Content

Traffic-related Emissions and Immissions 2015

Introduction

Original situation

In the past, the reduction of emissions from industrial and domestic heating was the main focus of air quality planning. In these segments, sizeable reductions of airborne pollutant emissions could be achieved through extensive rehabilitation programmes and plant closures. Improvements were also achieved in the area of traffic, but nonetheless, traffic is the largest single source of both current and future air pollutants – not only in Berlin – and is the determining factor for the course of future action in air quality planning.

Due to historical development conditions, the spatial residential structure of Berlin and Brandenburg is “traffic-efficient”. No other region in Germany has anywhere near such favourable conditions. Especially characteristic of Berlin are the clearly polycentric structures and the intensive utilization of space in the inner city, as well as in the centres on the periphery, with intensive large- and small-scale multiple uses, as well as a lower degree of suburbanization compared to other large cities. Only 20 % of the population lives in the surrounding suburbs, whereas for example around 2.5 million inhabitants live in the city region of Frankfurt am Main, of which only slightly more than 710,000 inhabitants are registered within the city limits. However, also in and around Berlin the development of the relations between the city and its surroundings has led to the developments typical for metropolitan areas. Whereas in 2002 only around 123,000 commuters were coming to Berlin daily from the surroundings (= about 10 % of employed persons with mandatory social insurance payments), in mid-2014 there were already 266,000 commuters (= 21 % of employed persons with mandatory social insurance payments). An additional 84,000 Berliners were commuting to the surroundings (AfS 2017). However, compared with other metropolitan areas, this proportion is still relatively low (e.g. in Frankfurt/Main it amounts to around 60 % of inbound commuters).

Since reunification, the city of Berlin has been confronted with a considerable increase in traffic. The number of the motor vehicles registered in Berlin increased by 23 % between 1989 and 2002, when a high point of 1,440,000 was achieved. This figure has since dropped continuously over the course of several years and is now at 1,409,642 motor vehicles (as of January 1, 2017, cf. Table 1), after a recent upturn.

Link to: Vergrößern
Table 1: Number of motor vehicles and trailers in the State of Berlin 2006 - 2017 (each reference date: Jan. 1)
Image: according to Statistical Office for Berlin-Brandenburg, Statistical Yearbooks, only in German

The traffic volume on the Berlin road network has, according to the Emissions Register, decreased only slightly, from 12,641,300,000 vehicle-km in 2005 to 11,651,900,000 vehicle-km in 2014. In future, however, traffic growth is to be expected in road freight transport, which is very impact-intensive; even just the steady increase in the number of registered vehicles of this category suggests this (cf. Table 1).

These far-reaching changes have not ended yet. The increase in non-local traffic is caused, among other things, by the continuing expansion of the combined Berlin-Brandenburg residential and commercial area; the intensification of international economic interdependence; and, especially in Berlin, increasing interdependence with Eastern Europe.

The contribution of motor vehicle traffic to air pollutant concentrations: Origins and trends

Berlin’s motor vehicle traffic has for years now been the cause not only of considerable noise immissions in significant problem areas (see also Maps 07.05.1 and 2, Strategic Noise Maps, Road Traffic; 2017 Edition), but also of air pollution, especially since other categories that originally contributed to air pollution in Berlin have been substantially reduced. Table 2 shows the combined emissions of all of Berlin’s sources of major pollutants since 1989 according to the current state of knowledge.

Since the fall of the Berlin Wall in 1989, many industrial enterprises have been rehabilitated or shut down, and the use of brown coal for fuel for home furnaces in Berlin’s residential areas has been replaced with heating oil, natural gas, or district heating (cf. Map 08.02.1 Predominant Heating Types, Supply Shares of Individual Energy Carriers; 2010 Edition). In 1989, domestic heating and industry were significant sources of sulphur dioxide and particulate pollutants, but these have been reduced substantially. Between 2002 and 2015, total emissions of nitrogen oxides were reduced by approx. 17 %, and of particulate matter by almost 40 %. During emissions calculations in 2015, the analysis of relevant polluters was extended significantly. This limits the comparability of emissions by heating systems with those measured in previous years. A new emissions report was drawn up to calculate emissions in 2015. In addition to the previous analysis of statistical parameters, this report includes a survey and considers a multitude of stakeholders. The final report (only in German) is available on the website of the Senate Department for the Environment, Transport and Climate Protection.

Link to: Vergrößern
Table 2: Emissions in Berlin by polluter groups, 1989 to 2015
Image: Umweltatlas Berlin

The particulate emissions from motor vehicle exhausts, which are an especially great health threat, also decreased by more than 90 % between 1989 and 2015. This finding agrees substantially with the measurements of diesel soot detected in urban canyons – the major component of motor vehicle exhaust emissions. The measured concentration of diesel exhaust particulates at Measurement Station 174 of the Berlin Clean Air Measurement Network (BLUME) on Frankfurter Allee in the borough of Friedrichshain dropped by 50 % during the period 2000 – 2015 (cf. also the evaluation of Map 03.12.1, Station 174). However, since the particulate matter emissions from abrasion and resuspension of road transport decreased far less and, road traffic is the second greatest source of particulate matter in Berlin, after “other sources”. Road traffic, including abrasion and resuspension, in 2015 accounted for 25 % of the particulate emissions of PM10 in Berlin, while other sources accounted for 50 %.

By the beginning of the 1990s, road traffic had replaced industrial plants as the main source of nitrogen oxides in Berlin. As of 2015, street traffic produced 39 % of the nitrogen oxides in Berlin, whereas industrial plants accounted for 33 % of total emissions.

Especially high in relative terms is the pollution from motor vehicle traffic in the inner city, where over one million people live in an area of 100 km2. If current trends for use of and competition for space continue, motor vehicle traffic will increase especially strongly here. If current conditions continue, freight transport will encounter a particularly major increase in bottlenecks in the streets.

In order to counteract these developments, which are to some extent incompatible with urban living and threatening to public health, two mutually complementary planning strategies have been developed for Berlin:

With the revised Urban Development Plan for Traffic, the Berlin Senate in a resolution of March 29, 2011 presented an updated action plan which combines the possible and necessary steps for the further development of the Berlin traffic system for the coming years with a long-term strategic orientation. The core of the action plan is a catalogue of measures that were previously analyzed in detail and coordinated for effectiveness, acceptability and fundability. With regard to the future development of traffic in Berlin and the surrounding area, the investigations for the Berlin Air Quality Plan are based on this long-term action plan.

The “Health and Safety” section, one of the key strategic components of the Urban Development Plan for Traffic, includes a number of important strategies to limit the increase of motor vehicle traffic and its associated effects, with the goal of a reduction of air and noise pollution in the primary road network.

The target date for the Urban Development Plan for Traffic is 2025, which is rather long-term; however, with its “Mobility Programme 2016”, it also takes short- and medium-term requirements into account (more information under: Urban Development Plan for Traffic (SenUVK 2016b, only in German)).

The standardized Air Quality Plan mandated by the EU, titled “Air Quality Plan 2011-2017”, was adopted by the Berlin Senate on June 18, 2013.

Under Europe-wide standards, the Air Quality Plan data must include information on:

  • pollution measurements,
  • the causes of high air pollution levels,
  • the frequency and degree of instances in which the limits are exceeded,
  • pollution immission and the proportions of the immission for each causative factor (e.g. industry, commerce, domestic heating, traffic),
  • planned measures, and a schedule for implementation; and
  • a prognosis of the goals to be achieved by such measures.

The present Air Quality Plan provides information about the legal framework and the prevailing situation, and describes the causes of air pollution. The measures take into account the developments to date of the condition of the air (through 2010), and future trends through 2020. The focal point is the presentation of a range of potential measures and their evaluation. Based on the effectiveness of these measures, a strategy will be developed for the Berlin Air Quality Plan. The Air Quality Plan documents that Berlin, like many other large German and European cities, faces a major challenge to meet the new EU limits.

The essential results can be summarized as follows: the locally generated segment of the pollution, the share which can only be reduced by Berlin measures, accounts for about 36 % of the particulate pollution measured at a primary road; it is caused by the urban background (approx. 17 %) and by the local sources from road traffic (approx. 19 %). The urban background pollution share is caused mostly by road traffic (7.5 % of total PM10 pollution). The remainder (9.5 %) stems mainly from other sources (approx. 7.5 %, including construction activity with transport, wood burning as additional heating in private households, resuspension through strong wind and the like) as well as from Berlin domestic heating and industry and power plants.

The results of the measurements of recent years and the comprehensive model calculations carried out for 2015 lead, among other things, to the following conclusions:

  • The measured NO2 pollution both in the Berlin suburbs and in residential areas and along primary roads has been consistently high since 2002, and in urban canyons it almost always exceeds the limit of 40 µg/m3 for protecting human health. Annual mean values of 48 µg/m3 along primary roads, 27 µg/m3 in inner-city residential areas and 14 µg/m3 on the outskirts were measured in 2016. Very similar values had already been observed in 2001. Despite improvements in exhaust gas technology and despite a slight reduction in motor vehicle traffic in Berlin, the expected reduction in NO2 immissions has not occurred.
  • One of the reasons for this is the strong increase in the number of diesel vehicles in Berlin. Whereas in 2002 approx. 14 % of all cars and light commercial vehicles had diesel engines, this proportion increased to approx. 35 % in 2014. Diesel vehicles emit significantly more nitrogen oxides than gasoline-powered vehicles. The share of NO2 in the exhaust has also increased in the last 10 years from less than 10 % to more than 40 %. Thus, diesel vehicles contribute disproportionately to the NO2 pollution along primary roads. It has also turned out that diesel vehicles with the newer exhaust emissions standard Euro 5 sometimes produce higher NOx emissions than diesel vehicles with the older Euro 3 and 4 standards.
  • In contrast to the measurements of the pollution along primary roads, the NO2 prognoses for 2015 calculated in 2009 indicated an average decrease of 17 %. The NO2 pollution of the inner-city residential areas was also supposed to decrease by more than 20 % by 2015 according to the predictive calculations of 2009. The calculations of 2009 were based on efficient exhaust gas treatment systems in diesel vehicles, mainly with the newer emission standards (Euro 5 and Euro 6). The Euro 5 standard only became mandatory for cars with diesel engines on January 1, 2011, so that the emission factors of these vehicles were still very uncertain at the time the prognoses were made.

More detailed notes on the effects of air pollutants, the applicable legal regulations and further background information can be found in the accompanying text of the 2011 edition of the Environmental Atlas (SenStadtUm 2011).