Open Journal of Acoustics Vol.04 No.03(2014), Article ID:48862,9
pages
10.4236/oja.2014.43011
Loudness Summation and Weightings for Loudness and Environmental Noise Assessment
Juhani Parmanen
Espoo, Finland
Email: ej.parmanen@gmail.com
Copyright © 2014 by author and Scientific Research Publishing Inc.
This work is licensed under the Creative Commons Attribution International License (CC BY).
http://creativecommons.org/licenses/by/4.0/
Received 1 July 2014; revised 23 July 2014; accepted 20 August 2014
ABSTRACT
A stationary loudness model has been built up on the basis of the former ISO 226: 1987 concerning equal-loudness-level contours. The loudness and loudness level expressions derived in the study include the same parameters as used when determining the equal-loudness-level contours of the former ISO standard. However, as an additional main idea, a loudness summation rule has been proposed in the study. Moreover, the loudness expressions have been normalised to give the same values for people who have a similar sense of hearing. It has also been found that the loudness expressions include basically two different weightings. The first weighting is a conservative frequency weighting in the domain of sound pressure level, and the second weighting consists of coefficients applied to the weighted sound pressure levels. The latter have the greatest effect on the very low-frequency range. Finally, the paper includes a new way to use the A-weighting which takes into account the compressed character of the equal-loudness-level contours at the low frequency range. This method remarkably transforms the character of the A-weighting as a measure for low-frequency environmental noise.
Keywords:
Loudness, Loudness Level, Loudness Summation, Frequency Weightings, A-Weighting, Low Frequency Noise
1. Introduction
In [1] it was shown that an equal-loudness-level contour can be calculated according to an equation of the following type:
, (1)
where
is the stimulus sound pressure level, dB, and
(or also
when not a constant parameter) is the equal-loudness level (parameter) of the contour
considered, phon. The constant 3.30 comes from S. Stevens’ power law [2] which shows
that at 1000 Hz, loudness is proportional to sound intensity (sound pressure squared)
according to the relation
. (2)
Additionally, in Equation (1),
(the root notation)
represents the inverse of the exponent of intensity at each frequency band which
has the value of 3.3 (0.3 ≈ 1/3.3) at 1000 Hz band and takes the value shown in
Table 1 at the other 1/3 octave band frequencies,
and finally,
(in Table 1) is a frequency weighting defined in the domain of
sound pressure level at each frequency band.
Both parameters
and
in Table 1 were determined based on the former
ISO 226: 1987 [3] . The parameter
was determined at each band from
because this quantity was found to be practically constant at each frequency band
(the former ISO 226: 1987 and the current ISO 226: 2003 [4] differ in this respect),
so that
. (3)
The weighting
was determined from the 40-phon contour using the equation
. (4)
The equal-loudness-level contours [3] and the contours constructed according to
Equation (1) are shown in Figure 1. The contour
complexes are so similar that they could be replicas of each other. In [1] , the
author also suggested that the method to calculate loudness or loudness level would
be
, (5)
(here “lg” is log based on 10) by assuming that the loudness in different 1/3-octave
bands integrate by direct adding. However, perhaps this is not the case. On the
other hand, it seems prominent that Equation (5) and the former equal-loudness-level
contours ISO 226 [3] have the same acoustically definable parameters
and
although the parameters do not exist in the former ISO 226.
Table 1. Roots (determined
based on the range between equal-loudness-level contours 20 - 70 phon [3] ) and
the
-
weighting (calculated based on the 40-phon contour [3] ) and the A-weighting
.
Figure 1. Equal-loudness-level contours from ISO 226: 1987 [3] and the respective contours derived in [1] .
However, irrespective of the similarities of the contour complexes above, no rules to connect the different frequency bands with respect to achieve the total loudness seem to be available. Therefore, some questions arise here. The questions are:
· What is the meaning of the factor 33 before the log operator “lg” and should the loudness level equation include a constant additive term?
· Does the assumed adding process work?
· What is the connection between the loudness level equation and the equations based on the A-weighted sound pressure levels?
This study attempts to give an answer to these questions. Of course, many questions remain outside this paper. These include for example: numerous time-varying effects concerning signal types in general, signal/loudness summation (time), effects of signal duration, caused adaptation, etc. In addition, critical bands (overlapping, for example) are also not considered in this paper. The latter may also have consequences on the stationary model considered here. On the other hand, however, a well-defined stationary loudness model may be necessary when developing more advanced dynamic loudness models.
2. Terms, Summation and Weightings
2.1. Factor “33”
In the following, to avoid the use of the unit “phon” and its definition [5] , we
define a decibel as having a logarithmic base of two (2) including an additive constant
of 40 and denote the units of such a decibel by dB2. Then, for any positive
quantity
. (6)
Thus here,
clearly
makes sense so far as
makes sense, and
unequivocally determines the defined logarithmic quantity in units of dB2
and vice versa. Therefore, in this paper, the quantity
(later also
or
)
has been used as the primary quantity for direct loudness sensation. In particular,
if
happens to be a loudness function or expression [5] , the following relation between
the loudness level
or
in phons and the loudness in sones is valid [5]
. (7)
Here the loudness level
(or generally
)
of a sound is expressed as
phons when it is judged by normal observers to be equally loud to a pure tone (or
a narrow band noise) at the frequency of 1000 Hz which has the sound pressure level
of
decibels. In particular, the relation has been defined to hold exactly by denoting
as 40 phons the equal-loudness-level contour which crosses 40 dB at the decibel
axis. Additionally, the standard [5] includes the following note:
· The term phon, without a qualifying abbreviation, should be reserved for the expression of loudness levels determined by direct subjective measurement.
Moreover, the standard [6] states the following note:
· Experimental confirmation of this relation (Equation (7)) exists over the range 40 to 105 phons, and its use outside this range should be recognized as an extrapolation.
Therefore, in the following, we use the term “loudness level”, but “dB2” as the unit of such a level defined above. Namely, in this study the direct loudness sensation S (in sones) is proportional to the subjective magnitude as estimated by normal observers and the loudness level has been defined only mathematically as stated above. Therefore, the notes in standards [5] and [6] are not restrictive in this study. In addition, some definitions are needed for reference purposes. As stated in [7] by the author, a sound in sound pressure levels (dB) at 1000 Hz (see above) is designated to represent the loudness S of one sone (=40 phons respectively). Such a sound must be defined for reference purposes (referring to normal hearing) and to fix the subjective loudness level and the loudness function unequivocally at the physical dB axis. If such a sound is designated to be a tone or narrow band noise of 40 dB at 1000 Hz frequency band (representing one sone for normal observers), the logarithmic decibel and phon coincide at 1000 Hz by definition. However, that also concerns dB2, because the definitions of the phon and dB2 levels do not differ at the point considered, so that
. (8)
when deriving the equal-loudness-level complexes in [1] , Stevens’ power law [2] was assumed to hold over the whole sound pressure level range. Therefore Equation (2) must be written [7] as
. (9)
Then Equation (9) is satisfied if
takes the value
,
and as a consequence, Equation (5) takes the form
(10)
which is the same as Equation (5) and thus no additive constant is needed here. The conclusion here is: the loudness function (the direct subjective, normalised strength of auditory perception) is now (in sones) a non-lo- garithmic equation of type
. (11)
when replacing the root
by
,
Equation (11) can be written as follows
(12)
where the last equation shows how the loudness levels in 1/3-octave bands (, dB2)
should be taken into account when the calculations are based on S. Stevens’ power
law and the logarithmic definitions above.
2.2. Loudness summation
As concluded above, the actual loudness is proportional to the total sum
of
terms
. (13)
Then if, for example, one considers a case where only two terms exist, the sum becomes
. (14)
If, now, it happens that both bands
have approximately the same loudness level value (45 dB2 with
for
example),
becomes
.
Thus one can see that we have doubled the one single loudness value. That would
mean that, in this case, the loudness level has increased by approximately 10 dB2.
However, the sound pressure level has increased by only 3 dB. Therefore some reservations
arise here. Namely, based on the power law we needed 10 dB to be added to the sound
pressure level at 1000 Hz to get double loudness and 10 dB2 more in loudness
level. Therefore here, we define the summation (by hypothesis) by the following
rule:
. (15)
Thus, Equation (15) differs from Equation (13) in that respect that the exponent
of
is –(23/33) instead of zero in Equation (13). In addition Equation (15) has been
written in a certain manner including an average in the last parentheses. The loudness
level (dB2) now becomes
. (16)
In the case of the sum
above, one now gets
having a value of
which is 1.23 times the one single loudness value giving 3 dB2 more in
loudness level. By using Equation (15), (16) can also be written in the form
. (17)
A formally similar equation to Equation (17), with respect to the number
of the frequency bands and average, can be written for the usual A-weighted sound
pressure level, i.e.
. (18)
Thus it seems that the numerous measurements and calculations with the A-weighted sound pressure levels support the chosen summation rule (the hypothesis of the study). Then, the total summation-adjusted loudness expression, the direct subjective normalised strength of auditory perception, is finally (in sones) an equation, still non-logarithmic, of type
. (19)
Here the first factor in parentheses includes a normalising procedure giving one sone whenever the rest of the
expression takes the value of,
and the second factor in parentheses with the averaging n control the
loudness summation as defined above.
2.3. The A-weighting
In [1] the author performed some comparisons between the frequent A-weighted sound
pressure levels
and levels which take into account Stevens’ power law. The expressions considered
were respectively as follows:
(20)
, (21)
where
was an abbreviation of the words Loudness Related A-weighted Level. Here the unit
dB2 as defined above has also been assumed to apply to Equation (21)
and the A-weighted sound pressure level Equation (20). This helps to see behind
the logarithmic total levels by determining the total loudness function using the
inverse relation between the loudness and loudness level. In such a case the loudness
expression
(A-wei-
ghted) from which Equation (20) has been derived is
. (22)
The respective loudness expression
for Equation (21) is
. (23)
One can easily verify that the applications
and
give the desired dB2-levels
shown in Equations (20) and (21). Concerning the difference between the expressions
(22) and (23), only the root 3.3 has been removed with respect to the parentheses
and sum, and in Equation (23) the root 3.3 does not concern the number
of frequency bands. Of course, such a difference is very important [1] and on the
basis of the measurements by Tachibana and his colleagues [8] - [10] , it seems
that the variation of the last average in the parentheses with the exponent of 1/3.3
takes too great and uncontrolled values. Namely, in [1] the respective identities
to Equations (20) and (21) were also written
, (24)
. (25)
The author [1] deduced here that in Equations (24) and (25), only the third log
terms
and
differ and that the latter term
is always smaller than the first term
.
Additionally, both terms are positive or equal to zero. The equality sign only appears
when both terms are zero. This result supported the measurements by Tachibana and
his colleagues [8] - [10] showing that the loudness level is closely related to
the arithmetic mean (by adding
)
of the sound pressure levels. An example here was a calculation with different noises
added with a 1000-Hz tone performed by Hellman and Zwicker [11] with the loudness
calculations based on the standard ISO 542B [5] (and partly supported by subjective
measurements). The data for broad band noise (BBN) in the frequency range 100 -
7000 Hz with the tone (Tone) are listed in Table 2.
The results [11] concerning pink noise and added different tones are shown in Figure 2, showing that the loudness of the tone-noise complexes and the respective A-weighted total sound pressure levels (Equations (20) and (24)) are partly negatively correlated.
The same figure has been repeated (Figure 3) when
replacing the A-weighted sound pressure level by the level expression according
to Equation (25), the only difference with respect to Equation (23) being that the
power law has been taken into account in the third log term.
The difference between Figure 2 and Figure 3 is dramatic. In particular, in Case 2, the difference
between
and
is very large: the values are 18.7 and 4.6 dB2 respectively and the difference
becomes 14.1 dB2. On the other hand, in Case 7, the respective values
are 3.1 and 1.0 dB2 with a difference of only 2.1 dB2. The
conclusion here is that the A-weighting would correlate much better with loudness
if the power law was taken into account when assessing noise in general (see the
order of the case points (x-axis) in Figure 2 versus
in Figure 3).
In terms of loudness, the respective levels
according to Equations (16) or (17) become as shown in
Figure 4. The deviations from a straight line in Figure
4 are also small, but
cannot separate Cases 1, 4 and 6. That seems to occur because of the same broad
band noise spectrum in these cases. The respective tones are 76, 81 and 86 dB, which
is not enough to separate the levels with respect to loudness. If the tone was removed
from the 1000 Hz to 200 Hz frequency band, the respective levels
were 87.6, 88.1, and 88.8 dB2. The reasons for these deviations can be
explained by writing for
an equation similar to Equation (24) or (25), i.e.
. (26)
Table 2. Unweighted sound pressure levels and respective tone levels [11] , and A-weighted pink noise total levels.
Figure 2. A-weighted levels and the respective loud- ness levels [11] .
Figure 3. A-weighted levels LRAL, dB2 [1] and the respective loudness levels [11] .
Figure 4. LLL levels, dB2 and the respective loudness levels [11] .
Equation (26) has generally similar properties to Equation (25). However, the main
part of the loudness level consists of the first sum/average (a linear sum with
the coefficients)
and
.
The third log term is such that it takes the value zero if the spectrum
coincides with an equal-loudness-level contour within the whole frequency band range
(
bands)
under consideration. On the other hand, now the total loudness level includes two
frequency weightings: the first weighting is the conservative
-weighting
in the domain of sound pressure level and the second weighting is a coefficient
concerning the weighted terms
.
The coefficient
takes the values from 1.90 to 1.00 and the maximum values appear at the lowest frequencies.
Therefore, the tones separate more effectively in the low-frequency range. In particular,
this is of great importance when assessing low-frequency noise. Finally, the double-weighting
property of Equation (26) vs Equation (25) has a dramatic consequence: none of the
equal-loudness-level contours is an inverse frequency weighting of a known or defined
frequency weighting alone (A-weighting concerning 40-phon, for example).
In [12] Schomer stated: “The hypothesis to this paper is that the equal-loudness-level contours can be used as a dynamic weighting function that varies with frequency and level.” However, when taking into account the above statement concerning the double-weighting, this hypothesis does not make sense, and it must be rejected. In fact, Schomer did not define any weighting but only determined the loudness levels using the equations given in the former ISO 226 [3] . Schomer also suggested calculating the overall phon level from 1/3-octave band phon levels by summation on an energy basis. In this paper the summation is based on the power law. Therefore, Schomer’s overall phon levels differ from the levels calculated in this study in such a way that the following applies:
(27)
which can be easily verified using Equations (12), (22) and (23), for example.
Finally, because the comparison of the different equal-loudness-level contours with
the frequency weightings applied to sound pressure levels does not make sense, a
new way to apply the A-weighting is achieved by replacing the
-weighting
in Table 1 by the A-weighting. Then, the A-weighted
loudness/annoyance function from Equation (19) becomes
, (28)
and the respective levels from Equation (16) become
. (29)
Here, Equations (28) and (29) are based on a similar structure to the equations
concerning loudness and loudness levels. Only the weighting has been changed to
the A-weighting, because this weighting is mostly used when assessing noise from
the annoyance point of view. Because of the similarities to the terms in the former
ISO 226 [3] , the equal loudness/annoyance level contours can now be constructed
(maintaining the compressed character of the equal-level contours in the low-frequency
range) using Equation (1) above. In Figure 5, the
40-phon contours [3] and [4] have been drawn. The 40-dB2(A) equal-level
contour (the A-weighting replacing the fixed frequency weighting
derived for the former ISO 226 [3] ) has been drawn in the same figure.
One can see that the most severe (or the most sensitive) contour, in particular
in terms of the low-frequency range, is the contour including the A-weighting which
replaces the frequency weighting in an auditory perception system. At the high-frequency
range the respective sensitiveness remains unchanged because of the small values
of the coefficients.
Finally, one may suggest that the system has no singularity below the 20 Hz frequency
band. Rather, the system continues to the left. Therefore, the new way of applying
the A-weighting may also render it suitable for assessing very low-frequency noise
from, for example, wind turbines [13] .
3. Conclusions
A loudness or a loudness level function requires that it is normalised so that it gives the same loudness value and loudness level for people who have similar (normal) hearing. In the study, a certain logarithmic base of two was used with an additive constant of 40 dB2 when determining the loudness levels, and the levels were only used for numerical assignment (separated from the direct loudness sensation which is seen as non-logarithmic
Figure 5. The 40-phon equal-loudness-level contours of ISO 226: 2003, and of ISO 226: 1987 and the 40-dB2(A) equal-level contour.
through out the whole study) in the way that we use decibels for characterising the sound pressures. The logarithmic base was chosen on the basis of Stevens’ power law and gave the first final result (Equation (10)) that the derived loudness level does not need any additive constant in this respect.
As regards loudness summation it was stated that loudness or a loudness level expression includes a main problem of how to proceed when connecting the loudness values at different frequency bands. The problem is important because, in practice, the number of the frequency bands has to be a variable. In the study the hypothesis was that when applying a direct summation of loudness at each frequency band, the number of the frequency bands has too great an effect on the final result. Therefore, the exponent of the number of bands in a loudness expression has to take a negative value instead of zero in the direct summation process. The exponent value has been chosen (by hypothesis) to be –23/33 in this study. The proposed method was supported by the finding that the A-weighted total sound pressure level formally includes a similar summation rule. Lacking subjective data, this rule has not been otherwise tested in the study. However, this was the second main result (Equation (16) and (17)) of the study.
It was also shown that the expression of loudness and loudness level expressions
can be written as identical formulas so that one can separate some essential parts
which finally define the behaviour of the whole loudness system and expressions.
The third main result (Equation (26)) revealed that the total loudness level includes
two frequency weightings of different types: the first weighting is a conservative
weighting in the domain of sound pressure level, and the second weighting is a coefficient
applied to the weighted sound pressure level terms
.
Finally, the double-weighting property of the auditory perception system seemed
to have a surprising consequence for loudness and loudness levels: none of the equal-loudness-level
contours is an inverse frequency weighting alone.
Finally, because the comparison of the different equal-loudness-level contours with
the frequency weightings did not seem to make sense, a new way of applying the A-weighting
for annoyance purposes was proposed which entailed replacing the loudness system
weighting by the A-weighting. Then it was found that the most severe 40-phon (or
40-dB2) contour, for example, in particular as regards the low-frequency
range, is the contour derived on the basis of the A-weighting. This was the final
main result (Equation (29)) of the study.
References
- Parmanen, J. (2007) A-Weighted Sound Pressure Level as a Loudness/Annoyance Indicator for Environmental Sounds— Could It Be Improved? Applied Acoustics, 68, 58-70. http://dx.doi.org/10.1016/j.apacoust.2006.02.004
- Stevens, S. (1961) The Psychophysics of Sensory Function. In: Rosenblith, W., Ed., Sensory Communication, MIT Press, Boston.
- International Standardization Organization. ISO 226: 1987 (E) Acoustics—Normal Equal-Loudness-Level Contours. Geneva.
- International Standardization Organization. ISO 226: 2003 (E) Acoustics—Normal Equal-Loudness-Level Contours. Geneva.
- International Standardization Organization. ISO 532: 1975 (E) Acoustics—Method for Calculating Loudness Level. Geneva.
- International Standardization Organization. ISO 131: 1979 (E) Acoustics—Expression of Physical and Subjective Magnitudes of Sound or Noise in Air. Geneva.
- Parmanen, J. (2012) Some Reasons to Revise the International Standard ISO 226: 2003: Acoustics—Normal Equal- Loudness-Level Contours. Open Journal of Acoustics, 2, 143-149. http://dx.doi.org/10.4236/oja.2012.24016
- Tachibana, H., Hamada, Y. and Sato, F. (1988) Loudness Evaluation of Sounds Transmitted through Walls—Basic Experiments with Artificial Sounds. Journal of Sound and Vibration, 127, 499-506. http://dx.doi.org/10.1016/0022-460X(88)90375-6
- Tachibana, H., Yano, H. and Sonoda, Y. (1990) Subjective Assessment of Indoor Noises—Basic Experiments with Artificial Sounds. Applied Acoustics, 31, 173-184. http://dx.doi.org/10.1016/0003-682X(90)90059-4
- Tachibana, H., Sonoda, Y., Iwamoto, K., Kuwano, S. and Namba, S. (1993) Validity of Arithmetic Average of Sound Pressure Levels in Octave Bands as a Loudness Index. Journal of the Acoustical Society of Japan (E), 14, 197-204. http://dx.doi.org/10.1250/ast.14.197
- Hellman, R. and Zwicker, E. (1987) Why Can a Decrease in dB(A) Produce an Increase in Loudness? Journal of the Acoustical Society of America, 82, 1700-1705. http://dx.doi.org/10.1121/1.395162
- Schomer, P.D. (2000) Loudness-Level Weighting for Environmental Noise Assessment. Acta Acustica united with Acustica, 86, 49-61.
- Salt, A.N. and Lichtenhan, J.T. (2014) How Does Wind Turbine Noise Affect People? Acoustics Today, 10, 20-28.