Introduction to adding compatible sound levels
Decibel readings cannot be added as ordinary numbers. A decibel is a logarithmic expression of a ratio, so this calculator converts each entered level to a relative linear quantity, combines those quantities, and converts the answer back to decibels. It supports the normal energy sum for independent sound sources, an in-phase coherent pressure sum for a narrow special case, and background subtraction for a measured total.
For machines, traffic, fans, people, and most environmental noise, choose the incoherent energy sum. Two equal independent sources increase the level by 3.01 dB, not 6 dB. Coherent mode is appropriate only when signals have a stable phase relationship and reach the receiver in phase. The weighting selector labels the result as dB SPL, dBA, or dBC; it does not convert one weighting into another.
All entries must describe the same receiver position, operating period, and measurement definition. A 90 dBA source has ten times the relative energy of an 80 dBA source, so their independent combination is about 90.41 dBA. This is also why arithmetic averaging of sound-level readings is generally misleading: linear energy, rather than displayed dB values, must be averaged or summed.
Formulas for logarithmic decibel addition
A level compares like quantities. In the general expression below, and have the same units, while is 10 for an energy or mean-square ratio and 20 for a pressure-amplitude ratio.
For sound pressure in air, the two equivalent forms are shown here. The standard reference is . Negative dB values are valid because a pressure can be below that reference.
For independent sources with levels through , add each relative energy ratio , then take the logarithm of the sum.
If every source has level , the total is . The total cannot be below the loudest compatible input. For two independent levels, the difference form makes the small effect of a quiet source clear.
A source 10 dB below the loudest adds about 0.41 dB to an incoherent total; one 20 dB below adds about 0.04 dB. The calculator uses a largest-level reference internally, which avoids unnecessarily large intermediate numbers without changing the result.
The 3.01 dB and 6.02 dB addition regimes
Independent sources add mean-square pressure, producing the familiar 3.0103 dB increase for two equal sources. Perfectly coherent, in-phase signals add pressure amplitudes and therefore produce 6.0206 dB for two equal signals.
For unequal coherent inputs, sum pressure ratios rather than energy ratios.
Real sources may be partly correlated. The expression below shows why phase and correlation can change the result. This calculator deliberately offers only the two clear limiting cases; broadband machinery, traffic, and unrelated loudspeakers normally belong in incoherent mode.
Worked example: four packaging-line machines
Suppose four independently operating machines measure 88.5, 84.2, 81.0, and 78.4 dBA at the same operator position. Their relative energy terms are as follows; the displayed figures are rounded only for explanation.
Using full precision gives a combined level of 90.67 dBA. The 88.5 dBA machine is the leading contributor, but removing it would not remove the other machines. A realistic control estimate replaces its input with the expected treated level, then recalculates the total.
The contribution table is a screening tool: it identifies dominant terms and the upper-bound saving if one source vanished completely. Measurements should still represent the same production state, microphone position, and operating conditions before they are used for a control decision.
Formula for removing a background level
In background-subtraction mode, measure the total with the target source operating and the residual background with it stopped. The residual must be lower than the total. Subtract linear energies, not the displayed dB values.
The requirement is . A separation below 3 dB is highly uncertain; 3 to 10 dB needs caution; above 10 dB usually needs a small correction. For example, 70 dBA total and 60 dBA background produces about 69.54 dBA for the source, not 10 dBA.
The correction C is negative. At 10 dB separation it is about −0.46 dB; at 3 dB it is about −3.02 dB and very sensitive to ordinary meter variation. Re-measure instead of forcing an answer when the background is equal to or above the measured total.
Frequency weighting, duration, and position assumptions
Do not mix dBA, dBC, and unweighted dB SPL in one calculation. A-weighting, C-weighting, and unweighted measurements respond differently across frequency, so conversion requires spectral data. Likewise, use compatible time settings: an instantaneous maximum and a fifteen-minute equivalent level are not interchangeable. When noise changes over time, duration-weighted equivalent level is the relevant quantity.
Source addition describes simultaneous contributions at one receiver. Sequential events need the duration terms above. Every entered source should also apply at the same observation point. Under ideal free-field point-source conditions, a distance change follows this approximation.
The ideal relation predicts a 6.02 dB decrease for each doubling of distance from a compact point source. Rooms, barriers, ground effects, reflections, directivity, and line-like sources can change that behavior. A local sound-pressure result is not a sound-power rating for the equipment.
How to use the decibel source list
Select the addition mode and the label matching your compatible meter readings. Enter one source level per row; blank rows are ignored and negative values are accepted. Use background subtraction only for a measured total and a lower residual background. Press Calculate combined level to see the total, rise above the loudest source, source count, and contribution breakdown.
Copy link saves the current mode, weighting, and entered values in the URL. Copy result copies the visible outcome, and Download summary creates a CSV file after a calculation. Keep available decimal places while entering values, then report a sensible number of decimals that matches measurement uncertainty.
For an inventory, measure each source at the receiver with that source operating alone where practical. Do not enter several readings that were each measured while all equipment was already running, because that counts the same energy repeatedly. A rise near 3 dB often indicates two similarly important independent sources; a total almost identical to the loudest source indicates that the others are collectively minor.
Limitations of this sound-level calculation
This calculator performs compatible logarithmic level arithmetic. It does not model changing source operation, sound propagation, directivity, barriers, room reverberation, tones, phase cancellation, or regulatory corrections. Coherent mode assumes positive in-phase addition and should not be used as a general loudspeaker-room prediction.
Results are only as reliable as the inputs. Instrument tolerance, calibration, weather, microphone placement, and source variability can easily exceed the calculator’s displayed decimal precision. The occupational duration context is illustrative and not a compliance or dose determination. Formal work should document the meter, calibration, weighting, averaging period, location, operating state, and background conditions.
Common questions about decibel addition
Why do two equal independent sources add only 3.01 dB?
They double linear energy, and ten times the base-ten logarithm of two is 3.0103 dB. Two 80 dB independent sources therefore produce about 83.01 dB.
Can dBA, dBC, and dB SPL values be mixed?
No. Combine only levels using the same weighting and compatible measurement conditions. Weighting conversion requires frequency-spectrum information.
Can this calculator estimate a noise-control benefit?
Yes. Replace a source level with its expected treated value and recalculate. Do not remove it unless its contribution at the receiver will genuinely disappear.
Sources and standards for sound-level arithmetic
These equations follow established acoustical definitions and measurement guidance. Consult the applicable current standard for a formal survey or compliance decision.
- NIOSH, Criteria for a Recommended Standard: Occupational Noise Exposure, Publication 98-126. Read the NIOSH publication.
- OSHA, 29 CFR 1910.95 — Occupational Noise Exposure. Read OSHA 1910.95.
- IEC 61672-1 and ISO 1996-1 and ISO 1996-2 for sound-level measurement and environmental sound guidance.