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VOC Testing: Identify Volatile Organic Compounds Indoors

Laboratory speciation of indoor VOCs using sorbent-tube sampling and thermal-desorption gas chromatography — identifying individual compounds, attributing sources and quantifying occupant exposure.

VOC Testing: Identify Volatile Organic Compounds Indoors

Method

TD-GC/MS

Compounds

100+ speciated

TVOC reference

<300 µg/m³

Detection limit

<1 µg/m³

01

Why VOC testing matters

Indoor VOC concentrations typically run two to five times outdoor levels, and after refurbishment can spike to fifty times higher for weeks. Many of the compounds responsible — benzene from glues, formaldehyde from MDF, toluene from paints, terpenes from cleaning chemistry — are odourless or pleasant-smelling at concentrations that already pose health risk.

Without speciated data, response is guesswork. With it, source control becomes a single targeted intervention rather than a building-wide overhaul.

VOC testing is most valuable after fit-out, in complaint investigations where occupants report headaches or irritation that resolves on leaving the building, and in any project that has to satisfy WELL, BREEAM or insurer requirements with defensible data.

02

Which compounds we measure

A typical speciation report covers four families.

Aromatic hydrocarbons. Benzene (WHO: no safe threshold), toluene, ethylbenzene, xylenes — emitted by adhesives, paints, solvents and fuel-burning equipment.

Aldehydes. Formaldehyde, acetaldehyde, hexanal — emitted by composite wood products, foam insulation and some textiles. Measured with DNPH cartridges in parallel with sorbent tubes.

Terpenes and limonenes. Pinene, limonene, eucalyptol — emitted by cleaning chemistry, air fresheners and wood finishes. Their secondary reaction products (with ozone) are often more irritating than the parent compounds.

Chlorinated and halogenated species. Tetrachloroethylene from dry-cleaning, chloroform from chlorinated water, methylene chloride from paint stripper — uncommon but important when present.

03

How the sampling works

The sampling protocol is straightforward and designed to be defensible in front of an auditor.

1. Pre-sample walk-through. Locate sources, identify representative breathing-zone positions, and select duplicate locations for QA.

2. Tube preparation. Sorbent tubes are conditioned and sealed at the laboratory, with field blanks travelling alongside the active samples to detect contamination during transport.

3. Active sampling. A low-noise personal sampling pump draws air through the tube at a measured flow rate, typically 50–100 ml/min, for 4–8 hours during representative occupancy.

4. Thermal desorption GC-MS. The lab heats the tube to release trapped compounds into the gas chromatograph. Each compound is identified by its mass spectrum and retention time, and quantified against a calibration standard.

5. Quality assurance. Field blanks, duplicate samples, and surrogate spikes verify the result before it appears in your report.

04

How results are interpreted

A raw species list is not a finding. Interpretation is where the value lies.

Benchmarking. Each species is compared against the appropriate reference — WHO IAQ guideline, UK HSE workplace exposure limit, German AGÖF orientation value, or industry comfort threshold.

Source attribution. Compound ratios fingerprint emission sources. A high limonene-to-formaldehyde ratio points to cleaning chemistry; a benzene-dominant profile points to traffic ingress or solvent storage.

Exposure context. Concentrations are weighted by occupancy hours to estimate dose, not just peak. A 200 µg/m³ formaldehyde reading at 03:00 in an empty office matters less than a 60 µg/m³ reading at 11:00 in a busy meeting room.

05

From results to remediation

Effective VOC remediation follows a hierarchy.

Source elimination. Removing the emitting material is always the most efficient solution. After fit-out, this often means a managed bake-out period before re-occupancy rather than a permanent change.

Substitution. Low-emission alternatives certified to Indoor Air Comfort Gold, GREENGUARD Gold or the M1 classification displace high-emitters in cleaning, finishes and furniture.

Dilution by ventilation. Increased outdoor air supply lowers indoor concentration in proportion to air-change rate. Pair with a ventilation assessment when this is the dominant control.

Activated-carbon filtration. Where source and ventilation cannot fully resolve the problem, a properly sized activated-carbon stage in the AHU removes residual VOCs and odours. Carbon depth and contact time determine effectiveness — surface-treatment products are largely cosmetic.

06

When to commission VOC testing

Five scenarios make VOC testing the right tool.

Post-refurbishment clearance before occupants return, especially after new flooring, paint, MDF joinery or foam insulation.

Complaint investigation where occupants report headache, eye irritation, sore throat or fatigue that resolves on leaving the building.

WELL or BREEAM submission where speciated baseline data is a precondition of certification.

Pre-purchase or pre-lease due diligence on a building with unknown history.

Industrial or laboratory environments where specific compounds are handled and exposure has to be quantified.

07

Frequently asked questions

What is a VOC and why test for it?

Volatile organic compounds are carbon-based chemicals that evaporate at room temperature. They include irritants, allergens and known carcinogens such as benzene and formaldehyde. Testing identifies which compounds are present and at what concentration, so source control can be targeted rather than guessed.

Isn't a consumer TVOC sensor good enough?

Consumer total-VOC sensors give a single index figure that mixes everything together. They are useful for trend spotting but cannot tell limonene from benzene. For source attribution, health risk assessment or post-refurbishment clearance, laboratory speciation is the only defensible method.

How is the sample actually collected?

Air is drawn through a sorbent tube — typically Tenax TA or carbograph — for a controlled period of four to eight hours. The tube traps VOCs onto its packing material. Back in the laboratory, thermal desorption releases the compounds into a gas chromatograph mass spectrometer for identification and quantification.

What concentrations are considered a problem?

Total VOC below 300 µg/m³ is widely accepted as a comfort target. For individual species, the WHO indoor air quality guidelines set health-based references — for example formaldehyde 100 µg/m³ over 30 minutes, benzene with no safe threshold. The report puts every measured species against its appropriate reference.

Can you trace a smell back to its source?

Yes. By combining grab samples taken close to suspected sources with room-average sorbent samples and a process of pattern-matching against known emission profiles, we can usually trace a complaint to a specific material, product or process within one site visit.

How does indoor air quality VOC testing differ from a TVOC sensor reading?

Indoor air quality VOC testing speciates each compound in the laboratory — naming benzene, formaldehyde, toluene and the rest with their individual concentrations against WHO and HSE references. A TVOC sensor returns a single index that lumps everything together. For compliance reporting, complaint investigation or post-refurbishment clearance, only speciated VOC testing is defensible.

Next step

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