Do something for our planet, print this page only if needed. Even a small action can make an enormous difference when millions of people do it!
Personal tools
For the public:
Ask your question
Press room
The EEA Web CMS works best with following browsers:
Internet Explorer is not recommended for the CMS area.
If you have forgotten your password, we can send you a new one.
Skip to content. | Skip to navigation
Emissions of persistent organic pollutants (POPs) decreased between 1990 and 2016 in the EEA-33, e.g. hexachlorobenzene (HCB) by 95 %, polychlorinated biphenyls (PCBs) by 75 %, dioxins and furans by around 70 % and polycyclic aromatic hydrocarbons (PAHs) by 83 %. Although the majority of countries report that POP emissions fell during this period, some report that emissions increased. In 2016, the most significant sources of emissions for these POPs included the ‘Commercial, institutional and households’ (23 % of HCB, 26 % of dioxins and furans, 36 % of PAHs and 16 % of PCBs) and ‘Industrial processes and product use’ (41 % of HCB, 65 % of PCBs and 40 % of PAHs) sectors.
Read more
Across the EEA-33 countries, emissions of lead decreased by 93 %, mercury by 71 % and cadmium by 64 % between 1990 and 2016. The majority of the decrease in lead emissions occurred by 2004 mainly as a result of the phase out of leaded petrol across Europe. The largest emission source presently is 'Energy use in industry', contributing around one-third of total emissions. Since 1990 the two sectors contributing most to the decrease in mercury emissions are 'Energy use in industry' and 'Industrial processes and product use'.
Europe aims to have a strong, growing and low-carbon industry with closed material cycles. Currently, industry remains a significant source of pollutant releases to Europe’s environment. Releases of pollutants to air and water by European industry have generally decreased during the last decade. Environmental regulation and improved pollutant abatement technology, among other factors, have led to decreasing pollutant releases to air and water in Europe. Soil contamination in Europe is, among other things, linked to industrial activity. Waste transfers from industrial facilities in the EU have remained relatively stable in the last decade.
A significant reduction in the consumption of ozone-depleting substances (ODS) has been achieved by the EEA-33 countries since 1986. This reduction has been largely driven by the 1987 United Nations Environment Programme (UNEP) Montreal Protocol. Upon entry into force of the Montreal Protocol, EEA-33 consumption was approximately 420 000 ozone-depleting potential tonnes (ODP tonnes). Consumption values around zero were reached in 2002 and have remained consistently so ever since. S ince the early 1990s, th e European Union (EU) has taken additional measures, in the shape of EU law, to reduce the consumption of ODS. In many aspects, the current EU regulation on substances that deplete the ozone layer (1005/2009/EC) goes further than the Montreal Protocol and it has also brought forward the phasing out of hydrochlorofluorocarbons (HCFCs) in the EU.
Large combustion plants are responsible for a significant proportion of anthropogenic pollutant emissions. In 2015, large combustion plant emissions of sulphur dioxide (SO 2 ) and nitrogen oxides (NO x ) accounted for 44 % and 14 %, respectively, of EU-28 totals. Since 2004, emissions from large combustion plants in the EU-28 have decreased by 77 % for SO 2 , 49 % for NO x and 81 % for dust. The largest plants (greater than 500 megawatt thermal (MWth)) account for only 24 % of large combustion plants but are responsible for around 80 % of all large combustion plant SO 2 , NO x and dust emissions. In 2015, of a total of 3 418 large combustion plants, 50 % of all emissions came from just 40, 89 and 47 plants for SO 2 , NO x and dust, respectively. One indicator of the environmental performance of large combustion plants is the ratio between emissions and fuel consumption (i.e. the implied emission factor). The implied emission factors for all three pollutants decreased significantly between 2004 and 2015 for all sizes of large combustion plant.
There are 3 418 large combustion plants in the EU-28. The number of such plants increased by 19 % between 2004 and 2015. Most of this increase occurred between 2004 and 2010, while there was a slight downward trend from 2012 onwards. There was a 10 % increase in installed capacity in the EU-28 between 2004 and 2015. This increase occurred between 2004 and 2012, followed by a downward trend from 2012 onwards. The actual use of this capacity, in terms of fuel input, remained broadly stable between 2004 and 2010, although there was a decrease in 2009 that can largely be attributed to the financial crisis. Since 2010, fuel input has decreased, and in 2015 was 17 % lower than in 2010. From 2004 to 2015, other solid fuels (mainly coal) and natural gas were consistently the main sources of fuel input. The types of fuel consumed most in 2015 were solid fuels (mainly coal; 55 % of total fuel consumption) and natural gas (26 %). Despite this, since 2006 the amount of input from fossil fuels has been decreasing. This reflects the shift in Europe’s energy system away from oil, coal and gas to more renewable sources ( EEA, 2017 ). The installed capacity of large combustion plants in Europe is not equally distributed: Germany, Spain, Italy and the United Kingdom accounted for more than half of total fuel input and operating capacity in 2015.
Local soil contamination in 2011 was estimated at 2.5 million potentially contaminated sites in the EEA-39, of which about 45 % have been identified to date. About one third of an estimated total of 342 000 contaminated sites in the EEA-39 have already been identified and about 15 % of these 342 000 sites have been remediated. However, there are substantial differences in the underlying site definitions and interpretations that are used in different countries. Four management steps are defined for the management and control of local soil contamination, namely site identification (or preliminary studies), preliminary investigations, main site investigations, and implementation of risk reduction measures. Progress with each of these steps provides evidence that countries are identifying potentially contaminated sites, verifying if these sites are actually contaminated and implementing remediation measures where these are required. Some countries have defined targets for the different steps. Thirty of the 39 countries surveyed maintain comprehensive inventories for contaminated sites: 24 countries have central national data inventories, while six countries, namely Belgium, Bosnia-Herzegovina, Germany, Greece, Italy and Sweden, manage their inventories at the regional level. Almost all of the inventories include information on polluting activities, potentially contaminated sites and contaminated sites. Contaminated soil continues to be commonly managed using “traditional” techniques, e.g. excavation and off-site disposal, which accounts for about one third of management practices. In-situ and ex-situ remediation techniques for contaminated soil are applied more or less equally. Overall, the production sectors contribute more to local soil contamination than the service sectors, while mining activities are important sources of soil contamination in some countries. In the production sector, metal industries are reported as most polluting whereas the textile, leather, wood and paper industries are minor contributors to local soil contamination. Gasoline stations are the most frequently reported sources of contamination for the service sector. The relative importance of different contaminants is similar for both liquid and solid matrices. The most frequent contaminants are mineral oils and heavy metals. Generally, phenols and cyanides make a negligible overall contribution to total contamination. On average, 42 % of the total expenditure on the management of contaminated sites comes from public budgets. Annual national expenditures for the management of contaminated sites are on average about EUR 10.7 per capita. This corresponds to an average of 0.041 % of the national GDP. Around 81 % of the annual national expenditures for the management of contaminated sites is spent on remediation measures, while only 15 % is spent on site investigations. It should be noted that all results derive from data provided by 27 (out of 39) countries that returned the questionnaire, and not all countries answered all questions.
The number of organisations registered under the EMAS standard rose by 50% during the period 2003-2010, while organisations from EU countries certified according to the international ISO 14001 standard more than quadrupled in the period 2001-2009. This indicates that private companies and public institutions in the EU are increasingly engaging in environmental management.
All A B C D E F G H I J K L M N O P Q R S T U V W X Y Z
For references, please go to https://www.eea.europa.eu/themes/industry/indicators or scan the QR code.
PDF generated on 14 Nov 2018, 08:40 AM
Engineered by: EEA Web Team
Software version: EEA Plone KGS 18.10.30
Software updated on 30 October 2018 07:23 from version 18.10.24
CMS login Site usage Software updates history Code for developers
We use cookies to record some preference settings and to analyse how visitors use our web site. Cookies do not contain any personal information about you. If you wish, see how to delete/disable cookies in your web browser. See also our privacy policy.
CMS login
Site usage
Software updates history
Code for developers
Document Actions
Share with others