☠️ Dioxins and PCBs (GC-HRMS)

Environmental PN-EN 1948-1

Determination of polychlorinated dibenzo-p-dioxins (PCDD), dibenzofurans (PCDF) and dioxin-like PCBs by high-resolution gas chromatography mass spectrometry (GC-HRMS). One of the most difficult environmental analyses.

Overview

Dioxins (PCDD/PCDF) and dioxin-like polychlorinated biphenyls (dl-PCBs) are among the most toxic anthropogenic substances — persistent organic pollutants (POPs) covered by the Stockholm Convention. Their determination requires the use of highest class analytical equipment — gas chromatography coupled with high-resolution mass spectrometry (HRGC/HRMS) with mass resolution ≥ 10 000.

Standard PN-EN 1948 defines methods for sampling and analysis of emissions from stationary sources (chimneys, incinerators), but GC-HRMS technique is also used for analysis of dioxins in food (Regulation (EU) 2023/915), feed, soil, sewage sludge and biological samples. Results are expressed in TEQ (toxic equivalent) using WHO-2005 toxicity equivalency factors (TEF).

The analytical procedure is extremely complex and costly — requires multi-stage extraction, cleanup on multilayer columns (silica, alumina, activated carbon), analysis on GC-HRMS with selected ion detection (SIM) and quantification by isotope dilution method (using ¹³C-labeled internal standards). Cost of single analysis is 3 000–8 000 PLN.

In Poland, dioxin analyses are performed by few laboratories, including Laboratory of Trace Analysis (dioksyny.pl), J.S. Hamilton Poland, ALS Poland and Institute of Environmental Protection. ISO 17025 accreditation in this area requires participation in interlaboratory comparison studies (e.g. INTERCAL).

Method principle

The method is based on isotope dilution — known amounts of ¹³C-labeled internal standards (17 PCDD/PCDF congeners and 12 dl-PCBs) are added to the sample. After extraction and multi-stage cleanup, the extract is analyzed on gas chromatograph with capillary column (DB-5ms or DB-Dioxin) coupled with magnetic sector mass spectrometer with resolution ≥ 10 000 R (10% valley). Detection in SIM (Selected Ion Monitoring) mode — molecular and fragment ions for each congener are monitored. Quantification based on ratio of analyte to ¹³C standard signals.

Applications

Key parameters

ParameterValue
Mass spectrometer resolution≥ 10 000 R (10% valley definition)
Limit of detection0.1–1 pg TEQ/g (food), 0.01 ng TEQ/Nm³ (emission)
Number of congeners17 PCDD/PCDF + 12 dl-PCB = 29 analytes
TEF factorsWHO-2005 (2,3,7,8-TCDD = 1.0)
Limit in food (meat)2.5 pg WHO-TEQ/g fat (PCDD/F), 5.0 pg (sum TEQ)
Analysis cost3 000–8 000 PLN / sample

Standard

Standard number
PN-EN 1948-1:2006 + PN-EN 1948-4:2013+A1:2014
Title (PL)
Emisje ze źródeł stacjonarnych — Oznaczanie stężenia masowego PCDD/PCDF i dioksynopodobnych PCB
Title (EN)
Stationary source emissions — Determination of the mass concentration of PCDDs/PCDFs and dioxin-like PCBs

Step-by-step procedure

1. Addition of internal standards

Add known amounts of ¹³C-labeled internal standards PCDD/PCDF and dl-PCB to sample (10–50 g). Mix.

⏱ Time: 15 min

2. Extraction

Perform toluene-acetone extraction (Soxhlet 16h or ASE). For liquid samples — liquid-liquid extraction.

⏱ Time: 4–16 h • 🌡 Temperature: 100–120°C (ASE)

3. Cleanup — acidic column

Pass extract through multilayer silica column (acidic H₂SO₄ layer, basic KOH, neutral). Elution with hexane.

⏱ Time: 60 min

4. Cleanup — alumina column

Pass through aluminum oxide column. Elution: fraction 1 (hexane — discard), fraction 2 (DCM/hexane — collect).

⏱ Time: 30 min

5. Cleanup — carbon column

Pass through activated carbon AX-21 column on Celite. Separation of mono-ortho PCB from PCDD/PCDF and non-ortho PCB.

⏱ Time: 60 min

6. Concentration

Evaporate eluents to ~50 µL under nitrogen stream. Add recovery standards. Transfer to GC vial.

⏱ Time: 30 min

7. GC-HRMS analysis

Analysis on DB-5ms column (60 m). Temp program: 120°C→200°C (20°C/min)→280°C (3°C/min)→310°C (10 min). SIM mode, resolution ≥ 10 000.

⏱ Time: 60–90 min

8. Identification and quantification

Identify congeners based on retention time and isotope ratio (±15% of theoretical value). Calculate concentrations by isotope dilution method.

9. TEQ calculation

Multiply concentration of each congener by appropriate TEF (WHO-2005). Sum TEQ for PCDD/PCDF and dl-PCB separately and combined.

10. Quality control

Check recovery of internal standards (25–150%). Analyze blank sample, duplicate and CRM in each series.

Required equipment and apparatus

EquipmentExampleIndicative price
GC-HRMS (magnetic sector)Thermo DFS, Waters AutoSpec Ultima, JEOL JMS-800D1 500 000–3 000 000 PLN
Automated extraction system (ASE)Thermo Dionex ASE 350, Büchi SpeedExtractor E-916100 000–200 000 PLN
Automated cleanup systemFMS PowerPrep, Fluid Management Systems200 000–400 000 PLN
Concentrator (evaporator)Zymark TurboVap II, Büchi Syncore30 000–60 000 PLN
Cleanup columns (multilayer)Silica columns (acidic/basic), alumina, activated carbon AX-21500–2 000 PLN / disposable set
GC capillary columnAgilent DB-5ms (60 m × 0.25 mm × 0.25 µm), Restek Rtx-Dioxin22 000–4 000 PLN

Reagents, media and consumables

ReagentCASDetails
¹³C PCDD/PCDF standards (internal)MixtureWellington Labs EPA-1613 LCS — 16 ¹³C-labeled PCDD/PCDF congeners, ~8 000 PLN / ampoule
¹³C dl-PCB standards (internal)Wellington Labs WP-LCS — 12 ¹³C-labeled dl-PCBs, ~5 000 PLN / ampoule
Native standards (calibration)Wellington Labs EPA-1613 CS1–CS5 — set of 5 concentrations for calibration curve
Toluene (pesticide grade)108-88-3Purity ≥ 99.9%, Merck Suprasolv, for extraction and GC analysis
Hexane (pesticide grade)110-54-3Purity ≥ 99%, for cleanup on silica columns
Dichloromethane (pesticide grade)75-09-2Purity ≥ 99.9%, for extraction and elution from cleanup columns
Concentrated sulfuric acid7664-93-9For preparation of acidic layer of silica column (44% H₂SO₄ on silica)
Activated carbon AX-21For separation of planar PCB fraction from PCDD/PCDF on carbon column

Health and safety (OHS)

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