PHARMA LAB · PL-05-011

Particle Counter Calibration: Size, Counting and Flow

Acceptable flow does not prove that every channel counts correctly. Review each parameter, reference and configuration before authorising use.
Technical illustration of two optical particle counters connected to a closed comparison chamber on a laboratory bench.

Read a particle counter calibration by parameter: flow, size response and counting provide different evidence. An overall conclusion is not justified unless the report states which channels, conditions and tests it covers. Start with the technology and intended use, then connect every result to its reference and the decision it must support.

1. Which counter are you assessing?

This article concerns airborne optical particle counters measuring light scattered by individual particles, often called LSAPCs. They are not liquid light-obscuration counters, condensation counters or aerosol photometers. Their principles, measurands and methods differ: do not transfer tests or criteria indiscriminately between these families.

On 1 October 2026, the ISO catalogue lists ISO 21501-4:2018, confirmed in 2023, with Amendment 1:2023 and a future revision under development. Its public scope includes size response, efficiency, resolution, false counts, maximum concentration, flow and time. We checked the catalogue and abstract, not the full normative text: claiming conformity requires the applicable edition, amendment and complete procedure.

Identify serial number, sensor, firmware, enabled channels, settings, probe and tubing actually included. State whether data are raw counts, concentrations or already corrected values. Instrument calibration does not define cleanroom monitoring locations or replace qualification and the environmental programme.

2. Optical size and references

The counter relates the light signal to size through its response to reference particles. Optical equivalent diameter does not necessarily equal a geometric dimension measured by microscopy: shape, refractive index and optical characteristics influence the signal. A real aerosol differing from reference spheres may therefore be classified differently; this does not justify arbitrary changes to thresholds.

A size threshold is not an exact measurement of every particle. Distinguish cumulative channels, collecting events above a threshold, from differential intervals: adding cumulative counts counts some events more than once. Size resolution describes the ability to distinguish nearby responses and must be separated from size-setting error and the last display digit.

For reference material, check assigned property, value, uncertainty, size distribution, batch, validity and storage/use conditions. A nominal diameter on the bottle does not replace the certified value. Uncertainty in mean diameter and spread of particle diameters within the material are also different quantities: do not treat them as the same budget contribution.

The historical NIST SRM 1691 certificate illustrates the distinction between nominal designation and certified property. The copy consulted gives an expiry date of 20 March 2023; it is a documentary example, not a reference recommended for current testing. Always check the actual certificate for the material used.

3. Parameter, test and evidence matrix

The following original matrix helps specify and review the service. It is neither an ISO protocol nor a tolerance table.

ParameterComparison and referenceResult to retainInterpretation limit
Size responseParticles with assigned size and documented methodResponse, thresholds assessed, error and uncertaintyDoes not demonstrate counting at all concentrations
Counting efficiencyComparable concentrations with a suitable referenceRatio, size, concentration and uncertaintyComparing two counts without volumes is insufficient
Size resolutionCharacterised distribution and instrument responseEvaluated width and material contributionNot the same as threshold error
Flow and timeTraceable references in the relevant configurationDeviations, conditions and resulting volumeDo not demonstrate correct size classification
Background/false countsFiltered configuration, defined duration and volumeObserved events and test conditionsZero events do not demonstrate sensitivity
Concentration and responseMethod assessing coincidence limits and return to backgroundVerified range, conditions and anomaliesDo not extrapolate beyond demonstrated coverage

4. Counting, flow and background

For efficiency, compare concentrations referring to comparable populations and conditions. A basic relationship is η = Cinstrument/Creference, with any corrections justified by the method. Comparability depends on size, aerosol distribution, transport, dilution, losses and synchronisation; two instruments next to one another do not automatically receive equivalent samples.

For number concentration, C = N/V relates events to the relevant volume. Check flow, time and volume convention, distinguishing the setting from the measured value. Tubing can change particle transmission even when air volume is correct. Explore flow calibration without confusing it with complete particle counter calibration.

At high concentrations, simultaneous events in the sensing zone may alter counting and classification: a low-concentration test does not demonstrate the entire range. A background test must also state duration, volume, filter and configuration. Zero events in a finite sample prove neither an absolutely zero background nor correct detection when particles are present.

Have aerosol tests performed by suitable personnel and facilities using materials and containment specified by the method. Do not open the optical system or bypass safeguards to “see” the beam; do not use improvised aerosols. This article concerns metrological review, not aerosol generation instructions.

5. Uncertainty and report coverage

Assess a budget consistent with each result: material property, counting reference, transmission, repeatability, event statistics, volume and threshold setting may contribute differently. Do not count the same uncertainty twice or ignore correlations between shared references. For U = ku, distinguish standard uncertainty u, expanded uncertainty U and coverage factor k.

For a comparable quantity, define e = indication − reference and c = −e. This convention does not mean subtracting one number from every count is sufficient: changing a threshold changes the distribution of events among channels. A response correction must be technically justified, implemented and verified within its scope.

Request results for relevant parameters and channels, criteria, decision rule, configuration and limitations. Retain data before and after authorised interventions. A missing result does not mean a pass, and a generic “calibrated” label cannot fill a coverage gap.

6. Simulated example: acceptable flow, abnormal size response

A simulated report compares indicated flow of 28.50 L/min with a reference of 28.30 L/min: e = +0.20 L/min, U = 0.10 L/min with k = 2. The example's internal requirement is |e| ≤ 0.85 L/min, and the agreed decision rule requires |e| + U ≤ limit. Since 0.30 ≤ 0.85, this flow point meets that rule.

In the same report, the size-response analysis method assigns 0.560 µm to reference particles of 0.500 µm: e = +0.060 µm, U = 0.010 µm with k = 2. For a simulated internal limit of 0.040 µm, 0.070 > 0.040: the size test does not meet the rule. These limits are invented for the example, not attributed to ISO.

Do not conclude “instrument compliant” from flow alone. Identify affected uses and channels, retain evidence, assess impact on previous data, and agree restrictions, interventions and relevant new tests with authorised functions. Neither invalidate every result automatically nor reinstate the whole range on the strength of a single satisfactory point.

Connect the decision to metrological traceability and measurement uncertainty. Find related topics in the Calibration and Laboratory Metrology hub.

7. Sources and consultation limits

Checked: 1 October 2026. Matrix and example are original GuideGxP material. No normative table is reproduced.

  1. ISO 21501-4:2018 and Amendment 1:2023 — status and scope checked on official public pages; full text not consulted.
  2. Chen, Fletcher and Cheng, Calibration of Aerosol Instruments, 2011, chapter 21 — author copy hosted by NIST; physical principles and parameters, not an updated conformity standard.
  3. NIST SRM 1691, certificate dated 25 February 2016 — historical example of assigned property and validity, expired on 20 March 2023.
Technical content for informed decisions; it does not replace the approved procedure, applicable requirements or the instrument manual.

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