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Noise annoyance and its measurement

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Słyszenie w środowisku<br />

Wykład VII<br />

Anna Preis, email:<br />

apraton@amu.edu.pl<br />

24.04.2013


How to test if soundscape changes into noisescape?<br />

<strong>Noise</strong> <strong>annoyance</strong> <strong>and</strong> <strong>its</strong> <strong>measurement</strong><br />

Anna Preis<br />

apraton@amu.edu.pl


L<strong>and</strong>scapes


Soundscape


Soundscape<br />

The Tuning of the World formalized the soundscape terminology Schafer had devised<br />

during his field studies with the WSP:<br />

Background sounds he defined as “keynotes” (in analogy to music where a keynote<br />

identifies the fundamental tonality of a composition around which the music<br />

modulates);<br />

Foreground sounds (intended to attract attention) are termed “sound signals.”<br />

Sounds that are particularly regarded by a community <strong>and</strong> <strong>its</strong> visitors are called<br />

“soundmarks”—in analogy to l<strong>and</strong>marks.<br />

Natural examples of the latter include geysers, waterfalls <strong>and</strong> wind traps while<br />

cultural examples include distinctive bells <strong>and</strong> the sounds of traditional activities.<br />

(Schafer 1977a: 9, 55-56, 173-175, 272-275; Truax 1978: 68, 119, 127; 1984: 22,<br />

58-60).<br />

K. Wrightson, (2000) An Introduction to Acoustic Ecology.The Journal of Acoustic<br />

Ecology, 1(1).<br />

Soundscape exists through human perception of the acoustic environment<br />

A. L. Brown (2010) Soundscapes <strong>and</strong> environmental noise management <strong>Noise</strong><br />

Control Eng. J., 58(5)


Underst<strong>and</strong>ing urban <strong>and</strong> natural soundscapes<br />

• Dick Botteldooren, Department of Information Technology, Ghent University, Gent,<br />

Belgium.<br />

• Catherine Lav<strong>and</strong>ier, Laboratory MRTE, University of Cergy Pontoise, F-95000<br />

Cergy Pontoise, France<br />

• Anna Preis, Institute of Acoustics, Adam Mickiewicz University, Poznan, Pol<strong>and</strong><br />

• Daniele Dubois, Institut Jean le Rond d'Alembert, Equipe LAM, CNRS, France,<br />

INCAS3, Assen, The Netherl<strong>and</strong>s.<br />

• Itziar Aspuru, Labein-Tecnalia, Environmental Unit, Spain<br />

• Catherine Guastavino, McGill University, School of Information Studies <strong>and</strong><br />

CIRMMT (Centre for Interdisciplinary Research on Music, Media <strong>and</strong> Technology),<br />

Montréal, QC, Canada.<br />

• Lex Brown, Griffith School of Environment, Griffith University, Nathan 4111,<br />

Australia<br />

• Mats Nilsson, Department of Psychology, Stockholm University, Sweden<br />

• Tjeerd C. Andringa, Artificial Intelligence, University of Groningen, The<br />

Netherl<strong>and</strong>s. INCAS3, Assen, TheNetherl<strong>and</strong>s.<br />

Working Group 1 of the COST action<br />

“Soundscapes of European cities <strong>and</strong><br />

l<strong>and</strong>scapes”


Professor Lex Brown, Griffith University, Australia<br />

<strong>Noise</strong> Control<br />

Approach<br />

Sound as waste<br />

Concerns sound of discomfort<br />

Human response related to<br />

level of sound<br />

Measures by integrating across<br />

all sound sources<br />

Manages by reducing level<br />

Soundscape Approach<br />

Sound as resource<br />

Concerns sounds of preference<br />

Preference often unrelated to<br />

level - quiet not the objective<br />

Requires differentiation<br />

between sound sources –<br />

wanted sound from unwanted<br />

sound<br />

Manages by “wanted sounds”<br />

masking “unwanted sounds”


Sound environment versus noise environment<br />

Soundscape<br />

• Perception <strong>and</strong> recognition of<br />

different sound sources in the<br />

environment<br />

• Soundscape perception: auditory<br />

scene analysis based on streams<br />

segregation<br />

• Criteria of segregation: loudness,<br />

pitch, timbre, location<br />

• Scaling the preferences of<br />

different soundscapes<br />

<strong>Noise</strong>scape<br />

• Occurrence of noise which disturbs<br />

perception to such a degree that it is<br />

impossible to recognize sound sources in<br />

the environment<br />

• <strong>Noise</strong>scape as a source of disturbance of<br />

human activity such as communication,<br />

work, studying<br />

• <strong>Noise</strong>scape threshold: degree of<br />

disturbance which makes the<br />

performance of a given activity<br />

ineffective<br />

• Speech intelligibility in noise is well<br />

defined <strong>and</strong> could be a measure of noise<br />

<strong>annoyance</strong> related to communication<br />

activity


Disturbed l<strong>and</strong>scape


Disturbed soundscape = noisecape<br />

White noise<br />

Specific noise


<strong>Noise</strong> <strong>annoyance</strong><br />

Traditional approach<br />

• L DEN one noise index<br />

• <strong>Noise</strong> maps for different sound<br />

sources<br />

• St<strong>and</strong>ardized method of noise<br />

<strong>annoyance</strong> scaling<br />

• <strong>Noise</strong> parameter is scaled<br />

• Annoyance is related to noise<br />

parameter<br />

• (Dose –response characteristics<br />

%HA versus L DEN )<br />

<strong>Noise</strong>scape approach<br />

• Difficulty in performing a<br />

given activity disturbed by<br />

noise is scaled<br />

• The degree of difficulty in<br />

performing a given activity is<br />

a measure of noise<br />

<strong>annoyance</strong> assessment<br />

• <strong>Noise</strong> <strong>annoyance</strong> assessment<br />

depends on the degree of<br />

disturbance in the human<br />

activity


Traditional approach: noise <strong>annoyance</strong> in rest<br />

• ISO/TS 15660:2003, recommended by ICBEN<br />

• verbal rating scale: Thinking about the last (...12 months or so),when<br />

you are here at home, how much does noise from (….noise source...)<br />

bother, disturb, or annoy you?<br />

• (1) Not at all? (2) Slightly? (3) Moderately? (4) Very? (5) Extremely?<br />

• numerical rating scale: Thinking about the last (...12 months or<br />

so),what number from zero to ten best shows how much you are<br />

bothered, disturbed, or annoyed by the presented noise events?<br />

• If you are not at all annoyed choose zero, if you are extremely<br />

annoyed choose ten, if you are somewhere in between, choose a<br />

number between zero <strong>and</strong> ten.<br />

Preis, A., Kaczmarek, T., Wojciechowska, H., Żera, J., Fields, J.M. (2003), "Polish version of the st<strong>and</strong>ardized noise<br />

reaction questions for the community noise surveys," International Journal of Medicine <strong>and</strong> environmental Health<br />

16(2): 155-159


<strong>Noise</strong> <strong>annoyance</strong> related to rest <strong>and</strong><br />

communication activity<br />

• <strong>Noise</strong> disturbs<br />

rest<br />

• <strong>Noise</strong> disturbs<br />

communication activity<br />

traditional scaling of<br />

noise <strong>annoyance</strong> (ISO/TS<br />

15660:2003,<br />

recommended by ICBEN)<br />

verbal rating scale<br />

numerical rating scale<br />

difficulty of comprehending<br />

speech in noise is a<br />

measure of noise<br />

<strong>annoyance</strong><br />

speech intelligibility score


<strong>Noise</strong> <strong>annoyance</strong> scale related to noise parameters<br />

sound<br />

parameters of<br />

sound increase<br />

L, S, R, F<br />

different models<br />

of noise <strong>annoyance</strong><br />

unwanted sound<br />

= NOISE<br />

<strong>Noise</strong> <strong>annoyance</strong> scale related to communication - speech intelligibility scores<br />

work<br />

work<br />

disturbance<br />

<strong>Noise</strong>scape- measure of work<br />

disturbance<br />

soundscape<br />

noise<br />

communication<br />

communication<br />

disturbance<br />

<strong>Noise</strong>scape-measure of<br />

communication disturbance<br />

Speech<br />

intelligibility in<br />

noise<br />

rest<br />

rest<br />

disturbance<br />

<strong>Noise</strong>scape- measure of rest<br />

disturbance


Rest<br />

<strong>Noise</strong> <strong>annoyance</strong> scaling


<strong>Noise</strong> <strong>annoyance</strong> scaling<br />

Communication activity


<strong>Noise</strong>scape related to the communication activity<br />

Equal difficulty in speech recognition<br />

Equal <strong>annoyance</strong> rating<br />

SRT ---- 50% speech recognition<br />

Averaged speech reception thresholds for nine<br />

environmental noises expressed as an arithmetical<br />

means <strong>and</strong> 95% of coincidence interval.<br />

The measure of difficulty of speech comprehension<br />

for nine noises expressed as medians <strong>and</strong> their<br />

interquartile ranges.<br />

A. Preis, H. Hafke-Dys, T. Kaczmarek, T. Gjestl<strong>and</strong> (2011) The relationship between speech reception thresholds <strong>and</strong> the<br />

assessment of <strong>annoyance</strong> caused by different environmental noises <strong>Noise</strong> Control Eng. J. 59 (4), 408-414.


One point relationship between noise <strong>annoyance</strong><br />

<strong>and</strong> speech intelligibility<br />

Difficulty in speech<br />

comprehension<br />

<strong>annoyance</strong> related to<br />

communication activity<br />

Speech intelligibility<br />

What about the other points?


The relationship between speech intelligibility <strong>and</strong><br />

the assessment of <strong>annoyance</strong> caused by<br />

environmental noises<br />

Anna Preis, Honorata Hafke-Dys, Tomasz Kaczmarek<br />

Institute of Acoustics, Adam Mickiewicz University, Poznan, Pol<strong>and</strong><br />

Truls Gjestl<strong>and</strong><br />

SINTEF ICT, Trondheim, Norway


Aim of the study<br />

To find out if the speech intelligibility in noise can be<br />

used as the <strong>annoyance</strong> measure of this noise<br />

To assess the difficulty in speech comprehension in<br />

noise<br />

• Aniansson, G., Bjὂrkman, M., “Traffic noise <strong>annoyance</strong> <strong>and</strong> speech intelligibility in persons with normal<br />

<strong>and</strong> person with impaired hearing” Journal of Sound <strong>and</strong> Vibration 88(1), 99-106, (1983).<br />

• Ellis L.W, Pakulski L., “Judgments of speech intelligibility <strong>and</strong> speech <strong>annoyance</strong> by mothers of children<br />

who are deaf or hard of hearing” Perceptual <strong>and</strong> motor skills 96, 324-8, (2003).


<strong>Noise</strong> L AeqT (dB) SRT (dB)<br />

Bus_in 83.5 -28.6<br />

Tram_1_in 76.5 -23.4<br />

Train_out 75.0 -20.4<br />

Tram_out 73.9 -15.1<br />

Street 73.8 -13.0<br />

School_in 73.5 -10.0<br />

Plane_out 71.8 -9.8<br />

Babble noise 68.2 -7.7<br />

50% speech intelligibility<br />

Speech level was 65dB <strong>and</strong> noise level was respectively -6, -4, -2,<br />

0=SRT, 2, 4, 6. Each subject was presented with his SRT from the<br />

previous experiment


Experiments<br />

Experiment I:<br />

part 1: speech intelligibility was measured for eight<br />

environmental noises at seven signal-to-noise ratios (SNRs).<br />

part 2: for these SNR values, the participants assessed the<br />

difficulty in speech comprehension<br />

Experiment II:<br />

the st<strong>and</strong>ard method of noise <strong>annoyance</strong> assessment was used<br />

to the same noises as in Experiment I<br />

Participants<br />

nineteen university students, 8 males <strong>and</strong> 11 females aged<br />

between 20 <strong>and</strong> 25, took part in both psychoacoustic<br />

experiments


Are they equal or not?<br />

Annoyance related to<br />

communication activity<br />

• difficulty in speech<br />

comprehension<br />

Annoyance related to<br />

the rest<br />

• traditional noise <strong>annoyance</strong><br />

assessment<br />

speech communication<br />

rest?<br />

Experiment 1 part 2 Experiment 2


Speech samples<br />

The Polish sentence matrix test (PSMT). The speech was presented to<br />

the participants at the constant level of 65 SPL.<br />

The PSMT consists of 10 names, 10 verbs, 10 numerals, 10 adjectives,<br />

<strong>and</strong> 10 nouns, i.e. a total of 50 different words that can be used<br />

to build 100000 different sentences. More details <strong>and</strong> properties of<br />

a PSMT can be found in Ozimek et al., 2010.


<strong>Noise</strong> samples - maskers<br />

• noise in a school corridor during the break.<br />

• a busy road taken about 35 meters from the middle of the<br />

road.<br />

• a bus interior (Neoplan) during normal drive conditions.<br />

• a tram type 105N2k-2000 interior during the normal drive<br />

conditions.<br />

• a jet airplane over-flight.<br />

• an Inter-City train pass-by taken 25 m from the rail track.<br />

• a tram type 105n pass-by taken 25 m from the rail track.<br />

• babble noise (uniform noise created from a speech by<br />

averaging a large number of a Polish-language speech<br />

material).


Experiment I - part 1:<br />

Psychometric curve for speech intelligibility scores<br />

• The method of constant stimuli was used to obtain the<br />

speech intelligibility function for 7 values of SNR: -6 dB, -4<br />

dB, -2 dB, 0 dB, 2 dB, 4 dB, 6 dB. (SNR 0dB=SRT)<br />

• Each masker (8 environmental noises) was presented with a<br />

list of 20 sentences consisting of 5 r<strong>and</strong>omly chosen words<br />

from the Polish sentence matrix test (PSMT)<br />

• After the utterance of a sentence, a five column (names,<br />

verbs, numerals, adjectives) - 50-word push-button panel<br />

was displayed on an LCD screen. The participants’ task was<br />

to indicate words from the played-back sentence <strong>and</strong><br />

confirm their choice with the ‘OK’ button


Experiment I - part 2:<br />

Assessment of difficulty in speech comprehension<br />

After each utterance the participants were prompted to assess their difficulty in<br />

comprehending speech on an ascending scale from 0 to 10, where 0 means not at all<br />

difficult <strong>and</strong> 10 extremely difficult<br />

Push-button with a question about the difficulty in speech comprehension


Experiment I -results


Experiment I: results presented for each SNR


A<strong>annoyance</strong> rating – speech intelligibility<br />

y=9.0403e -0.749x


Experiment II:<br />

Assessment of noise <strong>annoyance</strong> presented alone<br />

Push-button with the question about the noise <strong>annoyance</strong><br />

scaling


Comparison of <strong>annoyance</strong> assessment


Results of Experiment I <strong>and</strong> II


Comparison of <strong>annoyance</strong> assessment


Conclusions<br />

• The best approximation of the relationship between the speech<br />

intelligibility <strong>and</strong> difficulty in speech comprehension is the following<br />

exponential function y=9.0403e -0.749x . This relationship was<br />

obtained for 7 different SNR values of eight environmental noises<br />

(Experiment I)<br />

• The differences between <strong>annoyance</strong> ratings which were assigned to<br />

the same noises during different activities, are not statistically<br />

significant (Experiment I <strong>and</strong> II) for SNR= 0, 2, 4, 6.<br />

• The outcome of this study is restricted to the situation where<br />

speech is presented to the listener at 65 dB sound level <strong>and</strong> the<br />

Polish sentence matrix test (PSMT) test is applied


• Thank you for your kind attention!<br />

• Dr Honorata Hafke-Dys, dr Tomasz Kaczmarek – co-authors of<br />

the presented results<br />

• Mgr Paweł Libiszewski , dr Jędrzej Kociński –technical<br />

assistance<br />

• This work was supported by the grant from the Polish-<br />

Norwegian Research Fund – project no. PNRF-167-AI-1/07.


Polish-Norwegian Research Fund<br />

Quality of public life determined by good hearing <strong>and</strong> speech<br />

communication<br />

SP 1<br />

Auditory research in the light of<br />

speech intelligibility<br />

SP 2<br />

Speech intelligibility as an index of the<br />

quality of public life<br />

WP 1<br />

Development of<br />

new sentence<br />

intelligibility tests<br />

for children <strong>and</strong><br />

improvement of<br />

recently designed<br />

tests for adults<br />

WP 2<br />

Development of new<br />

environment noise <strong>annoyance</strong><br />

index related to intelligibility<br />

data<br />

WP 3<br />

Application of new<br />

intelligibility tests to<br />

assessment of acoustic<br />

quality of hearing aids<br />

<strong>and</strong> implants<br />

WP 4<br />

Intelligibility tests aimed at<br />

evaluation of acoustic<br />

quality of public buildings<br />

<strong>and</strong> improvement of<br />

Internet <strong>and</strong> telephone<br />

procedures for self-testing<br />

intelligibility

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