At a glance
| Chemical family | Polycyclic aromatic hydrocarbon (PAH) — four-ring |
| CAS number | 129-00-0 |
| Classification | IARC Group 3 (not classifiable for human carcinogenicity); ACGIH Biological Exposure Index (BEI) compound — 1-hydroxypyrene metabolite used as biomarker for total PAH exposure |
| Where you encounter it | Fire smoke and soot, vehicle exhaust, cigarette smoke, grilled and charred food, asphalt, coal tar, wildfire smoke, indoor combustion sources |
| Sleep micro environment relevance | Transfers from contaminated skin and PPE to bedding during sleep; continues to absorb into skin during prolonged sleep contact; the urinary biomarker 1-OHP measured in morning urine reflects overnight absorption |
| Activated carbon capture | High — pyrene is well-suited to activated carbon adsorption based on volatility and lipophilicity; demonstrated in firefighter PPE post-fire decontamination research |
Regulatory & certification status
Where Pyrene stands across the major regulatory systems and the certifications a bedroom product might carry. Each row links to the governing instrument; where a jurisdiction has no specific measure, that is stated plainly rather than left blank.
| European Union | REACH Substance of Very High Concern: pyrene (CAS 129-00-0, EC 204-927-3) was added to the Candidate List on 15 January 2019 on the basis of its PBT (Article 57(d)) and vPvB (Article 57(e)) properties, not carcinogenicity. It is not on the Authorisation List (Annex XIV), and it is not among the eight PAHs named in the Annex XVII entry 50 restriction (which names benzo[a]pyrene, benzo[e]pyrene, benzo[a]anthracene, chrysene, benzo[b]/[j]/[k]fluoranthene and dibenzo[a,h]anthracene, but not pyrene). No harmonised CLP classification in Annex VI was independently confirmed against a primary instrument. Regulatory — ECHA |
| United States | Pyrene is on the TSCA Inventory but has no chemical-specific TSCA risk evaluation or regulatory action. Under California Proposition 65, parent pyrene (CAS 129-00-0) is not individually listed: a direct search of the official OEHHA Proposition 65 list (both the Excel and PDF editions) finds no entry for CAS 129-00-0. Only benzo[a]pyrene (CAS 50-32-8) and certain substituted PAHs (e.g. dibenzopyrenes, nitropyrenes, indeno[1,2,3-cd]pyrene, cyclopenta[cd]pyrene) appear on the list. Regulatory — OEHHA |
| Canada | Polycyclic aromatic hydrocarbons (PAHs) are listed as a class on the CEPA Schedule 1 List of Toxic Substances, following the 1994 Priority Substances List (PSL1) assessment that concluded PAHs as a class are 'toxic' under CEPA; pyrene was one of the nine PAHs for which sufficient data allowed individual assessment in that report. Federal risk-management measures, however, target specific higher-concern PAHs (such as benzo[a]pyrene) rather than naming pyrene individually. The exact set of risk-managed PAHs was not independently re-verified here because the cited Government of Canada page could not be retrieved at the time of checking. Regulatory — Government of Canada |
| Australia | No specific restriction identified. A chemical-specific AICIS/IMAP assessment or IChEMS (Industrial Chemicals Environmental Management Standard) listing for pyrene (CAS 129-00-0) was not confirmed against an official Australian source. Regulatory — AICIS |
| United Kingdom | Great Britain largely inherits the pre-Brexit EU position: pyrene was carried onto the GB (UK REACH) SVHC Candidate List from the EU Candidate List. No GB-specific divergence (an additional GB restriction or a distinct GB harmonised classification) for pyrene was independently identified, and the GB mandatory classification picture was not separately verified against a primary instrument. Regulatory — HSE |
| International | The IARC Monographs classify pyrene (CAS 129-00-0) in Group 3 — not classifiable as to its carcinogenicity to humans — as recorded in the official IARC List of Classifications (Supplement 7 and Volume 92; 2010 evaluation). This is distinct from benzo[a]pyrene, which IARC classifies as Group 1 (carcinogenic to humans, Volume 100F). Pyrene is not an individually listed substance under the Stockholm Convention. Regulatory — IARC |
| Certifications | OEKO-TEX STANDARD 100: covered — pyrene (CAS 129-00-0) is explicitly named in the standard's polycyclic-aromatic-hydrocarbon list (verified in the published Annex limit-value/individual-substances document, where it appears as 'Pyrene / Pyren 129-00-0'). It is captured under the sum-of-PAHs parameter; the dedicated individual PAH limit values apply to benzo[a]pyrene and a subset of PAHs rather than to pyrene specifically. CertiPUR-US: not addressed — its foam technical guidelines do not mention PAHs or pyrene (the published guidelines cover VOC emissions, prohibited flame retardants, formaldehyde and heavy metals). GREENGUARD/GREENGUARD Gold: a low-VOC chamber-emissions certification whose criteria list does not name pyrene or PAHs. Industry — OEKO-TEX · CertiPUR-US |
| The 72-hour test window | Largely missed. Pyrene is a four-ring, higher-molecular-weight PAH with very low volatility (a semi-volatile SVOC) that sorbs to particles and migrates into settled house dust rather than off-gassing, so a short ~72h VOC emissions chamber test does not reliably capture it; PAH detection instead relies on solvent extraction of dust or material samples. Inferred — from the compound's volatility/emission profile versus the VOC focus of short chamber tests |
What it is
Pyrene (C₁₆H₁₀) is a four-fused-ring aromatic hydrocarbon, the smallest PAH composed entirely of fused benzene rings in the peri-fused arrangement characteristic of larger PAHs. It is a pale yellow solid at room temperature with a sharp aromatic odor. Pyrene forms in essentially every combustion process — wildfires, structure fires, vehicle exhaust, cooking, cigarette smoke, industrial coal burning — and is therefore one of the most ubiquitous environmental PAHs.
The chemistry that makes pyrene useful as a biomarker: pyrene undergoes hepatic metabolism via cytochrome P450 to a relatively stable hydroxylated metabolite, 1-hydroxypyrene (1-OHP), which is then conjugated and excreted in urine. The ratio of 1-OHP to total pyrene exposure is consistent enough across individuals and exposure scenarios that measuring 1-OHP in urine reliably indicates total PAH exposure — not just pyrene specifically. This makes 1-OHP the workhorse biomarker for occupational PAH biomonitoring, even for jobs where the PAH of concern is benzo[a]pyrene or naphthalene rather than pyrene itself.
The skin absorption properties of pyrene have been less directly studied than its smaller and larger PAH cousins. The 2024 Probert et al. study of fireground PAH percutaneous absorption tested naphthalene, phenanthrene, and benzo[a]pyrene in porcine skin from artificial sweat — placing pyrene's expected absorption between phenanthrene (6.8%) and benzo[a]pyrene (0.03%) based on molecular size and lipophilicity. The exact dermal flux for pyrene under sweaty firefighter skin conditions is a measurable gap in the published data. Inferred from Probert et al. 2024 data on adjacent PAHs
How it gets to the bedroom
From the fire ground onto firefighter skin
Pyrene is among the most abundant PAHs measured in post-fire skin wipes from firefighters. Published studies have reported pyrene concentrations on firefighter neck and hand skin in the 1–50 ng/cm² range after structural fires, with substantial individual variability based on fire characteristics, PPE use, and hygiene practices. Peer-reviewed The 2024 Probert study's finding of 60-minute or longer lag times for PAH dermal absorption means that the window between fire response and shower is the highest-leverage intervention point. For firefighters who return home and sleep before showering, that window extends into the sleep period. Peer-reviewed — Probert et al. 2024, Toxics
From firefighter PPE onto rest surfaces
Turnout gear contaminated during fire response carries pyrene and other PAHs back to the station and home. The 2022 Mayer et al. characterization of firefighter PPE off-gassing measured PAH off-gassing rates of 47–74 μg/m³ from gear in storage, with measurable air concentrations in surrounding spaces. Peer-reviewed In fire halls where turnout gear is stored adjacent to or in the same building as rest areas, this off-gassing contributes to ambient PAH concentrations in the breathing zone above sleep surfaces.
From wildfire smoke deposition
Wildfire smoke contains substantial pyrene, with smoke-affected indoor environments showing surface PAH deposition that persists for weeks to months after the smoke event. The 2025 Deeleepojananan et al. study of wildfire smoke chemical adsorption onto indoor surfaces documented PAH deposition onto fabrics, with surface concentrations determined by compound polarity and volatility. Peer-reviewed For households affected by wildfire smoke, bedding deposition is a meaningful exposure pathway that continues long after the smoke has dispersed.
From cooking and combustion sources
High-temperature cooking — particularly grilling, broiling, and charring — produces pyrene that enters indoor air and deposits onto nearby surfaces. Households with frequent indoor grilling, or with kitchens that share air with bedrooms, accumulate pyrene on bedding over time. Tobacco smoke contains substantial pyrene, and thirdhand smoke residues on bedding continue to release pyrene slowly.
From vehicle exhaust infiltration
Pyrene is among the PAHs in diesel and gasoline exhaust. Bedrooms near busy roads or attached garages show measurable pyrene infiltration, with concentrations correlated to traffic patterns. The infiltration rate is lower for pyrene than for the smaller, more volatile PAHs (naphthalene, acenaphthene), but the persistence of pyrene on indoor surfaces makes it a longer-lasting indoor reservoir.
What the research says
Documented health effects
Pyrene is classified by IARC as Group 3 (not classifiable for human carcinogenicity) — distinguishing it from its more dangerous PAH cousin benzo[a]pyrene (Group 1) and pyrene's other neighbors. The lack of classification does not mean pyrene is safe; it means the specific evidence for pyrene-attributable carcinogenicity at human-relevant exposures has been insufficient to support a higher classification. The PAH class as a whole shows clear evidence of carcinogenicity from mixed exposure, and pyrene is part of the mixture.
The more important health-research role of pyrene is as the biomarker for total PAH exposure. Urinary 1-OHP has been used to characterize firefighter occupational exposure across hundreds of published studies. The 2023 Wolffe et al. UK Firefighter Contamination Survey series, while not directly measuring 1-OHP, documented exposure patterns and outcomes that the 1-OHP biomonitoring literature has corroborated quantitatively. Peer-reviewed — Wolffe et al. 2022 Sci Reports — Cancer incidence; Wolffe et al. 2023 Sci Reports — Mental health
The 2024 Cardona et al. systematic review of breast cancer-related chemical exposures in firefighters identified PAHs (including pyrene as a class indicator) among the twelve chemical groups with both documented firefighter exposure and breast cancer associations — particularly relevant for the para-occupational exposure of firefighter partners, who are predominantly female. Peer-reviewed
For firefighter populations
The morning-urine 1-OHP measurement is well-established as an index of overnight PAH absorption following a fire response. Studies have shown that firefighters who shower thoroughly before bed have substantially lower morning 1-OHP than those who do not — which is the most direct evidence available for the importance of the sleep period as a continued absorption window. Peer-reviewed
The 2023 Wolffe et al. mental health paper found that 61% of UK firefighters reported sleep problems, and firefighters with sleep problems were 4.2× more likely to report any mental health disorder. Peer-reviewed — Wolffe et al. 2023, Sci Reports The contamination-sleep-mental-health linkage, with pyrene as a marker for the broader PAH exposure load, is now empirically grounded.
Open questions
The specific contribution of bedding-pyrene-to-skin re-absorption to overnight 1-OHP accumulation — versus inhalation of pyrene off-gassing from bedding into the breathing zone — has not been quantitatively partitioned in any published study. Both pathways are plausible and likely co-occurring; the relative contribution affects intervention design. Speculation
What helps reduce exposure
Tier 1 — Most effective. For firefighters, immediate decontamination before bed: shower within the lag time window (under 60 minutes from fire response where possible), dedicated cleaning of turnout gear, and complete separation of fire-ground clothing from bedding. The 2024 Probert finding that PAH absorption has a lag of approximately 60 minutes means rapid decontamination is genuinely effective.
Tier 2 — Worth considering. Mattress and pillow encasements that fully seal foam materials reduce direct foam-to-air emission and reduce dust migration from mattress to breathing zone. Frequent bedding wash cycles at high temperatures reduce accumulated pyrene on textile surfaces. HEPA-and-VOC air purifiers in the bedroom reduce ambient pyrene concentrations during sleep.
Tier 3 — Larger interventions. Strict spatial separation between firefighter turnout gear storage and sleeping quarters in fire halls. This is the single highest-leverage architectural intervention based on the published gear-off-gassing data. For households affected by wildfire smoke, professional smoke remediation of bedrooms (rather than just visible surfaces) addresses the soft-furnishing reservoir that continues to release deposited PAHs.
The Embr capture system addresses pyrene effectively. The activated carbon fiber cloth in the capture layer adsorbs mid-range PAHs including pyrene well at sleep-environment temperatures and humidities. The bidirectional architecture intercepts pyrene traveling from foam and bedding sources into the breathing zone (bottom-up) and pyrene transferring from contaminated skin onto bedding (top-down) in the same media.
What does NOT help
Air fresheners and "smoke odor neutralizers" do not remove pyrene from bedding. They mask the volatile odor compounds without affecting the deposited PAHs. The persistence of PAH on bedding is independent of perceptible odor — wildfire-affected bedding can contain measurable pyrene long after the smoke smell is gone.
Standard machine washing partially removes accumulated PAH from bedding but does not address foam-core contamination. PAH that has migrated into pillow foam or mattress materials is not removed by surface washing. For severely smoke-affected bedding, replacement is more reliable than aggressive washing.
Showering only in the morning is insufficient for firefighters returning from fire response. The 60-minute lag time finding from Probert 2024 means that the absorption process is well-advanced by the next morning. The shower-before-bed window is the high-leverage intervention; the morning shower addresses what has already been absorbed.
Open research questions
- The dose-response between morning urinary 1-OHP and the bedding-mediated re-absorption pathway specifically — versus inhalation of off-gassing PAHs from contaminated PPE and skin — has not been partitioned in any published firefighter cohort study. Speculation
- The performance of activated carbon fiber cloth for pyrene capture under realistic sleep-environment conditions with simultaneous capture of co-occurring PAHs is part of the Embr V1 chamber-testing research program.
- The duration of pyrene persistence on bedding fabrics under realistic household conditions (washing frequency, ventilation, occupancy patterns) has not been longitudinally measured in any published field study.
Citations
- International Agency for Research on Cancer. Pyrene (Group 3 — Not classifiable for human carcinogenicity). IARC Monographs. Regulatory
- American Conference of Governmental Industrial Hygienists. 1-Hydroxypyrene Biological Exposure Index. Regulatory
- Probert C et al. (2024). Percutaneous Absorption of Fireground Contaminants: Naphthalene, Phenanthrene, and Benzo[a]pyrene in Porcine Skin in an Artificial Sweat Vehicle. Toxics. Peer-reviewed
- Mayer AC et al. (2022). Characterizing exposure to benzene, toluene, and naphthalene in firefighters wearing different types of new or laundered PPE. International Journal of Hygiene and Environmental Health. PMC9903203 Peer-reviewed
- Deeleepojananan C et al. (2025). Wildfire smoke chemical adsorption onto indoor surfaces. Environmental Science & Technology. PMC12044693 Peer-reviewed
- Wolffe TAM et al. (2022). Cancer incidence amongst UK firefighters. Scientific Reports. DOI 10.1038/s41598-022-26619-8 Peer-reviewed
- Wolffe TAM et al. (2023). Mental health of UK firefighters. Scientific Reports. DOI 10.1038/s41598-023-39637-x Peer-reviewed
- Cardona B et al. (2024). Breast Cancer-Related Chemical Exposures in Firefighters. Toxics. Peer-reviewed
- Mayer AC, Chen IC, Fent K et al. (2025). NIOSH Wildland Firefighter Exposure and Health Effects (WFFEHE) study — urinary PAH metabolite increases. Annals of Work Exposures and Health. Peer-reviewed
- International Association of Fire Fighters / NIOSH. Firefighter Cancer Cohort Study — PAH exposure documentation. Peer-reviewed
Frequently asked questions
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What does 1-hydroxypyrene in urine actually measure?
It measures recent PAH exposure across the whole PAH family — not just pyrene specifically. Pyrene metabolizes to 1-OHP at consistent enough rates that 1-OHP concentration in urine reflects total PAH exposure during the preceding 24–48 hours. This is why occupational health programs use 1-OHP as the standard PAH biomarker even when the PAH of concern is benzo[a]pyrene or another compound — the metabolic shorthand is reliable enough to substitute.
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Should firefighters shower before sleeping?
Yes, based on the 2024 Probert et al. lag time finding. PAHs including pyrene have approximately 60-minute lag times before dermal absorption begins in earnest. Showering within that window substantially reduces total absorbed dose. For firefighters returning from fire response, the choice between shower-and-then-sleep versus sleep-and-shower-in-morning is consequential for next-day urinary 1-OHP and for cumulative chronic exposure.
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Is pyrene specifically dangerous, or is it just a marker?
Both, in different ways. Pyrene is not classified by IARC as a human carcinogen on its own evidence base, but it is part of the PAH mixture that is well-established as carcinogenic. The PAH class as a whole — not pyrene alone — is the documented health concern. Pyrene's specific role is as the most reliable biomarker for total PAH exposure assessment.
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How long does pyrene stay on bedding after a wildfire smoke event?
Weeks to months in the absence of intervention, based on the 2025 Deeleepojananan et al. surface adsorption work. PAHs including pyrene partition onto soft furnishing surfaces and release slowly back into the air. Washing bedding helps reduce surface load; replacing severely smoke-affected bedding is more reliable for foam-core reservoirs.
Related compounds
This page describes documented chemistry and exposure pathways. It does not provide medical advice. Firefighters concerned about occupational exposure should consult their occupational health program or physician.
Last reviewed May 16, 2026.