ALS NATA Accreditation now extends to PFAS in Biota
The Guidance Statement issued by EnHealth (April 2017) considered ingestion of food contaminated with PFAS to be the major exposure pathway for human health, with risk-based guidance values for Total Daily Intake (TDI) provided for PFOS/PFHxS (20ng/kgbw/day) and PFOA (160ng/kgbw/day). These values have also been adopted in EPA’s recently issued interim statement on PFAS (October 2017).
ALS has recently completed a comprehensive validation on a diverse range of plant and animal matrices for which NATA accreditation has been granted. ALS NATA accreditation covers all Perfluoroalkyl Sulfonic Acids, Perfluoroalkyl Carboxylic Acids and (n:2) Fluorotelomer Sulfonic Acids as listed in the Table 1 (with the exception of Perfluorobutanoic Acid in fish for which accreditation is pending). Accreditation covers the range of biota types, including aquatic species, plants & grasses, and fruits & vegetables. Non-accredited analytes and matrices are still covered by this method and will be flagged as such on the analytical report.
UNIQUE ANALYTICAL CHALLENGES FOR BIOTA SAMPLES
Biota is a broad term, encompassing a diverse range of matrix types. Biota matrices present unique challenges for analysis in that co-extracted components such as proteins, lipids (fats) and pigments have the potential to interfere with detector response (i.e. through enhancement or suppression effects, and through isobaric interferences). A mechanism of clean-up is required to remove or deplete the interfering components. ALS method validation comprised a comprehensive range of biota matrices to ensure method robustness across the biota spectrum, including aquatic species, plants & grasses, and fruits & vegetables.
For the analytical subsample to be representative of the sample submitted, the sample must be well homogenised. Biota samples can include a combination of both soft parts (e.g. flesh, guts, leaves, etc.) and very hard parts (e.g. shells, bone, branches, etc.) presenting particular challenges for sample homogenisation. ALS has developed comprehensive sample homogenisation procedures including specific apparatus aimed at ensuring that the subsample taken for analysis best represents the sample as submitted.
The decision to test the entire plant/animal sample or only a particular component would be dependent on the site conceptual model and the identified exposure pathways to be investigated. For human exposure, only the edible portion of the sample may be of interest. In the case of crustaceans such as crabs for example, only the meat inside the shell may be of relevance as opposed to the entire crab, including shell. Ideally, only that component of the sample required for analysis should be submitted to the laboratory for analysis. If subsampling a particular component of the submitted sample is required to be performed by the laboratory, this information needs to be clearly communicated to the laboratory prior to sample submission. Note, additional preparation charges may apply depending on the complexity of the procedure required for subsampling. Unless otherwise requested, ALS will process the whole sample as submitted.
Particular attention needs to be paid to field sampling practices in general when sampling for PFAS, but in particular for biota to avoid the potential for sample cross contamination. The WA Department of Environment Regulation’s interim guideline on assessment and management of PFAS provides specific details in terms of field sampling protocols for PFAS, of note is the requirement to change gloves between samples. Glass containers and containers with Teflon components should be avoided. Samples can be submitted to the laboratory in zip-lock bags (double bagging recommended) or in HPDE plastic containers (both of which can be supplied by ALS).
^ Analytes for which NATA accreditation is pending
** NATA accreditation pending for PFBA in Fish