Lay Summary
Chemical contaminants can enter aquatic environments from natural and human sources and may accumulate in fish and crustaceans. Monitoring programmes are undertaken to assess the presence of these substances in seafood intended for human consumption and to provide data on contaminant levels in the food supply.
This report presents the findings of a survey of wild caught fish and crustaceans landed in Northern Ireland between April 2024 and March 2025. Samples from a range of commercially harvested species were analysed for selected heavy metals and per- and polyfluoroalkyl substances (PFAS).
The study contributes to ongoing surveillance of chemical contaminants in seafood and provides information on contaminant concentrations in species landed in Northern Ireland. The data generated support the assessment of compliance with food safety requirements and contribute to the evidence base used to monitor contaminant trends over time.
Details of the monitoring programme, analytical methods and study findings are presented in the main body of this report.
Executive Summary
Seventy-eight (78) samples of wild caught fish and crustaceans were collected between April 2024 and March 2025 by authorised sampling officers in Northern Ireland. The samples were collected from the main landing areas and fish processing establishments.
Forty-four (44) samples were analysed for the heavy metal contaminants mercury, lead and cadmium. Thirty-four (34) samples were tested for per- and polyfluoroalkyl substances (PFAS).
Commission Regulation (EU) 2023/915 of 25 April 2023 on maximum levels for certain contaminants in food sets the regulatory limits for these contaminants in the matrices tested.
Concentrations of mercury, lead and cadmium were less than the maximum EU regulatory limits for all samples tested.
Concentrations of PFAS were below the EU regulatory limits for these compounds for all samples tested.
Introduction
Background to study
The public analyst business unit of Eurofins Food Testing Ireland Limited was engaged by the Food Standards Agency (FSA) in Northern Ireland to assess the levels of various heavy metals and per- and polyfluoroalkyl substances (PFAS) chemical contaminants in a number of species of wild caught fish and crustaceans landed in Northern Ireland between April 2024 and March 2025.
Aims and objectives of the study
The official control surveillance programme is undertaken to comply with Article 70 of Commission Implementing Regulation (EU) 2019/627 (EU, 2019) which requires a monitoring programme to be established for wild caught fishery products to control compliance with EU legislation on contaminants. This is an ongoing annual programme.
Regulation (EC) No. 2023/915 (EU, 2023) sets down the maximum levels for certain contaminants in food, including fishery products. The data has the potential to provide support to certifying officers in their attestation of the compliance of wild caught fishery products landed in Northern Ireland with contaminants legislation when signing Export Health Certificates.
The purpose of the work was to determine concentrations of defined chemical contaminants in wild caught fishery products and to assess whether the levels were within the prescribed limits (EU, 2023), and therefore that the products were safe for placing on the market in these respects.
Materials and Methods
Samples
Seventy-eight (78) samples of wild caught fish and crustaceans were collected between April 2024 and March 2025 (Appendix A) by authorised sampling officers in Northern Ireland. Forty-four (44) samples were analysed for the contaminants mercury, lead and cadmium (heavy metals). Thirty-four (34) samples were tested for per- and polyfluoroalkyl substances (PFAS).
The type and number of samples of each species collected for analyses were determined based on the quantity of that species landed in Northern Ireland and any previous exceedances. The species sampled were:
-
Bream
-
Brown crab
-
Norway Lobster
-
Eel
-
Haddock
-
Herring
-
Mackerel
On receipt at the laboratory (Eurofins Food Testing Ireland Limited, Dublin, Ireland) each sample was assigned a unique laboratory reference number, and the sample details were logged into a database.
Sample Preparation
For fish (including bream, eel, herring and mackerel), the maximum levels of heavy metals and PFAS apply to the muscle meat of the fish unless the fish are intended to be eaten whole, in which case the maximum levels apply to the whole fish.
For crustaceans other than crabs (including Norway Lobsters), the maximum levels of heavy metals and PFAS apply to muscle meat from the appendages and the abdomen, which means that the cephalothorax of crustaceans is excluded.
In case of crabs (infraorder Brachyura), the maximum levels of heavy metals and PFAS apply to the muscle meat from appendages only.
For king scallops (Pecten maximus), a bivalve mollusc, the maximum levels of heavy metals and PFAS apply to the adductor muscle and gonad only.
The relevant tissue for each sample was separated and homogenised in a blender. The aliquots for each analysis were immediately weighed out, and the remaining material was stored in a freezer.
The samples tested for heavy metals (cadmium, mercury and lead) were analysed by Eurofins WEJ Contaminants GmbH in Hamburg, Germany, in line with the requirements of Commission Regulation (EC) No 333/2007 (EU, 2007).
The testing was done using an in-house method based on EN ISO 15763: Determination of trace elements - determination of cadmium, mercury and lead in foodstuffs by Inductively coupled plasma mass spectrometry (ICP MS) after pressure digestion. Aliquots of homogenised test sample material were digested in an acid solution using a high-pressure microwave system. The solution was diluted as required before analysis. Quantification of the four elements was by ICP MS. The method is accredited to ISO 17025 by DAkkS, the German Accreditation Service, and the laboratory is a designated Official Laboratory by the German State of Hamburg.
Per- and polyfluoroalkyl substances analysis
The samples tested for PFAS were analysed at Eurofins GfA Lab Service GmbH in Hamburg, Germany, in line with the requirements of Commission Implementing Regulation (EU) 2022/1428 (EU, 2022a).
The testing was done using an in-house method, reference GLS OC 400 2025-12, using LC-MS/MS. The method is accredited to ISO 17025 by DAkkS, the German Accreditation Service, and the laboratory is a designated Official Laboratory by the German State of Hamburg.
The following analytes were determined:
Table 1.PFAS analytes included in the analytical method and their abbreviations.
| Analyte |
Abbreviation |
| Perfluorooctane sulfonic acid |
PFOS |
| Perfluorooctanoic acid |
PFOA |
| Perfluorononanoic acid |
PFNA |
| Perfluorhexanesulfonic acid |
PFHxS |
| Perfluorobutanoic acid |
PFBA |
| Perfluoropentane acid |
PFPeA |
| Perfluorohexanoic acid |
PFHxA |
| Perfluorheptanoic acid |
PFHpA |
| Perfluorodecanoic acid |
PFDA |
| Perfluoroundecanoic acid |
PFUnDA |
| Perfluorododecanoic acid |
PFDoDA |
| Perfluorotridecanoic acid |
PFTrDA |
| Perfluorotetradecanoic acid |
PFTeDA |
| Perfluorohexadecanic acid |
PFHxDA |
| Perfluorooctadecanic acid |
PFODA |
| Perfluorobutanesulfonic acid |
PFBS |
| Perfluoropentanesulfonic acid |
PFPeS |
| Perfluoroheptane sulphonate |
PFHpS |
| Perfluorononanesulfonic acid |
PFNS |
| Perfluorodecanesulfonic acid |
PFDS |
| Perfluoroundecane sulfonic acid |
PFUnDS |
| Perfluorododecane sulfonic acid |
PFDoDS |
| Perfluorotridecane sulfonic acid |
PFTrDS |
| 9-Chlorohexadecafluoro-3-oxanonane-1-sulfonic acid |
F-53 B Major |
| 11-Chloroeicosafluoro-3-oxaundecane-1-sulfonic acid |
F-53 B Minor |
| Hexafluoropropylene oxide dimer acid |
HFPO-DA (GenX) |
| Ammonium 4,8-dioxa-3H-perfluorononanoate |
ADONA |
| Perfluoro-3,7-dimethyloctane acid |
PF-3,7-DMOA |
| 1H,1H,2H,2H-Perfluorohexanesulfonic acid |
4:2 FTS |
| 6:2 Fluorotelomer sulfonic acid |
6:2 FTS (H4PFOS) |
| 8:2 Fluorotelomer sulfonic acid |
8:2 FTS |
| 10:2 Fluorotelomer sulfonic acid |
10:2 FTS |
Results
The concentrations of the contaminants measured in all seventy-eight samples were determined and compared to limits prescribed in Commission Regulation (EU) 2023/915 (EU, 2023).
Certificates of Analysis made under the provisions of the Food Safety (Sampling and Qualifications) Regulations (NI) 2013 were issued to the appropriate sampling officers and the Food Standards Agency. Results were also uploaded electronically to the UKFSS food database operated by the Food Standards Agency.
Concentrations of mercury, cadmium and lead were below the regulatory limits for these compounds. Details are provided in Table 3 in Appendix B.
Per- and polyfluoroalkyl substances analysis
Limits for certain PFAS are prescribed in Commission Regulation (EU) 2023/915 (EU, 2023):
-
Perfluorooctane sulfonic acid (PFOS)
-
Perfluorooctanoic acid (PFOA)
-
Perfluorononanoic acid (PFNA)
-
Perfluorhexanesulfonic acid (PFHxS)
-
Sum of PFOS, PFOA, PFNA and PFHxS
Concentrations of these PFAS were below the regulatory limits for these compounds. Details are provided in Table 4 in Appendix B.
Discussion
This official control surveillance programme examined the presence of selected heavy metals and per- and polyfluoroalkyl substances (PFAS) in fish and crustacean samples and assessed their compliance with the requirements of Commission Regulation (EU) 2023/915.
The results indicate that all seventy-eight samples analysed complied with the applicable maximum levels for mercury, cadmium, lead and regulated PFAS established under Commission Regulation (EU) 2023/915.
Mercury, cadmium and lead were not detected at concentrations exceeding the maximum levels prescribed in Commission Regulation (EU) 2023/915.
Per- and polyfluoroalkyl Substances (PFAS)
The concentrations of PFOS, PFOA, PFNA and PFHxS, as well as the sum of these compounds, were below the relevant regulatory limits in all samples analysed.
In addition, Commission Recommendation (EU) 2022/1431 on the monitoring of perfluoroalkyl substances in food requests EU Member States to test for the presence of compounds which are similar to PFOS, PFOA, PFNA and PFHxS, in order to support a dietary exposure assessment and assess the need to regulate these substances in specific commodities (EU, 2022b).
The concentrations of these additional PFAS are detailed in Table 5 in Appendix B.
Acknowledgements
Eurofins Food Testing Ireland Limited.
Mid Ulster District Council
Newry, Mourne & Down District Council
Appendices
Appendix A: Sample details
Table 2.Details of wild caught fish and crustacean samples collected between April 2024 and March 2025.
| Sample Number |
Full Product Text Description |
Landing Date |
Sampling Area/Point |
| FSAWF120 |
Norway Lobster |
03/07/2024 |
East Coast (NI) |
| FSAWF121 |
Norway Lobster |
03/07/2024 |
East Coast (NI) |
| FSAWF122 |
Norway Lobster |
03/07/2024 |
East Coast (NI) |
| FSAWF123 |
Norway Lobster |
03/07/2024 |
East Coast (NI) |
| FSAWF124 |
Norway Lobster |
03/07/2024 |
East Coast (NI) |
| FSAWF125 |
Norway Lobster |
03/07/2024 |
East Coast (NI) |
| FSAWF126 |
Norway Lobster |
15/06/2024 |
East Coast (NI) |
| FSAWF127 |
Norway Lobster |
01/06/2024 |
East Coast (NI) |
| FSAWF128 |
Norway Lobster |
05/06/2024 |
East Coast (NI) |
| FSAWF129 |
Norway Lobster |
14/05/2024 |
East Coast (NI) |
| FSAWF130 |
Herring |
11/08/2024 |
East Coast (NI) |
| FSAWF131 |
Herring |
11/08/2024 |
East Coast (NI) |
| FSAWF132 |
Herring |
13/08/2024 |
East Coast (NI) |
| FSAWF133 |
Mackerel |
11/08/2024 |
East Coast (NI) |
| FSAWF134 |
Mackerel |
11/08/2024 |
East Coast (NI) |
| FSAWF135 |
Mackerel |
13/08/2024 |
East Coast (NI) |
| FSAWF136 |
Haddock |
04/08/2024 |
East Coast (NI) |
| FSAWF137 |
Herring |
20/08/2024 |
East Coast (NI) |
| FSAWF138 |
Herring |
26/08/2024 |
East Coast (NI) |
| FSAWF139 |
Herring |
28/08/2024 |
East Coast (NI) |
| FSAWF140 |
Mackerel |
22/08/2024 |
East Coast (NI) |
| FSAWF141 |
Mackerel |
22/08/2024 |
East Coast (NI) |
| FSAWF142 |
Mackerel |
28/08/2024 |
East Coast (NI) |
| FSAWF143 |
Herring |
29/08/2024 |
East Coast (NI) |
| FSAWF144 |
Herring |
23/08/2024 |
East Coast (NI) |
| FSAWF145 |
Brown Crab |
11/11/2024 |
East Coast (NI) |
| FSAWF146 |
Brown Crab |
18/11/2024 |
East Coast (NI) |
| FSAWF147 |
Brown Crab |
19/11/2024 |
East Coast (NI) |
| FSAWF148 |
Brown Crab |
19/11/2024 |
East Coast (NI) |
| FSAWF149 |
Brown Crab |
15/11/2024 |
East Coast (NI) |
| FSAWF150 |
Brown Crab |
17/11/2024 |
East Coast (NI) |
| FSAWF151 |
Brown Crab |
15/11/2024 |
East Coast (NI) |
| FSAWF152 |
Brown Crab |
20/11/2024 |
East Coast (NI) |
| FSAWF153 |
Brown Crab |
18/11/2024 |
East Coast (NI) |
| FSAWF154 |
Brown Crab |
14/11/2024 |
East Coast (NI) |
| FSAWF155 |
Brown Crab |
24/11/2024 |
East Coast (NI) |
| FSAWF156 |
Brown Crab |
24/11/2024 |
East Coast (NI) |
| FSAWF157 |
Herring |
02/11/2024 |
East Coast (NI) |
| FSAWF158 |
Herring |
08/11/2024 |
East Coast (NI) |
| FSAWF159 |
Herring |
09/11/2024 |
East Coast (NI) |
| FSAWF160 |
Herring |
14/11/2024 |
East Coast (NI) |
| FSAWF161 |
Herring |
16/11/2024 |
East Coast (NI) |
| FSAWF162 |
Mackerel |
16/11/2024 |
East Coast (NI) |
| FSAWF163 |
Mackerel |
14/11/2024 |
East Coast (NI) |
| FSAWF164 |
Mackerel |
08/11/2024 |
East Coast (NI) |
| FSAWF165 |
Mackerel |
02/11/2024 |
East Coast (NI) |
| FSAWF166 |
Mackerel |
13/10/2024 |
East Coast (NI) |
| FSAWF167 |
Mackerel |
31/10/2024 |
East Coast (NI) |
| FSAWF168 |
Norway Lobster |
28/01/2025 |
East Coast (NI) |
| FSAWF169 |
Norway Lobster |
28/01/2025 |
East Coast (NI) |
| FSAWF170 |
Norway Lobster |
28/01/2025 |
East Coast (NI) |
| FSAWF171 |
Haddock |
05/01/2025 |
East Coast (NI) |
| FSAWF172 |
Haddock |
08/01/2025 |
East Coast (NI) |
| FSAWF173 |
Haddock |
10/01/2025 |
East Coast (NI) |
| FSAWF174 |
Haddock |
12/01/2025 |
East Coast (NI) |
| FSAWF175 |
Haddock |
12/01/2025 |
East Coast (NI) |
| FSAWF176 |
Haddock |
15/01/2025 |
East Coast (NI) |
| FSAWF177 |
Haddock |
19/01/2025 |
East Coast (NI) |
| FSAWF178 |
Haddock |
22/01/2025 |
East Coast (NI) |
| FSAWF179 |
Haddock |
28/01/2025 |
East Coast (NI) |
| 811CN/A/2619 |
Eel |
25/09/2024 |
Lough Neagh |
| 811CN/A/2620 |
Eel |
25/09/2024 |
Lough Neagh |
| 811CN/A/2621 |
Eel |
25/09/2024 |
Lough Neagh |
| 811CN/A/2622 |
Bream |
25/09/2024 |
Lough Neagh |
| 811CN/A/2623 |
Bream |
25/09/2024 |
Lough Neagh |
| 811CN/A/2624 |
Bream |
25/09/2024 |
Lough Neagh |
| 811CN/A/2647 |
Bream |
23/10/2024 |
Lough Neagh |
| 811CN/A/2648 |
Bream |
23/10/2024 |
Lough Neagh |
| 811CN/A/2649 |
Eel |
23/10/2024 |
Lough Neagh |
| 811CN/A/2650 |
Eel |
23/10/2024 |
Lough Neagh |
| 811CN/A/2651 |
Bream |
13/11/2024 |
Lough Neagh |
| 811CN/A/2652 |
Eel |
13/11/2024 |
Lough Neagh |
| 811CN/A/2653 |
Eel |
13/11/2024 |
Lough Neagh |
| 811CN/A/2659 |
Bream |
04/12/2024 |
Lough Neagh |
| 811CN/A/2672 |
Bream |
11/12/2024 |
Lough Neagh |
| 811CN/A/2673 |
Bream |
11/12/2024 |
Lough Neagh |
| 811CN/A/2674 |
Eel |
11/12/2024 |
Lough Neagh |
| 811CN/A/2675 |
Eel |
11/12/2024 |
Lough Neagh |
Appendix B: Tables
Table 3.Mercury, cadmium and lead concentrations in wild caught fish and crustaceans.
(Concentrations are not corrected for recovery.)
Bream
| Sample Number |
Species |
Mercury (mg/kg) |
Cadmium (mg/kg) |
Lead
(mg/kg) |
| 811CN/A/2622 |
Bream |
0.024 |
0.007 |
<0.02 |
| 811CN/A/2623 |
Bream |
0.026 |
<0.005 |
<0.02 |
| 811CN/A/2647 |
Bream |
0.058 |
0.017 |
<0.02 |
| 811CN/A/2651 |
Bream |
0.084 |
<0.005 |
<0.02 |
| 811CN/A/2672 |
Bream |
0.049 |
<0.005 |
0.04 |
| Maximum levels set out in Commission Regulation (EU) 2023/915 |
0.50 |
0.050 |
0.30 |
Brown Crab
| Sample Number |
Species |
Mercury (mg/kg) |
Cadmium (mg/kg) |
Lead
(mg/kg) |
| FSAWF145 |
Brown Crab |
0.070 |
<0.005 |
<0.02 |
| FSAWF146 |
Brown Crab |
0.039 |
<0.005 |
<0.02 |
| FSAWF148 |
Brown Crab |
0.081 |
<0.005 |
<0.02 |
| FSAWF150 |
Brown Crab |
0.043 |
<0.005 |
<0.02 |
| FSAWF152 |
Brown Crab |
0.057 |
<0.005 |
<0.02 |
| FSAWF154 |
Brown Crab |
0.10 |
<0.005 |
<0.02 |
| FSAWF156 |
Brown Crab |
0.044 |
<0.005 |
<0.02 |
| Maximum levels set out in Commission Regulation (EU) 2023/915 |
0.50 |
0.50 |
0.50 |
Norway Lobster
| Sample Number |
Species |
Mercury (mg/kg) |
Cadmium (mg/kg) |
Lead
(mg/kg) |
| FSAWF120 |
Norway Lobster |
0.16 |
0.006 |
<0.02 |
| FSAWF121 |
Norway Lobster |
0.16 |
0.007 |
0.02 |
| FSAWF122 |
Norway Lobster |
0.18 |
0.007 |
0.04 |
| FSAWF124 |
Norway Lobster |
0.59* |
0.011 |
0.05 |
| FSAWF125 |
Norway Lobster |
0.20 |
0.009 |
0.08 |
| FSAWF128 |
Norway Lobster |
0.088 |
<0.005 |
0.02 |
| FSAWF129 |
Norway Lobster |
0.38 |
0.014 |
0.02 |
Maximum levels set out in Commission Regulation
(EU) 2023/915 |
0.50 |
0.50 |
0.50 |
* The reported concentration exceeded the maximum level of 0.50 mg/kg; however, when measurement uncertainty was taken into account, the result was considered compliant with Commission Regulation (EU) 2023/915.
Eel
| Sample Number |
Species |
Mercury (mg/kg) |
Cadmium (mg/kg) |
Lead
(mg/kg) |
| 811CN/A/2619 |
Eel |
0.041 |
<0.005 |
<0.02 |
| 811CN/A/2621 |
Eel |
0.042 |
0.008 |
<0.02 |
| 811CN/A/2650 |
Eel |
0.067 |
0.006 |
<0.02 |
| 811CN/A/2653 |
Eel |
0.11 |
<0.005 |
<0.02 |
| 811CN/A/2674 |
Eel |
0.25 |
<0.005 |
<0.02 |
Maximum levels set out in Commission Regulation
(EU) 2023/915 |
0.50 |
0.050 |
0.30 |
Haddock
| Sample Number |
Species |
Mercury (mg/kg) |
Cadmium (mg/kg) |
Lead
(mg/kg) |
| FSAWF136 |
Haddock |
0.14 |
<0.005 |
<0.02 |
| FSAWF171 |
Haddock |
0.055 |
<0.005 |
<0.02 |
| FSAWF173 |
Haddock |
0.12 |
<0.005 |
<0.02 |
| FSAWF175 |
Haddock |
0.11 |
<0.005 |
<0.02 |
| FSAWF177 |
Haddock |
0.11 |
<0.005 |
<0.02 |
| FSAWF179 |
Haddock |
0.12 |
<0.005 |
<0.02 |
Maximum levels set out in Commission Regulation
(EU) 2023/915 |
0.50 |
0.050 |
0.30 |
Herring
| Sample Number |
Species |
Mercury (mg/kg) |
Cadmium (mg/kg) |
Lead
(mg/kg) |
| FSAWF130 |
Herring |
0.040 |
<0.005 |
<0.02 |
| FSAWF131 |
Herring |
0.041 |
<0.005 |
<0.02 |
| FSAWF132 |
Herring |
0.032 |
<0.005 |
<0.02 |
| FSAWF138 |
Herring |
0.032 |
<0.005 |
<0.02 |
| FSAWF143 |
Herring |
0.030 |
<0.005 |
<0.02 |
| FSAWF158 |
Herring |
0.057 |
<0.005 |
<0.02 |
| FSAWF160 |
Herring |
0.053 |
<0.005 |
<0.02 |
Maximum levels set out in Commission Regulation
(EU) 2023/915 |
0.30 |
0.050 |
0.30 |
Mackerel
| Sample Number |
Species |
Mercury (mg/kg) |
Cadmium (mg/kg) |
Lead
(mg/kg) |
| FSAWF133 |
Mackerel |
0.042 |
<0.005 |
<0.02 |
| FSAWF134 |
Mackerel |
0.086 |
<0.005 |
<0.02 |
| FSAWF135 |
Mackerel |
0.061 |
<0.005 |
<0.02 |
| FSAWF142 |
Mackerel |
0.040 |
<0.005 |
<0.02 |
| FSAWF163 |
Mackerel |
0.033 |
0.024 |
<0.02 |
| FSAWF165 |
Mackerel |
0.027 |
0.026 |
<0.02 |
| FSAWF167 |
Mackerel |
0.024 |
0.021 |
<0.02 |
Maximum levels set out in Commission Regulation
(EU) 2023/915 |
0.30 |
0.10 |
0.30 |
Table 4.PFAS results for wild caught fish and crustaceans, where limits are prescribed in Commission Regulation (EU) 2023/915 (EU, 2023).
(Concentrations are not corrected for recovery.)
Bream
| Sample Number |
Species |
PFOS
µg/kg |
PFOA
µg/kg |
PFNA
µg/kg |
PFHxS
µg/kg |
PFAS(4) Total
µg/kg |
| 811CN/A/2624 |
Bream |
0.64 |
< 0.100 |
< 0.100 |
< 0.100 |
0.64 |
| 811CN/A/2648 |
Bream |
1.3 |
< 0.100 |
0.14 |
< 0.100 |
1.44 |
| 811CN/A/2659 |
Bream |
1.24 |
< 0.100 |
< 0.100 |
< 0.100 |
1.24 |
| 811CN/A/2673 |
Bream |
0.94 |
< 0.100 |
< 0.100 |
< 0.100 |
0.94 |
| Maximum levels set out in Commission Regulation (EU) 2023/915 |
35 |
8.0 |
8.0 |
1.5 |
45 |
Brown Crab
| Sample Number |
Species |
PFOS
µg/kg |
PFOA
µg/kg |
PFNA
µg/kg |
PFHxS
µg/kg |
PFAS(4) Total
µg/kg |
| FSAWF147 |
Brown Crab |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
None detected |
| FSAWF149 |
Brown Crab |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
None detected |
| FSAWF151 |
Brown Crab |
0.17 |
0.66 |
0.14 |
< 0.100 |
0.97 |
| FSAWF153 |
Brown Crab |
0.18 |
0.41 |
< 0.100 |
< 0.100 |
0.59 |
| Maximum levels set out in Commission Regulation (EU) 2023/915 |
3.0 |
0.70 |
1.0 |
1.5 |
5.0 |
Norway Lobster
| Sample Number |
Species |
PFOS
µg/kg |
PFOA
µg/kg |
PFNA
µg/kg |
PFHxS
µg/kg |
PFAS(4) Total
µg/kg |
| FSAWF123 |
Norway Lobster |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
None detected |
| FSAWF126 |
Norway Lobster |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
None detected |
| FSAWF127 |
Norway Lobster |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
None detected |
| FSAWF170 |
Norway Lobster |
< 0.100 |
0.18 |
< 0.100 |
< 0.100 |
0.18 |
| FSAWF168 |
Norway Lobster |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
None detected |
| FSAWF169 |
Norway Lobster |
< 0.100 |
0.12 |
< 0.100 |
< 0.100 |
0.12 |
| Maximum levels set out in Commission Regulation (EU) 2023/915 |
3.0 |
0.70 |
1.0 |
1.5 |
5.0 |
Eel
| Sample Number |
Species |
PFOS
µg/kg |
PFOA
µg/kg |
PFNA
µg/kg |
PFHxS
µg/kg |
PFAS(4) Total
µg/kg |
| 811CN/A/2620 |
Eel |
1.6 |
0.10 |
< 0.100 |
< 0.100 |
1.7 |
| 811CN/A/2649 |
Eel |
0.57 |
< 0.100 |
< 0.100 |
< 0.100 |
0.57 |
| 811CN/A/2652 |
Eel |
1.1 |
0.17 |
0.14 |
< 0.100 |
0.41 |
| 811CN/A/2675 |
Eel |
0.86 |
< 0.100 |
< 0.100 |
< 0.100 |
0.86 |
| Maximum levels set out in Commission Regulation (EU) 2023/915 |
35 |
8.0 |
8.0 |
1.5 |
45 |
Haddock
| Sample Number |
Species |
PFOS
µg/kg |
PFOA
µg/kg |
PFNA
µg/kg |
PFHxS
µg/kg |
PFAS(4) Total
µg/kg |
| FSAWF172 |
Haddock |
0.56 |
< 0.100 |
0.16 |
< 0.100 |
0.72 |
| FSAWF174 |
Haddock |
0.42 |
< 0.100 |
0.12 |
< 0.100 |
0.54 |
| FSAWF176 |
Haddock |
0.50 |
< 0.100 |
0.13 |
< 0.100 |
0.63 |
| FSAWF178 |
Haddock |
0.34 |
< 0.100 |
0.11 |
< 0.100 |
0.45 |
| Maximum levels set out in Commission Regulation (EU) 2023/915 |
2.0 |
0.20 |
0.50 |
0.20 |
2.0 |
Herring
| Sample Number |
Species |
PFOS
µg/kg |
PFOA
µg/kg |
PFNA
µg/kg |
PFHxS
µg/kg |
PFAS(4) Total
µg/kg |
| FSAWF137 |
Herring |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
None detected |
| FSAWF139 |
Herring |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
None detected |
| FSAWF144 |
Herring |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
None detected |
| FSAWF157 |
Herring |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
None detected |
| FSAWF159 |
Herring |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
None detected |
| FSAWF161 |
Herring |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
None detected |
| Maximum levels set out in Commission Regulation (EU) 2023/915 |
2.0 |
0.20 |
0.50 |
0.20 |
2.0 |
Mackerel
| Sample Number |
Species |
PFOS
µg/kg |
PFOA
µg/kg |
PFNA
µg/kg |
PFHxS
µg/kg |
PFAS(4) Total
µg/kg |
| FSAWF140 |
Mackerel |
0.91 |
< 0.100 |
< 0.100 |
< 0.100 |
0.91 |
| FSAWF141 |
Mackerel |
0.95 |
< 0.100 |
< 0.100 |
< 0.100 |
0.95 |
| FSAWF162 |
Mackerel |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
None detected |
| FSAWF164 |
Mackerel |
0.23 |
< 0.100 |
< 0.100 |
< 0.100 |
0.23 |
| FSAWF166 |
Mackerel |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
None detected |
| Maximum levels set out in Commission Regulation (EU) 2023/915 |
2.0 |
0.20 |
0.50 |
0.20 |
2.0 |
Table 5.PFAS results for wild caught fish and crustaceans, where no limits are prescribed in Commission Regulation (EU) 2023/915 (EU, 2023).
Bream
| Sample Number |
Species |
PFDA µg/kg |
PFUnDA µg/kg |
PFDoDA µg/kg |
PFTrDA µg/kg |
PFBS µg/kg |
PFBA µg/kg |
PFPeA µg/kg |
PFHxA µg/kg |
PFHpA µg/kg |
PFTeDA µg/kg |
PFHxDA µg/kg |
| 811CN/A/2624 |
Bream |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
| 811CN/A/2648 |
Bream |
0.251 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
| 811CN/A/2659 |
Bream |
0.195 |
0.174 |
< 0.100 |
< 0.300 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
| 811CN/A/2673 |
Bream |
0.14 |
0.14 |
< 0.100 |
< 0.300 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
| Sample Number |
PFODA µg/kg |
PFPeS µg/kg |
PFHpS µg/kg |
PFNS µg/kg |
PFDS µg/kg |
PFUnDS µg/kg |
PFDoDS µg/kg |
PFTrDS µg/kg |
F-53 B Major µg/kg |
F-53 B Minor µg/kg |
HFPO-DA µg/kg |
ADONA µg/kg |
| 811CN/A/2624 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.500 |
< 0.100 |
| 811CN/A/2648 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.500 |
< 0.100 |
| 811CN/A/2659 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.500 |
< 0.100 |
| 811CN/A/2673 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.500 |
< 0.100 |
| Sample Number |
PF-3,7-DMOA µg/kg |
4:2 FTS µg/kg |
6:2FTS µg/kg |
8:2 FTS µg/kg |
10:2 FTS µg/kg |
PFAS (32) Total µg/kg |
| 811CN/A/2624 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.500 |
0.64 |
| 811CN/A/2648 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.500 |
1.69 |
| 811CN/A/2659 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.500 |
1.6 |
| 811CN/A/2673 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.500 |
1.2 |
Brown Crab
| Sample Number |
Species |
PFDA µg/kg |
PFUnDA µg/kg |
PFDoDA µg/kg |
PFTrDA µg/kg |
PFBS µg/kg |
PFBA µg/kg |
PFPeA µg/kg |
PFHxA µg/kg |
PFHpA µg/kg |
PFTeDA µg/kg |
PFHxDA µg/kg |
| FSAWF147 |
Brown Crab |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
| FSAWF149 |
Brown Crab |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
| FSAWF151 |
Brown Crab |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
| FSAWF153 |
Brown Crab |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
| Sample Number |
PFODA µg/kg |
PFPeS µg/kg |
PFHpS µg/kg |
PFNS µg/kg |
PFDS µg/kg |
PFUnDS µg/kg |
PFDoDS µg/kg |
PFTrDS µg/kg |
F-53 B Major µg/kg |
F-53 B Minor µg/kg |
HFPO-DA µg/kg |
ADONA µg/kg |
| FSAWF147 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.500 |
< 0.100 |
| FSAWF149 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.500 |
< 0.100 |
| FSAWF151 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.500 |
< 0.100 |
| FSAWF153 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.500 |
< 0.100 |
| Sample Number |
PF-3,7-DMOA µg/kg |
4:2 FTS µg/kg |
6:2FTS µg/kg |
8:2 FTS µg/kg |
10:2 FTS µg/kg |
PFAS (32) Total µg/kg |
| FSAWF147 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.500 |
None detected |
| FSAWF149 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.500 |
None detected |
| FSAWF151 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.500 |
0.97 |
| FSAWF153 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.500 |
0.59 |
Norway Lobster
| Sample Number |
Species |
PFDA µg/kg |
PFUnDA µg/kg |
PFDoDA µg/kg |
PFTrDA µg/kg |
PFBS µg/kg |
PFBA µg/kg |
PFPeA µg/kg |
PFHxA µg/kg |
PFHpA µg/kg |
PFTeDA µg/kg |
PFHxDA µg/kg |
| FSAWF123 |
Norway Lobster |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
| FSAWF126 |
Norway Lobster |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
| FSAWF127 |
Norway Lobster |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
| FSAWF170 |
Norway Lobster |
< 0.100 |
0.20 |
0.16 |
0.44 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
| FSAWF168 |
Norway Lobster |
< 0.100 |
0.16 |
0.14 |
0.40 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
| FSAWF169 |
Norway Lobster |
< 0.100 |
0.22 |
0.20 |
0.58 |
< 0.100 |
< 0.300 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
| Sample Number |
PFODA µg/kg |
PFPeS µg/kg |
PFHpS µg/kg |
PFNS µg/kg |
PFDS µg/kg |
PFUnDS µg/kg |
PFDoDS µg/kg |
PFTrDS µg/kg |
F-53 B Major µg/kg |
F-53 B Minor µg/kg |
HFPO-DA µg/kg |
ADONA µg/kg |
| FSAWF123 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.500 |
< 0.100 |
| FSAWF126 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.500 |
< 0.100 |
| FSAWF127 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.500 |
< 0.100 |
| FSAWF170 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.500 |
< 0.100 |
| FSAWF168 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.500 |
< 0.100 |
| FSAWF169 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.500 |
< 0.100 |
| Sample Number |
PF-3,7-DMOA µg/kg |
4:2 FTS µg/kg |
6:2FTS µg/kg |
8:2 FTS µg/kg |
10:2 FTS µg/kg |
PFAS (32) Total µg/kg |
| FSAWF123 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.500 |
None detected |
| FSAWF126 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.500 |
None detected |
| FSAWF127 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.500 |
None detected |
| FSAWF170 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.500 |
0.98 |
| FSAWF168 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.500 |
0.7 |
| FSAWF169 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.500 |
1.1 |
Eel
| Sample Number |
Species |
PFDA µg/kg |
PFUnDA µg/kg |
PFDoDA µg/kg |
PFTrDA µg/kg |
PFBS µg/kg |
PFBA µg/kg |
PFPeA µg/kg |
PFHxA µg/kg |
PFHpA µg/kg |
PFTeDA µg/kg |
PFHxDA µg/kg |
| 811CN/A/2620 |
Eel |
0.17 |
0.29 |
0.11 |
< 0.300 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
| 811CN/A/2649 |
Eel |
0.12 |
0.16 |
0.18 |
< 0.300 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
| 811CN/A/2652 |
Eel |
0.18 |
0.17 |
< 0.100 |
< 0.300 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
| 811CN/A/2675 |
Eel |
0.10 |
0.12 |
< 0.100 |
< 0.300 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
| Sample Number |
PFODA µg/kg |
PFPeS µg/kg |
PFHpS µg/kg |
PFNS µg/kg |
PFDS µg/kg |
PFUnDS µg/kg |
PFDoDS µg/kg |
PFTrDS µg/kg |
F-53 B Major µg/kg |
F-53 B Minor µg/kg |
HFPO-DA µg/kg |
ADONA µg/kg |
| 811CN/A/2620 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.500 |
< 0.100 |
| 811CN/A/2649 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.500 |
< 0.100 |
| 811CN/A/2652 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.500 |
< 0.100 |
| 811CN/A/2675 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.500 |
< 0.100 |
| Sample Number |
PF-3,7-DMOA µg/kg |
4:2 FTS µg/kg |
6:2FTS µg/kg |
8:2 FTS µg/kg |
10:2 FTS µg/kg |
PFAS (32) Total µg/kg |
| 811CN/A/2620 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.500 |
2.3 |
| 811CN/A/2649 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.500 |
1.0 |
| 811CN/A/2652 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.500 |
0.79 |
| 811CN/A/2675 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.500 |
1.1 |
Haddock
| Sample Number |
Species |
PFDA µg/kg |
PFUnDA µg/kg |
PFDoDA µg/kg |
PFTrDA µg/kg |
PFBS µg/kg |
PFBA µg/kg |
PFPeA µg/kg |
PFHxA µg/kg |
PFHpA µg/kg |
PFTeDA µg/kg |
PFHxDA µg/kg |
| FSAWF172 |
Haddock |
0.11 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
| FSAWF174 |
Haddock |
0.10 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
| FSAWF176 |
Haddock |
0.11 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
| FSAWF178 |
Haddock |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
| Sample Number |
PFODA µg/kg |
PFPeS µg/kg |
PFHpS µg/kg |
PFNS µg/kg |
PFDS µg/kg |
PFUnDS µg/kg |
PFDoDS µg/kg |
PFTrDS µg/kg |
F-53 B Major µg/kg |
F-53 B Minor µg/kg |
HFPO-DA µg/kg |
ADONA µg/kg |
| FSAWF172 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.500 |
< 0.100 |
| FSAWF174 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.500 |
< 0.100 |
| FSAWF176 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.500 |
< 0.100 |
| FSAWF178 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.500 |
< 0.100 |
| Sample Number |
PF-3,7-DMOA µg/kg |
4:2 FTS µg/kg |
6:2FTS µg/kg |
8:2 FTS µg/kg |
10:2 FTS µg/kg |
PFAS (32) Total µg/kg |
| FSAWF172 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.500 |
0.83 |
| FSAWF174 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.500 |
0.64 |
| FSAWF176 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.500 |
0.64 |
| FSAWF178 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.500 |
0.45 |
Herring
| Sample Number |
Species |
PFDA µg/kg |
PFUnDA µg/kg |
PFDoDA µg/kg |
PFTrDA µg/kg |
PFBS µg/kg |
PFBA µg/kg |
PFPeA µg/kg |
PFHxA µg/kg |
PFHpA µg/kg |
PFTeDA µg/kg |
PFHxDA µg/kg |
| FSAWF137 |
Herring |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
| FSAWF139 |
Herring |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
| FSAWF144 |
Herring |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
| FSAWF157 |
Herring |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
| FSAWF159 |
Herring |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
| FSAWF161 |
Herring |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
| Sample Number |
PFODA µg/kg |
PFPeS µg/kg |
PFHpS µg/kg |
PFNS µg/kg |
PFDS µg/kg |
PFUnDS µg/kg |
PFDoDS µg/kg |
PFTrDS µg/kg |
F-53 B Major µg/kg |
F-53 B Minor µg/kg |
HFPO-DA µg/kg |
ADONA µg/kg |
| FSAWF137 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.500 |
< 0.100 |
| FSAWF139 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.500 |
< 0.100 |
| FSAWF144 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.500 |
< 0.100 |
| FSAWF157 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.500 |
< 0.100 |
| FSAWF159 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.500 |
< 0.100 |
| FSAWF161 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.500 |
< 0.100 |
| Sample Number |
PF-3,7-DMOA µg/kg |
4:2 FTS µg/kg |
6:2FTS µg/kg |
8:2 FTS µg/kg |
10:2 FTS µg/kg |
PFAS (32) Total µg/kg |
| FSAWF137 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.500 |
None detected |
| FSAWF139 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.500 |
None detected |
| FSAWF144 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.500 |
None detected |
| FSAWF157 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.500 |
None detected |
| FSAWF159 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.500 |
None detected |
| FSAWF161 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.500 |
None detected |
Mackerel
| Sample Number |
Species |
PFDA µg/kg |
PFUnDA µg/kg |
PFDoDA µg/kg |
PFTrDA µg/kg |
PFBS µg/kg |
PFBA µg/kg |
PFPeA µg/kg |
PFHxA µg/kg |
PFHpA µg/kg |
PFTeDA µg/kg |
PFHxDA µg/kg |
| FSAWF140 |
Mackerel |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
| FSAWF141 |
Mackerel |
< 0.100 |
0.10 |
< 0.100 |
< 0.300 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
| FSAWF162 |
Mackerel |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
| FSAWF164 |
Mackerel |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
| FSAWF166 |
Mackerel |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.100 |
| Sample Number |
PFODA µg/kg |
PFPeS µg/kg |
PFHpS µg/kg |
PFNS µg/kg |
PFDS µg/kg |
PFUnDS µg/kg |
PFDoDS µg/kg |
PFTrDS µg/kg |
F-53 B Major µg/kg |
F-53 B Minor µg/kg |
HFPO-DA µg/kg |
ADONA µg/kg |
| FSAWF140 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.500 |
< 0.100 |
| FSAWF141 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.500 |
< 0.100 |
| FSAWF162 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.500 |
< 0.100 |
| FSAWF164 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.500 |
< 0.100 |
| FSAWF166 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.100 |
< 0.500 |
< 0.100 |
| Sample Number |
PF-3,7-DMOA µg/kg |
4:2 FTS µg/kg |
6:2FTS µg/kg |
8:2 FTS µg/kg |
10:2 FTS µg/kg |
PFAS (32) Total µg/kg |
| FSAWF140 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.500 |
0.91 |
| FSAWF141 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.500 |
1.05 |
| FSAWF162 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.500 |
None detected |
| FSAWF164 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.500 |
0.23 |
| FSAWF166 |
< 0.100 |
< 0.100 |
< 0.300 |
< 0.300 |
< 0.500 |
None detected |