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EnviroSHaPER Noise Model
David Morley, Imperial College London
EnviroSHaPER Noise Model
Generate noise exposure at points (addresses)
User-friendly application
Based on the new CNOSSOS-EU standard model
Simplified approach for national scales
Noise exposure
Noise exposure
Common metrics used in epidemiology
LAEQ16 16hr day average 07:00 – 23:00
LDAY 12hr day average 07:00 – 19:00
LEVE 4hr evening average 19:00 – 23:00
LNIGHT 8hr night average 23:00 – 07:00
LDEN 24hr average weighted towards night and
evening
CNOSSOS-EU Framework
A harmonised method for Europe to
allow comparison between countries
Rail, Aircraft, Industrial and Road
sources
A full (complex) sound propagation
model to assign noise levels to
receptors
In this application, both source
definition and propagation needs to
be simplified
EnviroSHaPER Input Data
Data set Description Use
Traffic flow Number of vehicles per hour on a road segment On a particular road segment, the number of vehicles defines
the total noise source
Vehicle type Relative proportion of light vehicles (e.g. passenger cars)
and heavy vehicles (e.g. lorries, buses)
A heavy vehicle contributes more noise than a light vehicle
Speed limits Maximum legal limit or average speed (if available)
according to road class and vehicle type
The speed of a vehicle effects the associated sound power
output
Road network Spatial layout of the road network Sound propagation and contribution at a receptor is based on
the distance to, and the number of nearby roads and
associated traffic flows
Road junction type Presence of roundabouts or crossings on a road
segment
Influence on acceleration and deceleration and vehicle engine
noise
Land cover Land cover types over the study area (buildings,
grassland, woodland, water bodies etc.)
Distinction between sound absorbent (e.g. vegetation) and
sound reflective surfaces (e.g. concrete)
Building heights Height and location of buildings Buildings act as a barrier to sound propagation
Air temperature Annual average air temperature As air temperature increases, traffic noise will decrease
Prevailing wind direction Expected proportion of time wind can be expected from
a certain direction (by quadrant)
A favourable (following) wind direction can aid sound
propagation
Road surface type and age Road surface material (e.g. concrete, asphalt) and age
(condition)
Older roads and specific surface types lead to higher rolling
noise levels
Studded tyre usage Relative proportion of vehicles using studded (snow)
tyres
Studded tyre use contributes to higher rolling noise levels
Road gradient Slope of each road segment Influence on acceleration and deceleration and vehicle engine
noise
Topography Elevation model of the study area Line-of-sight between noise sources and receivers for sound
propagation
EnviroSHaPER Input Data
Land cover
Building heights
Road geography
Traffic flow
EnviroSHaPER Input Data
Morley, D.W., de Hoogh, K., Fecht, D.,
Fabbri, F, Bell, M. , Goodman, P.S.,
Elliott, P., Hodgson, S., Hansell, A., and
Gulliver, J. International scale
implementation of the CNOSSOS-EU
road traffic noise prediction model for
epidemiological studies (in press)
Environmental Pollution
EnviroSHaPER Modelling
For each receptor point:
1) Find road segments within 500m
2) Project source-receptor ‘ray paths’
3) Calculate source noise at these points
4) Calculate propagation of noise along ray
path to receptor
5) Exponentially sum values for each path
EnviroSHaPER Modelling
Source traffic noise
DATA SOURCES
•Road network geography
•Traffic flow for light and heavy vehicles
SOUND POWER EMMISION
•Rolling noise: Road surface (type, age)
•Propulsion noise: Engine noise (road
gradient, vehicle speed), vehicle type
EnviroSHaPER Modelling
Sound propagation
Noise levels at a receptor is the accumulation of noise along all
propagation paths
Propagation is a function of:
Distance from the source
Angle of view of to the road segment
Atmospheric absorption
Meteorological conditions
Land cover
EnviroSHaPER Modelling
Sound propagation
EnviroSHaPER Application
A user-friendly windows interface
Runs in PostGIS behind the scenes
EnviroSHaPER Application
Dialogue boxes to specify inputs
All inputs ArcGIS shapefiles
Very few other options
EnviroSHaPER Application
Receptors CORINE polygons
Generalised building heights Road network and traffic flow
EnviroSHaPER Application
As each receptor is processed:
Noise estimations shown
Map of roads in range
• At the end:
Histogram of predictions
Clickable points on OSM
base
Summary
CNOSSUS-EU model designed to allow comparable noise models for
Europe
Is extremely detailed (localised), but here is simplified to more general
(regional) situations.
Implementation
User-friendly front-end to a PostGIS spatial data base
Requires PostGIS is installed (but runs behind the scenes)
Output is ArcGIS shapefile and .csv for Excel
See the User Guide for full details
David Morley: d.morley@imperial.ac.uk
Acknowledgement
The research leading to these results has received funding from the
European Union Seventh Framework Programme (FP7/2007-2013) under
grant agreement n° 261433 (Biobank Standardisation and Harmonisation
for Research Excellence in the European Union - BioSHaRE-EU)

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BioSHaRE: EnviroSHAPER Noise Model and The Rapid Inquiry Facility (RIF); linking environment and health - Anna Hansell and David Morley - Imperial College London

  • 1. EnviroSHaPER Noise Model David Morley, Imperial College London
  • 2. EnviroSHaPER Noise Model Generate noise exposure at points (addresses) User-friendly application Based on the new CNOSSOS-EU standard model Simplified approach for national scales
  • 4. Noise exposure Common metrics used in epidemiology LAEQ16 16hr day average 07:00 – 23:00 LDAY 12hr day average 07:00 – 19:00 LEVE 4hr evening average 19:00 – 23:00 LNIGHT 8hr night average 23:00 – 07:00 LDEN 24hr average weighted towards night and evening
  • 5. CNOSSOS-EU Framework A harmonised method for Europe to allow comparison between countries Rail, Aircraft, Industrial and Road sources A full (complex) sound propagation model to assign noise levels to receptors In this application, both source definition and propagation needs to be simplified
  • 6. EnviroSHaPER Input Data Data set Description Use Traffic flow Number of vehicles per hour on a road segment On a particular road segment, the number of vehicles defines the total noise source Vehicle type Relative proportion of light vehicles (e.g. passenger cars) and heavy vehicles (e.g. lorries, buses) A heavy vehicle contributes more noise than a light vehicle Speed limits Maximum legal limit or average speed (if available) according to road class and vehicle type The speed of a vehicle effects the associated sound power output Road network Spatial layout of the road network Sound propagation and contribution at a receptor is based on the distance to, and the number of nearby roads and associated traffic flows Road junction type Presence of roundabouts or crossings on a road segment Influence on acceleration and deceleration and vehicle engine noise Land cover Land cover types over the study area (buildings, grassland, woodland, water bodies etc.) Distinction between sound absorbent (e.g. vegetation) and sound reflective surfaces (e.g. concrete) Building heights Height and location of buildings Buildings act as a barrier to sound propagation Air temperature Annual average air temperature As air temperature increases, traffic noise will decrease Prevailing wind direction Expected proportion of time wind can be expected from a certain direction (by quadrant) A favourable (following) wind direction can aid sound propagation Road surface type and age Road surface material (e.g. concrete, asphalt) and age (condition) Older roads and specific surface types lead to higher rolling noise levels Studded tyre usage Relative proportion of vehicles using studded (snow) tyres Studded tyre use contributes to higher rolling noise levels Road gradient Slope of each road segment Influence on acceleration and deceleration and vehicle engine noise Topography Elevation model of the study area Line-of-sight between noise sources and receivers for sound propagation
  • 7. EnviroSHaPER Input Data Land cover Building heights Road geography Traffic flow
  • 8. EnviroSHaPER Input Data Morley, D.W., de Hoogh, K., Fecht, D., Fabbri, F, Bell, M. , Goodman, P.S., Elliott, P., Hodgson, S., Hansell, A., and Gulliver, J. International scale implementation of the CNOSSOS-EU road traffic noise prediction model for epidemiological studies (in press) Environmental Pollution
  • 9. EnviroSHaPER Modelling For each receptor point: 1) Find road segments within 500m 2) Project source-receptor ‘ray paths’ 3) Calculate source noise at these points 4) Calculate propagation of noise along ray path to receptor 5) Exponentially sum values for each path
  • 10. EnviroSHaPER Modelling Source traffic noise DATA SOURCES •Road network geography •Traffic flow for light and heavy vehicles SOUND POWER EMMISION •Rolling noise: Road surface (type, age) •Propulsion noise: Engine noise (road gradient, vehicle speed), vehicle type
  • 11. EnviroSHaPER Modelling Sound propagation Noise levels at a receptor is the accumulation of noise along all propagation paths Propagation is a function of: Distance from the source Angle of view of to the road segment Atmospheric absorption Meteorological conditions Land cover
  • 13. EnviroSHaPER Application A user-friendly windows interface Runs in PostGIS behind the scenes
  • 14. EnviroSHaPER Application Dialogue boxes to specify inputs All inputs ArcGIS shapefiles Very few other options
  • 15. EnviroSHaPER Application Receptors CORINE polygons Generalised building heights Road network and traffic flow
  • 16. EnviroSHaPER Application As each receptor is processed: Noise estimations shown Map of roads in range • At the end: Histogram of predictions Clickable points on OSM base
  • 17. Summary CNOSSUS-EU model designed to allow comparable noise models for Europe Is extremely detailed (localised), but here is simplified to more general (regional) situations. Implementation User-friendly front-end to a PostGIS spatial data base Requires PostGIS is installed (but runs behind the scenes) Output is ArcGIS shapefile and .csv for Excel See the User Guide for full details David Morley: d.morley@imperial.ac.uk
  • 18. Acknowledgement The research leading to these results has received funding from the European Union Seventh Framework Programme (FP7/2007-2013) under grant agreement n° 261433 (Biobank Standardisation and Harmonisation for Research Excellence in the European Union - BioSHaRE-EU)