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Fast and Accurate Determination of Algal Toxins in Water Using Online Preconcentration and UHPLC-Orbitrap Mass Spectrometry

Applications | 2016 | Thermo Fisher ScientificInstrumentation
Sample Preparation, LC/HRMS, LC/MS, LC/MS/MS, LC/Orbitrap
Industries
Environmental
Manufacturer
Thermo Fisher Scientific

Summary

Significance of the Topic


Algal toxins produced by cyanobacteria pose serious health risks to humans and animals, requiring reliable monitoring of water supplies in compliance with WHO guidelines. Rapid and sensitive analysis methods are essential for early warning and management of drinking water sources.

Objectives and Study Overview


The study aimed to develop a fast, accurate column-switching method combining online preconcentration with high-resolution full-scan Orbitrap mass spectrometry for quantifying microcystin variants (LR, RR, YR) and nodularin in raw and treated water.

Methodology and Used Instrumentation


The method used 1 mL water injections into a Thermo Scientific EQuan MAX online UHPLC system. A Hypersil GOLD aQ trap column captured toxins under 98:2 water/acetonitrile with 0.1% formic acid, then switched to a Hypersil GOLD analytical column for elution. Detection was performed on a Thermo Scientific Exactive Orbitrap mass spectrometer in positive electrospray full-scan mode at 50 000 resolving power. Samples were filtered (0.45 µm GF) and analyzed within three days of collection.

Main Results and Discussion


Exact mass measurements and carbon isotope patterns confirmed toxin identities with high confidence. Retention times ranged 2.6–2.8 min. Calibration was linear over 100–1000 pg/mL (r² = 0.9971–0.9996), with reproducibility within ±15%. Online preconcentration achieved the same enrichment as offline SPE of 200 mL to 2 mL, but with only 1 mL injections. Analysis time per batch of five samples dropped from ~12.3 h (conventional) to ~2 h (online), an 80% reduction. Method detection limits were 0.009–0.035 ng/mL and quantitation limits 0.03–0.11 ng/mL. Recovery rates ranged 70.3–113.7% with precision 2.5–10.9%. Environmental samples from multiple river basins and treatment plants showed toxin levels below detection, while cyanobacterial concentrates revealed microcystin-LR.

Benefits and Practical Applications


  • High-throughput screening with <5 min run times per sample
  • Elimination of lengthy offline SPE reduces labor and solvent use
  • Full-scan data enable retrospective analysis for non-target toxins
  • Compliance with stringent international water quality limits

Future Trends and Potential Applications


Integration with automated monitoring networks and expansion to other cyanotoxins such as anatoxin and aplysiatoxin are promising. Advances in miniaturized UHPLC-Orbitrap platforms and data-driven retrospective screening will further enhance early warning capabilities.

Conclusion


The optimized online preconcentration UHPLC-Orbitrap method provides rapid, sensitive, and accurate detection of key algal toxins in water, significantly improving throughput and resource efficiency while meeting international safety guidelines.

References


  1. World Health Organization. Toxic Cyanobacteria in Water: A Guide to Their Public Health Consequences, Monitoring and Management; WHO: Geneva, 1999; pp. 163–164.
  2. Henriksen AS, Olli K. Sedimentation and Buoyancy of Aphanizomenon cf. flos-aquae (Nostocales, Cyanophyta) in a Nutrient-Replete and Nutrient-Depleted Coastal Area of the Baltic Sea. Phycologia. 1996;35:94–101.
  3. Repavich WM, Meisner LF, Sonzogni WC, Standridge JH, Wedepohl RE. Cyanobacteria (blue-green algae) in Wisconsin waters: acute and chronic toxicity. Water Res. 1990;24:225–231.
  4. Lee JJ, Kim HB, Moon JS, Lee JA, Lee HJ, Park HK, Park JH, Seo JK. Assessment of Microcystin Analysis Methods for Convenient Monitoring. Proc. Korean Soc. Water Fall 2010 Conf.; 2010; pp. 643–644.
  5. Sivonen K. Cyanobacterial Toxins. In Encyclopedia of Microbiology, 3rd ed.; 2009; pp. 290–307.
  6. Jang JH, Kim YS, Choi JW. Rapid Analysis of Microcystins in Water. J. Korean Soc. Water Environ. 2012;28(6):843–850.
  7. Lawton LA, Codd GA, Edwards C. Extraction and HPLC Method for Microcystins in Raw and Treated Waters. Analyst. 1994;119:1525–1530.
  8. Harada K, Matsuura K, Suzuki M. Analysis and Purification of Toxic Peptides from Cyanobacteria by RP-HPLC. J. Chromatogr. A. 1988;448:275–283.
  9. Yu SJ, Han EY, Hwang JY, Ryu JK, Yoon YS. Analysis of Microcystins in Daecheong Reservoir using HPLC. J. Korean Soc. Water Environ. 1999;15(4):517–526.
  10. Petrovic M, Barcelo D, Tavazzi S. Column-switching System with Restricted Access Pre-column for Integrated Sample Cleanup and LC-MS of Alkylphenolic Compounds and Steroid Sex Hormones in Sediment. J. Chromatogr. A. 2002;971(20):37–45.
  11. Zweigenbaum JA, Beattie KA, Codd GK, Henion JD. Direct Analysis of Microcystins by Microbore LC-ESI Ion-Trap MS/MS. J. Pharm. Biomed. Anal. 2000;23(4):723–733.
  12. Cong L, Chen Q, Huang B, Lu B, Ren Y, Zhang J. Determination of Trace Microcystins in Water Using LC-MS/MS. Anal. Chim. Acta. 2006;569:157–168.
  13. Kim JH, Kim HC, Yun MA. Simultaneous Determination of Cyanotoxins in Water by LC-MS/MS. J. Korean Soc. Water Environ. 2009;25(4):597–605.
  14. Fastner J, Flieger I, Neumann U. Optimized Extraction of Microcystins from Field Samples: Comparison of Solvents and Procedures. Water Res. 1998;32(10):3177–3181.

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