Indoor Air Quality and Chemical Exposure
We spend approximately 90% of our time indoors. The quality of that air shapes health, participation, and accessibility — especially for people living with MCS, asthma, and other chronic conditions.
The Built Environment as a Health and Accessibility Issue
Indoor environments are where Canadians spend the vast majority of their time. Yet indoor air can contain significantly higher concentrations of pollutants than outdoor air — from VOCs emitted by cleaning products, personal care products, building materials, and furnishings, to biological contaminants like mould spores.
For people living with MCS, asthma, COPD, or rhinitis, these exposures can determine whether a person can enter, remain in, or meaningfully participate in a space. Climate change is increasing reliance on indoor environments, while energy-efficient building design reduces natural air exchange — concentrating pollutants in tighter spaces.
The Accessible Air in the Built Environment Project
Accessible Air in the Built Environment: Scent/Fragrance-Free Policies, VOC Emissions, and Accessibility in Canadian Workplaces
Product Testing
VOC emissions tested from 15 commonly used products — conventional (fragranced) and fragrance-free/ECO-labelled. Results compared to product labels.
Building IAQ Testing
IAQ testing across 32 Canadian buildings (16 with fragrance-free policies, 16 without). Measured TVOCs, 35 specific VOCs, formaldehyde, PM₂.₅, CO₂, CO, temperature, and humidity.
Qualitative Focus Groups
10 focus groups on Zoom with 60 participants living with disabilities. Anonymous discussions capturing lived barriers, impacts, and solutions.
Key Study Findings
- Fragrance-free buildings kept TVOCs at or below the 500 µg/m³ guideline
- Non-fragrance-free spaces averaged over 1,200 µg/m³ — more than double
- Statistically significant TVOC reduction in meeting rooms (p<0.05)
- Acetone, toluene, and xylenes 2–7× higher in non-scent-free offices
- Fragranced products: 190 VOCs detected; fragrance-free/"green": 90 VOCs
- Both categories contain neurotoxins, carcinogens, and TRP sensitizers
- Most product labels disclosed 0–3.8% of detected VOCs
- Misleading terms like "unscented" do not guarantee freedom from emissions
- Several detected VOCs are known activators of TRPV1 and TRPA1 chemosensory receptors
- Repeated exposure may contribute to receptor sensitization — amplifying future reactions
- This mechanism may help explain heightened reactivity and the development or worsening of MCS
- 72% of focus group participants were dissatisfied or extremely dissatisfied with indoor environments
- 67% of occupants in scent-free buildings received no education on the policy
- Policy adaptability scored 0% across all 17 fragrance-free buildings surveyed
- Monitoring and enforcement each scored only 27%
TVOC Levels by Space — With Policy vs. No Policy
Difficulty Accessing Built Environments (Focus Groups, n=50)
What's Actually in the Air — and in the Products
| VOC | Found In | Health Classification | Detected (spaces) |
|---|---|---|---|
| Ethanol | Glass cleaners, laundry, air fresheners, hand soap | IrritantTRP Sensitizer | 96 (100%) |
| Acetone | Carpet cleaner, disinfectants, all-purpose cleaners | IrritantTRP Sensitizer | 95 (99%) |
| Toluene | Disinfectant wipes, bathroom cleaners, laundry | TeratogenEDC | 91 (94.8%) |
| Acetaldehyde | Laundry products, disinfectants, hand soap | Carcinogen (EPA)TRP Sensitizer | 83 (86.5%) |
| D-Limonene | Air fresheners, laundry, ECO disinfectants | TRP SensitizerForms formaldehyde | 77 (80.2%) |
| Benzene | Unscented hand soap | Probable CarcinogenEDC | 50 (52%) — mostly no-policy |
| Formaldehyde | Building materials, furniture — also in personal care products as byproduct | Known Carcinogen | Both policy groups |
| D5 Siloxane | Personal care products — found in scent-free spaces despite policies | Probable EDCPersistent environmental impact | Detected in scent-free hospitals |
The Label Problem
Most products disclosed 0–3.8% of the VOCs detected during testing. Terms like "fragrance," "parfum," and "unscented" can hide dozens of undisclosed chemicals. An ECO label does not guarantee freedom from hazardous air pollutants. Product selection should be based on emission characteristics and third-party certification — not label claims alone.
"People think it's about disliking a smell. But for me, breathing in perfume is like breathing in pure chlorine. That's the problem — the confusion between the two."
Participant 011-FR — Accessible Air in the Built Environment Focus Groups, ASEQ-EHAQ
Four Types of Barriers to the Built Environment
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Attitudinal Barriers
Systemic Barriers
Informational Barriers
ECO-labelled products still emit hazardous air pollutants including TRP sensitizers
Physical Barriers
Most Challenging Physical Barriers (Focus Groups, n=50)
What Works — and Where Policies Fall Short
Average Implementation Level Across 17 Fragrance-Free Buildings
What effective fragrance-free policies include
Critical Healthcare Finding
One healthcare facility had a fragrance-free policy in place — but TVOC levels reached 26,000 µg/m³: over 50× the recommended guideline. Occupants reported bothersome odours, air freshener use, and multiple adverse health events including asthma attacks and cardiovascular problems. TVOC levels above 3,000 µg/m³ are associated with occupant complaints and sensory irritation (Bernstein et al., 2008).
Mould as an Indoor Air Quality and Health Issue
Common Health Symptoms
Irritation of eyes, nose, and throat
Who Is Most at Risk
Remediation Levels (CCIAQB Guide)
- Small isolated areas <1 m² — trained building staff with basic PPE
- Mid-sized areas 1–3 m² — containment required; limited access during remediation
- Large areas 3–10 m² — full containment; professional remediation recommended
- Extensive contamination >10 m² — specialist contractors required; occupants must vacate
Prevention Priorities
Inspect regularly for water damage and repair within 24–48 hours. Ensure adequate ventilation in high-humidity areas. For people with MCS, even small-scale mould remediation can trigger significant reactions — advance notice and temporary relocation are important accommodations.
What Needs to Change
Key Resources on Indoor Air Quality
Accessible Air in the Built Environment
ASEQ-EHAQ's first-of-its-kind mixed-methods study on IAQ, fragrance-free policies, VOC emissions, and accessibility in Canadian workplaces. Funded by Accessibility Standards Canada.
➡ Read the Full ReportHealth Problems Caused by Mould — Québec.ca
Official guidance from the Gouvernement du Québec on mould-related health effects, symptoms, at-risk populations, and prevention strategies.
➡ View Québec.ca GuideMould — CCOHS Workplace Resource
The Canadian Centre for Occupational Health and Safety provides fact sheets and guidance on mould in workplace environments, with occupational health and safety context.
➡ View CCOHS ResourceCCIAQB Guide — Module 10: Mould
The Canadian Committee on Indoor Air Quality and Buildings guide for building managers on mould assessment, remediation levels, prevention, and HVAC management.
⬇ Download Guide (PDF)Fragrance-Free Health Care
Resources from ASEQ-EHAQ on implementing fragrance-free practices in healthcare settings — provider guidance, signage, and accommodation frameworks.
➡ View ResourceEco Living Guide
ASEQ-EHAQ's partner guide to healthier, lower-emission daily alternatives — covering cleaning, personal care, and home products, with ecolabel guidance.
➡ View Eco Living Guide