Lyons
  • W D Scott
  • D Mage
  • G Ozolins
  • P Peterson
  • A Webster
  • R Orthofer
  • V Vandeveerd
  • M H Gwynne
  • J H Schmidt
  • J Schmidt
Kuttler, W., 1996. Aspekte der Angewandten Stadtklimatologie. Geowissenschaften 14, 221}228. Lyons, T.J., Scott, W.D., 1990. Principles of Air Pollution Met-eorology. Belhaven Press, London. Mage, D., Ozolins, G., Peterson, P., Webster, A., Orthofer, R., Vandeveerd, V., Gwynne, M., 1996. Urban air pollution in megacities of the world. Atmospheric Environment 30, 681}686. Mayer, H., 1993. Urban bioclimatology. Experientia 49, 957}963. Mayer, H., 1996. Human-biometeorologische Probleme des Stadtklimas. Geowissenschaften 14, 233}239. Mayer, H., Haustein, Ch., 1994. Air pollution caused by motor-tra$c in urban spaces. Meteorol. Zeitschrift, N.F. 3, 138}142. Mayer, H., Schmidt, J., 1993. Analyse der Ozonkonzentrationen an Sonn-und Werktagen. Res. Rep., Meteorol. Inst. Univ. Freiburg. Mayer, H., Schmidt, J., 1994a. Trendanalyse von Immissions-zeitreihen in Baden-Wu K rttemberg und Bayern. Meteorol. Zeitschrift, N.F. 3, 116}121. Mayer, H., Schmidt, J., 1994b. Methoden zur Regionalisierung der NO -Immissionsdaten. Res. Rep., Meteorol. Inst. Univ. Freiburg. Nester, K., 1995. In#uence of sea breeze #ows on air pollution over the Attica peninsula. Atmospheric Environment 29, 3655}3670.
Chemical Principles of Environ-mental Pollution Air quality in the Russian Federation Ac-counting for meteorological e!ects in measuring urban ozone levels and trends
  • B J Alloway
  • D C Ayres
  • P Royle
  • J A Steiberg
  • L J Yang
Alloway, B.J., Ayres, D.C., 1993. Chemical Principles of Environ-mental Pollution. Blackie Academic & Professional, London. Bezuglaya, E.Y., 1996. Air quality in the Russian Federation. WMO Bulletin 45, 132}135. Bloom"eld, P., Royle, J.A., Steiberg, L.J., Yang, Q., 1996. Ac-counting for meteorological e!ects in measuring urban ozone levels and trends. Atmospheric Environment 30, 3067}3077.
Overview of air pollution in European cities Umweltbun-desamt World Urabanization Prospects. The 1992 Revision City air quality trends } Analysis of the winter-time NO pollution in the Tokyo Metropolitan area
  • R Sluyter
Sluyter, R., 1996. Overview of air pollution in European cities. WMO Bulletin 45, 123}128. UBA, 1998. Umweltdaten Deutschland 1998. Umweltbun-desamt. Erich Schmidt Verlag, Berlin. UN, 1993. World Urabanization Prospects. The 1992 Revision. United Nations. UNEP/WHO, 1993. City air quality trends } Vol. 2. WHO PEP/93 26, UNE93 26P GEMS 93.A.2, Genf. Uno, I., Ohara, T., Wakamatsu, S., 1996. Analysis of the winter-time NO pollution in the Tokyo Metropolitan area. At-mospheric Environment 30, 703}713.
Aspekte der Angewandten Stadtklimatologie
  • Kuttler
Kuttler, W., 1996. Aspekte der Angewandten Stadtklimatologie. Geowissenschaften 14, 221}228.
Analyse der Ozonkonzentrationen an Sonn-und Werktagen
  • H Mayer
  • J Schmidt
Mayer, H., Schmidt, J., 1993. Analyse der Ozonkonzentrationen an Sonn-und Werktagen. Res. Rep., Meteorol. Inst. Univ. Freiburg.
Air quality in the Russian Federation
  • Bezuglaya
Bezuglaya, E.Y., 1996. Air quality in the Russian Federation. WMO Bulletin 45, 132}135.
Overview of air pollution in European cities
  • Sluyter
Sluyter, R., 1996. Overview of air pollution in European cities. WMO Bulletin 45, 123}128.
World Urabanization Prospects. The 1992 Revision
UN, 1993. World Urabanization Prospects. The 1992 Revision. United Nations.
City air quality trends }
  • Unep Who
UNEP/WHO, 1993. City air quality trends } Vol. 2. WHO PEP/93 26, UNE93 26P GEMS 93.A.2, Genf.
Methoden zur Regionalisierung der NO2-Immissionsdaten
  • H Mayer
  • J Schmidt
Mayer, H., Schmidt, J., 1994b. Methoden zur Regionalisierung der NO -Immissionsdaten. Res. Rep., Meteorol. Inst. Univ. Freiburg.
Ozone on an urban and regional scale – with special reference to the situation in the Netherlands
  • Guicherit