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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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