🏭 Volatile organic compounds in emissions

Environmental PN-EN 13649

Determination of mass concentration of individual volatile organic compounds (VOC) in waste gases from stationary sources by sorption on activated carbon with solvent or thermal desorption and GC-FID/MS analysis.

Overview

Volatile organic compounds (VOC) emitted from stationary sources (chimneys, emitters) pose a serious environmental problem — they are precursors of tropospheric ozone and photochemical smog, and many of them exhibit carcinogenic effects (benzene, formaldehyde, vinyl chloride). VOC emission control is required by IED Directive 2010/75/EU, Ministry of Environment Regulation on emission standards and integrated permits.

Standard PN-EN 13649 describes the method of sampling gases emitted from stationary sources onto sorbent tubes filled with activated carbon or other sorbents, followed by solvent desorption (carbon disulfide CS₂) or thermal desorption, and chromatographic analysis GC-FID or GC-MS. Version CEN/TS 13649:2014 extended the standard with the option of thermal desorption on TD tubes, eliminating the need to use toxic CS₂.

The method is used by accredited measurement laboratories performing emission measurements commissioned by industrial plants (printing houses, paint shops, chemical, petrochemical, pharmaceutical industries). Results are expressed as mass concentration of individual compounds in mg/m³ at standard conditions, referred to dry gas and conventional O₂ content.

Proper sampling requires isokinetic or proportional sampling from the emitter duct using a heated probe and transport line to prevent condensation.

Method principle

Waste gas is sampled from the emitter duct using a heated probe and passed through sorbent tubes filled with activated carbon (SKC, Anasorb) or polymeric sorbents (Tenax TA, Chromosorb). VOCs adsorb on the sorbent surface. After sampling, fibers are desorbed: (1) by solvent method — washing with CS₂ and analysis of solution on GC-FID, or (2) by thermal method — heating TD tube in thermal desorber (e.g. 300°C) and transport of desorbed analytes with carrier gas (He/N₂) onto GC column with FID or MS detection. Identification based on retention times (FID) or mass spectra (MS), quantification using calibration curves.

Applications

Key parameters

ParameterValue
Measurement range0.1–10 000 mg/m³ (depending on compound)
Detection limit0.01–0.1 mg/m³ (TD-GC-MS)
Sampling time30 min – 4 h (depending on concentration)
Sampling flow0.1–1.0 L/min (sorbent tubes)
Probe temperature≥120°C (prevent condensation)
Repeatability±10–15% (depending on compound and concentration)

Standard

Standard number
PN-EN 13649:2002 (CEN/TS 13649:2014)
Title (PL)
Emisje ze źródeł stacjonarnych — Oznaczanie stężenia masowego indywidualnych gazowych związków organicznych — Metoda z sorpcją i desorpcją rozpuszczalnikową lub termiczną
Title (EN)
Stationary source emissions — Determination of the mass concentration of individual gaseous organic compounds — Sorptive sampling method followed by solvent extraction or thermal desorption

Step-by-step procedure

1. Field equipment preparation

Check pump and probe tightness. Prepare sorbent tubes (activated carbon or TD). Calibrate rotameter/gas meter.

⏱ Time: 30 min

2. Probe mounting in emitter

Insert heated probe into emitter duct through measurement ports. Connect heated line (≥120°C) to sorbent tubes.

⏱ Time: 20 min • 🌡 Temperature: ≥120°C

3. Gas parameter measurement

Measure temperature, pressure, gas velocity in duct, humidity. Determine standard conditions (273 K, 101.3 kPa, dry gas).

⏱ Time: 15 min

4. Sample collection on sorbent tubes

Start pump — flow 0.1–1.0 L/min. Sample for 30 min – 4 h. Use 2 tubes in series (main + control).

⏱ Time: 30 min – 4 h

5. Sample securing

Cap tubes with PTFE plugs. Place in sealed containers, transport coolers. Transport to laboratory within <24 h.

⏱ Time: 10 min

6. Solvent desorption (CS₂)

In laboratory break tube, transfer sorbent to vial. Add 1–2 mL CS₂. Shake 30 min. Centrifuge.

⏱ Time: 45 min

7. Alternative: thermal desorption (TD)

Place TD tube in thermal desorber. Program: 300°C/10 min, focus trap -10°C → 300°C, transfer to GC.

⏱ Time: 20 min • 🌡 Temperature: 300°C

8. GC-FID or GC-MS analysis

Inject 1 µL (CS₂) or transfer from TD. Temperature program: 40°C/3 min → 10°C/min → 250°C. Identification and quantification.

⏱ Time: 30–45 min

9. Calibration and calculations

Determine concentrations from calibration curves. Convert to standard conditions (273 K, 101.3 kPa, dry gas, conventional O₂).

⏱ Time: 15 min

10. Quality control

Analysis of blank (clean tube), duplicate, control sample with standard. Recovery of control tube <5% of main tube.

⏱ Time: 30 min

Required equipment and apparatus

EquipmentExampleIndicative price
Gas chromatograph with FIDAgilent 8890 GC-FID, Shimadzu GC-2030 Nexis100 000–250 000 PLN
Gas chromatograph with MSAgilent 7890B/5977B GC-MS, Shimadzu GCMS-QP2020 NX250 000–500 000 PLN
Thermal desorberMarkes TD100-xr, PerkinElmer TurboMatrix80 000–200 000 PLN
Sampling pump with rotameterGilian GilAir-5, SKC AirChek Touch3 000–8 000 PLN
Heated emission probeTitanium isokinetic probe, Paul Gothe, TCR Tecora15 000–40 000 PLN
Sorbent tubes with activated carbonSKC 226-01, Anasorb CSC 150/75 mg15–30 PLN/pc.
TD tubes with Tenax TAMarkes C1-AXXX-5003, ∅6.4 mm × 89 mm80–150 PLN/pc.

Reagents, media and consumables

ReagentCASDetails
Carbon disulfide (CS₂) pure75-15-0Solvent for desorption from activated carbon, ultrapure ≥99.9%, 1 L
Activated carbon (sorbent)7440-44-0Granulated, 20/40 mesh, thermally activated, for sorbent tubes
Tenax TA (polymeric sorbent)24938-68-92,6-diphenyl-p-phenylene oxide, 60/80 mesh, for thermal desorption
VOC standards in CS₂ or methanolCertified mixtures: BTEX, alcohols, esters, ketones, chlorinated — for GC calibration
Calibration gases (BTEX in N₂)Cylinders with standard gas mixtures 1–100 ppm, accredited certificate
Helium or nitrogen UHP 5.07440-59-7GC carrier gas, purity ≥99.999%, 50 L cylinder

Health and safety (OHS)

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