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ENVIRONMENTAL PROTECTION AGENCY Monitoring, Analysing and Reporting on the The Environmental Protection Agency (EPA) is responsible for Environment protecting and improving the environment as a valuable asset • Monitoring air quality and implementing the EU Clean Air for for the people of Ireland. We are committed to protecting people Europe (CAFÉ) Directive. and the environment from the harmful effects of radiation and • Independent reporting to inform decision making by national pollution. and local government (e.g. periodic reporting on the State of Ireland’s Environment and Indicator Reports). The work of the EPA can be divided into three main areas: Regulating Ireland’s Greenhouse Gas Emissions • Preparing Ireland’s greenhouse gas inventories and projections. 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The work is carried out across five Offices: • Office of Environmental Sustainability Water Management • Monitoring and reporting on the quality of rivers, lakes, • Office of Environmental Enforcement transitional and coastal waters of Ireland and groundwaters; • Office of Evidence and Assessment measuring water levels and river flows. • Office of Radiological Protection • National coordination and oversight of the Water Framework • Office of Communications and Corporate Services Directive. The EPA is assisted by an Advisory Committee of twelve members • Monitoring and reporting on Bathing Water Quality. who meet regularly to discuss issues of concern and provide advice to the Board.
Air Quality in Ireland 2015 Key Indicators of Ambient Air Quality Dr. Micheál O’Dwyer National Ambient Air Quality Programme Office of Radiological Protection
Published by Environmental Protection Agency An Ghníomhaireacht um Chaomhnú Comhshaoil PO Box 3000 Johnstown Castle Estate County Wexford, Ireland Telephone: +353 53 9160600 Lo Call: 1890 33 55 99 Fax: +353 53 9160699 Email: info@epa.ie Web site: www.epa.ie ISBN: 978-1-84095-697-9 © Environmental Protection Agency 2016 Although every effort has been made to ensure the accuracy of the material contained in this publication, complete accuracy cannot be guaranteed. Neither the Environmental Protection Agency nor the author(s) accept any responsibility whatsoever for loss or damage occasioned or claimed to have been occasioned, in part or in full, as a consequence of any person acting or refraining from acting, as a result of a matter contained in this publication. Parts of this publication may be reproduced without further permission, provided the source is acknowledged.
Air Quality In Ireland 2015 Contents Contents .................................................................................................................................................. 3 Index of figures ....................................................................................................................................... 5 Index of tables......................................................................................................................................... 6 Acknowledgments................................................................................................................................... 7 Glossary ................................................................................................................................................... 8 Executive Summary ............................................................................................................................... 10 1. Introduction .................................................................................................................................. 13 National Ambient Air Quality Monitoring Programme ..................................................................... 13 Air pollution and human health ........................................................................................................ 13 Air pollution, ecosystems and climate .............................................................................................. 13 WHO air quality guidelines ............................................................................................................... 14 Irish and EU air quality legislation..................................................................................................... 14 Report objectives and coverage ....................................................................................................... 14 Air quality zones 2015 ....................................................................................................................... 15 Air quality monitoring network 2015................................................................................................ 16 European air quality .......................................................................................................................... 16 2. Nitrogen oxides (NOX) ................................................................................................................... 17 3. Sulphur dioxide (SO2) .................................................................................................................... 18 4. Carbon monoxide (CO).................................................................................................................. 19 5. Ozone (O3) ..................................................................................................................................... 20 6. Particulate matter (PM10).............................................................................................................. 22 7. Particulate matter (PM2.5) ............................................................................................................. 24 8. Benzene and volatile organic compounds (VOCs) ........................................................................ 26 9. Heavy metals ................................................................................................................................. 27 10. Polycyclic aromatic hydrocarbons (PAH) .................................................................................. 29 11. Dioxins, PCBs and Brominated Flame Retardants survey ......................................................... 31 11.1 Origins of Dioxins in Air ......................................................................................................... 31 11.1.1 PCBs............................................................................................................................... 32 3
Air Quality In Ireland 2015 11.1.2 Toxicity of Dioxins and PCBs ......................................................................................... 32 11.1.3 Persistent Organic Pollutants (POPs) & the Stockholm Convention............................. 33 11.2 Survey Results ....................................................................................................................... 33 11.2.1 Summary ....................................................................................................................... 34 11.2.2 Dioxins ........................................................................................................................... 34 11.2.3 PCBs............................................................................................................................... 34 11.2.4 Dioxins & PCBs .............................................................................................................. 34 11.2.5 Comparison with earlier surveys and with other international studies. ...................... 34 11.2.6 Brominated Dioxins and Furans (PBDD/PBDF) ............................................................. 36 11.3 Brominated Flame Retardants (BFR) Study. ......................................................................... 36 11.3.1 General .......................................................................................................................... 36 11.4 Non Dioxin PCB results .......................................................................................................... 38 11.5 Conclusions and Outlook ...................................................................................................... 38 12. EMEP and Air quality research .................................................................................................. 39 12.1 European Monitoring and Evaluation Programme (EMEP) .................................................. 39 12.2 Air quality research ............................................................................................................... 40 12.2.1 Title: National mapping of GHG and non‐GHG emissions sources, Ole‐Kenneth Nielsen, Aarhus University ............................................................................................................ 42 12.2.2 Title: Particulate Matter from Diesel Vehicles: Emission and Exposure in Ireland, A. McNabola, University of Dublin, Trinity College (TCD) ................................................................. 42 12.2.3 Title: AEROSOURCE, C. O’Dowd, National University of Ireland Galway (NUIG) .......... 42 13. Key Statistics from Air Enforcement ......................................................................................... 43 14. Conclusion and future challenges ............................................................................................. 44 Appendix A – Summary data tables ...................................................................................................... 46 References ............................................................................................................................................ 69 4
Air Quality In Ireland 2015 Index of figures Figure 1.1 Impacts of air pollution (source: EEA 2014) ......................................................................... 13 Figure 1.2 EU vs WHO exposure levels to air pollution (source: EEA 2014) ......................................... 15 Figure 1.3 Air quality zones in Ireland in 2015...................................................................................... 15 Figure 1.4 Air Quality Monitoring Stations in 2015 .............................................................................. 16 Figure 1.5 Concentrations of NO2 across EU Member States in 2013 .................................................. 16 Figure 2.1 Trend in NO2 concentrations for zones in Ireland 2005 ‐ 2015 ........................................... 17 Figure 3.1 Annual mean SO2 concentrations 2005 ‐ 2015 ................................................................... 18 Figure 4.1 8‐hour maximum CO concentrations in Cork and Dublin, 2004 ‐ 2015 ............................... 19 Figure 5.1 Annual Mean Ozone concentrations across Europe 2013 ................................................... 20 Figure 5.2 8‐hour daily maximum concentrations at individual stations compared to the WHO guideline value for ozone...................................................................................................................... 21 Figure 5.3 AOT40 at rural background stations, 2004 ‐ 2015 ............................................................... 21 Figure 6.1 Annual mean PM10 concentrations 2005‐2015.................................................................... 22 Figure 6.2 PM10 concentrations across Europe in 2013 ........................................................................ 23 Figure 7.1 Annual mean PM2.5 concentrations 2009‐2015 ................................................................... 25 Figure 8.1 Annual mean concentrations for VOC ozone precursors including Benzene at Rathmines, Dublin 2005‐2015.................................................................................................................................. 26 Figure 9.1 Lead, Arsenic, Cadmium, Nickel concentrations in Ireland 2009 ‐ 2015 ............................. 28 Figure 10.1 Annual mean PAH (BaP) concentration 2009‐2015 ........................................................... 30 Figure 10.2 Annual mean values for PAH (BaP) at individual stations in Ireland in 2015 with reference to EEA air quality estimated reference level for BaP ............................................................................ 30 Figure 11.1 Dioxins/Furans 2015 ‐ Data Compared with 2000‐2015 Averages .................................... 35 Figure 11.2 Dioxins/Furans + PCBs 2015 ‐ Data Compared with 2000‐2015 Averages ........................ 36 5
Air Quality In Ireland 2015 Index of tables Table 11.1 Summary of dioxin survey results 2015 .............................................................................. 35 Table 11.2 Summary of milk fat data for PBDEs ................................................................................... 37 Table 12.1 summary of ongoing EPA funded air quality related projects ............................................ 41 Table A1 Summary of the Air Quality Directive's limit values, target values, long‐term objectives, information and alert threshold values for the protection of human health....................................... 46 Table A2 WHO air quality guidelines (AQG), interim targets (IT) and EEA estimated reference levels (ERL) for PM, O3, NO2, BaP, SO2, CO, and toxic metals, in μg/m3, excepting BaP, CO, Cd and Pb. ..... 47 Table A3 Summary of Air Quality Directive critical levels, target values and long‐term objectives for the protection of vegetation................................................................................................................. 48 Table A4 Summary statistics for hourly NO2 concentrations in Ireland in 2015 .................................. 49 Table A5 Summary statistics for hourly NOX concentrations in Ireland in 2015 .................................. 50 Table A6 Summary statistics for hourly SO2 concentrations in Ireland in 2015 ................................... 51 Table A7 Summary statistics for rolling 8‐hour CO concentrations in Ireland in 2015......................... 52 Table A8 Summary statistics for rolling 8‐hour ozone concentrations in Ireland in 2015 ................... 53 Table A9 AOT40 values from rural stations (Zone D) in Ireland, 2010 – 2015...................................... 54 Table A10 Summary statistics for daily PM10 concentrations in Ireland in 2015 .................................. 55 Table A11 Summary statistics for daily PM2.5 concentrations for Ireland in 2015 ............................... 56 Table A12 Summary statistics for chemical composition of PM2.5 in 2015 .......................................... 57 Table A13 Summary statistics for daily benzene concentrations in Ireland in 2015 ............................ 58 Table A14 Summary statistics for daily ozone precursor VOCs concentrations at Rathmines in 2015 59 Table A15 Summary statistics for daily ozone precursor VOCs concentrations at Kilkenny in 2015 ... 60 Table A16 Summary statistics for monthly lead, arsenic, cadmium and nickel concentrations in Ireland in 2015 ...................................................................................................................................... 61 Table A17 Summary statistics for monthly mercury concentrations in 2015 ...................................... 62 Table A18 Summary statistics for monthly metal deposition concentrations in 2015......................... 63 Table A19 Summary statistics for monthly PAH concentrations in 2015 ............................................. 64 Table A20 Summary statistics for monthly PAH deposition concentrations in 2015 ........................... 65 Table A 21 Summary statistics for daily ozone precursor VOCs concentrations at Portlaoise in 2015 66 Table A22 Milk fat related PCDD/F and PCB‐TEQ values determined in the background samples A1 ‐ A 25 .......................................................................................................................................................... 67 Table A23 Milk fat related PCDD/F and PCB‐TEQ values determined in the potential impact samples B1 ‐ B 18 ................................................................................................................................................ 68 6
Air Quality In Ireland 2015 Acknowledgments The author wishes to acknowledge the contributions of his colleagues, Kevin Delaney, Patrick Malone, Lin Delaney, Cathal Ruane, Patrick Kenny and Barbara Rafferty in the National Ambient Air Quality Programme. Additional support in monitoring and analysis is provided by EPA staff in Dublin, Castlebar, Monaghan, Mallow and Limerick with support in data collection and reporting from colleagues in the Environmental Research Centre, Air Cross Office Team, IT and GIS teams. The input of personnel from local authorities, the Health Service Executive, Met Éireann and NUI Galway and others who provided data for inclusion in this report is also acknowledged 7
Air Quality In Ireland 2015 Glossary > Greater than AOT40 This is a measure of the overall exposure of plants to ozone. It is the sum of the excess hourly concentrations greater than 80 µg/m3 and is expressed as ug/m3 hours. Only values measured between 08:00 and 20:00 Central European Time each day from May to July are used for the calculation. (The name AOT40 refers to 40ppb which is the same as 80 µg/m3) As Arsenic AEI Average exposure indicator Assessment Threshold Concentration at which varying levels of monitoring must be implemented Cd Cadmium CAFE Clean Air for Europe Directive (2008/50/EC) CEC Council of the European Communities C6H6 Benzene CLRTAP Convention on Long‐Range Transboundary Air Pollution CO Carbon monoxide DECLG Department of Environment, Community and Local Government EC European Commission EC/OC Elemental carbon/organic carbon EMEP European Monitoring and Evaluation Programme EPA Environmental Protection Agency EU European Union Hg Mercury LAT Lower assessment threshold Limit value Level to be attained and not exceeded mg/m3 Milligrammes per cubic metre na Not applicable ng/m3 Nanogrammes per cubic metre NH3 Ammonia Ni Nickel 8
Air Quality In Ireland 2015 NO Nitric oxide NO2 Nitrogen dioxide NOx Oxides of nitrogen O3 Ozone PAH Polycyclic aromatic hydrocarbon Pb Lead PM10 Particulate matter with diameter < 10 µm PM2.5 Particulate matter with diameter < 2.5 µm ppb Parts per billion SO2 Sulphur dioxide Target value Level to be attained where possible over a given period Troposphere Region of the atmosphere from ground level to ~10‐15 kilometres Stratosphere Region of the atmosphere from ~15 kilometres to 50 kilometres VOCs Volatile organic compounds yr year UAT Upper assessment threshold µm Micron µg/m3 Microgrammes per cubic metre µg/m3.h Microgrammes per cubic metre hours µg/m2/day Microgrammes per square metre per day Zone A Dublin Zone B Cork Zone C Galway, Limerick, Waterford, Clonmel, Kilkenny, Sligo, Drogheda, Wexford, Athlone, Bray, Carlow, Dundalk, Ennis, Naas, Tralee, Celbridge, Letterkenny, Mullingar, Navan, Newbridge, Portlaoise, Greystones and Leixlip. Zone D Remainder of State (excluding Zones A, B and C) 9
Air Quality In Ireland 2015 Executive Summary Air Quality in Ireland 2015 Air monitoring data from 31 stations in the National Ambient Air Quality Monitoring Network was assessed against legislative limit and target values for the protection of human health and vegetation. Air monitoring data was also compared to the World Health Organisation (WHO) guideline values (EEA estimated reference level used for PAH). Report highlights include: No levels above the EU limit value were recorded at any of the ambient air quality network monitoring sites in Ireland in 2015 WHO guideline values were exceeded as follows: Ozone at 7 monitoring sites Particulate Matter PM10 at 16 monitoring sites (24hr WHO guideline) Particulate Matter PM2.5 at 8 monitoring sites (24hr WHO guideline) Particulate Matter PM2.5 at 1 monitoring site (annual WHO guideline) EEA reference levels were exceeded as follows PAH at 4 monitoring sites The dioxin survey 2015 shows levels recorded are similar or lower than those from previous surveys and from studies undertaken in other EU countries This report summarises the current state of research in air quality supported by the EPA in 2015 This report also summarises some key statistics from work undertaken in air enforcement in 2015 by the EPA. Challenges The links between poor air quality and human health are well understood with the 2014 report by the European Environment Agency (EEA) estimating that around 1,200 deaths in Ireland in 2012 were directly linked to air pollution, while for Europe the figure was approximately 400,000 deaths. It is now apparent that the EU limit value levels are inadequate to protect people from the harmful effects of air pollutants and the WHO has intimated that there is no safe limit for air pollution. Along 10
Air Quality In Ireland 2015 with the clear health benefits in improving air quality in Ireland, there is also an economic saving in doing so, highlighted by the recent OECD report on the economic cost of air pollution (OECD 2016). In general air quality in Ireland is good and compares favourably with other EU member states, largely as a result of our relative absence of large cities, weather and access to predominantly clean air masses from the south west. However this status is a comparison, relative to our European neighbours many of whom are in exceedance of EU limit values for pollutants such as particulate matter, ozone and nitrogen dioxide. It is also much too dependent on the vagaries of our weather. When we compare our air quality levels to those recommended by the World Health Organisation, the situation is less positive. We face challenges in reducing our levels of particulate matter (both PM10 and PM2.5) and ozone to below those recommended by the WHO Air Quality Guidelines. Particulate matter in Ireland is predominantly sourced from solid fuel burning and it is in this area where much of the reductions can be made. As the improvement in our economy continues we will also face challenges to comply with EU legislation for pollutants emitted from car exhausts. Economic activity will likely be mirrored by increases in NOX emissions, particularly in urban areas. City centre and urban monitoring sites in Ireland are approaching EU limit values for NO2, and it is probable that we will see limit value exceedances in the near future unless mitigation steps are taken. Actions A key part of the approach to tackling these issues is better engagement with the public on the topic of air quality. The first step in this process is an increased access to air quality data and information. This is highlighted in the EPA’s proposed National Ambient Air Quality Monitoring Programme (AAMP) which is currently out for public consultation. This programme proposes three main pillars along with under‐pinning supporting actions: A greatly expanded national monitoring network Modelling and forecasting capability Citizen engagement and citizen science initiatives Coinciding with the introduction of this AAMP, the EPA is now calling for movement towards the adoption of the more health appropriate WHO Air Quality Guidelines, in particular for particulates and ozone, as the legal standards across Europe and in Ireland. Reductions in levels of particulate matter in Ireland can begin with the consumer, who once properly informed can make decisions that will impact on their local air quality, particularly with regard to their choice of home heating fuel. Any shift from burning of solid fuel to cleaner, more energy efficient methods of home heating will result in cleaner air quality for the consumer, their family and neighbours with a resultant improvement in their health. With regard to vehicle exhaust emissions, although it is hoped that technological advances will go some way to addressing this issue, this approach cannot be solely relied upon and complimentary measures to mitigating the problem will be needed such as the transition of individuals from private fossil fuel powered motor cars to alternative modes of transport such as walking, cycling and public transport and policy incentives to promote a transition to more environmentally friendly and sustainable options such as electric motor powered vehicles. 11
Air Quality In Ireland 2015 The scientific community’s understanding of air pollution and its health implications is constantly evolving and we need to work to communicate these changes and their importance to the public and policy makers. This understanding will be crucial for individuals to make informed decisions on a range of choices that have implications on their local air quality. Although the problems are many, they are not insurmountable and it is heartening to know that the power to make changes and provide solutions is within our control. Measures such as policy changes, price incentives, and provision of clean alternatives for transport and home heating, support for clean air choices, education and the decisions made by individual consumers all have a role to play in maintaining and improving our air quality. 12
Air Quality In Ireland 2015 1. Introduction Air pollution and human health National Ambient Air Quality Air pollution is the single largest environmental Monitoring Programme health risk in Europe (EEA 2015). Cardiovascular In order to protect our health, vegetation and complications like heart disease and stroke are the ecosystems, EU Directives set down air quality main causes of premature death attributed to air standards for a wide variety of pollutants. The pollution (WHO 2014). Air pollution itself is current standards are contained in the Clean Air for responsible for 80% of cases of premature death in Europe (CAFE) Directive (EP & CEU, 2008) and the Europe (2014). This negative impact on human Fourth Daughter Directive (EP & CEU, 2004). These health also has considerable negative impact on Directives also include rules on how Member States European member state economies, with working should monitor, assess and manage ambient air days lost, reduced productivity and increased quality. medical costs (OECD 2016). The EPA, as the National Reference Laboratory, is tasked with coordinating and managing this Air pollution, ecosystems and climate monitoring programme. A nationwide network of 31 Air pollution also has impacts on vegetation, soil monitoring stations measures levels of air pollutants and water quality. For example NH3, NOX and SO2 in each zone and delivers this information in real‐ contribute to the acidification of soil and water and time to the public at www.airquality.epa.ie. ground‐level ozone damages agricultural crops, forests and plants. Many air pollutants are also The EPA has issued for public consultation a National climate forcers – for example the black carbon Ambient Air Quality Monitoring Programme, which constituent of particulate matter and tropospheric will includes a proposed revision of the monitoring ozone to name but two. Figure 1.1 shows an network and crucial actions to increase provision of overview of the impacts of air pollution. air quality information to the public and improve citizen engagement in this area. Figure 1.1 Impacts of air pollution (source: EEA 2014) 13
Air Quality In Ireland 2015 Report objectives and coverage Irish and EU air quality legislation This report provides an overview of the situation The EPA is the designated competent authority for the for ambient air quality in Ireland in 2015. It is implementation of all Irish and EU ambient air quality based on monitoring data from 31 stations that legislation. It is assisted in its role by the local authorities and were in operation during the year. Measured other partners, and it carries out ambient air quality concentrations are compared with both: EU monitoring, which contributes to what is known as the legislative standards and WHO air quality ‘National Ambient Air Quality Monitoring Network’. The EPA guidelines) for a range of air pollutants. The air manages this monitoring network and is responsible for all quality analysis presented here is based on reporting to stakeholders – which include the public and the concentration measurements of the following EU. The EPA is also the National Reference Laboratory (NRL) pollutants: for air quality for Ireland. sulphur dioxide; The results of air quality monitoring in 2015 presented in this report are compared to the limit and target values in the nitrogen dioxide and oxides of nitrogen; latest EU legislation, the Clean Air for Europe (CAFE) Directive carbon monoxide; (EP and CEU, 2008) and the Fourth Daughter Directive (EP ozone; and CEU, 2004). The CAFE Directive is an amalgamation of the Air Quality Framework Directive and its subsequent First, particulate matter ‐ PM10 and PM2.5; Second and Third Daughter Directives. The CAFE Directive benzene and volatile organic compounds was transposed into Irish legislation by the Air Quality (VOCs); Standards Regulations 2011 (S.I. No. 180 of 2011).The 4th Daughter Directive was transposed by the Arsenic, Cadmium, heavy metals ‐ lead, arsenic, cadmium, Mercury, Nickel and Polycyclic Aromatic Hydrocarbons in nickel and mercury; Ambient Air Regulations 2009 (S.I. No. 58 of 2009). polycyclic aromatic hydrocarbons (PAH); Further details on air quality legislation can be found at elemental carbon/organic carbon www.epa.ie/air/quality/standards/ and in previous air quality (EC/OC) as part of PM2.5 speciation; and reports www.epa.ie/pubs/reports/air/quality/. anions and cations as part of PM2.5 speciation. WHO air quality guidelines The pollutants of most concern in terms of health This report makes reference to the World Health impacts are particulate matter, PAH and, to a Organisation (WHO) air quality guidelines for particulate lesser extent, ozone and nitrogen dioxide. The matter (PM10), ozone, nitrogen dioxide and sulphur dioxide sources and impact of these air pollutants, (WHO, 2005); and also the WHO air quality guidelines current levels in Ireland and trends over time for update, which includes PM2.5 (Air Qual Atmos Health, 2008). each pollutant are outlined in this report. A These guidelines were developed by the WHO, to inform chapter on dioxins in the Irish environment is policy makers and provide appropriate air quality targets also included. Dioxins are not included in the air worldwide, based on the latest health information available. quality network but are measured separately in Figure 1.2 below details a comparison of EU limits and WHO milk samples. guideline values for six pollutants in EU urban areas (WHO guideline for BaP in the figure below is based on the EEA air quality reference level). When the stricter WHO guideline values are applied a significantly higher proportion of the urban population are exposed to harmful levels of air pollution (EAA, 2014). 14
Air Quality In Irreland 2015 2 Figurre 1.2 EU vs WHO W exposure levels to air pollution p (sourrce: EEA 2014)) Air qualitty zones 2015 2 EU legislatioon on air quaality requiress that Membber States divvide ory into zonees for the asssessment annd management their territo of air qualitty. The zoness in place in Ireland in 22015 are shoown in Figure 1.33. Zone A is the Dublin conurbationn, Zone B is the Cork conurb bation with Zone C com mprising 23 large townss in Ireland with h a populatiion >15,000. Zone D is the remain ning area of Irelaand. The air quaality in each h zone is asssessed and classified with w respect to uupper and lower assesssment threshholds based on measurements over thee previous fiive years. Uppper and low wer assessment thresholds are prescriibed in the legislation for each pollutaant. The num mber of monitoring locat ions required is dependent o on populatio on size and whether w ambbient air quaality concentratioons exceed the upper assessment threshold, are between the upper and d lower asseessment thr esholds, or are below the lo ower assessmment threshoold. Figurre 1.3 Air quallity zones in Irreland in 2015 15
Air Quality In Irreland 2015 2 Air A qualitty monittoring ne etwork 2015 2 The T 31 mo onitoring sttations tha at were employed in 2015 and whose w data was w used in n compiling this annual report are shown s in Figure 1.4. Th here were no changes to o the air quality monittoring netwo ork in 2015. European E air qualitty Since the 19770s the EU has attempte ed to use environmentaal policy as the t main insstrument to o improve air quality. To o a large exttent this has been very succeessful, with h great eductions in the primaryy pollutants across re a all member m sstates andd a no oticeable im mprovementt in air qu uality. Howe ever, air pollution scieence is also improving and our understanding of the impact of poor p air quality on health is growing an nd new Figure 1.4 Aiir Quality Mon nitoring Statioons in 2015 hallenges aree facing Euro ch ope over thee coming decades. In late 201 13, the European co ommission p proposed a new n Clean Air A Policy Package for Europe, wh hich aims to o ensure co ompliance w with existingg legislation by 2020 and to further improve Eu urope’s air quality by 2030 and th hereafter (EC C 2013). Figgure 1.5 sh hows annual average concentrattions of nitrogen dioxxide (NO2) for the Europe ean wide monitoring m network (please note that these graphs are p produced using 2013 airr quality data). As eevident in the graphics NO2 exceedances are very com mmon acrosss most of Europe, indiccating that NO2 is a problem pollutant for European member states. Figure 1.5 Co oncentrations of NO2 acrosss EU Member States S in 2013 16
Air Quality In Ireland 2015 2. Nitrogen oxides (NOX) Where does NOX come from? Why do we monitor NOX? NOX refers to the two pollutants: nitric oxide (NO) and nitrogen dioxide NO2 concentrations are closely associated with (NO2). They are produced during combustion at high temperatures with traffic volumes. As a result, sensitive individuals the main sources in Ireland coming from vehicles and power stations. including asthmatics, elderly people and The industrial sector is also a significant contributor to NOX levels in children are more susceptible to NO2 exposure Ireland, particularly the cement production industry. The majority of closer to heavily trafficked roadways. Elevated NOX emissions are comprised of NO, with typically 5 ‐ 10% being directly NO2 exposure can lead to health impacts emitted NO2. Diesel engines tend to emit a higher percentage of NO2. including Details with regard to ambient air quality standards and WHO guideline respiratory related issues values for NOx and other pollutants are listed in Appendix A. liver impacts Elevated NOX concentrations impact on 2015 Results and trends ecosystems. NOX levels can contribute to the acidification and eutrophication of soils and 50 water, which can lead to changes in species 45 Annual limit value diversity. NOX also acts as a precursor to ozone 40 and also is involved with the production of 35 secondary organic aerosol (SOA). Annual Mean µg/m3 30 Zone A Traffic 25 Zone A Background Outlook for NOX levels in Ireland 20 Zone B 15 Traffic Due to our continued reliance on fossil fuelled 10 Zone C combustion engine transport, NO2/NOX levels 5 will remain a problem pollutant in our Irish Zone D towns and cities. In fact, the problem will likely 0 be exacerbated with the continued increase in economic activity, as NOx concentrations would be expected to rise accordingly. Coupled with Figure 2.1 Trend in NO2 concentrations for zones in Ireland 2005 ‐ 2015 favourable meteorological conditions for the build‐up of NO2, it is probable that we will see exceedances of the NO2 limit value in the near NO2 concentrations were monitored at 15 locations across Ireland in future. Although there is some hope that 2015. NO2 values for all monitoring sites in Ireland were below the technological advances in the future may lead annual limit value in 2015. Details regarding annual averages and other to lower NOX emissions from individual cars statistics are available in Table A4 of Appendix A. (EURO 6 emissions standards), this technology Figure 2.1 shows the trend for NO2 across Ireland for 2005 to 2015. will take time to make an impact on the levels Levels across all zones of Ireland have remained relatively static since as they stand. A more certain route to 2005, with signs of a slight increasing trend in the years 2008 ‐ 2010. mitigating the problem of NOX, is for individuals During this period NO2 levels were close to the limit value at Dublin City to prioritise public transport and alternative and Cork City centre monitoring sites, with the limit value exceeded in modes of transport over use of the private Dublin in 2009. However, NO2 levels decreased in general from 2010 to motor car. Transport policy in Ireland should 2012. This downward trend appears to have stabilised with NO2 values also further reflect this priority and should go showing something of an increase again in 2013 and 2014 at some further in attempting to tackle the problem of locations, such as the Zone B traffic site. air pollution, whether through the use of alternative modes of transport or alternative The reason for the decrease in NO2 concentrations from 2010 to 2012 fuels, including electric motor powered could partly be due to meteorological conditions (a predominance of transport. wet and windy weather), as well as a decrease in traffic numbers for the period, reflective of the downturn in the economy. 17
Air Quality In Ireland 2015 3. Sulphur dioxide (SO2) Where does SO2 come from? Why do we monitor SO2 SO2 is a gas which is formed when sulphur containing fuels Health effects from elevated levels of SO2 include (mainly coal and oil) are burned in power stations, domestically, Aggravation of asthma and elsewhere. Volcanic eruptions are the predominant natural source of sulphur dioxide. Reduce in lung function Details with regard to ambient air quality standards and WHO Inflammation of the respiratory tract guideline values for SO2 and other pollutants are listed in General discomfort, anxiety and headaches Appendix A. SO2 is also a contributor to acidification of rivers and lakes. 2015 Results and Trends Outlook for SO2 concentrations in Ireland 25 Smaller towns may be more vulnerable Vegetation annual limit value 20 to higher SO2 levels due to increased coal or peat usage. Although it is Annual Mean µg/m3 Zone A (traffic) expected that SO2 concentrations across 15 Zone A (background) Ireland will remain low for the Zone B foreseeable future, it will be important 10 Zone D for the consumer to maintain awareness of their choice of home heating fuel and where possible to 5 choose cleaner alternatives over coal and peat. Further volcanic activity in Iceland, due to its ability to influence 0 SO2 concentrations here in Ireland, must 2005 2006 2007 2008 2009 2010 2011 2012 2013 2014 2015 also be monitored in the future. Figure 3.1 Annual mean SO2 concentrations 2005 ‐ 2015 SO2 was measured at 10 stations in 2015. The results of individual stations are listed in Table A6 of Appendix A. No exceedances of the daily EU limit or the WHO guideline values were recorded in 2015. Figure 3.1 shows the trend in annual mean SO2 concentrations across Ireland since 2005. Levels have been consistently low in Ireland in that period. This is reflective of the shift in fuel choice across Ireland in both the residential heating sector and the energy production sector, from sulphur containing bituminous coal to those fuels which are low in SO2 production such as natural gas. 18
Air Quality In Ireland 2015 4. Carbon monoxide (CO) Where does CO come from? Why do we Monitor Carbon Monoxide? Carbon monoxide is a colourless gas, formed from incomplete Elevated concentrations of carbon monoxide in oxidation during combustion of fuel. Sources of CO in Ireland are ambient air can lead to mainly from vehicles, although tobacco smoke and poorly heart disease adjusted and maintained combustion devices, such as boilers, contribute also. CO concentrations tend to be higher in areas with damage to the central nervous system heavy traffic congestion. fatigue and headaches Details with regard to ambient air quality standards and WHO guideline values for CO and other pollutants are listed in Appendix A. 2015 Results and Trends 12 Limit vlaue 10 8 Dublin mg/m3 6 Cork 4 2 0 2005 2006 2007 2008 2009 2010 2011 2012 2013 2014 2015 Outlook for CO concentrations Figure 4.1 8‐hour maximum CO concentrations in Cork and Dublin, 2004 ‐ Carbon monoxide concentrations in Ireland 2015 are expected to stay low for the foreseeable future. CO was measured at five locations in 2015; the results are detailed in Table A7 of Appendix A. Levels in 2015 are very similar to concentrations observed in from 2005 to 2014 and are below the limit value. Measured concentrations were also below the WHO air quality guideline values. Trends in CO concentrations in Dublin and Cork since 2005 are shown in Figure 4.1. Levels have remained low over the period with all levels recorded below the limit value set out in the CAFE Directive and WHO guideline. 19
Air Quality In Irreland 2015 2 5. Ozone (O3) Where W do oes ozone come Why d do we mon nitor ozone e? frrom? Elevatedd concentrattions of ozone can decrrease lung fu unction. It can also Ozzone is forrmed as a secondary aggravaate respirato ory ailmentss in sensitivve individuals e.g. asth hmatics, poollutant in the tropospherre from the individuuals with lungg disease ch hemical reacction of NO OX, CO and olatile organic compounds (VOCs) in vo th he presence of sunlight. Ozone can Ozonee ‐ A transb boundary issue alsso be preseent in the troposphere duue to down nward flux from the ozzone‐rich sttratosphere, where it occcurs naturally and has an n important ro ole in abssorbing harmful UV radiation. Ozone is readily traansported from Atlaantic and Euuropean regions due to the t natural movement off air massess. Ground‐ levvel ozone is depleted d through re eactions w with trafffic‐emitted poollutants; theerefore levels of ozone ural areas than in urban arre higher in ru arreas. Deetails with regard to ambient air quuality standards and WHO O guideline vaalues for ozone and otherr pollutants arre listed in TTable A1, Table A2 and Taable A3 of Appendix A. Figure 5..1 Annual Mea an Ozone conccentrations accross Europe 2013 2 Figure 55.1 shows thhe concentra ations of ozoone in Irelan nd in the Eu uropean context . The impaccts of ground level ozonne can be seen s in central and southerrn Europe, paarticularly byy those counntries with larger cities and high sunshin e levels. How wever the inffluence of baackground levvels of ozonee can be seen aalong the western se eaboard, wiith Ireland experiencin ng this phenommenon. Ozone cconcentrations are strong gly influenceed by meteorrological connditions; stable aanticyclones over o Ireland with warm s unny weathe er are more likely l to producee higher levvels of ozone. This ca n arise from local em missions; particul arly the interaction of oxxides of nitroggen, VOCs annd sunlight or o it can be duee to transbo oundary sources from tthe rest of Europe and d other contine nts. The lack of high presssure stable aiir masses durring recent su ummers is refleccted in the relatively low le evels of ozonne observed during d these years. y 20
Air Quality In Ireland 2015 2015 Results and Trends Outlook for ozone concentrations in 160 Ireland 8-hr daily maximum µg/ m3 140 120 Short acute ozone pollution WHO guideline 100 episodes are infrequent in 80 Ireland; however they have 60 happened in the past and will 40 happen in the future. They 20 0 are most likely to occur in Zone A (Dublin) Zone B (Cork) Zone C (21 Zone D summer months when there biggest towns) (remainder of is a stable anti‐cyclone over country) Ireland bringing settled, warm weather. Movement of Figure 5.2 8‐hour daily maximum concentrations at individual stations compared polluted air masses from to the WHO guideline value for ozone Europe are more likely to occur during these periods, Ozone concentrations recorded in 2015 were below the EU limit value for with the air masses likely to human health. There were six days recorded with maximum average 8‐hour mean concentrations >120 µg/m3, all at our Monaghan remote site – Kilkitt. contain high levels of ozone. When compared to the WHO guideline value shown in Figure 5.2, seven monitoring stations were above this guideline value. Summary statistics for Because ozone levels in individual stations are contained in Table A8 of Appendix A Ireland are highly influenced by transboundary sources, 9000 attainment of the Long‐Term 8000 Galway objective (LTO) and remote 7000 Long‐term objective compliance with the WHO Monaghan guideline value will only occur AOT40 (µg/m3).h 6000 remote 5000 Laois should hemispheric ozone regional 4000 Kerry remote levels reduce. This will require a European, and possibly 3000 Mayo near global, effort to reduce 2000 town emissions of ozone 1000 precursors. 0 Figure 5.3 AOT40 at rural background stations, 2004 ‐ 2015 Figure 5.3 shows the AOT40 for five rural background stations for the years 2005‐2015. The AOT40 is an indicator of exposure of vegetation to ozone during the growing season, when vegetation is more susceptible to damage from pollutants. Rural background stations are classified as remote, regional or near‐city depending on their proximity to urban areas. Ozone levels are higher in remote regions and tend to be highest along the western seaboard (indicated by the Galway and Kerry sites) and lower in the east of the country (indicated by the Monaghan site). 21
Air Quality In Ireland 2015 6. Particulate matter (PM10) Where does particulate matter (PM10) come from? Why do we monitor PM10? PM10 are particles with diameters of 10 μm or less. These particles can Elevated levels of PM10 can cause the include direct emissions such as dust, emissions from combustion following health effects: engines, emissions from the burning of solid fuels or natural sources cardiovascular disease such as windblown salt, plant spores and pollens. These direct emissions are known as primary PM10. PM10 can also be produced indirectly by lung diseases formation of aerosols as a result of reactions of other pollutants such as heart attacks and arrhythmias NOX and SO2; these are known as secondary PM10. In Ireland the main sources are solid fuel burning and vehicular traffic. Agriculture is also a significant source of secondary particulate matter, primarily through formation of aerosols from ammonium nitrates for example. Details with regard to ambient air quality standards and WHO guideline values for ozone and other pollutants are listed in Table A1, Table A2 and Table A3 of Appendix A. 2015 Results and Trends 50 45 Annual limit value 40 Zone A traffic Annual Mean µg/m3 35 Zone A background 30 Zone B traffic 25 WHO air quality guideline Zone C 20 Zone D 15 10 5 0 2005 2006 2007 2008 2009 2010 2011 2012 2013 2014 2015 Figure 6.1 Annual mean PM10 concentrations 2005‐2015 PM10 was monitored at eighteen stations across Ireland in 2015; the results and summary statistics for individual stations are available in Table A10 of Appendix A. Mean concentrations are below the annual limit value of 40 µg/m3. With respect to WHO air quality guideline values, no monitoring stations exceeded the annual guideline value. However, when measuring against the WHO 24‐hour mean guideline value (50 µg/m3), sixteen monitoring stations had daily mean values > 50 µg/m3. Figure 6.1 displays the trend in PM10 annual mean concentration from 2005 to 2015. In cities, traffic emissions are the main source of PM10, while in smaller towns or those areas not connected to the natural gas grid, emissions from residential solid fuel combustion dominate. The air quality in cities benefits from increased use of gas in place of solid fuel, and a ban on the use of bituminous coal, with the result that levels of PM10 are similar across all zones. Despite large differences in population number Zone D has similar PM concentrations compared to Zones A and B. This is most likely due to residential solid fuel emissions in Zone D which in this zone are a more significant source than traffic emissions. 22
Air Quality In Irreland 2015 2 Ou utlook for P PM10 conccentrationss Loooking at the ttrend analyssis for the lasst decade (Figgure 6.1) it is clear that there t has beeen no discerrnible decreaase in PM P 10 concen ntrations acrooss Ireland. Although A aveerage concentrations are e below the EU limit valu ue, they bord der the e WHO air qu uality guideline value. To o see a reduuction in the impact of PM P 10 on the hhealth of thee populationn, a connsistent decrrease in emissions is req quired. The i mpetus for thist decrease e could comme from an adoption of the t WH HO air qualityy guideline value v across the EU. The reductions in emissions across Irela nd will require a changee in the e choices individual custo omers make in the fuels tthey use to heat their ho omes, with a significant shift s from so olid fue el use to cleaaner alternattives. Impro oving the awwareness of consumers c of o the relatioonship betwe een health and air quality and ssupporting clean c air choices, will be eessential to achieve thesse goals. PM M10 ‐ a Euro opean view w Figu ure 6.2 PM10 cconcentrationss across Europ pe in 2013 As can be seen from Figuree 6.2 above forf 2013, PM M10 concentraations vary considerably c throughout Europe. Mu uch of this t variation n stems from m dominant fuel f use on a regional basis, for taskss such as hom me heating oro even the use u of solid s fuel forr outdoor coo oking, with the t use of woood in the Mediterranea M n states a siggnificant sou urce of PM. 23
Air Quality In Ireland 2015 7. Particulate matter (PM2.5) Where does particulate matter PM2.5 come from? Why do we monitor particulate matter PM2.5? PM2.5 or ‘fine’ particulate matter is particle pollution made of a mixture of solids and liquids of size 2.5 μm or less. It is composed of a number of PM10 and PM2.5 include inhalable particles that varying components depending on its source. These can include acids such are small enough to penetrate the thoracic as nitrates and sulphates, VOCs, metals, and soil or dust particles. This region of the respiratory system. The health PM2.5 can be emitted directly into the atmosphere or can be formed effects of inhalable PM are well documented. secondarily. For example, sulphate particles are formed by the chemical They are due to exposure over both the short reaction of SO2 in the atmosphere after its release from power plants or term (hours, days) and long term (months, industrial facilities. PM2.5 is considered a better indicator of man‐made years) and include: particulate matter than PM10. respiratory and cardiovascular Details with regard to ambient air quality standards and WHO guideline morbidity, such as aggravation of values for PM2.5 and other pollutants are listed in of Appendix A asthma, respiratory symptoms and an increase in hospital admissions; mortality from cardiovascular and respiratory diseases and from lung cancer (WHO, 2013) National Emission Reduction Target for PM2.5 The CAFE Directive (2008/50/EC) requires Member States to determine the PM2.5 average exposure indicator (AEI). The value will decide the national exposure reduction target (NERT) which must be met by 2020. Based on historical levels of PM2.5, Ireland is required to reduce levels by 10% on or before 2020. This equates to a 1µg/m3 reduction from 10.4µg/m3 to 9.4µg/m3. 24
Air Quality In Ireland 2015 Data 2015 Results 30 Annual limit value 25 Coleraine St. 20 Annual Mean µg/m3 Rathmines Marino 15 Cork Ennis Longford 10 Claremorris WHO air quality guideline Bray 5 Finglas 0 2009 2010 2011 2012 2013 2014 2015 Figure 7.1 Annual mean PM2.5 concentrations 2009‐2015 The CAFE Directive introduced mandatory monitoring of PM2.5. Figure 7.1 details results at 7 stations from 2009 to 2015. Levels in Ireland are below both the stage one and stage two limit values of 25 and 20 µg/m3 (stage one was to be attained by 2015, with stage two attainment by 2020). PM2.5 results for individual stations are detailed in Table A11 of Appendix A. With regards to WHO air quality guideline values, Ireland exceeds the annual WHO guideline value for PM2.5 at 1 of the 9 stations monitored. When looking at the 24hr average WHO guideline value, 8 out of the 9 monitoring stations are above this guideline value. Summary statistics for chemical composition of PM2.5 in 2015 are shown in Table A12 of Appendix A Outlook for PM2.5 concentrations There have been no exceedances of the EU limit value for PM2.5 (25µg/m3) in Ireland. However as can be seen from Figure 7.1 concentrations in general are above the WHO air quality guideline value. PM2.5 is considered a better marker than PM10 for anthropogenic air pollution and thus it is evident in Ireland that human activities are impacting on air quality with the potential to negatively impact on human health. The levels observed have a variety of sources including contributions from the commercial, industrial, and agriculture sectors. However the largest contribution in Ireland comes from the residential sector with solid fuel combustion being the predominant source. Steps have been taken in recent years to mitigate this problem with the extension of the bituminous coal ban; however a total shift from solid fuel combustion is needed before large improvements will be noticed. Under the National Emissions Reduction Target (NERT) set for each country by the European Commission, Ireland’s obligation is to decrease PM2.5 concentrations by 10% by 2020. The timely implementation of sectoral emission reduction polices will be key to achieving this target. One aspect of particulate matter pollution which may be important in the future is ‘black carbon’. Black carbon is the fraction of PM2.5 which strongly absorbs light, and it may be included into the National Emissions Ceiling Directive in the future. Black carbon is also a key concern for the recently formed Climate and Clean Air Coalition of which Ireland is a member. The synergy of air quality and climate change issues, in particular short lived climate pollutants such as methane, black carbon and ozone, is a key concern for this coalition. 25
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