Purpose & when to use

Inhalation Risk Assessment turns measured aerosol, particle size distribution (PSD), and gas-phase chamber data into estimates of scenario exposure, intake, and margin of safety (MoS). We document each assumption and maintain traceability of measured inputs under ISO 17025 quality controls. Benchmark selection and risk framing are aligned, when applicable, with OSHA PEL, NIOSH REL, EPA OPPT/OCSPP, OECD 412/413, ICH Q9, or REACH inhalation DNEL frameworks:

  1. Consumer spray exposure comparisons use chamber time series, PSD inputs, and OSHA PEL or NIOSH REL benchmarks to rank product modes under defined room-use scenarios.
  2. Room-applied aerosol safety reviews combine release-rate measurements, ventilation assumptions, and EPA OPPT/OCSPP exposure logic for label support or product-use limitations.
  3. Powder or dust scenario assessments pair particle-size data with breathing-rate assumptions and OECD 412/413 toxicology context to estimate intake and uncertainty drivers.
  4. Formulation or device change reviews use measured emissions, scenario sensitivity, and ICH Q9 risk framing to identify whether particle size, release rate, or duration drives MoS.
  5. International safety dossiers translate exposure outputs into REACH inhalation DNEL comparisons, with EPA and OECD context when relevant, for documented market-access communication.

Use this service when the decision depends on exposure during realistic product use, not emissions alone. Before modeling begins, the study plan defines the scenarios, inputs, benchmarks, and uncertainty bounds. This keeps each reported MoS traceable to measured data and clearly stated assumptions.

Built for sprays, powders, rooms, and devices

Risk assessment is useful wherever emissions become an inhalation question: consumer aerosols, drug-delivery systems, respiratory protection, medical devices, air treatment units, and room-applied products.

  • Drug deliveryInhaled or intranasal products
  • Respiratory protectionMask and filter contexts
  • Medical devicesUse-related emissions
  • Air treatmentRoom-scale exposure scenarios
  • Spray aerosolConsumer and industrial sprays

Instrumentation & measurement ranges

Risk models start with measured inputs. We document the scenario assumptions and toxicology benchmarks alongside the calculations.

0.3 – 20 µmparticle-size

Chamber particle and aerosol time series

Particle counts, PSD, and decay curves from chamber studies define airborne concentration over time, including peak and time-weighted values for each product-use condition.

0.001 ppm – 100 ppmconcentration

Gas and VOC analytical inputs

VOC, by-product, or gas measurements are incorporated when the inhalation question includes vapor-phase exposure as well as particle-phase aerosol or powder emissions.

1 – 120 minuse-duration

Scenario and breathing-rate model set

Room volume, ventilation, use duration, frequency, and breathing assumptions convert measured concentrations into intake or exposure estimates for defined users.

1 ratio – 1000 ratioMoS

Toxicology benchmark and MoS calculations

Benchmark inputs such as PEL, REL, DNEL, or study-derived points of departure are recorded with unit conversions and uncertainty factors before MoS is calculated.

Test method options

MethodStrengthsTradeoffAligned with
Screening scenario assessment (chamber data plus benchmarks)
  • Ranks products, use modes, or rooms using measured concentration data and OSHA PEL or NIOSH REL comparison points when occupational benchmarks fit.
  • Produces transparent MoS tables that show which assumption changes the result: release rate, room volume, ventilation, breathing rate, or use duration.
Screening assumptions can dominate the answer, so the output should guide decisions rather than replace a refined exposure assessment.
OSHA PEL / NIOSH REL
Refined time-series assessment (PSD and transient peaks)
  • Uses measured PSD and concentration time series to model peak, time-weighted, and size-informed inhalation exposure for sprays, powders, and device emissions.
  • Supports EPA OPPT/OCSPP consumer exposure logic and OECD 412/413 toxicology context when measured exposure needs a documented hazard benchmark.
Requires richer measurement datasets and more review time because size-resolved concentration, decay, and benchmark selection all need traceable documentation.
EPA OPPT / OCSPPOECD 412/413
Sensitivity and dossier support (MoS decision frame)
  • Maps ventilation, room size, frequency, duration, and benchmark choices to MoS sensitivity, supporting ICH Q9 risk-based decisions and change reviews.
  • Translates scenario outputs into REACH inhalation DNEL comparisons when downstream communication or international safety documentation needs a clear exposure basis.
Benchmark selection and uncertainty factors must be agreed before modeling, or the final MoS can appear precise while remaining decision-dependent.
ICH Q9REACH inhalation DNEL

Setup configurations

A useful inhalation risk assessment starts by defining the scenario, not by opening a spreadsheet. Before calculations begin, we confirm how the product is used, what measurement data are available, which population is being evaluated, the applicable benchmark source, and the decision threshold. The items below establish the inputs needed to make the final MoS traceable and reviewable:

Exposure profile

Use duration, frequency, distance from source, room volume, ventilation, and occupancy assumptions defined for each scenario before model runs begin.

Sample matrix

Particles, powders, droplets, gases, VOCs, or mixed-phase emissions identified so concentration data and benchmarks are applied to the correct hazard basis.

Flow & actuation profiles

Spray duration, actuation count, release rate, settling period, and breathing-rate assumptions documented for each user or room-use condition.

Calibration & verification

Source datasets checked for units, timestamps, calibration status, blanks, and conversion factors before they enter exposure or MoS calculations.

Chain of custody

Input files, calculation versions, benchmark references, and report tables controlled so each final result can be traced back to its source.

Compliance frame for inhalation risk assessment

The quality framework distinguishes accredited laboratory controls from the regulatory and toxicology references used to guide the model. ISO 17025 supports traceability for measured inputs, while the other references inform benchmark selection and scenario logic.

  • ISO 17025AccreditedQuality-system control for measurement traceability, records, and technical review.
  • OECD 412/413AlignedRepeated-dose inhalation toxicology context for benchmark interpretation.
  • OSHA PEL / NIOSH RELAlignedOccupational exposure limits used when the scenario warrants comparison.
  • EPA OPPT / OCSPPAlignedConsumer and environmental exposure logic for relevant product categories.

Key data outputs & reporting

Inhalation risk assessment results are organized by scenario and linked directly to the underlying assumptions for technical review. Reports include the measured input datasets, exposure estimates for each condition, MoS calculations, the rationale for benchmark selection, and sensitivity results showing which assumptions materially affect the answer. Calculation tables retain units, conversions, and source references, making the path from chamber data to the final decision metric clear.

Primary outputs

  • Exposure estimates by scenario, including peak and time-weighted concentration where the source data supports both views.
  • MoS calculations with benchmark selection, uncertainty factors, unit conversions, and assumption notes tied to each result.
  • Sensitivity tables showing which inputs drive risk: particle size, release rate, room volume, ventilation, breathing rate, or use duration.
  • Driver attribution and uncertainty discussion focused on the measurements and assumptions most likely to change the conclusion.

Deliverables

#FormatContents
01PDF reportMethods, scenarios, benchmark rationale, MoS tables, sensitivity discussion, and interpretation limits.
02CSV / XLSX datasetsCalculation tables, scenario inputs, unit conversions, and model outputs.
03FiguresScenario comparisons, MoS ranking plots, and sensitivity visuals for review packages.

QA / QC & data integrity

Risk-assessment quality depends on traceable measurements and disciplined calculations from the initial review through final reporting. We check source datasets, assumptions, units, conversions, and benchmark references before interpreting the results. The calculation record is then preserved so reviewers can follow how every exposure estimate and MoS value was derived.

Input-data review covering calibration status, units, timestamps, blanks, replicate handling, and measurement limits.

Calculation workbook version control with locked source tables and documented formula checks.

Benchmark-source documentation for each PEL, REL, DNEL, or toxicology point of departure used.

Scenario consistency review across room size, ventilation, use duration, frequency, and breathing-rate assumptions.

Independent technical review of units, conversions, uncertainty factors, and MoS interpretation before report release.

Why ARE Labs

ARE Labs connects technical topics to practical study design, method selection, controlled aerosol work, and reportable evidence without turning technical pages into sales pages.

Reviewed byJamie Balarashti (25 yrs - cascade & inhalation methods) - Weston Schaper (7 yrs - real-time sizing & nanoparticle work)
17025Accredited testing
900+Studies Performed
17+Years in operation
300+Clients supported

Common questions

Product safety, inhalation, consumer aerosol, and regulatory teams often begin with the same scoping questions: which inputs are required, how MoS is calculated, how room scenarios are compared, and how benchmark selection affects interpretation. The answers below cover those points and explain what the assessment can include. Contact us if your product, exposure route, intended population, or benchmark framework falls outside the scenarios described here.

Q.Do you need chamber data to start?
A.Measured chamber data are preferred because they anchor the model to observed conditions. When no data exist, we can scope a screening assessment using documented assumptions, but the results will be identified as assumption-driven.
Q.Can the assessment include particles and VOCs?
A.Yes. We can include particle, droplet, powder, gas, or VOC inputs when the study provides defensible measurements and an appropriate benchmark for each exposure component.
Q.What is margin of safety?
A.Margin of safety compares the estimated exposure with a selected benchmark or point of departure. The report identifies the benchmark and documents the units, uncertainty factors, and assumptions used to calculate each MoS value.
Q.Can you model different rooms and ventilation rates?
A.Yes. Sensitivity runs can vary room volume, ventilation, exposure duration, use frequency, and breathing rate to show which assumptions have the greatest effect on estimated exposure and MoS.
Q.What do I receive?
A.You receive a PDF report, calculation tables, documented scenario inputs, MoS results, sensitivity figures, and a traceable explanation of the benchmark selections and main sources of uncertainty.