Results from first Danish full scale test section with poroelastic road surface

Similar documents
Intermediate Report on Rolling Resistance

Effect of road surfaces on road traffic noise on the public roads of Japan. --An investigation based on tyre/road noise measurement--

NordTyre - the potential for noise reduction using less noisy tyres and road surfaces

Noise from electric vehicles. Measurements

Reduction of vehicle noise at lower speeds due to a porous open-graded asphalt pavement

30 Different Tyres On 4 Surface Types - How Do Truck Tyre Noise Levels Relate to the Test Surface

Low noise surfaces for urban streets

Development of low noise tyres in EC project SILENCE

DI Manfred Haider arsenal research. WG leader of PIARC TC 4.2 WG B Road Traffic Noise , Geneva Presentation to UN ECE/TRANS/ WP.

Measurement of Tire/Pavement Noise

Final report on noise and rolling resistance

Rolling noise of 15 heavy duty vehicle tyres on 12 different road surfaces

Water influence on skid resistance. Standardisation: input of the HERMES programme

A quiet poroelastic road surface manufactured in a normal asphalt mixing plant

REPEATABILITY OF CPX TYRE/ROAD NOISE MEASUREMENTS. Gillian Adams, Frits Kamst and Stephen Pugh ASK Consulting Engineers, Brisbane, Australia

NordTyre the potential for noise reduction using less noisy tyres and road surfaces

Road vehicle noise reduction by low noise road surfaces in Japan

High Friction Surfaces and Other Innovative Pavement Surface Treatments for Reduced Highway Noise

The INDOT Friction Testing Program: Calibration, Testing, Data Management, and Application

Rehabilitated PCC Surface Characteristics

Passenger car tyres AUTHOR(S) CLIENT(S) CLASS. THIS PAGE ISBN PROJECT NO. NO. OF PAGES/APPENDICES

CASE STUDY OF TYRE NOISE: ASSESSMENT AND COMPARISON OF DIFFERENT ROAD SURFACES

Round robin tests in the Netherlands

Research Update Construction Conference Charles Holzschuher, P.E. February 3, Florida Department of Transportation

Non-contact Deflection Measurement at High Speed

ALTERNATIVE SYSTEMS FOR ROAD SURFACE CPX MEASUREMENTS

Shunsuke TANAKA and Kimio MARUYAMA

Implementation and Thickness Optimization of Perpetual Pavements in Ohio

Noise Generated by Tyres Designed for Electric Vehicles - Results of Laboratory Experiments

Environmentally friendly pavements: Results from noise measurements SINTEF ICT. Truls Berge, Frode Haukland, Asbjørn Ustad

Labelling road surfaces

Truls Berge SINTEF ICT, Dept. of Acoustics, P.O.Box 4760 Sluppen, NO-7465 Trondheim, Norway,

ROSANNE Results after 2 years of project duration Roland Spielhofer, AIT BUDAPEST, HUNGARY 2015

Assessing Pavement Rolling Resistance by FWD Time History Evaluation

CNOSSOS-EU, some first experiences

Insert the title of your. Recent research on surface texture

On the prediction of rail cross mobility and track decay rates using Finite Element Models

Contribution of the tyre to further lowering tyre/road noise

TABLE OF CONTENTS. Appendix 1 Correlation analysis ISO surfaces.48 Appendix 2 Correlation analysis SMA surfaces.. 50

The effect of grinding and grooving on the noise generation of Portland Cement Concrete pavement

QUIET-TRACK: Track optimisation and monitoring for further noise reduction

Motor Vehicles Working Group (MVWG)

Gauge Face Wear Caused with Vehicle/Track Interaction

Special edition paper

Research and analysis of noise emitted by vehicles according to the type of surface roads and driving speed

Reduction of Vehicle Noise at Lower Speeds Due to Quieter Pavement. By Paul R Donavan

Economic and Social Council

Studies by Hong Kong officials during the European tour

CONTRIBUTION OF ALTERNATIVE ROAD SURFACES TO NOISE ABATEMENT

Characterisation of low-noise tyres for the roads of Hong Kong

Measurement of noise from electrical vehicles and internal combustion engine vehicles under urban driving conditions

- New Superpave Performance Graded Specification. Asphalt Cements

Measurement methods for skid resistance of road surfaces

The development and use of the Skid Resistance and Smart Ravelling Interface Testing Device

DaimlerChrysler Alternative Particulate Measurement page 1/8

inter.noise 2000 The 29th International Congress and Exhibition on Noise Control Engineering August 2000, Nice, FRANCE

Economic and Social Council

RESULTS OF PHYSICAL WORKSHOP 1 st Australian Runway and Roads Friction Testing Workshop

INTERIOR NOISE OF A KOREAN HIGH-SPEED TRAIN IN TUNNELS

EME2 Pavement and mix design. Laszlo Petho, Pavements Manager Fulton Hogan.

Dynamic characteristics of railway concrete sleepers using impact excitation techniques and model analysis

NCAT Report EFFECT OF FRICTION AGGREGATE ON HOT MIX ASPHALT SURFACE FRICTION. By Pamela Turner Michael Heitzman

ROSANNE Rolling resistance round robin test & draft standard preparation. MIRIAM Workshop, Sterrebeek, 19 May 2016

New vehicule noise emission values to update the French Guide du bruit

INTER-NOISE AUGUST 2007 ISTANBUL, TURKEY

ABOUT THE ROLLING RESISTANCE TRAILER AND PARAMETERS INFLUENCING ROLLING RESISTANCE

CPX tyre/road noise measurements in Queensland Noise characteristics of various road surfaces

Field Evaluation of Noise Reducing Pavement: A Controlled Experiment. prepared by

inter.noise 2000 The 29th International Congress and Exhibition on Noise Control Engineering August 2000, Nice, FRANCE

SEAUPG 2009 CONFERENCE-HILTON HEAD ISLAND, SOUTH CAROLINA

Improving the Performance of Asphalt Surfacing

DELIVERABLE D5.11. Part 3: Measurement of emitted tyre/road noise

WP5 - Computational Mechanics B5 - Temporary Vertical Concrete Safety Barrier MAIN REPORT Volume 1 of 1

Investigating lateral porosity effect on air pumping noise from connected road cavities with CFD simulations

SPECIFICATION FOR SKID RESISTANCE INVESTIGATION AND TREATMENT SELECTION

Improvements for reduction of the brake squeal noise at Seoul metro rolling stock on tracks

Models for rolling resistance In Road Infrastructure Asset Management systems

Use of New High Performance Thin Overlays (HPTO)

Towards silent tracks and roads: beating the roughness

Results of HCT- vehicle combinations

Characterization of particle emissions from a marine diesel engine: Influence of sampling temperature on particle number, size, and morphology

Deliverable D3.3. Parameters influencing rolling resistance and possible correction procedures

Development of long life structural asphalt

Noise Resist. - you need to improve the noise reduction of your existing sound enclosure

SULFUR EXTENDED ASPHALT INVESTIGATION - LABORATORY AND FIELD TRIAL

WET GRIP TEST METHOD IMPROVEMENT for Passenger Car Tyres (C1) GRBP 68 th session

inter.noise 2000 The 29th International Congress and Exhibition on Noise Control Engineering August 2000, Nice, FRANCE

AUTOMOTIVE EMC TEST HARNESSES: STANDARD LENGTHS AND THEIR EFFECT ON RADIATED EMISSIONS

What s going on with European Specifications?

Sound transmission across plenum windows with non-parallel glass panes

Pearls from Martin J. King Quarter Wave Design

ANALYTICAL AND EXPERIMENTAL STUDY OF SLEEPER SAT S 312 IN SLAB TRACK SATEBA SYSTEM

Road Vehicle noise Regulations and standardization Impacts and Stakes

Acoustic design of the air transparent soundproofing wall

The complex analysis of tram noise in relation to changes in dynamic mobility of tram wheel

MN Roads Low Volume Road Testing to Validate the Purdue TPTA Textures and Predicted Joint Effects

Falling Weight Deflectometer

Laboratory Alignment Procedure for Improving Reproducibility of Tyre Wet Grip Measurement

Economic and Social Council

NCHRP Project 1-44: Measuring Tire-Pavement Noise at the Source APPENDIX C. Results of Test Parameter Evaluation

Transcription:

Results from first Danish full scale test section with poroelastic road surface Hans BENDTSEN 1 ; Rasmus Stahlfest Holck SKOV 2 ; Bent ANDERSEN 3 ; Julien CESBRON 4 1, 2, 3 Danish Road Directorate (DRD), Denmark 4 LUNAM Université, IFSTTAR, AME, LAE, France ABSTRACT The first Danish test section with poroelastic road surface (PERS) was constructed on August 27th 2013 at the Kalvehave test site in Denmark, as a part of the EU project PERSUADE. The test section is 75 m long and has the width of one driving lane. The yearly daily traffic is 4000 with 10 % heavy vehicles. The speed limit is 80 km/h and the estimated real speed is somewhat lower. The pavement is optimized for low emission of tyre-road noise by using a high built in air void, small aggregates and elastic material. The pavement has a porous structure and is composed of stone and rubber aggregates with a maximum aggregate size of 5 mm and the binder used is polyurethane. The pavement type has been developed and tested in the laboratory. An intensive monitoring program was started at the Kalvehave test site even before the test section was opened for normal traffic. The monitoring program includes measuring noise, acoustical absorption, elasticity, permeability, friction, rolling resistance and visual inspections. Measurements of noise using the SPB road side and the CPX trailer methods have been repeated continuously over the first 9 months of the lifetime of the PERS pavement. Keywords: 52.3 Road traffic noise. 11.7.1 Tires and road-tire interactions 1. INTRODUCTION PERSUADE is the acronym for PoroElastic Road SUrface: an innovation to Avoid Damage to the Environment [1]. The project aims at developing the experimental concept of poroelastic road surfacing (PERS) into a feasible noise-abatement measure as an alternative to, for example, noise barriers. It is expected that PERS may provide substantially higher noise reductions than the best of conventional road paving materials. The specific feature of this new type of road surfacing is that it includes a substantial proportion of rubber granulates from recycled car tyres bound with the synthetic resin polyurethane. To gain experiences mixing and laying the PERS material outside the laboratory on a real road a small scale pre-test was constructed at the Danish Arnakke test site in October 2011. A series of measurements has been performed on this 10 square meter PERS pavement. The results indicate that this pavement has a good potential for achieving a high noise reduction, better than conventional porous asphalt [2]. On the background of these experiences a full scale test section with PERS material was constructed at the Kalvehave test site in Denmark 27 th August 2013 on a 75 m long section in one lane of a two lane highway in a rural area (see Figure 1 and 2). The width of the lane is about 3.5 m. The yearly daily traffic is 4000 with 10 % heavy vehicles. The speed limit is 80 km/h and the estimated real speed is somewhat lower. The test section was opened for normal traffic on August 30 th. The PERS material is composed of stone aggregates and rubber particles and the gluing agent is polyurethane. The maximum aggregate size is 5 mm both for stone aggregates and rubber particles. Since the PERS test section at Kalvehave was constructed a comprehensive series of measurements have been performed over a period of around 250 days in order to characterize the PERS pavement in relation to surface characteristics and noise [3]. 1 hbe@vd.dk 2 rass@vd.dk 3 bea@vd.dk 4 julien.cesbron@ifsttar.fr Inter-noise 2014 Page 1 of 10

Page 2 of 10 Inter-noise 2014 Figure 1 - The PERS test section just after construction. Figure 2 - Close up photo of the PERS test section. The light aggregates are stone material and the black are rubber material. 2. PROPERTIES OF THE PAVEMENT 2.1 Texture laser measurements The texture of the surface was measured with the DRD in-situ laser device at five places in the left wheel track. The texture profiles were recorded in five 1.5 m long parallel lines separated with 1 cm. The resolution of the instrument is 0.1 mm in the length direction (x) and 9 µm in the height direction (z). The laser is an LMI Selcom SLS5000 with 16 khz sampling frequency and a spot size of 0.1 mm, and the sample distance was set to 0.18 mm. For each recorded profile the mean profile depth (MPD) was determined per 100 mm according to the ISO 13473-1 standard. The average MPD of the five test positions is illustrated in Table 1. The results show that the average MPD are the same for position 9 m and 24 m, and for position 39 m and 69 m. The position 54 m is not similar to any of the other positions. When this 54 m position is left out the average MPD is 0.67 mm. For comparison the MPD of a new dense asphalt concrete with 11 mm aggregates is around 0.57 mm and for a new porous asphalt with 8 mm aggregates 0.86 mm. Table 1 - Average MPD over the 1.5 m distance at different positions in the left wheel track [3]. Position 9 m 24 m 39 m 54 m 69 m Avg. (excl. 54 m) Average MPD 0.58 mm 0.58 mm 0.75 mm 0.90 mm 0.75 mm 0.67 mm The texture spectrum were determined in 1/3 octave bands, in the range from 100-0.4 mm according to the technical specification ISO/TS 13473-4 from FFT analysis using an evaluation length Page 2 of 10 Inter-noise 2014

Inter-noise 2014 Page 3 of 10 of 1.475 m with offset and slope suppression. The average spectrums of the different positions are illustrated in Figure 3, together with a new porous asphalt ((PA) aggregate size 8 mm), an old asphalt concrete ( (AC11d) aggregate size 11 mm) and a new stone mastic asphalt ((SMA6+8) aggregate size 6 mm). In comparison with the spectrums for AC11d and PA the PERS should according to the Descornet/Sandberg model [6] have a lower noise level, as the texture levels are generally higher in the wavelength range from 8-0.4 mm, and lower or similar from 100-10 mm. Figure 3 - Average texture level in 1/3 octave bands at the Kalvehave PERS. Texture levels likewise measured with the in-situ laser, are included for a new porous asphalt (PA), an old asphalt concrete (AC11d) and a new stone mastic asphalt (SMA6+8) are included as references [3]. 2.2 Air void and permeability The built in air void has been measured to 27.7%. This must be considered as a high built in air void for example compared to the air void of two-layer porous pavements at the Danish Øster Søgade test site at 23 to 27 % when new [4].The DRD has used the Becker tube for determining the permeability. The principle of the method is measuring the time a certain height (100 mm) of a column of water uses to run out of the tube and into the asphalt. A transparent tube with a diameter of 140 mm is placed on the road, and the joint between the tube and the road is sealed with putty. The permeability is given as the flow out time in seconds. The average result from the Becker tube is 6.9 seconds which is the same as for a new two-layer porous asphalt [4]. It must be concluded that the PERS has a very fine permeability. 2.3 Mechanical impedance testing The mechanical impedance of the PERS at the Kalvehave test site was measured by IFSTTAR using the experimental setup described in [3]. Five different spots were tested along the 75 meters long test section. The measurement spots were equally spaced every 15 meters. The tests were performed in autumn 2013, in closed traffic conditions. The air temperature varied between 10.9 C and 12.9 C and the road surface temperature varied between 12.5 C and 24.0 C. Figure 4 gives the magnitude and the phase of the direct mechanical impedance measured at each spot. A similar behaviour is observed. At low frequency, there is a linear decrease which is typical of an ideal spring. At high frequencies, there is a linear increase which is typical of an ideal mass. At medium frequencies, there is a minimum value at a frequency corresponding to the resonance of the mass spring system. The minimum value corresponds to the damping of the system. At the resonance frequency a typical phase shift is also observed. The dynamic Young s modulus of the PERS has been assessed from a simple Single Degree Of Freedom (SDOF) system consisting in a mass over a parallel spring/dashpot assembly. The dynamic Young s modulus averaged on the five spots was 63.6 ± 26.4 MPa. The dynamic Young modulus of the PERS is about 150 times smaller than the dynamic Young modulus of a dense asphalt concrete (AC). Inter-noise 2014 Page 3 of 10

Page 4 of 10 Inter-noise 2014 Thus, despite some inhomogeneity of the PERS section, a rolling noise reduction due to elasticity may be expected since the stiffness of the PERS is close to the stiffness of standard tyres, leading to less tyre deflection and vibrations. 20 log Z d (db rel 1 N.s/m) 70 60 50 40 30 100 200 500 1000 2000 f (Hz) 180 Spot 5 Spot 4 Spot 3 Spot 2 Spot 1 100 φ Zd (deg) 0-100 -180 100 200 500 1000 2000 f (Hz) Figure 4 Comparison of the direct mechanical impedance for the five spots of the PERS [3]. 3. SPB NOISE RESULTS SPB roadside noise measurements have been performed by DRD three times in the first month after the construction of the PERS test section where the pavement was in a fine condition with no significant ravelling. It is not recommendable to perform SPB measurements during the winter season in Denmark where cars normally are using winter tyres that can have a different influence on the measured noise levels than summer tyres. The measurements were repeated in May 2014 where significant ravelling had occurred on the PERS test section. The number of vehicles included in the SPB measurements and the air temperature is presented in Table 2. It can be seen that the requirement for SPB measurements of 100 passenger cars is generally fulfilled. But there are all too few heavy vehicles. To get an impression of the order of magnitude of the noise from heavy vehicles for the PERS pavement all the four measurements have been clustered into one artificial measurement. Table 2 - Number of vehicles included and the air temperature recorded during the SPB measurements at the PERS pavement at Kalvehave [3]. Day 1 5 68 248 Number of passenger cars 92 88 100 99 Number of two axle heavy vehicles 6 6 6 8 Number of multi axle heavy vehicles 2 15 5 14 Air temperature [ C] 20.2 20.0 10.2 11.8 The L Amax levels for passenger cars can be seen in Table 3 were also the Danish reference levels from the Nordic prediction model Nord2000 are included for comparison. The Nord2000 reference is the average noise level for an eight years old dense asphalt concrete (AC11d) with 11 mm maximum aggregate size [5]. The noise for passenger cars has been corrected to 20 ºC using the normal conversion factor of -0.05 db/ºc for asphalt concrete. It can be argued that the temperature conversion factor for a PERS pavement with a high content of rubber differs from -0.05 db/ºc, but there is no better correction factor for PERS available. The average speed for passenger cars at the test site is around 65 km/h. The analysis has been performed at each SPB measurement at 50, 60 and 80 km/h. The speed of 50 and 80 km/h is just outside the confidence interval for these measurements and therefore the uncertainty is a little higher than for the results at 60 km/h. Page 4 of 10 Inter-noise 2014

Inter-noise 2014 Page 5 of 10 Table 3 - L Amax levels for passenger cars measured with the SPB method at three different speeds corrected to 20º Celsius [3]. Date Age; days after opening 50 km/h Speed 60 km/h 80 km/h 30. Aug. 2013 1 66.8 69.1 72.7 5. Sep. 2013 5 64.8 67.4 71.5 8. Nov. 2013 68 65.6 67.7 70.9 5. May 2014 246 64.0 67.0 71.7 Nord2000 ref. 8 years old 71.8 74.3 78.6 The SPB results are also shown in Figure 5 where it can be seen that from the day the test section was opened to traffic and 6 days later there is a reduction of the noise. For 60 km/h this is 1.7 db which is quite remarkable. In the period from day 5 to day 68 the noise levels seems to be stabilised. The noise reduction in relation to Nord 2000 is after 68 days 6.2, 6.6 and 7.7 db respectively for 50, 60 and 80 km/h. It must be remarked that a new dense asphalt concrete will have a noise level that will be around 2 db lower than the Nord2000 reference levels. After 248 days the noise level decreases about 1 db for speeds of 50 and 60 km/h. Figure 5 - L Amax levels for passenger cars measured with the SPB method at three different speeds corrected to 20º Celsius [3]. Figure 6 shows the spectra for passenger cars at 60 km/h. The 1.7 db reduction in the SPB level from the first day to the fifth day occurs in the frequency range from 800 to 1600 Hz where the noise from vibrations in the tyre caused by the surface texture is dominant. This can indicate that the surface texture becomes more even and smooth. After 248 days in May 2014 there is a remarkable change in the spectra. Below 630 Hz the noise level increases up to 5 db and over 630 Hz the noise level decreases up to 4 db. At this time significant ravelling has occurred on the PERS pavement and most of the stone aggregates are warn of leaving an uneven surface with a high proportion of soft rubber aggregate. This might partly be the explanation for the reduction in the frequency range from 630 to around 2000 Hz. A series of stripes with an angle of around 60 to the driving direction can be observed Inter-noise 2014 Page 5 of 10

Page 6 of 10 Inter-noise 2014 with a distance of around 2 to 5 meter. Other damaged areas on the pavement surface can also be observed. It is the judgement of the authors that this is caused by a snowplough driving on the road in the snow periods. This unevenness of the pavement might be part of the explanation for the increased noise under 630 Hz. 65 60 SPB 60 km/h 55 50 45 40 30. Aug. 2013 5. Sep. 2013 8. Nov. 2013 5. May 2014 Figure 6 - SPB spectra for passenger cars at 60 km/h [3]. In Figure 7 the spectra for the PERS pavement 68 days old having an SPB level of 67.7 db is compared to a new dense asphalt concrete with 11 mm aggregates (AC11d) at the Danish test section at Kongelundsvej [5] having an SPB level of 71.9 db. Comparing these two spectra the following can be seen: 1. From 160 to 800 Hz the PERS is 2 db lower than the AC11d. This can indicate that the PERS have smother texture caused by the smaller aggregate size (5 mm versus 11 mm) and is elastic compared to the AC11d. 2. From 1000 Hz to 2000 Hz the PERS is 5-6 db lower than the AC11d. In this frequency range the noise generated from vibrations in the tyre caused by the surface texture of the pavement is one of the dominant noise sources. This can also indicate that the PERS have smother texture than the AC11d. 3. From 2000 to 4000 Hz the PERS is 7 to 8 db below the AC11d. In this frequency range noise generated from air pumping is dominant. This indicates that the PERS has an open and porous structure. Figure 7 - SPB spectra for passenger cars at 60 km/h for the PERS when 68 days old [3] and data from Page 6 of 10 Inter-noise 2014

Inter-noise 2014 Page 7 of 10 new dense asphalt concrete with 11 mm aggregates at the Danish test section at Kongelundsvej [5]. During the SPB measurements it was for practical reasons only possible to include very few heavy vehicles (see Table 2) and therefore results from these vehicle categories cannot be included in the analysis. To get an impression of the order of magnitude of the noise from heavy vehicles for the PERS pavement all the four measurements have been clustered into one artificial measurement. The results are shown in Table 4 for a speed of 60 km/h where also the Danish reference levels from the Nordic prediction model Nord2000 are included for comparison. The result gives an indication that the PERS pavement for heavy vehicles has a SPB noise level 5 to 6 db below the Nord2000 reference level. This is around one db less noise reduction than for passenger cars. Table 4 - Artificial SPB level for heavy vehicles predicted by clustering the 4 SPB measurements performed at 60 km/h corrected to 20º Celsius [3]. Vehicle type Two axle heavy vehicles Multi axle heavy vehicles PERS at Kalvehave 77.0 78,6 Nord2000 ref. 81.7 84.3 4. CPX NOISE RESULTS DRD have performed CPX measurements at 50, 70 and 80 km/h four times after the opening of the test section. The main results as L Amax levels can be seen in Table 5 as well as in Figure 8. The results has been corrected to 20 C using the normal conversion factor of -0.03 db/ºcused by DRD for the SRTT tyre. The same tendencies as observed for the SPB results can be seen. For practical reasons the measurements at 70 km/h were not conducted on the 5 th of May 2014. Date Table 5 - Results of the CPX measurements with the SRTT tyre corrected to 20ºC [3]. Age (days after opening) 50 km/h Speed 70 km/h 80 km/h 30. Aug. 2013 1 87.0 91.9 93.6 5. Sep. 2013 5 85.9 90.4 92.0 23. Sep. 2013 23 85.4 90.5 91.7 5. May 2014 246 84.0-92.4 96,0 94,0 92,0 L Amax 90,0 88,0 86,0 84,0 5 7 8 82,0 0 50 100 150 200 250 300 Age in days Figure 8 - L Amax levels measured with the CPX method at three different speeds corrected to 20ºC [3]. Inter-noise 2014 Page 7 of 10

Page 8 of 10 Inter-noise 2014 The spectra for the CPX measurements with the SRTT tyre at 50 km/h are shown in Figure 9. The same tendencies as seen for the SPB results can be seen. 85 80 CPX 50 km/h 75 70 65 60 55 30 Aug. 2013 5 Sep. 2013 23 Sep. 2013 5 May 2014 Frequency [Hz] Figure 9 - CPX spectre for passenger cars at 50 km/h [3]. At day 5 the noise was also measured on the old asphalt concrete close to the PERS at Kalvehave. The results can be seen in Table 6. The noise reduction for the PERS in relation to the old pavement is around 7 db. Table 6 - CPX results for the old asphalt concrete and the PERS measuredon the 5 th of September 2013 with the SRTT tyre corrected to 20ºC [3]. Pavement 50 km/h 80 km/h PERS 85.9 92.0 Old asphalt concrete 92.4 99.2 5. ACOUSTICAL ABSORPTION Figure 10 - Impedance tube for measuring acoustical absorption. The acoustical absorption has been measured on drill cores taken from the pavement slabs that were produced at the roadside when the PERS pavement was constructed. Measurements are carried out according to ISO 10534-2 (Acoustics Determination of sound absorption coefficient and impedance Page 8 of 10 Inter-noise 2014

Inter-noise 2014 Page 9 of 10 I impedance tubes Part 2: Transfer-function method). The acoustical absorption measured in a B&K Type 4206 impedance tube, is measured at six cores drilled from test slabs. The impedance tube can be seen at Figure 10. Figure 11 - FFT spectrums of the absorption of the six cores [3]. The absorption measured at the six cores is illustrated in Figure 11. The absorption spectra for all of the cores have the same characteristics. Cores number 1 and 4 both have the maximum peak at 600-625 Hz, with a maximum absorption coefficient of 0.42. Cores number 2, 3, 5 and 6 have the maximum peak at 650-700 Hz, with a maximum absorption coefficient of 0.53. All of the six cores looked similar by visual inspection, and difference in maximum absorption coefficient could not be justified from that method. Figure 12 - Average absorption spectra in 1/3-octave bands [3]. The average absorption spectra in 1/3-octave bands is illustrated in Figure 12. The figure illustrates that the maximum absorption is in the 630 Hz band, with an absorption coefficient at 0.48. The absorption spectrum is a bit more shifted to lower frequencies, than expected from the thickness of the cores. A maximum absorption in the 1000 Hz band would be preferred, as the A-weighted sound pressure level emitted from the vehicles, are highest in that frequency band. Inter-noise 2014 Page 9 of 10

Page 10 of 10 Inter-noise 2014 6. CONCLUSION The SPB result for passenger cars at 60 km/h is 69.1 db. After 5 days the level has decreased 1.7 db which is quite remarkable. In the period from days 5 to 68 the noise level seems to be stabilized. The noise reduction in relation to Nord 2000 is after 68 days is 6.6 db. It must be remarked that a new dense asphalt concrete will have a noise level that will be around 2 db lower than the Nord2000 reference levels. After 248 days the noise level decreases about 1 db. The CPX measurements generally confirm these results. Comparing the spectra of the PERS to a new dense asphalt concrete with 11 mm aggregates (AC11d) the following can be observed: 1. From 160 to 800 Hz the PERS is 2 db lower than the AC11d. This can indicate that the PERS have smother texture caused by the smaller aggregate size (5 mm versus 11 mm) and is elastic compared to the AC11d. 2. From 1000 Hz to 2000 Hz the PERS is 5 to 6 db lower than the AC11d. In this frequency range the noise generated from vibrations in the tyre caused by the surface texture of the pavement is one of the dominant noise sources. This can also indicate that the PERS have smother texture than the AC11d. 3. From 2000 to 4000 Hz the PERS is 7 to 8 db below the AC11d. In this frequency range noise generated from air pumping is dominant. This indicates that the PERS has an open and porous structure. The result gives an indication that the PERS pavement for heavy vehicles has a SPB noise level 5 to 6 db below the Nord2000 reference level. This is one db less noise reduction than for passenger cars ACKNOWLEDGEMENTS The authors would like to thank the enthusiastic DRD and IFSTTAR staff for their work in performing measurements and analysis as well as the project coordinator Luc Goubert from the Belgian Road Research Centre (BRRC). This work is financed by the European Commission as well as by the Danish and French partners. The authors are grateful for the financial support for the major part of this project from the European Commission through its 7 th Framework Programme. REFERENCES 1. The PERSUADE homepage: http://persuade.fehrl.org/ 2. Bendtsen H, Olesen E, Pigasse G, Andersen B, Raaberg J, Kalman B, Cesbron J. Measurements at the Arnakke test site with small PERS sections. PERSUADE report; 2013. 3. Bendtsen H, Skov R, Stahlfest H, Andersen B, Olesen E, Neidel A, Raaberg J, Cesbron J. Performance of PERS at the Kalvehave test site. PERSUADE report; 2014. 4. Ellebjerg L, Bendtsen H. Two-layer porous asphalt lifecycle - The Øster Søgade experiment. Danish Road Directorate, Danish Road Institute, Report 165 (see: www.vejdirektoratet.dk); 2008. 5. Bendtsen H. Støjdæmpning over lang tid; støjreducerende tyndlagsbelægninger - Statusrapport 2010 (Noise reduction over long time, noise reducing thin layer pavements status report 2010 (in Danish with English summary)). Danish Road Directorate, Report (see: www.vejdirektoratet.dk); 2014. 6. Sandberg U, Ejsmont JA. Tyre/Road Noise Reference Book. INFORMEX (see: www.informex.info); 2002. Page 10 of 10 Inter-noise 2014