Area or personal air sampling: which one answers your question
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.
A personal sample is taken in the worker's breathing zone, with the worker wearing the pump. An area sample is taken at a fixed location in the room. These are not two grades of the same service, because they answer different questions, and a result that answers the wrong question will not support the conclusion you needed from it.
The short version
| Personal sample (breathing zone) | Area sample (fixed location) | |
|---|---|---|
| Who wears the pump | The worker | Nobody. It sits on a stand |
| Where the sample inlet sits | On the lapel or collar, in the breathing zone. The OSHA Technical Manual describes that zone as a hemisphere in front of the shoulders, with a radius of 6 to 9 inches | At a fixed location, usually at breathing height |
| Question it answers | What did this person breathe? | What is the air like at this location? |
| Can demonstrate compliance with a standard | Yes, under every standard | Only where the standard allows it. See below |
| Locates a source | Poorly | Well |
| Verifies that a control works | Indirectly | Directly |
| Follows the worker | Yes, including into and out of the dust or fume plume | No |
Why compliance usually takes personal samples
OSHA's exposure standards are written about workers, not about rooms. The silica standard builds its monitoring around what each worker breathes, and the other substance-specific standards generally do the same. The lead standard says it outright, requiring full-shift personal samples of at least seven continuous hours.
The reason behind this is physical. A worker moves through air where the concentration can vary by a factor of ten across a few feet. Workers lean into the work and stand where the part is, which is often exactly where the fume is. A sampler on a tripod 10 feet away collects different air than the air the worker is inhaling, and no general formula converts one into the other.
Where a standard requires personal sampling, area results do not satisfy that requirement. Not every standard requires it, however, so it pays to be exact about where it applies:
- Substance-specific standards set their own monitoring terms. These cover lead, silica, cadmium, benzene, hexavalent chromium and the rest, and several of them name personal breathing zone sampling directly.
- OSHA's general air contaminants standard holds Tables Z-1, Z-2 and Z-3 and several hundred substances. It sets limits on worker exposure, but it names no sampling method at all, personal or area. Under that standard, the test is whether the worker's exposure exceeded the limit, and personal sampling is the most direct proof of that.
What the noise standard spells out
OSHA's noise standard states the principle more fully than most standards do. It requires representative personal sampling where conditions make area monitoring a poor fit, and it names those conditions:
- High worker mobility. The worker moves between areas that have different sound levels.
- Significant variations in sound level. The sound level at the location itself changes over the shift.
- A significant amount of impulse noise. These are bursts that a fixed meter reading will miss or measure incorrectly.
The standard also ends with a clause that is easy to miss. Personal sampling is required in those conditions "unless the employer can show that area sampling produces equivalent results," the standard says. So even here, area sampling satisfies the standard if you show that it gives equivalent results. The showing is the employer's to make and it has to be documented, but the door is open and it is written into the standard.
Those three conditions make a useful general test, even for substances where the standard does not spell them out. Ask whether your people move, whether the process runs in cycles and whether exposure comes in bursts. If any of those is true, a fixed-location reading does not stand in for a personal one, except where you can show that it does.
→ Personal noise dosimetry · → Noise surveys
When area sampling is the right tool
Area sampling is the right choice much of the time, and it is not a budget option. It is the proper tool for a set of questions that personal sampling answers poorly or not at all.
Locating the source. A personal sample tells you a welder was at 4.2 milligrams per cubic meter of air (mg/m³), but it does not tell you where that exposure came from. It could be their own arc, the arc two bays over or the plasma table behind them. A grid of area samples run at the same time does tell you.
Verifying that a control works. Measure at the same fixed locations before and after a hood change, with the same process running, and the difference comes from the change. Personal samples move with the worker, so everything else that changed that day muddies the comparison.
Checking boundaries and background levels. Area samples show what is coming into the clean area, what is leaving through the roll-up door, and what the shop's baseline level is before the first arc strikes.
Continuous unattended monitoring. Fixed instruments run for days, and nobody wears a pump for days.
Screening before you commit to a full survey. Area samples cost less for each location, and they can tell you whether a full round of personal sampling is warranted at all.
Emergencies and confined space entry. Direct-reading area instruments are the right tool there, not personal samples that collect air over time.
What we recommend in practice
Most well-designed surveys use both types, for different purposes in the same visit, and the report then states clearly which results show whether you comply with the standard.
Two things are worth checking in any written sampling plan. First, if a compliance question is to be answered with area sampling, the plan should say which standard permits that and how equivalent results will be demonstrated. Second, an area result compared with a permissible exposure limit (PEL) should be labeled as what it is: a measure of conditions at one location, not of a worker's exposure.
Where you may not need either. Sometimes the question is whether there is any exposure at all. Published data that represents your process, or data from the manufacturer, may already cover your conditions, and in that case several standards permit an exposure assessment without sampling. That is a legitimate route, and it is worth checking before you buy pumps.
→ Using objective data in place of new monitoring
How we run it
A sound plan sets the number of personal samples by similar exposure group (SEG), meaning workers who do the same job the same way, not by headcount. Area samples go where they will answer a specific question written down before the visit, such as a suspected source, a control under evaluation or a boundary that matters.
Area results belong in the report under their own heading. They should be compared with the PEL only where that comparison is valid, and never used in place of a personal breathing zone result.
A defensible report states, for each sample, whether it was personal or area and where the sample inlet was located.
→ Similar exposure groups: how workers are grouped · → How to read an industrial hygiene report · → Air monitoring surveys
Plan a survey that answers the right question
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 1910.1000 Air Contaminants
- OSHA 29 CFR 1910.1025(d)(1)(ii) Lead
- OSHA 29 CFR 1910.1053(d) Respirable Crystalline Silica
- OSHA 29 CFR 1910.95(d)(1)(ii) Occupational Noise Exposure
