2) Relevance for environmental policy... 2. 4) Data sources and reporting... 5 5) References at the international level... 6



Similar documents
Revealing the costs of air pollution from industrial facilities in Europe a summary for policymakers

Costs of air pollution from European industrial facilities an updated assessment

What are the causes of air Pollution

The design of the Romanian national air quality monitoring network

Air Pollution. Copenhagen, 3 rd September Valentin Foltescu Project manager air quality European Environment Agency

UK Air Quality Monitoring Networks

EMISSIONS OF AIR POLLUTANTS IN THE UK, 1970 TO 2014

Impact Assessment of Dust, NOx and SO 2

Impacts of air pollution on human health, ecosystems and cultural heritage

Air Quality: Public Health Impacts and Local Actions

Air Quality Appraisal Damage Cost Methodology

Oil and Gas Air Quality Regulations and Permitting

Air quality in Europe 2015 report

Which filter class for supply air is required in a typical HVAC system?

Health effects of particulate matter and implications for policy in Europe

AIR QUALITY IN PARIS REGION 2014

2014 Aamjiwnaang Air Monitoring Station Results. Ministry of the Environment and Climate Change April 19, 2016

EEA Technical report No 6/2012

Ambient Air Monitoring at Deployment Locations in the Middle East

Emissions estimate from forest fires: methodology, software and European case studies

DEVELOPMENT OF NEEDS ASSESSMENT AND DESIGN OF AIR QUALITY MONITORING NETWORK

H- 3: Composition of the road motor vehicle fleet by fuel type. 2) Relevance for environmental policy... 2

FACT SHEET PROPOSED REVISIONS TO THE NATIONAL AMBIENT AIR QUALITY STANDARDS FOR SULFUR DIOXIDE

Economic and Social Council

Energy from Waste Combined Heat and Power Facility, North Yard, Devonport. Community Ambient Air Quality Monitoring Programme Report Quarter 4, 2015

2) Relevance for environmental policy ) Data sources and reporting ) References at the international level... 4

ISBN

Holcim EMR List of EN Standards and VDI Guidelines usable for Discontinuous Measurements in Cement Plants

RESIDENTIAL AND COMMERCIAL/INSTITUTIONAL NATURAL GAS AND LIQUEFIED PETROLEUM GAS (LPG) COMBUSTION

National Environment Protection (Ambient Air Quality) Measure

(Adopted May 6, 1977)(Amended June 2, 1978) (Amended April 4, 1980)(Amended July 9, 1982) (Amended September 8, 1995)(Amended June 13, 1997)

Issues/Concerns With Ambient Air Monitoring

Partnership in Environmental Governance. Swedish Environmental Protection Agency

i n d o o r a i r q u a l i t y I AQ EN 13779:2007 European standard Camfil Farr clean air solutions

42.1 Average Gaseous Composition of Dry Air in the Troposphere National Ambient Air Quality Standards (NAAQS) 628

NOVEL STRATEGIES FOR ASSESSMENT OF AMBIENT AIR QUALITY USING GIS AND ONLINE POLLUTION MONITORING TOOLS I. Jaykumar 2, V. Hima Bindu 2, P.

Birmingham City University / Students Union Aspects and Impacts Register. Waste. Impacts description

National Environment Protection (Ambient Air Quality) Measure. Appendix 6

Sludge Treatment Facility Stack Gas Monitoring Report February 2016

Air Pollution s, 1950s. Air Pollution Laws 1950s

The Ambient Air Monitoring System

Revised Health Impact Assessment Recommendation Document for

INTERACTIONS: ENERGY/ENVIRONMENT Fossil Fuel Energy Impacts on Health - Helena Ribeiro

Monitoring of air pollution spread on the car-free day in the city of Veszprém

Jytte Boll Illerup Morten Winther Erik Lyck Henrik Gundorph Bruun Department of Policy Analysis

Automotive Air Quality Sensors: industrial innovations to protect people s health

Guide to UK Air Pollution Information Resources June 2014

The Public Health Management of Chemical Incidents Case Study

Electronic Reporting to BTS

JRC- AQUILA Position Paper. Assessment on siting criteria, classification and representativeness of air quality monitoring stations

TESTIMONY OF LARRY J. GORDON, M.S., M.P.H. PRESIDENT, AMERICAN PUBLIC HEALTH ASSOCIATION BEFORE THE SENATE ENVIRONMENT AND PUBLIC WORKS COMMITTEE

TORONTO MUNICIPAL CODE CHAPTER 423, ENVIRONMENTAL REPORTING AND DISCLOSURE. Chapter 423 ENVIRONMENTAL REPORTING AND DISCLOSURE

measured (empirical) data from CCC. The modelled values are of value for all (ecosystem specific modelling work deposition)

Criteria for EUROAIRNET

FACT SHEET PROPOSED MERCURY AND AIR TOXICS STANDARDS

VARIATIONS TO STATE ENVIRONMENT PROTECTION POLICY (AIR QUALITY MANAGEMENT) AND STATE ENVIRONMENT PROTECTION POLICY (AMBIENT AIR QUALITY)

A GUIDANCE NOTE ON THE BEST PRACTICABLE MEANS FOR ELECTRICITY WORKS BPM 7/1 (2014)

EPA Requirements for Diesel Standby Engines In Data Centers. Bob Stelzer / CTO / Safety Power Inc. For 7x24 Fall 2014 Conference. 1.

Development of an Air Quality Monitoring Network for Kosovo

TR SUPPLEMENTARY REQUIREMENTS FOR THE ACCREDITATION OF CONTINUOUS AMBIENT AIR QUALITY MONITORING STATIONS

Clean Up Your Fleet. Introducing a practical approach to cleaner, more efficient fleet operation

Smoke Management Plan

The Regulatory Role of Chemical Mechanisms and Future Needs

POTENTIAL TO EMIT SUMMARY FIBERIGHT, LLC HAMPDEN, MAINE

Experimental study on atmospheric pollutant emissions from heating systems, in Italy

AN OVERVIEW OF AIR POLLUTION IN URBAN AREAS OF TANZANIA

Air Pollution Sampling and Analysis

Published in "Official Gazette of the Republic of Macedonia" No. 67/2004 LAW ON AMBIENT AIR QUALITY I. GENERAL PROVISIONS

LIFE CYCLE ASSESSMENT ON COTTON AND VISCOSE FIBRES FOR TEXTILE PRODUCTION

Invisible air pollution is the second biggest public health risk

An overview of Euro VI for trucks over 3.5t. Brought to you by Mercedes-Benz

Economic and Social Council

FLORIDA S OZONE AND PARTICULATE MATTER AIR QUALITY TRENDS

4. The role of fleets and fleet managers Role of REC?

Transcription:

A- 2: Ambient air quality in urban areas 1) General description... 2 1.1) Brief definition... 2 1.2) Units of measurement... 2 1.3) Context...2 2) Relevance for environmental policy... 2 2.1) Purpose... 2 2.2) Issue... 3 2.3) International agreements and targets... 3 a) Regional level... 3 b) Subregional level... 3 3) Methodology and guidelines... 5 3.1) Data collection and calculations... 5 3.2) Internationally agreed methodologies and standards... 5 4) Data sources and reporting... 5 5) References at the international level... 6 1

1) General description 1.1) Brief definition The number or percentage of days during a year when air pollution levels (for air pollutants such as at least: particulate matter 10 (PM 10 ), sulphur dioxide (SO 2 ), nitrogen dioxide (NO 2 ) and ground- level ozone (O 3 )) exceed the established limit values (maximum allowable annual and daily concentrations (MACs)) in urban areas with regular observations of air quality; Percentage of urban population (i.e. the total number of people living in urban areas with at least one monitoring station) in a country exposed to air pollution above the established limit values; Absolute values of concentration of pollutants in the air. 1.2) Units of measurement Days or percentage of days during a year with exceeded daily daily average limit values/allowable concentration; Percentage of urban population living in areas with exceeded limit values; Concentration of pollutants (μg or ng, as appropriate for a particular pollutant) in cubic metre (m 3 ) of air. 1.3) Context Relation to other indicators from the Guidelines: This indicator relates to indicator A- 1: Emissions of pollutants into the atmospheric air. 2) Relevance for environmental policy 2.1) Purpose The indicator provides a measure of the state of the environment in terms of air quality and the impact of air pollution on the population, the state of the environment and on vegetation/ecosystems. 2

2.2) Issue Increased concentrations of pollutants in the low layer of the atmosphere can have various adverse impacts on human health, vegetation/ecosystems and materials. Exposure to PM, measured as concentrations of PM 10 or PM 2.5 (particles with mean diameter of 10 and 2.5 µm, respectively) in ambient air, represents, together with heavy metals and persistent organic pollutants (POPs), one of the largest human health risks from air pollution. Short- term inhalation of high concentrations of suspended particulates PM 10 and PM 2.5 may cause increased symptoms for asthmatics, respiratory symptoms, reduced lung capacity and increased risk of serious diseases. Moreover, there is considerable evidence of negative impact on human health from carbon monoxide (CO), SO 2, nitrogen oxides (NO X ) and O 3 in ambient air. SO 2, NO X and ammonia (NH 3 ) cause acidification and/or eutrophication and O 3 has negative impact on vegetation. 2.3) International agreements and targets a) Regional level: The ECE Convention on Long- range Transboundary Air Pollution (CLRTAP) and its eight protocols commit the Parties to reducing and preventing air pollution by SO 2, NO X, NH 3, non- methane volatile organic compounds (NMVOC), O 3, PM, lead, mercury, cadmium and POPs. WHO Europe recommends in its guidelines guiding 1 air quality limit values for 32 main air pollutants; in the 2006 revision those for SO 2, nitrogen dioxide (NO 2 ), PM and O 3. b) Subregional level: The Environmental Strategy of countries of South- Eastern and Eastern Europe, Caucasus and Central Asia foresees, in particular, the optimization of standards for ambient air pollution in urban areas with respect to environmental impacts and to combined health impacts (based on WHO criteria). In the European Union, Directive 2008/50/EC of the European Parliament and of the Council on ambient air quality and cleaner air for Europe (Air Quality Framework Directive) has been adopted which regulates ambient air concentrations of PM 10, PM 2.5, SO 2, NO 2, CO, benzene, lead and O 3 and sets detailed rules for air quality assessment. Concentrations of arsenic, cadmium, nickel and polycyclic aromatic hydrocarbons (represented by benzo(a)pyrene) in ambient air are regulated by the Directive 2004/107/EC. Several types of standards are laid down by these directives: Limit values for the protection of human health (fixed levels to be attained within a given period of time period not to be exceeded once attained) for PM 10, PM 2.5, SO 2, NO 2, benzene, CO and lead, 1 Air Quality Guidelines for Europe (revision of Air Quality Guidelines for Europe 1987). WHO Regional Office for Europe, Bilthoven Division, 2000; Air Quality Guidelines Global update 2005. Particulate matter, ozone, nitrogen dioxide and sulfur dioxide. WHO Regional Office for Europe, 2005. 3

target values for the protection of human health (fixed levels to be attained where possible) for O 3, PM 2.5, arsenic, cadmium, nickel and benzo(a)pyrene, 2 alert thresholds (fixed levels beyond which there is a risk to human health from brief exposure) for SO 2, NO 2 and O 3, critical levels (fixed levels above which direct adverse effects may occur on some receptors, such as trees, other plants or natural ecosystems but not on humans) for SO 2 and NO X, long- term objective (fixed level to be attained in the long term, save where not achievable through proportionate measures with the aim of providing effective protection of human health and the environment) for O 3. In the case of PM 2.5, additional interim standards are set (average exposure indicator, exposure concentration obligation, national exposure reduction target). All limit values and target values except of those for SO 2, O 3 and CO are set as annual average values. In some cases, shorter- term limit values are set as well. The basic limit values for the protection of human health, as laid down by the above- mentioned directives, are as follows: PM 10 (annual average 40 μg/m 3, 24- hour limit value 50 μg/m 3, not to be exceeded more than 35 times a calendar year); compliance deadline 2005. PM 2.5 (target value and limit value for stage 1 - annual average 25 µg/m 3 ); compliance deadline 2015. PM 2.5 (limit value for stage 2 - annual average 20 µg/m 3 ); compliance deadline 2020. SO 2 (hourly limit value 350 μg/m 3, not to be exceeded more than 24 times a calendar year; 24- hour limit value 125 μg/m 3, not to be exceeded more than 3 times a calendar year); compliance deadline 2005. NO 2 (annual average 40 μg/m 3, hourly limit value 200 g/m 3, not to be exceeded more than 18 times a calendar year); compliance deadline 2010. Lead (annual average 0.5 μg/m 3 ); compliance deadline 2005. Benzene (annual average 5 μg/m 3 ); compliance deadline 2010. CO (maximum daily 8- hour mean 10 mg/m 3 ); compliance deadline 2005. O 3 (target value maximum 8- hour mean 120 μg/m 3, not to be exceeded more than 25 days a calendar year over 3 years); compliance deadline 2012. Arsenic (target value annual average 6 ng/m 3 ); compliance deadline 2012. Nickel (target value annual average 20 ng/m 3 ); compliance deadline 2012. Cadmium (target value annual average 5 ng/m 3 ); compliance deadline 2012. Benzo(a)pyrene (target value 1 ng/m 3 ); ); compliance deadline 2012. 2 Benzo(a)pyrene is understood as a representative of polycyclic aromatic hydrocarbons. 4

3) Methodology and guidelines 3.1) Data collection and calculations The data should be collected from an air quality- monitoring network which consists of fixed manual or automated monitoring stations which may be complemented by mobile stations. The selection strategy for site locations should focus on areas with the highest concentration of emission sources (industrial zones and highways) for direct warnings or on background monitoring stations in residential areas to get an overview of the general exposure of the country s urban population. The data from the monitoring should be calibrated in the National calibration laboratories and validated according to quality assurance/quality control (QA/QC) procedures introduced. 3.2) Internationally agreed methodologies and standards WHO Air Quality Guidelines for Europe covering 32 pollutants, ISO standards 13.040, Air quality or ECE 2012 Guidelines for Developing National Strategies to Use Air and Water Quality Monitoring as Environmental Policy Tools may be applied for monitoring purposes. Directive 2008/50/EC of the European Parliament and of the Council on ambient air quality and cleaner air for Europe sets detailed rules of air quality assessment including data quality objectives, assessment requirements (measurement or modelling), minimum number and siting of sampling points and reference methods. Detailed rules of reporting are set by the Commission Implementing Decision 2011/850/EU of 12 December 2011 laying down rules for Directives 2004/107/EC and 2008/50/EC of the European Parliament and of the Council as regards the reciprocal exchange of information and reporting on ambient air quality. Many references are available on the most appropriate and up- to- date air quality monitoring and analysis methods and on proven models estimating ambient air concentrations of air pollutants on the basis of data on emissions. 4) Data sources and reporting: Data on ambient air pollution concentrations are routinely collected in national monitoring networks. General data on air quality in urban areas are published in annual environmental reports, while actual data are being published at the municipal levels. The WHO Healthy Cities Network and the Air Quality and Health programme of the WHO Regional Office for Europe collect air quality data from participating national agencies. Eurostat, EEA and OECD collect air quality data from their Member States. 5

5) References at the international level: Air Quality Guidelines for Europe (revision of Air Quality Guidelines for Europe 1987). WHO Regional Office for Europe, Bilthoven Division, 2000: http://www.euro.who.int/en/health- topics/environment- and- health/air- quality/publications/pre2009/air- quality- guidelines- for- europe; Air Quality Guidelines Global update 2005. Particulate matter, ozone, nitrogen dioxide and sulfur dioxide. WHO Regional Office for Europe, 2005: http://www.euro.who.int/en/what- we- do/health- topics/environment- and- health/air- quality/publications/pre2009/air- quality- guidelines.- global- update- 2005.- particulate- matter,- ozone,- nitrogen- dioxide- and- sulfur- dioxide; Guidelines for Developing National Strategies to Use Air and Water Quality Monitoring as Environmental Policy Tools. ECE 2012. English and Russian edition: http://www.unece.org/index.php?id=30339; Human Exposure Assessment, Environmental Health Criteria Document 214, Program of Chemical Safety. WHO, 2000; Monitoring Ambient Air Quality for Health Impact Assessment. WHO Regional Publications, European Series, No. 85.2. WHO, 1999; Environmental Health Indicators: Framework and Methodologies. Prepared by D. Briggs, Occupational and Environmental Health. WHO, 1999; Directive 2008/50/EC of the European Parliament and of the Council on ambient air quality and cleaner air for Europe; Directive 2004/107/EC of the European Parliament and of the Council of 15 December 2004 relating to arsenic, cadmium, mercury and polycyclic aromatic hydrocarbons in ambient air; Commission Implementing Decision 2011/850/EU of 12 December 2011 laying down rules for Directives 2004/107/EC and 2008/50/EC of the European Parliament and of the Council as regards the reciprocal exchange of information and reporting on ambient air quality; Commission Decision 2004/461/EC of 29 April 2004 establishing a questionnaire to be used for annual reporting on ambient air quality assessment under Council Directives 96/62/EC and 1999/30/EC and under Directives 2000/69/EC and 2002/3/EC of the European Parliament and of the Council; Air Quality in Europe 2012 Report, EEA report No 4/2012; CLRTAP (Convention on Long- range Transboundary Air Pollution) and its protocols: http://www.unece.org/env/lrtap/welcome.html; WHO Europe: http://www.euro.who.int/en/what- we- do/health- topics/environment- and- health/air- quality; UNSD: http://unstats.un.org/unsd/environment/; EEA: http://themes.eea.europa.eu/ims/csi; Eurostat: http://epp.eurostat.ec.europa.eu/portal/page/portal/environment/introduction; European Commission. See http://ec.europa.eu/environment/air/index_en.htm; EIONET: http://acm.eionet.europa.eu. 6