Formaldehyde: why the action level and STEL set your schedule
This page explains what the rules and common practice call for. Every site is different, and what a survey or a filing needs at your facility is something we work out with you after we see it.
OSHA's formaldehyde standard has no accelerated monitoring schedule for results above the permissible exposure limit (PEL).
Most of OSHA's health standards increase your monitoring frequency when you exceed the PEL. Lead, silica and hexavalent chromium all move to monitoring every three months.
The formaldehyde standard does not work that way. Periodic monitoring is tied to two other numbers: the action level and the short-term exposure limit (STEL), which covers a 15-minute period. Exceeding the PEL of 0.75 parts per million (ppm) does not by itself change how often you must monitor.
That reads backwards until you see what it means, which is that the action level and the STEL do all the work. If your survey produced only an 8-hour time-weighted average (TWA), it did not produce the two results your monitoring schedule actually depends on.
Where we find it
- Histology and anatomic pathology labs. Grossing, the cutting up of tissue specimens, is the classic short-term exposure. It is brief and repeated, and it is often the only exposure in the building above the STEL.
- Mortuaries and embalming rooms.
- Manufacturing particleboard, medium-density fiberboard (MDF), plywood and hardboard. The exposure comes from applying urea-formaldehyde and phenol-formaldehyde resin, opening the press, hot stacking and sanding.
- Foundry core-making with phenol-formaldehyde binder systems.
- Permanent-press and durable-press textile finishing. Resin padding and curing ovens.
- Salon smoothing and keratin treatments. The gas is released during blow-drying and flat-ironing, not from the bottle at rest.
- Manufacturing resins, adhesives and coatings.
Exposure limits
| Value | Averaging time | |
|---|---|---|
| OSHA PEL | 0.75 ppm | 8-hour TWA |
| OSHA STEL | 2 ppm | 15 minutes |
| Action level | 0.5 ppm | 8-hour TWA |
| NIOSH REL | Treated as a carcinogen. 0.016 ppm shift average · 0.1 ppm ceiling limit, 15 minutes | |
| ACGIH TLV | 0.1 ppm shift average · 0.3 ppm STEL |
The REL is NIOSH's recommended exposure limit, and the TLV is the threshold limit value published by ACGIH. A ceiling limit is a concentration that must not be exceeded at any time.
The NIOSH REL is roughly 47 times lower than the OSHA PEL. That is not a small difference in how two organizations read the same data, because NIOSH classifies formaldehyde as a carcinogen and is asking a different question. It is worth knowing where you stand against the REL, above all in a histology lab where the staff are the same people for 20 years.
How we sample for it
| Sampling media | A glass sorbent tube packed with XAD-2 coated with 10% 2-HMP. It has a 150 mg sampling section and a 75 mg backup section. The same tube serves both sample types. |
| Full-shift TWA sample | 0.1 liters per minute (L/min) · 24 liters (L), which is four hours for each tube. A full shift takes consecutive tubes, with the results weighted by air volume. |
| STEL sample | 0.2 L/min · 3 L · 15 minutes |
| Analytical method | OSHA 52 (analysis by GC-NPD) |
| Sample type | Personal samples in the worker's breathing zone. Full-shift samples and separate 15-minute samples. |
| Laboratory | An independent, nationally accredited laboratory (accredited under the federal NVLAP program) |
One tube, two sampling strategies. The method collects the TWA sample and the STEL sample on the same type of coated tube, but they are separate samples, run at different flow rates for different durations.
A tube reports a single average for the whole time it ran. You therefore cannot split a full-shift sample to get a short-term result, and you cannot pull the two-hour grossing block out of the shift average after the fact.
The sampling plan has to identify the highest-exposure task before the visit, and someone has to be standing there when it happens with a second pump and a second tube. In a histology lab that task is grossing, in a particleboard plant it is opening the press or transferring resin, and in a salon it is the flat-iron pass. Miss it, and the survey comes back valid on paper and useless in practice.
The coating matters as well. Formaldehyde is not a solvent that plain charcoal can collect, so it needs a coating that reacts with it and holds it as a stable compound. On an uncoated tube, the result reads low.
What your results require you to do
The formaldehyde standard sets out these steps:
| Trigger | What the standard requires | Paragraph |
|---|---|---|
| At or above the action level (0.5 ppm, 8-hour TWA) | Repeat monitoring at least every 6 months | (d)(3) |
| At or above the STEL (2 ppm) | Repeat monitoring at least once a year under worst conditions | (d)(3) |
| Above the PEL | No additional step. The schedule is still set by the action level and STEL triggers | (d)(3) |
| A worker reports signs or symptoms of formaldehyde exposure | Prompt monitoring of the affected worker, whatever the last result was | (d)(2)(iii) |
| To stop monitoring | Two consecutive sampling periods, at least 7 days apart, below both the action level and the STEL | (d)(4) |
The symptom trigger sits outside the monitoring calendar. It does not depend on your last result, and it is not on a schedule. If a lab worker reports eye irritation, burning or respiratory symptoms, and there is a reasonable basis to link them to formaldehyde, you owe prompt monitoring even if your results were clean four months ago.
Note the criteria for stopping as well. They call for results below both limits, on two occasions, 7 days apart, so a single clean shift ends nothing.
→ See how often monitoring is required, by substance
The gap between the standard and the smell
Many people can smell formaldehyde, and feel it sting their eyes, at concentrations below the PEL, and individuals differ a great deal in when they notice it. This leads to two opposite mistakes in the same building.
Staff who can smell it assume they are overexposed, and they lose trust in a result that meets the limit. Staff who have become accustomed to it stop noticing it and assume nothing is there.
Neither instinct is data, and both shape how people behave. On one side people refuse respirators, and on the other they get careless about ventilation.
Most of the value of a survey here is that it settles the argument. A grossing station that measures 0.3 ppm as a shift average, with a 1.4 ppm short-term result, is a different problem to manage from a station at 0.9 ppm. You cannot tell them apart by walking into the room.
→ What to do when results exceed the PEL
Plan a formaldehyde survey
Ron Fleming has done this work himself since 1993. You talk directly to the person who does the job. No account managers. No call center. Our prices are well below the competition. Tell us what is going on and we will send a written scope of work and a price, at no cost.
Talk with us. No cost.References
The regulations and standards behind this page, with links to the official text, so you can check the source yourself.
- OSHA 29 CFR 1910.1048(d) Formaldehyde
- OSHA 29 CFR 1910.1048(d)(3) Formaldehyde
