AP3267 Noise Pollution

Mini-Experiment- Sound Power Measurement

Group Member: 
xxx
xxx
xxx

Date:
14th November, 2000

Experiment: 
Sound Power Measurement of and electric drill at outdoors.

Objective: 
„Y Practical using of the sound level meters for noise measurement.
„Y To determine the sound power and hence calculate the loudness of the source.

Procedure:
1.	Calibrate the sound level meter.
a) Internal calibration 
The K-factor for microphone was checked.
The measuring range FSD was set to "REF".
The Displayed Parameter was set to "SPL".
The Sens. Adj was adjusted until the display shows a value of 94.0 dB + 
K-factor by using a small screwdriver. 

b) Using sound level calibrator 
The measuring range FSD was set to 110 dB.
The Displayed Parameter was set to "SPL".
The calibrator was fitted over the microphone and the Sens. Adj was 
adjusted until the display shows a value of 93.8 dB by using a small 
screwdriver again.


2.	Measurement of Sound Pressure Levels
The setting was changed by holding hold down the button and use the „F and „G 
buttons to scroll through the options. 

Time W	Time weighting. "SLOW" or "FAST" should be selected.
Freq. W.	Frequency weighting. Most of your measurements will be made 
using the linear or flat filter "LƒÂƒu ƒu ƒuƒÈ" or "LƒÂ ƒu ƒÈ", the "A" 
weighting also needed.
Fr./Rdm.	Free field or random type sound field. Free field response was 
selected.
FSD	Full-scale deflection. This sets the range on the instrument. A 
suitable range was selected for the measurements. Sound goes 
out of range appears ƒî or „P for over range and U_ _ _ for under 
range. The scale was changed if both the above cases appear. 
The measurement was started again.
Displayed Parameter	"LEQ" was selected that's a long integration time 
setting. 
      ƒÓ
Reset All	Two buttons were pressed together start a new measurement 
	was started.		

Ext. Filter	The external octave filter was inserted or removed by switching 
the filter switches in or out.

3.	Experimental Procedure
a) 	The electric drill was placed outdoors on a hard road that's far away from 
reflecting objects such as buildings and cars. 
b) The x,y coordinate system was marked on the ground by using tape. The 
position of each of the five measuring points was also marked. A 
hemisphere of radius 1m was employed so the numbers in figure 1 were 
used directly.
c) The sound level meter was placed on the tripod provided safely so that the 
microphone was at the correct position and pointing towards the sound 
source. The foam ball over was put on the microphone for measurements 
outdoors in order to reduce wind noise. 
d) Leq (with linear filter on sound level meter and external filter switched in) 
was measured at each of the 5 points and for each octave filter. Leq without 
the octave filter (still on linear filter) and LeqA (using A weighted filter) 
were entered in the table provided as well. 
e) Sound source from other background sound sources such as cars was kept 
minimized to avoid errors.
f) The sound power of electric drill was determined by using the data. 
 

Figure 1	5-Point Measurement Locations for a Hemisphere





Discussion:
The sound source we used is an electric drill provided by Ruel that is relatively small, 
portable and able to produce a reasonable amount of steady noise. The sound power 
and loudness of the noise produced by the electric drill can then be calculated from 
the data recorded.

As the electric drill produces steady noise, the readings at each of the five measuring 
points for a hemisphere should be more or less the same. However, we found that the 
readings vary time to time at different positions. This may due to the following 
reasons.

Firstly, the background sound can never be neglected even though the background 
noise levels was at least 10dB lower than those from the electric drill. The location we 
carried out the experiment is a public car park and another group carried out the 
experiment at the same time next to us. We have abandoned those data that possibly 
influenced, nevertheless, sounds produced by the car passing by and other sound 
source still may affect the results.

The sound source is placed on the hard concrete ground, we assumed there is a little 
absorption by the ground and the sound is propagated into a hemisphere. However, 
the hemisphere is not propagate isotropically due to the wind naturally exists in the 
environment. Besides, when we perform the experiment, our body and instruments 
used may reflect or absorb some of the sound power. Thus, leads to inaccurate 
readings recorded.

To improve the accuracy of the data recorded, we have to wait for the number display 
settles down to a stable value before taking data. This can minimise the influence of 
fluctuations of the sounds. 

We should use more points instead of just five points to calculate the sound power of 
the electric drill. It is much more reliable to recording the Leq at more different points 
as to increase the accuracy but not just demonstrate the principle.

If possible, it would be better that all objects are far away from the sound source to 
avoid any influence caused. 

The sound level meter should be calibrated before starting the experiment and again 
after you have finished your measurements. For the instrument drifts by more than 
1dB then the overall measurements are not valid. It is remarkable that for quality 
instruments, calibration should merely be a check. Paid attention to any significant 
drift, as this may be a signal means that there is something wrong with the instrument.

The sound level meter is very expensive that is nearly over HK$30,000. We have to 
handle it with extreme care, especially the delicate microphone. Never get the 
instruments wet or get shocked.

Conclusion:

The sound power of the electric drill measured is 6.42 x 10 ¡V4   W and 1.46 x 10 ¡V4  W 
(A-weighted).

2

3

    Source: geocities.com/tokyo/dojo/3828/t_pic

               ( geocities.com/tokyo/dojo/3828)                   ( geocities.com/tokyo/dojo)                   ( geocities.com/tokyo)