Analysis of Nitrosamines in Drinking Water Using the Agilent 5977A Series GC/MSD System
Applications | 2013 | Agilent TechnologiesInstrumentation
Chloramination in water treatment can generate nitrosamines such as NDMA, classified as probable human carcinogens. Monitoring these trace contaminants in drinking water at sub-part-per-trillion levels is essential for public health protection and compliance with regulatory guidelines worldwide.
This study evaluates the Agilent 5977A Series GC/MSD System for detecting six nitrosamines in drinking water. The aim is to achieve limits of detection below those cited in EPA Method 521 without large-volume injection or MS/MS instrumentation.
Sample Preparation:
Calibration and Linearity:
The method enables:
Potential developments include:
The Agilent 5977A GC/MSD system in PCI mode offers reliable sub-ppt detection of nitrosamines, outperforming EPA Method 521 LODs with minimal injection volume and single-quadrupole instrumentation.
GC/MSD, GC/SQ
IndustriesEnvironmental
ManufacturerAgilent Technologies
Summary
Importance of Topic
Chloramination in water treatment can generate nitrosamines such as NDMA, classified as probable human carcinogens. Monitoring these trace contaminants in drinking water at sub-part-per-trillion levels is essential for public health protection and compliance with regulatory guidelines worldwide.
Objectives and Overview of Study
This study evaluates the Agilent 5977A Series GC/MSD System for detecting six nitrosamines in drinking water. The aim is to achieve limits of detection below those cited in EPA Method 521 without large-volume injection or MS/MS instrumentation.
Methodology and Instrumentation Used
Sample Preparation:
- 500 mL water samples extracted by solid-phase extraction following EPA 521 procedures.
- NDMA-d6 surrogate added pre-extraction; NDPA-d14 internal standard added post-concentration.
- Elution in methylene chloride; concentrated to 1 mL (500× enrichment).
- GC: Agilent 7890B with multimode inlet (MMI).
- MS: Agilent 5977A MSD in positive chemical ionization (PCI) mode using methane.
- Column: VF-624ms (20 m × 0.15 mm, 0.84 µm).
- Injection: 2 µL splitless; inlet at 250 °C.
- Oven: 35 °C (4 min) →195 °C at 10 °C/min →240 °C at 15 °C/min (2 min hold).
- Acquisition: Full scan m/z 40–200 and SIM for target/qualifier ions.
Main Results and Discussion
Calibration and Linearity:
- 0.5–50 ppb in methylene chloride; correlation coefficients ≥0.9985.
- LODs (3.3σ) ranged 0.018–0.166 ppb in extract (equivalent to 0.036–0.332 ppt in water).
- LOQs (10× LOD) ranged 0.182–1.662 ppb.
- Agilent GC/MSD LODs were 1.9–11× lower than EPA 521 despite a 10× smaller injection and use of single-quadrupole MS.
Benefits and Practical Applications
The method enables:
- High-sensitivity quantitation of nitrosamines without MS/MS.
- Smaller injection volumes for simpler operation.
- Reproducible results via automated sample preparation.
Future Trends and Possibilities
Potential developments include:
- On-line SPE integration for higher throughput.
- PCI/MS adaptation to other disinfection by-products.
- High-resolution mass spectrometry for enhanced selectivity.
Conclusion
The Agilent 5977A GC/MSD system in PCI mode offers reliable sub-ppt detection of nitrosamines, outperforming EPA Method 521 LODs with minimal injection volume and single-quadrupole instrumentation.
Used Instrumentation
- Agilent 7890B GC with MMI.
- Agilent 5977A MSD in PCI mode.
- Agilent 7696A Sample Prep WorkBench.
References
- EPA Method 521: Determination of Nitrosamines in Drinking Water by SPE-GC/MS/MS.
- Health Canada. Guidelines for Canadian Drinking Water Quality: NDMA.
- World Health Organization. Guidelines for Drinking-water Quality (2008).
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