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Laboratory Evaluation of Annoyance of Low Frequency Noise
The primary results of the listening tests are the scalings made by the test subjects. The
scalings are given as values between zero and ten as measured from the test subjects
indications on the response lines. All the results are shown in Annex A of this report. In
chapter 6 it is shown that the annoyance during day/evening and the annoyance at night are
very closely related and thus it suffice at this point to look at only one type of
annoyance recordings. Table 2 below shows the average subjective evaluation - made by the
reference group of listeners - of the annoyance during night from the various sound
examples.
Table 2.
Subjective assessment by the reference group of the annoyance from the noise examples
if the noise was heard at night. Annoyance rating is given on a scale from 0 (not
annoying) to 10 (very annoying).
Nominal presentation
level |
20 dB |
27.5 dB |
35 dB |
Noise example |
Subjective annoyance
Night |
Subjective annoyance
Night |
Subjective annoyance
Night |
Traffic noise |
1.6 |
3.4 |
5.2 |
Drop forge |
4.3 |
5.9 |
6.9 |
Gas turbine |
0.9 |
2.5 |
5.2 |
Fast ferry |
0.9 |
3.2 |
5.4 |
Steel factory |
1.0 |
2.7 |
4.9 |
Generator |
1.7 |
3.2 |
5.0 |
Cooling compressor |
2.7 |
4.4 |
6.0 |
Discotheque |
3.0 |
5.4 |
6.7 |
It can be seen from the results in this Table 2 that the subjectively assessed annoyance
increases when the same type of noise is played louder; this is a general as well as an
expected result. It can also be seen that the different types of noise are not assessed
equally annoying; apparently the noises from the drop forge, the discotheque and the
cooling compressor are evaluated as more annoying than the other types of noise. This
gives some promise for interesting results from a closer inspection of the different
objective assessment methods they should be able to give some form of explanation
why these types of noise are considered more annoying than the others. On the other hand
it can be seen that the traffic noise is just as annoying as the main part of the low
frequency noise examples. It was the intention that this type of noise should serve as a
reference noise (which was not a particularly low frequency noise), and the listening
experiments should then indicate how much more annoying a number of different low
frequency noises would appear. But it seems that the filtering applied to the traffic
noise has turned this into another low frequency noise example.
In order to investigate the structure lying behind the average data, the raw data from
each listening test were typed into a spreadsheet. For each data the following information
was also recorded: the age and gender of the test person, the repetition number (round 1
or 2), the sound example number, the nominal presentation level, the measured A-weighted
level (dB(A)), and the A-weighted level of the sound in the frequency range 10 Hz
160 Hz, LpA,LF.
All data were subsequently transformed to a statistical analysis program (Statgraphics
4.0). It was found that if one disregarded data near the endpoints of the scales, the
responses almost followed a normal distribution curve. However since many of the responses
were near one or the other of the endpoints, the primary results were not normal
distributed. Despite this lack of normality in the distribution of the data it was decided
to perform an analysis of variance. The analysis was made for each parameter separately.
Table 3 shows the significance levels of the influence from a number of different
factors upon the evaluations of the reference group. If the number is less than 0.05, this
factor has a significant effect on the evaluation on a 95% level or above (this means less
than 5 % probability for drawing a wrong conclusion). If the number is above 0.05 it
cannot be proved that this factor has a significant effect upon the relevant evaluation.
Table 3.
The significance level of different factors that may influence the evaluation by the
reference group.
|
Loudness |
Annoyance day |
Annoyance night |
Annoying? (Y/N) |
Noise example |
0.0000 |
0.0000 |
0.0000 |
0.0000 |
Nominal level |
0.0000 |
0.0000 |
0.0000 |
0.0000 |
dB (A) |
0.0000 |
0.0000 |
0.0000 |
0.0000 |
LpA,LF |
0.0000 |
0.0000 |
0.0000 |
0.0000 |
Repetition no. |
0.5814 |
0.6123 |
0.6804 |
0.1533 |
Gender |
0.1888 |
0.0001 |
0.0001 |
0.0654 |
It is seen from Table 3 that as expected the noise example, the nominal
level, the dB(A) level and the low-frequency level (LpA,LF), all have a
significant influence upon the evaluations from the test persons.
The repetition number (round 1 or round 2 with the same presentation) has no
significant influence, which shows the absence of a training effect. The gender of the
test persons has influence on the evaluation of annoyance during the day and during the
night but not on the evaluation of loudness and on the yes/no question about whether the
noise is annoying or not.
A corresponding analysis was made with the data from the special group. Since this
group has only four persons the data are very uncertain and highly dependent on random
variations. The result of the analysis is shown in Annex A. It is found that the noise
level influences the evaluations. The influence from noise example on the annoyance
evaluations is just at the limit of being significant.
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