New considerations for PM, black carbon and particle number concentration for air quality monitoring across different European cities

In many large cities of Europe standard air quality limit values of particulate matter (PM) are exceeded. Emissions from road traffic and biomass burning are frequently reported to be the major causes. As a consequence of these exceedances a large number of air quality plans, most of them focusing on traffic emissions reductions, have been implemented in the last decade. In spite of this implementation, a number of cities did not record a decrease of PM levels. Thus, is the efficiency of air quality plans overestimated? Do the road traffic emissions contribute less than expected to ambient air PM levels in urban areas? Or do we need a more specific metric to evaluate the impact of the above emissions on the levels of urban aerosols? This study shows the results of the interpretation of the variability of levels of PM, Black Carbon (BC), aerosol number concentration (N) and a number of gaseous pollutants in seven selected urban areas covering road traffic, urban background, urban-industrial, and urban-shipping environments from southern, central and northern Europe. The results showed that variations of PM and N levels do not always reflect the variation of the impact of road traffic emissions on urban aerosols. However, BC levels vary proportionally with those of traffic related gaseous pollutants, such as CO, NO₂ and NO. Due to this high correlation, one may suppose that monitoring the levels of these gaseous pollutants would be enough to extrapolate exposure to traffic-derived BC levels. However, the BC/CO, BC/NO₂ and BC/NO ratios vary widely among the cities studied, as a function of distance to traffic emissions, vehicle fleet composition and the influence of other emission sources such as biomass burning. Thus, levels of BC should be measured at air quality monitoring sites. During morning traffic rush hours, a narrow variation in the N/BC ratio was evidenced, but a wide variation of this ratio was determined for the noon period. Although in central and northern Europe N and BC levels tend to vary simultaneously, not only during the traffic rush hours but also during the whole day, in urban background stations in southern Europe maximum N levels coinciding with minimum BC levels are recorded at midday in all seasons. These N maxima recorded in southern European urban background environments are attributed to midday nucleation episodes occurring when gaseous pollutants are diluted and maximum insolation and O₃ levels occur. The occurrence of SO₂ peaks may also contribute to the occurrence of midday nucleation bursts in specific industrial or shipping-influenced areas, although at several central European sites similar levels of SO₂ are recorded without yielding nucleation episodes. Accordingly, it is clearly evidenced that N variability in different European urban environments is not equally influenced by the same emission sources and atmospheric processes. We conclude that N variability does not always reflect the impact of road traffic on air quality, whereas BC is a more consistent tracer of such an influence. However, N should be measured since ultrafine particles (<100 nm) may have large impacts on human health. The combination of PM₁₀ and BC monitoring in urban areas potentially constitutes a useful approach for air quality monitoring. BC is mostly governed by vehicle exhaust emissions, while PM₁₀ concentrations at these sites are also governed by non-exhaust particulate emissions resuspended by traffic, by midday atmospheric dilution and by other nontraffic emissions

New considerations for PM, Black Carbon and particle number concentration for air quality monitoring across different European cities

In many large cities of Europe standard air quality limit values of particulate matter (PM) are exceeded. Emissions from road traffic and biomass burning are frequently reported to be the major causes. As a consequence of these exceedances a large number of air quality plans, most of them focusing on traffic emissions reductions, have been implemented in the last decade. In spite of this implementation, a number of cities did not record a decrease of PM levels. Thus, is the efficiency of air quality plans overestimated? Do the road traffic emissions contribute less than expected to ambient air PM levels in urban areas? Or do we need a more specific metric to evaluate the impact of the above emissions on the levels of urban aerosols? This study shows the results of the interpretation of the 2009 variability of levels of PM, Black Carbon (BC), aerosol number concentration (N) and a number of gaseous pollutants in seven selected urban areas covering road traffic, urban background, urban-industrial, and urban-shipping environments from southern, central and northern Europe. The results showed that variations of PM and N levels do not always reflect the variation of the impact of road traffic emissions on urban aerosols. However, BC levels vary proportionally with those of traffic related gaseous pollutants, such as CO, NO2 and NO. Due to this high correlation, one may suppose that monitoring the levels of these gaseous pollutants would be enough to extrapolate exposure to traffic-derived BC levels. However, the BC/CO, BC/NO2 and BC/NO ratios vary widely among the cities studied, as a function of distance to traffic emissions, vehicle fleet composition and the influence of other emission sources such as biomass burning. Thus, levels of BC should be measured at air quality monitoring sites. During morning traffic rush hours, a narrow variation in the N/BC ratio was evidenced, but a wide variation of this ratio was determined for the noon period. Although in central and northern Europe N and BC levels tend to vary simultaneously, not only during the traffic rush hours but also during the whole day, in urban background stations in southern Europe maximum N levels coinciding with minimum BC levels are recorded at midday in all seasons. These N maxima recorded in southern European urban background environments are attributed to midday nucleation episodes occurring when gaseous pollutants are diluted and maximum insolation and O3 levels occur. The occurrence of SO2 peaks may also contribute to the occurrence of midday nucleation bursts in specific industrial or shipping-influenced areas, although at several central European sites similar levels of SO2 are recorded without yielding nucleation episodes. Accordingly, it is clearly evidenced that N variability in different European urban environments is not equally influenced by the same emission sources and atmospheric processes. We conclude that N variability does not always reflect the impact of road traffic on air quality, whereas BC is a more consistent tracer of such an influence. However, N should be measured since ultrafine particles (<100 nm) may have large impacts on human health. The combination of PM10 and BC monitoring in urban areas potentially constitutes a useful approach for air quality monitoring. BC is mostly governed by vehicle exhaust emissions, while PM10 concentrations at these sites are also governed by non-exhaust particulate emissions resuspended by traffic, by midday atmospheric dilution and by other non-traffic emissions

Agricultura y ruralidad europeas frente a la neutralidad presupuestaria y el nuevo marco financiero

La multifuncionalidad de la agricultura y ruralidad europeas parecían haber sido legitimadas en el contexto de las negociaciones agrícolas de la Ronda de Doha y de las demandas crecientes de una sociedad cada día más preocupada por la seguridad de los alimentos, el bienestar de los animales, y la protección del medio, todo ello conjugado en una agricultura sostenible. Sin embargo razones internas de hondo calado en una nueva Unión a veinticinco, como la neutralidad presupuestaria y el nuevo marco financiero, trastocan las vías y tendencias mantenidas hasta ahora. Las repercusiones traslucen una clara reorientación desde las líneas integradas hacia otra competitiva, mercantilista, que podría vislumbrar una vuelta de tuerca hacia enfoques pasados

An exploratory study on English teachers’ opinions in multicultural preschools

Developing plurilingualism is one of the objectives of the European Union and therefore the teaching of foreign languages (FLs) has acquired particular relevance in the last decade. Spain has made a great effort to promote an early start of the foreign language teaching in all its regions; however, there is an enormous gap between the legislative and methodological level, mainly due to the lack of uniformity regarding the decentralization of the education system (Calero, 2006). This target may be more challenging in places such as Ceuta or Melilla, two Spanish cities on the north coast of Africa, due to their particular multicultural context, where preschool classrooms are already multilingual, despite the FL. Based on the interpretative paradigm, this paper presents an exploratory study on English Foreign Language (EFL) teachers’ opinions at preschools in Ceuta and Melilla. We carried out eight interviews to EFL teachers analysing their own practice in these multicultural preschool classrooms, where monolingual and bilingual children share their learning experience with the common objective of developing their communicative competence in English. Conclusions suggest that the multicultural context within these two cities may cause some conflictive situations, mainly due to limited competence on Spanish and to null motivation towards the learning of FLs.HUM45

Macroglobulinemia de Waldenström con transformación a Linfoma del manto

La Macroglobulinemia de Waldenström (MW) es una enfermedad infrecuente con una incidencia de tres casos por millón de habitantes al año aproximadamente1 y cuyo diagnóstico siempre plantea importantes dudas. La edad media de diagnóstico es de 64 años siendo más frecuente en varones (60%) y en la raza caucasiana2. Se considera una patología progresiva, crónica y en general de curso lento. La causa más frecuente de muerte son las segundas neoplasias y de todas ellas la trasformación a linfoma inmunoblástico causa un pequeño porcentaje de ellas. Exponemos el caso de una mujer diagnosticada de Macroglobulinemia de Waldenström que presentó precozmente una trasformación a linfoma del manto con rápida y nefasta progresión. Waldenström's Macroglobulinemia (MW) is an uncommon disease with an incidence of three cases per million population per year approximately and whose diagnosis presents important questions always. The average age of diagnosis is 64 years being more frequent in males (60%) and Caucasian race. It is considered a progressive, chronic disease and slow course generally. The second malignancies are the most frequent cause of death and a small percentage of them transformation to Immunoblastic Lymphoma. We present the case of a diagnosed woman of Waldenström's Macroglobulinemia who presented a transformation to mantle cell lymphoma precociously with quick and grim progression

Emblems and spaces of power during the Argaric Bronze Age at La Almoloya, Murcia

The recent discovery of an exceptionally rich grave at La Almoloya in south-eastern Spain illuminates the political context of Early Bronze Age El Argar society. The quantity, variety and opulence of the grave goods emphasise the technological, economic and social dimensions of this unique culture. The assemblage includes politically and ideologically emblematic objects, among which a silver diadem stands out. Of equally exceptional character is the building under which the grave was found—possibly one of the first Bronze Age palaces identified in Western Europe. The architecture and artefacts from La Almoloya provide new insight into emblematic individuals and the exercise of power in societies of marked economic asymmetry.Introduction Argaric diadems as embodied emblems La Almoloya grave 38 Spaces of power Conclusion

Identification and quantification of organic aerosol from cooking and other sources in Barcelona using aerosol mass spectrometer data

PM1 (particulate matter with an aerodynamic diameter <1 μm) non-refractory components and black carbon were measured continuously together with additional air quality and atmospheric parameters at an urban background site in Barcelona, Spain, during March 2009 (campaign DAURE, Determination of the sources of atmospheric Aerosols in Urban and Rural Environments in the western Mediterranean).Positive matrix factorization (PMF) was conducted on the organic aerosol (OA) data matrix measured by an aerosol mass spectrometer, on both unit mass(UMR) and high resolution (HR) data. Five factors or sources could be identified: LV-OOA (low-volatility oxygenated OA), related to regional, aged secondary OA; SVOOA (semi-volatile oxygenated OA), a fresher oxygenated OA; HOA (hydrocarbon-like OA, related to traffic emissions); BBOA (biomass burning OA) from domestic heating or agricultural biomass burning activities; and COA (cook-ing OA). LV-OOA contributed 28 % to OA, SV-OOA 27 %, COA 17 %, HOA 16 %, and BBOA 11 %. The COA HR spectrum contained substantial signal from oxygenated ions (O:C: 0.21) whereas the HR HOA spectrum had almost exclusively contributions from chemically reduced ions (O:C:0.03). If we assume that the carbon in HOA is fossil while that in COA and BBOA is modern, primary OA in Barcelona contains a surprisingly high fraction (59 %) of non-fossil car-bon. This paper presents a method for estimating cooking organic aerosol in ambient datasets based on the fractions of organic mass fragments at m/z 55 and 57: their data points fall into a V-shape in a scatter plot, with strongly influenced HOA data aligned to the right arm and strongly influenced COA data points aligned to the left arm. HR data show that this differentiation is mainly driven by the oxygen-containing ions C₃H₃O+ and C₃H₅O+, even though their contributions to m/z 55 and 57 are low compared to the reduced ions C₄H+₇ and C₄H+₉. A simple estimation method based on the markers m/z 55, 57, and 44 is developed here and allows for a first-order-estimation of COA in urban air. This study emphasizes the importance of cooking activities for ambient air quality and confirms the importance of chemical composition measurements with a high mass and time resolution

Fossil versus contemporary sources of fine elemental and organic carbonaceous particulate matter during the DAURE campaign in Northeast Spain

We present results from the international field campaign DAURE (Determination of the sources of atmospheric Aerosols in Urban and Rural Environments in the Western Mediterranean), with the objective of apportioning the sources of fine carbonaceous aerosols. Submicron fine particulate matter (PM₁) samples were collected during February-March 2009 and July 2009 at an urban background site in Barcelona (BCN) and at a forested regional background site in Montseny (MSY). We present radiocarbon (¹⁴C) analysis for elemental and organic carbon (EC and OC) and source apportionment for these data. We combine the results with those from component analysis of aerosol mass spectrometer (AMS) measurements, and compare to levoglucosan-based estimates of biomass burning OC, source apportionment of filter data with inorganic composition + EC + OC, submicron bulk potassium (K) concentrations, and gaseous acetonitrile concentrations. At BCN, 87 % and 91 % of the EC on average, in winter and summer, respectively, had a fossil origin, whereas at MSY these fractions were 66 % and 79 %. The contribution of fossil sources to organic carbon (OC) at BCN was 40 % and 48 %, in winter and summer, respectively, and 31 % and 25 % at MSY. The combination of results obtained using the ¹⁴C technique, AMS data, and the correlations between fossil OC and fossil EC imply that the fossil OC at Barcelona is ∼47 % primary whereas at MSY the fossil OC is mainly secondary (∼85 %). Day-to-day variation in total carbonaceous aerosol loading and the relative contributions of different sources predominantly depended on the meteorological transport conditions. The estimated biogenic secondary OC at MSY only increased by ∼40 % compared to the order-of-magnitude increase observed for biogenic volatile organic compounds (VOCs) between winter and summer, which highlights the uncertainties in the estimation of that component. Biomass burning contributions estimated using the 14C technique ranged from similar to slightly higher than when estimated using other techniques, and the different estimations were highly or moderately correlated. Differences can be explained by the contribution of secondary organic matter (not included in the primary biomass burning source estimates), and/or by an overestimation of the biomass burning OC contribution by the ¹⁴C technique if the estimated biomass burning EC/OC ratio used for the calculations is too high for this region. Acetonitrile concentrations correlate well with the biomass burning EC determined by ¹⁴C. K is a noisy tracer for biomass burning

New considerations for PM, black carbon and particle number concentration for air quality monitoring across different European cities

In many large cities of Europe standard air quality limit values of particulate matter (PM) are exceeded. Emissions from road traffic and biomass burning are frequently reported to be the major causes. As a consequence of these exceedances a large number of air quality plans, most of them focusing on traffic emissions reductions, have been implemented in the last decade. In spite of this implementation, a number of cities did not record a decrease of PM levels. Thus, is the efficiency of air quality plans overestimated? Do the road traffic emissions contribute less than expected to ambient air PM levels in urban areas? Or do we need a more specific metric to evaluate the impact of the above emissions on the levels of urban aerosols? This study shows the results of the interpretation of the variability of levels of PM, Black Carbon (BC), aerosol number concentration (N) and a number of gaseous pollutants in seven selected urban areas covering road traffic, urban background, urban-industrial, and urban-shipping environments from southern, central and northern Europe. The results showed that variations of PM and N levels do not always reflect the variation of the impact of road traffic emissions on urban aerosols. However, BC levels vary proportionally with those of traffic related gaseous pollutants, such as CO, NO₂ and NO. Due to this high correlation, one may suppose that monitoring the levels of these gaseous pollutants would be enough to extrapolate exposure to traffic-derived BC levels. However, the BC/CO, BC/NO₂ and BC/NO ratios vary widely among the cities studied, as a function of distance to traffic emissions, vehicle fleet composition and the influence of other emission sources such as biomass burning. Thus, levels of BC should be measured at air quality monitoring sites. During morning traffic rush hours, a narrow variation in the N/BC ratio was evidenced, but a wide variation of this ratio was determined for the noon period. Although in central and northern Europe N and BC levels tend to vary simultaneously, not only during the traffic rush hours but also during the whole day, in urban background stations in southern Europe maximum N levels coinciding with minimum BC levels are recorded at midday in all seasons. These N maxima recorded in southern European urban background environments are attributed to midday nucleation episodes occurring when gaseous pollutants are diluted and maximum insolation and O₃ levels occur. The occurrence of SO₂ peaks may also contribute to the occurrence of midday nucleation bursts in specific industrial or shipping-influenced areas, although at several central European sites similar levels of SO₂ are recorded without yielding nucleation episodes. Accordingly, it is clearly evidenced that N variability in different European urban environments is not equally influenced by the same emission sources and atmospheric processes. We conclude that N variability does not always reflect the impact of road traffic on air quality, whereas BC is a more consistent tracer of such an influence. However, N should be measured since ultrafine particles (<100 nm) may have large impacts on human health. The combination of PM₁₀ and BC monitoring in urban areas potentially constitutes a useful approach for air quality monitoring. BC is mostly governed by vehicle exhaust emissions, while PM₁₀ concentrations at these sites are also governed by non-exhaust particulate emissions resuspended by traffic, by midday atmospheric dilution and by other nontraffic emissions

Early Language Education in Luxembourg

This chapter examines recent language education laws in Luxembourg as well as the ways in which early years practitioners appropriated the new policies and put them into practice. The chapter begins with a brief introduction of the linguistic landscape in Luxembourg and a summary of the dynamic development of the country’s early childhood education system. Special emphasis is put on recent changes in language education policies, which call for a more inclusive and multilingual early language education. Monolingual practices now need to open up to flexible language use and offer children opportunities to capitalize on their entire semiotic repertoire for communicating, meaning-making, and learning. The central concerns of this chapter are the ways in which policy changes influence educational practices in formal and non-formal settings and how professional development shapes this process. In order to address these questions, the authors review literature on language education policy, translanguaging and professional development and examine studies on early language education in Luxembourg. Next, they discuss recent initiatives of professional development in formal and non-formal early years settings as well as their outcomes. Finally, they present critical issues such as the practitioners’ reflexivity and responsibility and the sustainability of professional development. Future research directions include family language policies, partnerships between families and early childhood institutions and children’s languaging practices inside and across these institutions