an overview of directive 2015/996/ec (cnossos-eu) for ... · g. dutilleux - arpa - 08/06/2016 –...
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G. Dutilleux - ARPA - 08/06/2016 – Alessandria (IT)
Guillaume DutilleuxAcoustics Group, Laboratoire de Strasbourg, France
An overview of Directive 2015/996/EC (CNOSSOS-EU)for terrestrial sources
Direction territoriale Est
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2
Introduction
�Directive 2002/49/CE
� 2007 deadline� “Interim” methods� “Equivalent” methods
� Consistency issues
� Directive 2015/996/EC (CNOSSOS-EU)
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Outline
�Project organization
� General aspects� Emission� Propagation� Populations
� Pending issues
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CNOSSOS-EU project
2008 2012 1.7.2015Steering DG-JRCMS strongly involved
8 active working groups
Separation between aircraft and other sources
Steering DG-EnvExtrium consortiumMS (almost) not involved
Reference softwareAssessing candidate methods+ everything else !
3 parallel drafts of Annex II
2014
Selection of JRC 2012
Adoption by NRC
Translation
Publication
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CNOSSOS-EU structure
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RoadEmission
RoadEmission
RailEmission
RailEmission
IndustryEmissionIndustryEmission
AircraftNoise
AircraftNoise
Terrestrial propagationTerrestrial propagation
Population assignmentPopulation assignment
Quality frameworkQuality framework
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CNOSSOS-EU in general
� 2 harmonized methods
� Target: strategic noise mapping
� Octaves from 63 Hz to 8000 Hz
� Point source decompositions
� 2.5D path search
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Quality framework
�Accuracy of input values� +/- 2 dB on the emission level of the source� No confidence interval provided
�Use of default values� Not allowed unless disproportionately high costs
�Quality of the software used for calculations� Compliance with the certification of results against test cases
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Road emission
Omnidirectionalsources
2 components
Rolling
Propulsion
Reference conditions•Flow type•Gradient•Temperature•…
Speed-dependent spectrum
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Road emission - pavementsReference pavement•DAC 0/11 + SMA 0/11•2-7 years•Representative maintenance condition
Real world pavements
•Table for Dutch pavements•Computing new coefficients for each vehicle category
• SPB measurements• Converting existing models
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Road emission
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�Pavement emission not age-dependent
�Unsteady flow-type close to intersections only
paraison des corrections C1 et C2 pour le modèle CNOSSOS
A à 7.5m en niveau global pour les PL de catégorie 2 de la
L Am
ax (
dBA
)
�Exercise caution on tabulated data
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Railway emission
!!
41#!5 !6!0 !!
!!!!!!
!#1"!5 !6!* !!
!!!
Propulsion noise
Propulsion noise
SquealSqueal Impact noise
Impact noise
Bridge noiseBridge noise
Aerodynamicnoise
Aerodynamicnoise
Rolling noise
Rolling noise
Directivity
Horizontal Vertical
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Railway emissionDigi t 1 2 3 4
Descript or Vehicle type Number of ax les per vehicle
Br ake type Wheel measure
Explanation of the descriptor
A letter that describes the type
The actual number of axles
A letter that describes the brake type
A letter that describes the noise reduction measure type
Possible descriptors
h
high speed vehicle (>200 km/h)
1 c
cast-iron block
n
no measure
m
self-propelled passenger coaches
2 k
composite or sinter metal block
d
dampers
p
hauled passenger coaches
3 n
non-tread braked, like disc, drum, magnetic
s
screens
c
city tram or light metro self-propelled and non-self-propelled coach
4 o
other
d
diesel loco
etc.
e
electric loco
a
any generic freight vehicle
o
other (i.e. maintenance vehicles etc.)
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Railway emission
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�Rail roughness
�Very small set of tabulated vehicles
�Adapting to other (national) rolling stock ?
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Industrial sources
�Geometry� Source types� Discretization rules
�Sound power� Operating cycles� Directivity� Quite limited default database� Measurements are recommended
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Propagation – mean ground plane
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Propagation – ground absorption� Ground factor G
�Defined for each ground element�Average along a path: Gpath�Close to the source
G′ path � Gpath
dp
��zs þ zrð Þþ Gs � −
dp
��zs þ zrð Þif dp − ���zs zr
8>><
>>:Gpath otherwise
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Propagation – propagation conditions
Upward refraction
Downward refraction
Non refracting conditions
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Propagation – 2 conditions�Downward conditions (F)
�Homogeneous conditions (H)
� Safe-side estimate of upward refraction
� Occurrences of downward refraction � Long term sound level
20 %
40 %
60 %
80 %
100 %
N
30 °
60 °
90 °
120 °
150 °
180 °
210 °
240 °
270 °
300 °
330 °
06h−18h18h−22h22h−06h06h−22h
NICE
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Propagation – Aboundary
Diffraction ?Diffraction ? YesNo
Aboundary=Aground Aboundary=Adif
For each octave band
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Propagation – Aground,H
Cf ¼ dp
�þ �wdpe −
ffiffiffiwdp
p
�þ wdp
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Propagation – Aground,F
�Aground,F=Aground,H for a different geometry
�Corrected heights
�Floor
Source Turbulence Receiver
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Propagation – Adif - horizontal
∆dif �
��Ch ���þ ��λ
C″δ if ��λ
C″δ −
8>>><
>>>:� otherwise
Adif ¼ ∆dif ðS,RÞ þ ∆ground ðS,OÞ þ ∆ground ðOn ,RÞ
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Propagation – Adif – vertical edges
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Propagation – Reflections
�Vertical obstacles
�Image sources
�Absorption coefficient in diffuse field EN 1793-1
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Also available: attenuation by retrodiffraction
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Propagation – subset of NMPB 2008�Source NF S 31-133:2011
�Simplifications� No reflection on embankment slope� No small barrier� No body barrier interaction for railway noise
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Populations: VBEB 2007� Two levels of information
� Population data available� Population known at the scale of the building� Known at a more global scale
� Data not available -> habitable surface� By flat� By building� By larger entity� Unknown
�Allotment� Population at 4 m� At most 5 m broad segments at the receiver
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Conclusions� CNOSSOS-EU: a major step toward consistency� 1 model for terrestrial sources� 1 model for aircraft sources
� A few pending issues for the member states� Input data for emission models� Road (pavements)� Railway (rail roughness, rolling stock)
� Deriving occurrences from meteorological data� Quality assurance for software -> ISO 17534 series� Path finding algorithms not specified
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Guillaume DutilleuxGroupe AcoustiqueLaboratoire de Strasbourg
+33 3 88 77 46 [email protected]
Thank you for your attention
Direction territoriale Est