At 60 km/h the wind noise inside your helmet is already about 90 dB(A), and you notice it: your ears ring after a long ride (McCombe, J R Soc Med). Nothing rings in your lungs.
Part of our Rider health and pollution guide.
In a Thai sensor study, riders' own sensors frequently approached 100 µg/m³ while fixed monitors read below 50, and no sense in your body reports the difference (MobileSense, COMPASS '25).
So the long term effects of motorcycle riding sort themselves by one question: does your body warn you? Hearing does. Lung function does not, and that is the line this post keeps a ledger for.
Key takeaways
- Wind noise inside a helmet is about 90 dB(A) at 60 km/h and reaches 110 dB(A) at 160 km/h, so hearing effects announce themselves; particulate exposure has no equivalent alarm (McCombe, J R Soc Med).
- In Bangkok, motorcycle taxi drivers exposed to 50 µg/m³ PM10 or more had an FEV1/FVC 2.82% lower than motorcycle taxi drivers exposed to under 30 µg/m³ (95% CI −4.54% to −1.09%), in a study of 1,283 motorcycle taxi drivers and 600 taxi drivers (Arphorn et al., 2018).
- Across 107 studies, mostly from North America and Europe, each 10 µg/m³ of long-term PM2.5 carried a combined risk ratio of 1.08 (95% CI 1.06 to 1.09) for natural-cause mortality (Chen and Hoek, 2020).
- Illustrative arithmetic, not a measured rider hazard: an 8-hour rider carries a time-weighted on-road uplift of about 16.7 µg/m³, 3.3 times the WHO annual PM2.5 guideline of 5 µg/m³ (WHO, 2021; MobileSense).
What are the long term effects of motorcycle riding, and which ones warn you first?
Riding has long-term effects on hearing and on lung function, and the two behave differently. Hearing exposure announces itself in real time. Particulate exposure does not. Posture, vibration and sun are real too, but I have not sourced numbers for them here, so I am leaving them out rather than guessing.
The one that announces itself: hearing. Inside a helmet, wind noise measures about 90 dB(A) at 60 km/h and climbs to 110 dB(A) at 160 km/h, and modern helmets attenuate low-frequency wind noise very poorly (McCombe). It is loud, immediate and impossible to miss, which is exactly why riders manage it.
The one that stays quiet: lung function. In Bangkok, researchers compared 1,283 motorcycle taxi drivers with 600 enclosed-vehicle taxi drivers. The motorcycle drivers' mean FEV1/FVC was significantly lower (P < 0.001).
Within the motorcycle group, those exposed to 50 µg/m³ PM10 or more had an FEV1/FVC 2.82% lower (95% CI −4.54% to −1.09%) than those exposed to under 30 (Arphorn et al., J Air Waste Manag Assoc, 2018).
Read it carefully: it is cross-sectional, it measures PM10 rather than PM2.5, and exposure was estimated from Thailand's Pollution Control Department ambient data rather than personal monitors. It shows an association at one point in time, not a rider's decline over a career.
For scale, the population evidence is consistent. A systematic review and meta-analysis of 107 studies, mostly from North America and Europe, found a combined risk ratio of 1.08 (95% CI 1.06 to 1.09) for natural-cause mortality per 10 µg/m³ of long-term PM2.5, and noted that studies in low- and middle-income countries are still limited (Chen and Hoek, Environ Int, 2020).
For the rider-specific picture, see what the lung-imaging work on riders shows and how to protect your lungs if you ride all day.
Why is the national average the wrong dial? Dose is hours, not headlines
A rider's dose is concentration multiplied by hours multiplied by years. A national annual average speaks, weakly, to the first term for someone standing on a rooftop, and says nothing about the second or third. It is also not the air at your face.
The first gap is between the monitor and the road. In MobileSense, ten riders in Bangkok and Chiang Mai carried sensors from November 2023 to May 2024.
Fixed stations read below 50 µg/m³ while the riders' own sensors frequently approached 100 µg/m³, peaking at 133.8 µg/m³ on 30 January 2024, and six of the ten riders had a hazard quotient above 1 (COMPASS '25).
We took that study apart in How Bad Is Air Pollution for Motorcycle Riders, so I will not re-argue it. What this post adds is the conversion: that gap, expressed in hours.
The second gap is between the levers. You cannot change the city's rooftop number. You can change the hours you spend inside it and, with a filter, the concentration of what reaches your airway.
Vents and a cracked visor cannot reach that term. They move air only while you are moving; at a red light there is no ram pressure, and the air around your face is whatever the queue is emitting. We drew the mechanism in our piece on the shrinking haze interval.
The riding ledger has three terms, and only one is set by the air
Dose = concentration × hours × years
Not every number in this literature is alarming, and it is worth saying so.
A 2025 PLOS One study of 441 motorcycle taxi drivers across six central Thai provinces (January to March 2023) put the incremental lifetime cancer risk from PM-bound polycyclic aromatic hydrocarbons in Pathum Thani at 4.5 × 10⁻⁸ for PM10-bound and 7.8 × 10⁻⁸ for PM2.5-bound, and described risk in all six provinces as acceptable (Samana et al., PLOS One, 2025).
So the cancer arithmetic for that one class of compounds looked reassuring. The concern sits in the lung-function and mortality signals above.

Ride with filtered air
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Projecting the ledger: what five more years of riding adds up to
Everything in this section is synthesised. No agency has published these numbers. Each formula is printed so you can check it, and no figure is attributed to a study that did not publish it.
Step A: the time-weighted uplift. Take a working on-road increment of about 50 µg/m³ above the static reading, rounded from MobileSense's "below 50" against "approached 100". The 24-hour-average equivalent is 50 × (hours riding ÷ 24). Then apply the Chen and Hoek risk ratio as 1.08^(uplift ÷ 10) − 1.
| Rider profile | 24-h-equivalent uplift | Against WHO annual guideline (5 µg/m³) | Implied natural-cause mortality uplift* |
|---|---|---|---|
| 1 hour/day | 2.1 µg/m³ | 42% | about 1.6% |
| 2 hours/day | 4.2 µg/m³ | 83% | about 3.3% |
| 4 hours/day | 8.3 µg/m³ | 167% | about 6.6% |
| 8 hours/day | 16.7 µg/m³ | 333% | about 13.7% |
*Three caveats, all of which matter. First, the risk ratio comes from cohort studies of sustained ambient averages, so applying it to a short daily on-road spike is a log-linear extrapolation, not a measured rider hazard. Second, the 50 µg/m³ increment comes from ten riders in two Thai cities in the dry season.
Third, the WHO 5 µg/m³ figure is an annual ambient average (WHO, 2021), so the comparison shows scale, not compliance.
Step B: hours banked by 2031. A commuter on 2 hours a day, 250 days a year, for 5 years logs 2,500 on-road hours. A delivery rider on 8 hours a day, 300 days a year, for 5 years logs 12,000 hours, about 500 full days, inside that on-road increment.
Step C: the national line will not bail you out. Hold each country's 2020 to 2025 compound annual rate for six more years, using 2025 value × (1 + rate)^6, on IQAir's national annual means (IQAir).
| Country | 2020 | 2025 | Annual rate | 2031 (synthesised) | Multiple of WHO 5 |
|---|---|---|---|---|---|
| Indonesia | 40.7 | 30.0 | -5.9%/yr | 20.8 | 4.2 |
| Thailand | 21.4 | 17.8 | -3.6%/yr | 14.3 | 2.9 |
| Vietnam | 28.0 | 29.7 | +1.2%/yr | 31.9 | 6.4 |
| Philippines | 12.8 | 19.0 | +8.2%/yr | 30.5 | 6.1 |
The national line keeps improving, or doesn't. The rider term sits on top of it either way.
National annual mean PM2.5, µg/m³: measured 2020 to 2025, synthesised 2025 to 2031
Measured (IQAir, solid)Synthesised projection (dashed)
| Year | Indonesia | Vietnam | Philippines | Thailand | Type |
|---|---|---|---|---|---|
| 2020 | 40.7 | 28.0 | 12.8 | 21.4 | Measured (IQAir) |
| 2021 | 34.3 | 24.7 | 15.6 | 20.2 | Measured (IQAir) |
| 2022 | 30.4 | 27.2 | 14.9 | 18.1 | Measured (IQAir) |
| 2023 | 37.1 | 29.6 | 13.5 | 23.3 | Measured (IQAir) |
| 2024 | 35.5 | 28.7 | 14.8 | 19.8 | Measured (IQAir) |
| 2025 | 30.0 | 29.7 | 19.0 | 17.8 | Measured (IQAir) |
| 2026 | 28.2 | 30.1 | 20.6 | 17.2 | Synthesised projection |
| 2027 | 26.6 | 30.4 | 22.3 | 16.5 | Synthesised projection |
| 2028 | 25.0 | 30.8 | 24.1 | 15.9 | Synthesised projection |
| 2029 | 23.5 | 31.1 | 26.1 | 15.4 | Synthesised projection |
| 2030 | 22.1 | 31.5 | 28.2 | 14.8 | Synthesised projection |
| 2031 | 20.8 | 31.9 | 30.5 | 14.3 | Synthesised projection |
Read the two tables together. On the optimistic case, Indonesia's national average improves by about 9 µg/m³ between 2025 and 2031. For an 8-hour rider, the time-weighted on-road term alone (16.7 µg/m³) is larger than that whole improvement, and for a 2-hour commuter it is about half of it (4.2 µg/m³).
While you are actually riding, the increment is closer to 50. The dial that moves the ledger is not the one on the news.
Where this projection will probably break. The dashed Indonesia line assumes the 2020 to 2025 decline simply continues, and 2026 is a severe fire year.
IQAir reported on 13 September 2026 that more than 12.5 million people across seven Indonesian provinces have been exposed to haze, and that respiratory infections linked to the fires rose to 113,336 cases as of 9 September, roughly double the 50,891 recorded on 1 September (IQAir, 13 September 2026).
I would expect 2026's annual mean to land above the dashed line, so read that segment as the optimistic case. The 2023 jump in Indonesia's measured line, to 37.1, sits in the El Niño fire year we covered in the haze-interval piece.
You cannot shorten the commute. You can change the concentration term.
The ledger has three terms: concentration, hours, years. Most riders cannot cut the last two, because the commute is the job. The first is the one an active system changes.
Easi Breezi, our clip-on helmet air purifier, draws ambient air through a sealed intake and an H11 HEPA element rated ≥95% on PM2.5 and delivers it to the face, so the air reaching you has passed through a filter instead of being whatever the road is carrying.
Patent pending. That is an engineer's framing, not a health promise: we are not putting an on-road efficacy figure on it.
Frequently asked questions
What are the long term side effects of motorcycle riding?
The ones this post can source are hearing and lung function. Wind noise inside a helmet is about 90 dB(A) at 60 km/h. In a Bangkok study motorcycle taxi drivers exposed to 50 µg/m³ PM10 or more had a lower FEV1/FVC than those exposed to under 30 (Arphorn et al., 2018).
Posture, vibration and sun are real but not covered here.
Are long commutes bad for your health?
For the air, the ledger says hours matter as much as concentration: on the same on-road increment, an 8-hour rider carries four times the time-weighted uplift of a 2-hour rider (16.7 against 4.2 µg/m³). That is arithmetic on one exposure. I have not sourced the wider evidence on commuting and health, so I will not summarise it.
Is commuting on a motorcycle worth it?
That is a judgement about time, cost and risk that this post does not attempt to settle. On the air alone, the honest answer is that it depends on your hours, your city and whether anything filters what reaches your face. For deeper context, start with our rider air pollution guide.
How many hours on the road does a rider bank in five years?
On the assumptions above, a 2-hour commuter riding 250 days a year logs 2,500 hours over five years, and an 8-hour delivery rider riding 300 days a year logs 12,000, about 500 full days. Change the days and the total scales with it.
Ready to change the one term in your ledger you can?
Hours and years are set by the job. Concentration is the term a filter can change. See the Easi Breezi system, or stock replacement HEPA filters so it is ready when you are.
Written by Ash, mechanical engineer and founder of Easi Breezi, building an active HEPA filtration system for motorcycle helmets (patent pending). Based between Hong Kong and Bali, riding daily in the traffic this blog writes about.