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Infant Exposure Model (6-12 Months)

Crawling, Resuspension & Hand-to-Mouth Behaviours

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Step 1 — External (Gross) Infant Dose — Particles Entering the Body
External = (FQ_htm × Hrs_active × SA_hand × AF_hand × C_dust) + (C_resus × IR_breath × Hrs_active)

Step 2 — Systemic (Internal) Infant Dose — Particles Reaching the Bloodstream
Systemic = (FQ_htm × Hrs_active × SA_hand × AF_hand × C_dust) × Gut_Trans + (C_resus × IR_breath × Hrs_active) × (Pulm_frac × Pulm_Trans + MCC_frac × Gut_Trans)
The model first calculates the external dose — the total number of particles entering the infant's body from hand-to-mouth ingestion (contact frequency × active hours × hand surface area × dust adherence × dust concentration) plus resuspended dust inhalation. The systemic (internal) dose then applies size- and morphology-dependent kinetic translocation fractions: ingested particles pass through the gut barrier (Gut_Trans), while inhaled particles are split by the ICRP lung model into a pulmonary fraction (direct to bloodstream via Pulm_Trans) and an MCC fraction (swallowed → gut → systemic via Gut_Trans). Kinetic translocation fractions (Gut_Trans, Pulm_Trans) and life-stage modifiers are as defined in the Model Documentation page. ICRP-based lung deposition fractions (Pulm_frac + MCC_frac) determine the inhalation split.
1. Particle & Hazard Characterisation

Particle size and morphology drive the kinetic parameters that govern how external exposure translates into internal dose — specifically airway and lung deposition fractions, as well as placental, gut and pulmonary translocation fractions. These fractions are retrieved from a size- and morphology‑based kinetic lookup table derived from published values (see documentation). Clearance kinetics are not currently modelled; the framework currently assumes that once MNPs enter the systemic circulation they are not cleared. Polymer and chemical toxicity scores [Christopher et al. 2024] combine with automatic size/morphology modifiers to produce the final hazard score.

Particle Size

Source: [van Boxel 2025; ICRP 66]

Morphology

Source: [Sturm 2012; Zhou 1996]

Polymer & Chemical Profile

Source: [Christopher et al. 2024]

High EDI is expected for this life stage due to intense crawling and hand-to-mouth behaviours. Adjust dust concentrations to model a cleaner environment.

2. Infant Biometrics & Activity

Body Weight (BW) [kg]

Source: [WHO Child Growth Standards]

Active Crawling (Hrs_active) [hr/day]

Source: [EPA ExpoBox - Infant Activity]

Normalisation Metric

Source: [Standard RA Practice vs. Particle-Specific]

Using Body Weight is standard but may be less relevant for particle toxicology. 'Total Particle Load / day' provides the absolute particle flux.

3. Hand-to-Mouth Ingestion

Frequency (FQ_htm) [contacts/hr]

Source: [Xue et al. 2007 - Mouthing Frequencies]

Hand Surface Area (SA_hand) [m²]

Source: [EPA Exposure Factors Handbook]

Dust Adherence Factor (AF_hand) [mg/m²]

Source: [EPA Exposure Factors Handbook]

Default reduced from 5,000 to 1,000 mg/m² (0.1 mg/cm²) per EPA standard for dry indoor hands. Higher values (up to 10,000) may be appropriate for sweaty/sticky hands or outdoor play.

Dust Concentration (C_dust) [p/mg]

Source: [Zhang et al. 2021; Jenner et al. 2022]

Default revised from 500 to 50 p/mg following the Phase 0 audit. The previous 500 p/mg default (set when sizeWeight was removed) overshot the literature range. Jenner et al. (2022) report typical indoor settled dust MNP concentrations of 2–90 p/mg for inhalable fibres; 50 p/mg represents a conservative mid-range value.

4. Resuspension Inhalation

Resuspended Dust Conc. (C_resus) [p/m³]

Source: [Wu et al. 2021 - Infant breathing zone]

Active Breathing Rate (IR_breath) [m³/hr]

Source: [EPA - Infant short-term active]
5. Risk Matrix Options

Exposure Thresholds

Source: [User Defined]

Note on Thresholds

Exposure thresholds are currently arbitrary and user-definable. What constitutes Low, Medium and High in terms of daily particle exposures is to be resolved by scientific consensus.