Particles not otherwise specified

Insoluble or poorly soluble particles not otherwise specified form an occupational hygiene assessment category with specific conditions. It is not a label for any dust that has yet to be identified. Before applying a generic value, it must be justified that the material meets the criteria.

In brief

The generic particle reference may be used only when composition, solubility and low-toxicity conditions are met. It does not replace specific agent limits or classify unidentified dust as harmless. The sampling fraction and reference must always be technically consistent.

Contents
  1. Check that the category fits
  2. Identify before comparing
  3. Distinguish inhalable and respirable fractions
  4. Represent actual tasks
  5. Control generation and dispersion
  6. Review conclusions when the material changes
  7. Hypothetical example: sanding a component
  8. Related concepts
  9. References

A–Z dictionary →

Check that the category fits

The INSST occupational exposure limits database restricts this reference to particles without a specific limit that are insoluble or poorly soluble and have low toxicity. It excludes effects such as genotoxicity, sensitisation or harm other than pulmonary accumulation.

It also states that the particulate matter must not contain asbestos or crystalline silica. The traditional term “nuisance dust” does not demonstrate that these conditions are met.

Identify before comparing

The review must consider raw materials, additives, coatings and contaminants generated by the process. An apparently simple product may produce a particle mixture containing components requiring their own assessment.

If composition is unknown, further information or characterisation is needed. Measuring dust mass and comparing it directly with the generic value may conceal significant exposure to a specific substance.

Distinguish inhalable and respirable fractions

NTP 731 explains sampling conventions by particle size. Inhalable and respirable fractions represent different parts of the aerosol and require appropriate devices and criteria.

They are not synonyms for visually estimated “large dust” and “small dust”. The report must identify the measured fraction and compare it with the corresponding reference, without interchanging results.

Represent actual tasks

Royal Decree 374/2001 requires exposure conditions to be considered. The strategy must cover emitting tasks, process variations and groups of workers with comparable exposure.

Sampling far from the person or during a low-emission phase may not represent their shift. Record the activity, duration, equipment operating and circumstances influencing the result.

Control generation and dispersion

Prevention must act at source through supply forms, enclosures, extraction and handling methods that reduce emissions. Cleaning must prevent deposited material from becoming airborne again.

The absence of identified specific toxicity does not remove the need for control. Respiratory protection is selected according to the assessment and complements technical measures where necessary.

Review conclusions when the material changes

A change of supplier, composition or process may invalidate use of the generic category. The assessment must retain the justification for its selection and review it when new toxicological information or relevant results become available.

Numerical comparison also does not resolve other dust risks, such as fire or explosion where relevant. Occupational hygiene and safety assessments have different objectives and must be coordinated.

Hypothetical example: sanding a component

A workshop has a respirable dust measurement but changes the material used in its components. Before reusing the previous conclusion, it reviews composition and coating.

If a component with its own limit or hazards is identified, it adapts the analysis. The generic value is no longer used as a substitute for missing information.

References

  1. INSST occupational exposure limits: insoluble or poorly soluble particles not otherwise specified. Official source
  2. INSST NTP 731: aerosol assessment and sampling fractions. Official source
  3. Royal Decree 374/2001: chemical agent assessment. Official source

Editorial information

Publication date: 19 October 2026.

Editorial responsibility: Sabentis Editorial Team.

Author: Pablo RodríguezLinkedIn

Executive Vice President of the ORP International Foundation and Chief Financial Officer of Sabentis.

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