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Berlin Environmental Atlas

07.05 Strategic Noise Maps (Edition 2008)

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Overview

Legal Provisions and Competent Authorities

The "Directive of the European Parliament and of the Council relating to the assessment and management of environmental noise" came into force on 18th February 2002, when it was published in the Official Journal of the European Community. This opened for the European Community the path towards legal provisions which were also to apply to noise immission in the environment.

The German Federal Environmental Office (Umweltbundesamt) describes the objectives of the Directive as follows:
"Ensuring a high degree of health and environmental protection is part of the Community policies, one of the objectives being noise protection." To achieve this, "adverse effects of and annoyance caused by environmental noise must be prevented, avoided and reduced." This requires the following action:

  • determining the load caused by environmental noise by means of noise maps and according to assessment methods to be used by all of the Member States;
  • ensuring that the public is informed about environmental noise and its effects;
  • adoption of action plans through the Member States based on the results of noise maps and aiming at preventing and reducing environmental noise where necessary and particularly in cases where exposure levels might have effects that are detrimental to health and further aiming at maintaining environmental noise quality where it is good.

Furthermore, the Directive should form the basis for further development and enhancement of measures to reduce the noise emission of the most relevant noise sources and it should also inform the European Commission about the exposure caused by environmental noise in the Member States.

The "Senatsverwaltung für Gesundheit, Umwelt und Verbraucherschutz" (Senate Administration for Public Health, Social Services and Consumer Protection) ordered and implemented the noise mapping project for the Land of Berlin as provided in the requirements of the Noise Mapping Decree (34th BImSchV = Bundes-Immissionschutzverordnung or Federal Immission Protection Decree) in connection with Paras. 47 a-f of BImSchG (Bundes-Immissionschutzgesetz or Federal Immission Control Act) and Directive 22002/49/EC (Environmental Noise Directive), with the current LAI instructions on noise mapping taken into consideration.

The plan aimed at creating strategic noise maps and the related statistical evaluations (exposure for humans, dwellings, schools and hospitals in specific immission level classes). Results were prepared with regard to the following items for further utilization through the customer:

  • basis for reporting to the EU and for informing the public;
  • basis for drawing up action plans for noise reduction measures
    (noise reduction plans for Berlin (in german));
  • basis for managing the output data (data model care);
  • basis for re-calculation and evaluation of spatially defined areas.

Paras. 47 a-f of the Federal Immission Control Act (BImSchG) lay down the rules for implementing the EU Environmental Noise Directive according to German law. The Noise Mapping Decree (34th BImSchV) defines the requirements for noise maps according to Para. 47 c of BImSchG.

Noise maps must always be calculated. Calculations must comply with the preliminary EU-conforming calculation rules, which deviate from the Technical Codes that are binding according to national law in some aspects (see below, Calculation Methods).

Noise maps are to be reviewed and, if necessary, revised every five years after they have been drawn up.

The maps 07.05.12 - 07.05.15 (total noise of all traffic sources) are not a component of the "Directive of the European Parliament and of the Council relating to the assessment and management of environmental noise". These maps represent the attempt, to present a summing up contemplation of the single traffic noise-sources. Due to lacking knowledge about the dose-effect relationships, only an energy summation was proceeded. Therefore the contemplation of the total noise cannot meet the requirements to respect the burden-effects of the individual noise sources (cf. cumulative values of the noise exposure).

General description of main noise sources, based on their position, size and road traffic / mapping scope

The borders of the area under examination are the borders of the Land of Berlin. The following noise sources were examined:

  • Road traffic (motor vehicles including busses)
  • Streetcar traffic and above-ground subway traffic
  • Industrial and commercial areas with plants complying with Annex I of Directive 96/61/EC of the Council of 24th September 1996 concerning integrated pollution prevention and control (IPPC plants including power plant locations and Westhafen)
  • Air traffic (Tegel Airport)
  • Railway traffic according to the Allgemeines Eisenbahngesetz (AEG, General Railroad Law).

Included in the examination were further relevant main noise sources in the Brandenburg area adjoining the borders, which exceed the specified immission levels (excluding Schönefeld Airport).

Table 1 gives an overview of the noise sources included in the examination:

et705_01
Tab. 1: Main noise sources for noise mapping in the conurbation area of Berlin

Excel
[Table is also available as Excel-File (MS-Excel is required).]

Constraints considering the cumulative values of the noise exposure

Until now the described regulations do not intend any calculation of total-noise levels, the individual main-noise-sources are calculated and assessed separately from each other. However, the German Council of Environmental Advisors declared in 2004, S. 490, that " a cut of the noise-burden of the population can only be successful if the combination of several noise-sources will be taken into account".

Since the dose-effect--relationships are extremely difficult from the medical and psychological point of view when simultaneous effects of several sound sources are interacting, here a simplified approach was carried out:

  • All immission-value for the different main-noise-sources were assessed with the same level of annoyance; i.e. no use of sound-type-specific annoyance-factors through a bonus-malus-system
  • The individual noise levels are added only energetically.

(for more detailed information to the topic " total-noise-exposure " see the study of the TÜV (German Technical Inspection Service Immission Protection and Energy Systems)).

It is to take into account that there are some specific particularities of the logarithmic decibel scale. For instance, the volumes of two 50 dB(A) sound events sum up to 53 dB(A); however the ear feels this increasing of 3 dB(A) like a duplication of the disagreeableness. Two part-levels, one of 50 dB(A) and one of 60 dB(A) sum up to 60,4 dB(A).

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