Member State report / Art8 / 2018 / D11 / Belgium / NE Atlantic: Greater North Sea

Report type Member State report to Commission
MSFD Article Art. 8 Initial assessment (and Art. 17 updates)
Report due 2018-10-15
GES Descriptor D11 Energy, incl. underwater noise
Member State Belgium
Region/subregion NE Atlantic: Greater North Sea
Reported by RBINS - Scientific Service MUMM
Report date 2020-01-14
Report access ART8_GES_BE_20200110.xml

Belgian Part of the North Sea (ANS-BE-MS-1)

GES component
D11
D11
Feature
Impulsive sound in water
Continuous low frequency sound
Element
Element code
Element code source
Element 2
Element 2 code
Element 2 code source
Element source
Criterion
D11C1
D11C2
Parameter
Level of noise
Underwater sound level
Parameter other
Threshold value upper
185.0
Threshold value lower
Threshold qualitative
Geen positieve trend in jaargemiddelde
Threshold value source
Other (specify)
Other (specify)
Threshold value source other
Nationaal
Nationaal
Value achieved upper
198.0
Value achieved lower
172.0
Value unit
Decibels reference 1 microPascal squared second
Value unit other
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend
Unknown
Unknown
Parameter achieved
No
Unknown
Description parameter
Sound level expressed as zero to peak level (Lz-p) normalized to the level at 750 m from the source. Results of measurements of underwater noise during pile-driving.
Sound pressure within the 1/3 octave bands 63 and 125 Hz
Related indicator
Criteria status
Not good
Unknown
Description criteria
Element status
Description element
Integration rule type parameter
Not relevant
Not relevant
Integration rule description parameter
Integration rule type criteria
Not relevant
Not relevant
Integration rule description criteria
GES extent threshold
GES extent achieved
GES extent unit
GES achieved
GES expected to be achieved later than 2020, no Article 14 exception reported
Not assessed
Description overall status
A temporary displacement of porpoises was observed by pile driving for offshore wind turbines, but it is not known what effects this has on a population level. Given the measured and modelled noise levels, the assessment of the disturbance distance for porpoises during pile driving and their seasonal density (see Descriptor 1), a number of measures were taken to limit exposure and consequences for porpoises: 1) If the underwater noise level (Lz-p ) during pile driving is higher than 185 dB re 1μPa at 750 m from the source, noise mitigation measures must be applied, such as bubble curtains or an alternative technique that produces less noise. 2) Piling may not take place between January 1 and April 30, the period with the highest density of porpoises in Belgian waters (this measure took effect from 2014). 3) To prevent exposure, preventive measures such as acoustic deterrents and a procedure for gradually increasing the energy of the hammer must be applied. 4) Piling cannot be started or continued if marine mammals are observed in the vicinity of the sanctuary (200 - 500 m, depending on visibility and the type of marine mammals).
Due to the currently limited data set, no trend in environmental noise levels can be determined.
Assessments period
2011-2016
2011-2016
Related pressures
  • Input of anthropogenic sound (impulsive, continuous)
  • Input of anthropogenic sound (impulsive, continuous)
Related targets
  • D11.T1
  • D11.T2