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Speciation analysis of methylmercury via species specific isotope dilution GC-ICP-MS

Technical notes | 2018 | Thermo Fisher ScientificInstrumentation
GC, Speciation analysis, ICP/MS
Industries
Environmental
Manufacturer
Thermo Fisher Scientific

Summary

Importance of the Topic


Mercury is a pervasive environmental contaminant whose toxicity and bioaccumulation depend on its chemical form. Methylmercury (MeHg+) in particular poses significant risks to human health and ecosystems due to its biomagnification in food chains. Accurate speciation at trace and ultra-trace levels is therefore essential for environmental monitoring, risk assessment, and regulatory compliance.

Objectives and Study Overview


This study demonstrates the use of a Thermo Scientific Trace 1310 gas chromatograph coupled via a GCI 200 heated interface to a Thermo Scientific Element 2 high-resolution ICP-MS for species-specific isotope dilution GC-ICP-MS analysis of inorganic mercury and methylmercury. The goal was to validate performance in diverse matrices and establish sensitivity, precision, and accuracy benchmarks.

Methodology and Instrumentation


Instrumentation Used:
  • Trace 1310 GC with splitless injector and CP-Sil 5CB column (15 m×0.25 mm, 0.25 µm)
  • GCI 200 heated transfer line at 240 °C
  • Element 2 HR-ICP-MS with Pt tipped sampler and skimmer, low resolution, RF power 1150 W
  • Carrier and transfer gases: Ar, make-up gas as required

Sample Preparation:
  1. Spike with Me201Hg+ enriched tracer to achieve 201Hg/202Hg ≈ 1
  2. Biological samples: alkaline digestion (25% KOH in MeOH at 60 °C), acidify to pH 3.9, buffer, propylation with Na-tetrapropylborate, extract into n-hexane
  3. Water samples: direct buffering, propylation, hexane extraction, optional preconcentration by Ar blow-down
  4. Sediment: selective acidic extraction of organic Hg, tracer spike, propylation, hexane extraction
  5. GC separation: MeHgPr at 1.90 min, HgPr2 at 2.70 min; data acquisition for isotopes 200Hg, 201Hg, 202Hg

Data Analysis:
Isotope peaks were integrated and corrected for baseline. Concentrations of MeHg+ were calculated via isotope dilution considering sample mass, spike concentration, and measured isotope ratios.

Main Results and Discussion


Isotope ratio accuracy was within 1% deviation for natural ratios; the enriched 202Hg/201Hg ratio showed 2.7% deviation due to low 202Hg abundance. Certified reference material DORM-2 (4.47±0.32 mg/kg MeHg) yielded recoveries ≥98% with RSD ≤0.27% across triplicate injections and 1% across independent digests. Detection in ultrapure water down to 1 ng/L MeHg (1 pg injection) was demonstrated, with peak areas increasing from ~5 000 to ~70 000 for improved precision after evaporation preconcentration. Field water from the Weser River exhibited MeHg <0.1 ng/L with RSD up to 28%. CRM ERM-CC580 sediment (75.5±4 µg/kg MeHg) matched measured 74.9±0.75 µg/kg. Natural sediments showed MeHg levels of 0.6–2.3 µg/kg, representing 0.3–0.9% of total Hg.

Benefits and Practical Applications


This GC-HR-ICP-MS approach delivers rapid (<4 min) separation, species-specific quantification, and isotope verification, outperforming fluorescence-only methods by correcting for recovery losses and detecting side-reactions. It is applicable to diverse environmental and biological matrices for QA/QC, research, and regulatory monitoring.

Future Trends and Potential Applications


Advancements may include on-line microextraction, higher-throughput automation, broader organomercury speciation (e.g., ethylmercury), coupling with miniaturized sample preconcentration, and real-time field deployable systems for comprehensive environmental surveillance.

Conclusion


Species-specific isotope dilution GC-ICP-MS using the Trace 1310 GC, GCI 200 interface, and Element 2 HR-ICP-MS provides robust, accurate, and sensitive methylmercury speciation across varied sample types. Its precision, speed, and detection capabilities make it a gold standard for environmental mercury analysis.

References


  1. Driscoll C.T.; Mason R.P.; Chan H.M.; Jacob D.J.; Pirrone N. Environ. Sci. Technol. 2013, 47, 4967.
  2. Clarkson T.W.; Magos L. Crit. Rev. Toxicol. 2006, 36, 609.
  3. Lohren H.; Blagojevic L.; Fitkau R.; Ebert F.; Schildknecht S.; Leist M.; Schwerdtle T. J. Trace Elem. Med. Biol. 2015, 32, 200.
  4. Clémens S.; Monperrus M.; Donard O.F.X.; Amouroux D.; Guérin T. Talanta 2012, 89, 12.
  5. Heumann K.G. Anal. Bioanal. Chem. 2004, 378, 318.
  6. Bloom N.S.; Colman J.A.; Barber L. Fresenius’ J. Anal. Chem. 1997, 358, 371.
  7. Prichard E.; MacKay G.M.; Points J. In Trace Analysis: A Structured Approach… RSC, 1996, p. 95.
  8. Jackson B.; Taylor V.; Baker R.A.; Miller E. Environ. Sci. Technol. 2009, 43, 2463.

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