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Validation of HPLC method for scallops, clams and razors, and Pacific and Native oysters
Project Code: ZB1807;
- Turner, A.D. Hatfield R.G., Rapkova M, Higman W., Algoet M., Suarez-Isla B.A., Cordova M., Caceres C., van de Riet J., Gibbs R., Thomas K., Quilliam M., Lees D.N. (2011) Comparison of AOAC 2005.06 LC Official method with other methodologies for the quantitation of paralytic shellfish poisoning toxins in UK shellfish species. Journal of Analytical and Bioanalytical Chemistry 399(3),1257-1270
- Turner, A.D. Hatfield R.G., Rapkova-Dhanji M., Norton D.M., Algoet M., Lees D.N. (2010) Single laboratory validation of a refined AOAC HPLC method (2005.06) for oysters, cockles and clams in UK shellfish. Journal of AOAC International, 93(5),1482-1493
In response to an ever increasing need for alternative quantitative testing methods for shellfish, the Agency has commissioned research to develop and validate suitable chemical methods for the routine and official determination of shellfish biotoxins known to cause human illness.
In the investigation of the AOAC HPLC method for scallops, HPLC results showed acceptable method selectivity and linearity in both scallop extracts. Method performance characteristics were acceptable for the non-N-hydroxylated toxins oxidised by peroxide prior to HPLC quantitation. This included good evidence for acceptable toxin recovery, precision, ruggedness and sensitivity and with no evidence of matrix-related signal suppression. However, with poor method performance for N-hydroxylated toxins, the HPLC method would not be safe to implement for scallops in its current form and further work to improve the method performance is recommended.
With regard to clams and razors, validation results showed that the HPLC method was selective and sensitive enough to detect and quantify the presence of each toxin peak in both hard clams and razors. The linearity of the method was shown to be good over a wide range of toxin concentrations and toxin recoveries were similar to those described previously for other species. The precision of the method for both razors and hard clams was shown to be statistically acceptable over the short, medium and long – term and comparable to values reported previously for other species. Ruggedness experiments showed that the method was robust for all parameters investigated. Method performance results obtained throughout the study were used to calculate levels of Measurement Uncertainty (MU) for the analysis of PSTs in hard clams and razors, with results being generally lower and more consistent than the range of uncertainties reported previously for mussels.
With regard to oysters and cockles, validation results showed that the analysis of PSTs in oysters and cockles was selective and sensitive enough to detect and quantify the presence of each toxin peak. The relationship between HPLC instrumental response and toxin concentration was shown to be linear over an appropriate working range and toxin recoveries were similar to those described previously for mussels. The precision of the method for oysters and cockles was shown to be acceptable over the short, medium and long - term. Variability in method performance during these assessments was similar to or improved from values reported previously for mussels and all found to be statistically acceptable. Ruggedness experiments showed that the method was robust for all parameters investigated. Method performance results obtained throughout the study were used to calculate levels of Measurement Uncertainty (MU) for the analysis of PSTs in cockles and oysters, with results being generally lower and more consistent than the range of uncertainties reported previously for mussels.
An important part of all the validation studies carried out included parallel comparative analysis of the HPLC & MBA methods. Comparative results generally showed good correlation between the two methods for razors, clams and cockles, as determined previously in mussels. However, a high positive HPLC bias as compared with the MBA was observed in the quantitative analysis for pacific and native oysters, which was found not to be solely related to the use of highest toxicity equivalent factors (TEFs) or artificial enhancement of the HPLC response. Further work is therefore recommended to identify the potential cause of these differences. Comparative results for scallops were variable, but insufficient sample numbers were available to calculate any statistical significance. Relative performance of the HPLC method was particularly poor in queen scallops, where there were known recovery and sensitivity problems.
Overall, the results presented show the refined AOAC 2005.06 HPLC method in cockles, oysters, razors and clams behaves similarly to the method applied to mussels, where it has already been implemented for use. However, with poor method performance for N-hydroxylated toxins in scallops, the HPLC method would not be safe to implement in its current form for this species and further work to improve the method performance is recommended.
See also the related report ZB1803: Refinement and in-house validation of the AOAC HPLC method (2005.06): the determination of paralytic shelfish poisoning toxins by liquid chromatography and fluorescence detection, at:
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