空气污染一文列出了主要大气污染物，其中一些可能源于自然环境。虽然这种空气污染有时会成为新闻焦点，但其对健康的影响却并非一直是人们关注的重点。然而，在20世纪，这种大气污染显著减少（见图2）。在20世纪80年代，臭氧层的破坏和气候变化导致的风险为健康问题蒙上了阴影。2007年在法国举行了格勒纳勒环境圆桌会议（Grenelle de l’environnement），随后发布了一项奖励政策，鼓励顾客在购买机动车时考虑二氧化碳（CO2）的排放及其对环境变化带来的风险。
要确定全球颗粒物致死率，必须考虑到颗粒物的其他来源。非洲热带间地区热带草原区的大气受到野火的污染，其中大部分燃烧是人为造成的（图6，Brustet et al.[6]）。木材仍被广泛用于生火做饭。有些壁炉安装在通风不良的房间内。这些导致人类大量接触颗粒物和其他污染物。从南北半球旱季热带草原地区生物质燃烧产生的污染物传输到赤道森林，在那里发现的臭氧等二次污染物的含量与工业化国家观察到的水平相当。这也是风蚀产生的污染。风蚀产生的微粒浓度每立方米高达几百微克，这些颗粒通过大气环流长距离运输，远达数千公里之外（见图3）。当土壤干燥、植被稀少的情况下，风蚀的强度更大。这些颗粒的尺寸范围从0.1微米到100微米不等。
图7. 通过卫星和地面测量获得的2001-2006年全球 PM2.5浓度（微克/立方米）平均值。受影响最严重的地区是热带地区，特别是风蚀颗粒（沙尘）带来的影响。 [图片来源：Aaron Van Donkelaar et al.，Environmental Health Perspectives 2015，vol123，https://doi.org/10.1289/ehp.1408646]
然而，细颗粒物（PM2.5）浓度最高的地区是热带地区（图7）。细颗粒物与旱季高温（超过40°C）一样会对健康产生影响。ACASIS（Alerte aux Canicules Au Sahel et à leurs Impacts sur la Santé）研究计划旨在预测热浪并确定其对健康的影响。需要注意的是，高温通常对应于高浓度的颗粒物，这可能会导致协同效应。
[6] J.M. Brustet, J.B. Vickos, J. Fontan, A. Podaire, F. Lavenu, 1991, 5th International Symposium “Physical Measurements and Signatures in Remote Sensing”. ESA Courchevel 14-18 January, vol 1, p 663-671
[7] Florie Chevrier, Irena Ježek, Guillaume Brulfert, Grisa Močnik, Nicolas Marchand, Jean-Luc Jaffrezo et Jean-Luc Besombes « DECOMBIO – Contribution de la combustion de la biomasse aux PM10 en vallée de l’Arve : mise en place et qualification d’un dispositif de suivi », Pollution atmosphérique [En ligne], N°231 – 232, mis à jour le : 09/02/2017, URL: http://lodel.irevues.inist.fr/pollution-atmospherique/index.php?id=5952 (in french)
[8] J. Fontan, 2013, La météorologie à l’origine de tous nos maux ?, Vuibert Vuibert Sciences (in french)
[9] A. Lopez, J. Fontan, P. Boulard, 1982, Atmospheric Environment, vol 16, no. 2 p 283-292
Fine particles (PM 2.5), one of the major components of air pollution, are believed to be responsible for a large number of deaths in France and around the world. Those produced by diesel engines and by the combustion of wood in chimneys are often implicated. Gasoline engines emit ultrafine particles (less than 0.1), which are finer than those emitted by diesel engines and therefore difficult to take into account. Other important sources of fine particles, of different chemical nature, contribute to air pollution. Monitoring networks provide the mass concentration of fine particles and these measurements are correlated with health data. Are they representative of the harmfulness of fine particles and more particularly those emitted by diesel engines or wood combustion?
This section presents the two main sources of particulate matter currently implicated, particularly in France, those from diesel engines in passenger cars, and to a lesser extent those emitted by the combustion of wood in chimneys. There are other major sources of fine particulate matter, less well publicized, that can have health effects. In mass concentration measurements, used to assess the effects of particulate matter on humans, there is no differentiation according to the origin or nature of the particles. They do not all come from combustion and therefore have different physico-chemical properties. Some are of natural origin such as pollens, spores and bacteria; they can also, even in low concentrations, have health effects. For example, we can note the respective importance of the various sources emitting PM 2.5 in metropolitan France, according to CITEPA [1](Centre Interprofessionnel Technique d’Études de la Pollution Atmosphérique), and the evolution of these sources between 1990 and 2013 (see Figure 9 below).
Pollution is also present in the air in workplaces and living quarters. In some parts of the world, wind erosion and biomass combustion cause the suspension of many particles and other pollutants with little studied health effects (see section 7 below). They are quantified by extrapolating the effects observed in areas polluted by human activities. These pollution levels, which can be high, are transported by atmospheric circulation over very long distances around the globe as shown in the video [2] in Figure 3, but also in Figures 5 and 7.
Let us not forget the ultra-fine particles or nanoparticles emitted in particular by gasoline engines, whose number is very high, but the mass very low compared to that of fine particles (see Air pollution particles: what are they?). Although these particles are generally not considered in studies of the health effects of pollution, although they are often considered to be the most dangerous, they are present in airborne aerosols, associated with PM 2.5.
2. Diesel engines
Figure 4. Traffic on a highway at the entrance to Los Angeles, USA, illustrating the high density of fine particle sources. [Source: Downtowngal [CC BY-SA 3.0 (https://creativecommons.org/licenses/by-sa/3.0)]The diesel engines that equip passenger cars and heavy goods vehicles, which are very numerous on the roads (Figure 4), but also construction machinery, agricultural machinery, locomotives and ships have been a major cause of air pollution for many years because of their emissions of particles, hydrocarbons, sulphur compounds and nitrogen oxides.
One of the advantages of the diesel engine is its high energy efficiency. At the same power it consumes less fuel than gasoline engines and therefore emits less carbon dioxide. It is a self-igniting engine: the fuel (diesel fuel) is sprayed into the cylinder, the air is heated by compression, the diesel fuel ignites spontaneously without the need for spark plug ignition. Complete combustion would essentially produce carbon dioxide. However, the mixture is not homogeneous and combustion is not complete throughout the cylinder. The diesel droplets do not have time to evaporate and are only partially burned. There is therefore a formation of unburned particles, organic compounds (acetaldehyde, acrolein, benzene, formaldehyde, etc.), PAHs (Polycyclic Aromatic Hydrocarbons), carbon, nitrogen oxides, carbon dioxide, materials whose displacement can be observed on the video in Figure 3. Injection at very high pressures, designed to better spray the fuel, improves combustion and reduces particulate emissions. Particulate filters at the exhaust level are now mandatory. Their effectiveness is rarely questioned. The regeneration of the filters is in principle automatic.
The Paris City Hall, the French Ministry of Ecology, as well as other cities and governments, want to restrict the circulation of diesel passenger cars in the coming years. Car manufacturers are moving in the same direction, favouring electric or hybrid motors in their strategy for the future. The condemnation of diesel engines would lead to a faster renewal of old vehicles and the development of new types of engines.
The bonus-malus introduced following the Grenelle Environment Round Table did not take into account pollutants other than carbon dioxide (CO2), which can have health effects, including fine particles. This bonus-malus, which favours diesel engines, continues to be applied, but the price of diesel fuel is increased to discourage the purchase of diesel cars.
3. Gasoline engines
They are less implicated than diesel engines. In these engines, the explosion is initiated by an electric spark produced by a spark plug (spark ignition engines). The combustion is more homogeneous but there are also unburned and a much finer particle emission than in diesel engines. They are essentially ultrafine particles or nanoparticles with a size of less than 0.1 μm (see Air pollution particles: what are they?). Even if these nanoparticles are very numerous, the total mass is low. The new direct injection gasoline engines, with high pressure (100 bar) in the cylinders, allow fuel consumption savings. But, as in the case of diesel injection, there is an emission of nitrogen oxides and the formation of particles whose composition does not have to be very different from that of diesel engines but the size is smaller. In conventional engines these oxides are stopped by a catalytic converter. These new engines have pollution problems comparable to those of diesel. Particulate filters are not yet mandatory, but compliance with European regulations will make them essential.
4. European standards for passenger cars: particulate matter and nitrogen oxides
The emission standards concern the main pollutants emitted by passenger cars (diesel and gasoline). They are not limited to particles alone. Those defined at European level, called Euro, are regularly reviewed and made more and more stringent. They are expressed in mg/km (see Table 1 and article Outdoor Air Pollution: Understanding to Inform and Prevent). For diesel vehicles, from Euro 5 to Euro 6, the standard has been increased, for nitrogen oxides from 180 to 80 mg/km and for particulate matter from 5 to 4.5 mg/km. In 1992 with Euro 1 it was 140 mg/km. The last values cannot be reached without a filter. Due to the high temperatures in diesel or direct injection engines (1400°C), a larger quantity of nitrogen oxides NO and NO2 are formed, generally referred to as NOx. Diesel engines are thus considered as major sources of these pollutants. They actively participate in the chemistry and photochemistry of the atmosphere and give toxic secondary compounds. In particular, they are one of the components of the formation of highly oxidizing species such as ozone. For this reason, the emission standard for nitrogen oxides has been reduced by more than a factor of 2 with Euro 6 compared to Euro 5. It is 60 mg/km for gasoline engines. In 1992, NOx emissions were not regulated for any type of engine. Regulations have thus become more and more stringent, forcing manufacturers to make improvements in engine emissions.
Table 1. Evolution of Euro standards for diesel or gasoline vehicles from 1992 to 2014 in mg/km (except for particulate matter in number). *Only for direct injection gasoline cars operating in lean-burn (stratified combustion) mode. **Regulation 459/2012 allowed direct injection petrol cars to emit 6×1012 particles until 2017; they are now limited to 6×1011 as for diesel vehicles.
To limit nitrogen oxide emissions, petrol engines are equipped with a catalytic converter that oxidises carbon monoxide and unburned hydrocarbons and reduces nitrogen oxides. However, to be effective, the engine must be warm enough, which limits its effectiveness for short trips. In diesel engines, the catalyst oxidizes carbon monoxide and hydrocarbons. The air-fuel mixture being poor, i.e. rich in air and oxygen, the pot does not reduce nitrogen oxides.
An EGR (Exhaust Gas Recirculation) gas recirculation system reduces nitrogen oxide emissions in diesel engines by lowering the temperature of the exhaust gas, but not enough and must be accompanied by aftertreatment. There are currently two main ones. The selective catalytic reduction (SCR) system [3]. Its principle consists in injecting an aqueous solution of urea or Adblue which is transformed into gaseous ammonia and transforms NO2 into nitrogen. An injection and storage system for Adblue is required and the Adblue reservoir must be filled with about 15 litres every 15 to 20,000 kilometres. With the second process or “nitrogen oxide trap” these are trapped in a catalytic converter using precious metals, the oxides are then regularly transformed into nitrogen. The NOx trap is less expensive than the SCR system but less efficient. These systems are sensitive to outdoor temperature and require adjustments that may vary with the approval conditions. The emissions, measured on the bench, are criticised and must be supplemented by measurements made under vehicle operating conditions.
To take into account ultrafine particles, from Euro 5 onwards, a standard has been defined for the number of diesel engine particles, which must not exceed 6.1011 particles/km. For direct injection gasoline engines, this standard imposed a limit on the number of emissions to 6.1012 particles/km in September 2014, then to 6.1011 in 2017, as for Diesel engines. For carbon monoxide the standard is more stringent for diesel than for gasoline engines, respectively 500 and 1,000 mg/km.
With Euro 6 the emission standards for diesel and petrol engines are comparable. Diesel engines equipped with particulate filters must in principle emit fewer fine and ultra-fine particles than gasoline engines. If manufacturers actually comply with these standards and do not try to circumvent them as some of them appear to have done[4]for nitrogen oxides, condemning diesel engines alone may no longer be justified for new cars complying with the standards. However, emissions may depend on the conditions of use of the vehicle, making it more difficult to control emissions. It should be stressed that pollution today is mainly produced by the oldest vehicles, in particular Diesel. However, the cost of pollution control condemns the smallest cars. In April 2019 the European Union has adopted a regulation reducing in 2030 CO2 emissions of new cars by 37.5%, compared to 2021; this implies a reduction in the overall consumption of the vehicles and therefore a diminution in the associated polluting emissions.
Pollution from heavy goods vehicles emitted in urban areas, near roads and highways, is also evident at the regional level, where it contributes to increasing overall pollution. Freight transport by rail should be the rule. The recent law promoting people’s bus travel contributes to the increase in pollutant emissions, which are in addition to the emissions of heavy goods vehicles transporting goods. This type of transport (goods and people) is not implicated in emission control measures during pollution episodes. Moreover, unlike railways, the fair price of road transport infrastructure is not reflected in the cost of road transport, as motorway maintenance charges are not paid by heavy goods vehicles in proportion to the road wear they produce. The “ecotax”, applicable to the non-highway network, which would have made it possible to partially finance road infrastructure, was passed by the French parliament and then abandoned despite equipment already built. As shown in Figure 10, the high PM 10 concentrations provided by PREV’AIR [5] are observed for northern and central Europe for a large area that is not limited to urban areas. It is not enough to limit diesel car emissions in the centre of urban areas to have a good air quality.
In the case of heavy goods vehicles (and other equipment such as boats, locomotives, etc.), gasoline engines cannot replace diesel engines. It is often announced that, in the near future, these could be replaced by fuel cells, combined with electric motors. But this technology is not yet developed and it is not clear that it will be economically competitive with depolluted diesel engines.
In April 2019 the European Parliament adopted for the first time a proposal for a regulation of the CO2 emissions of Heavy Duty vehicles in the countries of the European Union. Heavy goods vehicles must reduce CO2 emissions by 15% by 2025 and by 30% by 2030, compared to 2019 emissions. The Council on Ministers still has to approve this regulation in May 2019. In addition, 2% of new vehicles will have to be low or zero emissions by 2025. The emissions of pollutants should diminish in a similar way.
6. Wood combustion
More recently, it is the open chimneys that are being challenged, particularly in the Île-de-France region, with a ban imposed by an order of the Paris Prefecture following the recommendation of the PPA (Plan de Protection de l’Atmosphère), followed by a cancellation of this authorisation following an intervention by the Minister for Ecology. Burning wood is a source of air pollution and in particular particulate matter, but it is also encouraged by tax benefits in the context of the forest-energy sector. Its use is not limited to the Île-de-France region, but it was publicized during this administrative episode.
Wood combustion contains a large number of pollutants, including various organic compounds, PAHs, dioxins and particles, which correspond to incomplete combustion. Emissions depend on the nature of the wood (hardwood and softwood), the water vapour content (important factor which must be less than 15%), the type of fireplace, the combustion temperature, which can vary from 300 to 700°C. The efficiency of combustion, emissions are all the more important when the temperature is low. Open chimneys have a very low efficiency of about 10% and emit a large number of particles. Inserts, modern stoves, have yields of up to 70%. In Île-de-France there are reportedly 100,000 open fireplaces.
The wood-energy sector has expressed its concern following the condemnation of the burning of wood. It encourages the use of wood, particularly for heating homes. On the other hand, ecologists protested against the abolition of the ban on wood in Paris. For representatives of the wood industry, the combustion of this material contributes only 5% to air pollution in the Île-de-France region; for the DRIEE (Direction Régionale de l’Industrie, de l’Environnement et de l’Énergie) this contribution amounts to 25% or 30%.
By way of comparison, in Canada and the United States, standards have been defined to increase and regulate the efficiency of wood-burning fireplaces. The EPA (the American Environmental Agency) has defined a certification of fireplaces that has been adopted in Canada. In France, manufacturers of stoves and inserts have defined standards presented under the acronym “Flamme Verte“, with stars to characterize performance. Since 2015, the best performers have had 5 stars and this level allows them to obtain tax advantages from the administration during installation. The 5-star green flame label corresponds to a combustion efficiency of 70%, carbon monoxide (CO) emissions of less than 0.3%, particles less than 90 mg/Nm3 (30 times less than an open fireplace). New classes are in prospect with 6 or 7 stars.
Table 2. Evolution of the green flame label standards. It should be noted that since 1 January 2018, the award of the label’s 6 and 7-star classes is subject to two new additional eligibility criteria on gaseous organic compounds and nitrogen oxides (NOx)
7. Biomass fires and wind erosion
Figure 6. Vegetation fires in the Savannah regions of West Africa (each black dot represents one fire). Image obtained on December 12, 1986 with channels 3 and 4 of the NOAA-AVHRR observation satellite channels 3 and 4. Each fire is lit by man to burn the herbs. About 1 km long or more, it spreads by sparing trees. The particles and gases emitted during combustion are transported to the forest area to the south. This pollution is in addition to particulate matter from wind erosion in the northern area.
To establish global PM mortality, other sources must be taken into account. Thus, the atmosphere of intertropical regions in Africa, in the savannah region, is polluted by wildfires, most of which are lit by human hands (Figure 6, according to Brustet et al. [6]). Wood is also still widely used for food preparation. Fireplaces are sometimes in poorly ventilated rooms. This results in significant exposures to particulate matter and other pollutants. Emissions from biomass combustion are transported from the savannah regions of the northern and southern hemispheres during their respective dry seasons to the equatorial forest where secondary compounds such as ozone are found at levels comparable to those observed in industrialized countries. This pollution is in addition to that produced by wind erosion, which leads to very high particle concentrations, a few hundred µg/m3, which are transported over long distances by atmospheric circulation, several thousand kilometres (see Figure 3). Erosion is more intense when the soil is dry and the vegetation rare. These particles have dimensions ranging from 0.1 to 100 µm.
This phenomenon of wind erosion is not specific to Africa. It occurs in all arid or semi-arid regions, for example in the Mediterranean regions. These particles are added to anthropogenic production, but their nature is very different and they do not have the same toxicity. The global extension of the health and mortality effects of particulate matter, particularly from satellite measurements, does not take into account their different properties from those of anthropogenic particles.
Figure 7. Global concentrations in µg/m3 of PM 2.5, obtained by satellite and ground measurements, averaged over the period 2001-2006. The most affected regions are in the tropics, especially with particles from wind erosion. [Source: Aaron Van Donkelaar et al, Environmental Health Perspectives 2015, vol123, https://doi.org/10.1289/ehp.1408646]However, the highest concentrations of fine particulate matter (PM 2.5) are found in intertropical regions (Figure 7). Their health effects are in addition to those due to very high temperatures in the dry season (over 40°C). The ACASIS (acronym for Alerte aux Canicules Au Sahel et à leurs Impacts sur la Santé) research program aims to predict heatwaves and define their health effects. It should be noted that high temperatures generally correspond to high concentrations of particulate matter, which should lead to synergy effects.
8. Other sources of particulate matter
Other sources of particulate matter are numerous. In road transport, to the particles resulting from the combustion of fuels, we must add the particles emitted with the wear and tear of tires, brakes and road surfaces. From the beginning of the 20th century, industrial activities and energy production with coal-fired and then oil-fired power plants were major emitters of pollutants, including particles of a very diverse chemical nature, some very toxic.
Figure 8. In the Arve Valley, between 2013 and 2015, changes in soot carbon concentrations from the combustion of firewood (in green, BCwood burning) and fossil fuels (in black, BCfossil fuel) from the three DECOMBIO programme sites. [Source: Reproduced with permission of the authors, see ref. [7].Particles may be emitted directly into the atmosphere or may result from chemical or photochemical reactions in the gas phase or in mists or fog. In the 1970s, an important manifestation was the acidification of precipitation that led to forest dieback in some areas of Europe and the United States. This type of pollution, called “transboundary pollution”, has now been controlled. Industrial sources, in particular, have now declined significantly due to plant closures, effluent treatment, etc.
To characterize the unburnt part of the particle, carbon, named soot carbon or black carbon, is measured (see Figure 8). Particulate matter from biomass combustion can be distinguished from that emitted from fossil fuel combustion [7]. This measure remains ad hoc and is not generalized in monitoring networks. It is not used to differentiate the toxicity of different particles and their health effects in the aerosol.
AIRPARIF (the body in charge of monitoring air pollution in the Île-de-France region) carries out emission inventories for the Île-de-France region. The published results are in the same direction with a reduction in emissions for road traffic and wood heating.
They are not measured as ultrafine particles in air pollution monitoring networks, which does not mean that they are not present and have no health effects. They are collected with fine particles and are confused with them because of their low mass. Their concentration must be measured in number per unit volume. Their penetration and deposition in the respiratory tract are analyzed in the article on the properties of particles (see Air pollution particles: what are they?).
Figure 11. Average daytime variations in concentrations (by number) of ultrafine particles in the city of Toulouse for different months of the year.
There are many sources of ultrafine particles. They are formed in particular during combustion but also result from reactions in the atmosphere between gases such as sulphur dioxide, nitrogen oxides and hydrocarbons, most often under the action of solar radiation. They are composed of sulphates, nitrates, carbon compounds. They can result from the condensation of metal vapours from industrial effluents. They can be of natural origin following, for example, the emission, by vegetation, of organic compounds such as terpenes, isoprene. With solar radiation they have a bluish appearance due to their small size which preferentially diffuses the short wavelengths of solar radiation (Rayleigh scattering, see Air pollution particles: what is it all about? and The colours of the sky). We sometimes talk about blue haze. These particles, resulting from the decomposition of plant species, are sometimes considered beneficial to health. They are or have been promoted in cities that were once classified as bioclimatic, such as Arcachon [8].
As with fine particles, concentrations of ultrafine particles are higher in the winter months, with the same type of diurnal variation for all months of the year: a minimum in late night, maxima in early morning and late day. Figure 11 shows the large number of particles between 104 and 105 particles per cm3, which is typical of an urban area. Fine particles represent only a small fraction of the number of these particles (a few tens per cm3) [9]. The midday decrease corresponds to the development of instability in the lower layers of the atmosphere, which is greater in summer than in winter. This diurnal variation is typical of local sources. (It is less pronounced for particulate matter, than for example for nitrogen oxides, showing a greater local contribution for nitrogen oxides in urban areas). Photochemistry is very active in summer with solar radiation. The composition of the air is not the same in summer and winter. Among the many pollutants of photochemical origin forming in the atmosphere is ozone, whose toxicity and oxidative power are well known. The very numerous ultrafine particles will coagulate with each other or attach to larger particles, thus limiting the life span of the finer ones; this coagulation does not affect the mass concentration, but only the properties of the particles.
10. Other difficulties in characterizing particulate pollution
We have seen that cars with diesel engines are not the only ones responsible for particle pollution. The mass concentration that is measured in monitoring networks (or by satellite or with models) does not take into account the nature and toxicity of particulate matter. These can absorb water vapour, especially if they are soluble particles. Depending on the hygrometric degree, this results in variations in their mass and size during sampling.
Air pollution, particularly in polluted urban areas, is a complex mixture of pollutants, including ultrafine particles, which have synergistic effects. It is therefore difficult to quantify everyone’s responsibility, particularly that of fine and ultrafine particles. Concentrations are very inhomogeneous, which complicates the determination of exposure doses and the implementation of sensors in pollutant measurement networks. The composition of the pollutant mixture varies with solar radiation, which leads to photochemical reactions and new and often more toxic pollutants. The physical and chemical characteristics of the particles are modified.
Meteorology affects health and well-being. This is the field of biometeorology. Temperature is the parameter whose effects, particularly on mortality, are best known. They depend on the climate and people’s lifestyles. They must be distinguished from the effects of particles or pollutants whose concentration variations are related to temperature variations. Living particles such as bacteria, viruses, spores, pollens are sensitive to weather conditions and can have health effects.
Air pollution levels have decreased significantly since air quality monitoring began in the 1950s, particularly for particulate matter as shown in Figure 2. Diesel engines were fewer in number but they were very polluting. The consequences on health effects are not quantified, except for episodes of very high pollution, such as those in the Meuse Valley or London. The identification of a very significant improvement in health (which can be assumed) would be an argument that would allow the public to better understand the issues involved in improving air quality.
11. Messages to remember
The harmfulness of particles emitted by diesel engines in cars is not debatable, but there are many other machines, including trucks, that run on diesel engines.
Newer cars are equipped with emission control systems that severely limit their emissions of particulate matter and nitrogen oxides.
There are many other sources of particulate matter causing high concentrations of particulate matter in the atmosphere, some of which are of natural origin. Some of them are likely to produce allergies.
The main sectors responsible for the production of fine particulate matter (PM 2.5) are the combustion of wood to heat homes, agriculture with the use of fertilizers, manufacturing industries and transport.
Ultrafine particles are collected with fine particles from which they are not separated due to their low mass. Their number is very high.
The Euro emission standards for engines, defined at European Union level, cover both fine particulate matter and nitrogen oxides. For both diesel and gasoline vehicles, the Euro 6 standard for particulate matter is 4.5 mg/km. This value cannot be reached without the addition of filters.
The complexity of the phenomena with regard to air pollution and its effects requires a completely multidisciplinary approach with doctors, epidemiologists, physicists, chemists, meteorologists, etc.
References and notes
Cover image. Emissions from diesel cars and wood-burning fireplaces, considered to be very harmful to health, are regularly charged. But other important sources exist, in particular heavy truck traffic, as well as, in some regions, wind erosion and biomass combustion [Source: editing from royalty-free images].
[4] The manufacturer Volkswagen had developed software that disabled the NOx emission control system when the test was completed, resulting in emissions well above the standards.
[6] J.M. Brustet, J.B. Vickos, J. Fontan, A. Podaire, F. Lavenu, 1991, 5th International Symposium “Physical Measurements and Signatures in Remote Sensing“. ESA Courchevel 14-18 January, vol 1, p 663-671
[7] Florie Chevrier, Irena Ježek, Guillaume Brulfert, Grisa Močnik, Nicolas Marchand, Jean-Luc Jaffrezo et Jean-Luc Besombes « DECOMBIO – Contribution de la combustion de la biomasse aux PM10 en vallée de l’Arve : mise en place et qualification d’un dispositif de suivi », Pollution atmosphérique [En ligne], N°231 – 232, mis à jour le : 09/02/2017, URL : http://lodel.irevues.inist.fr/pollution-atmospherique/index.php?id=5952 (in french)
[8] J. Fontan, 2013, La météorologie à l’origine de tous nos maux ?, Vuibert Vuibert Sciences (in french)
[9] A. Lopez, J. Fontan, P. Boulard, 1982, Atmospheric Environment, vol 16, no. 2 p 283-292
