Sammendrag
This report summarises results from the ongoing monitoring programme for veterinary border control on seafood products imported to Norway from countries outside the EU and the European Economic Area in 2021.
Samples were collected by personnel at the Norwegian Border Inspection Posts (BIP). The Institute of Marine Research (IMR) carried out the analytical work on behalf of the Norwegian Food Safety Authority (NFSA). We want to thank NFSA for good cooperation during the conduct of this monitoring programme. A risk assessment for different groups of imported products formed the basis for the selection of analytical activities, where current trend of hazards, as reported in The Rapid Alert System for Food and Feed (RASFF) notification system and the compositional nature of the products and origin formed an up-to-date basis for the risk assessment.
A total of 100 seafood samples, were examined by a selection of analytical methods and assays for microorganisms and undesirable chemical substances.
Selected microbiological analyses were performed on 84 of the samples, undesirable trace elements were measured in all 100 samples and persistent organic pollutants (POPs) were measured in 30 samples. The chemical spoilage indicator histamine was examined in a selection of 20 relevant samples. All values were below the maximum permitted level, when established.
1 - Introduction
As a member of the European Economic Area (EEA), Norway is obliged to monitor the conformity of food and feed products imported to the EEA area, (Commission Regulation (EC) 2019/1871). Included in this activity is analytical examinations of seafood with respect to microorganisms or the presence of undesirable substances. The Norwegian Food Safety Authority (NFSA) is the competent authority regarding veterinary border control in Norway. On behalf of NFSA, IMR carried out the analytical examination of the seafood samples in this monitoring programme and elaborated this report.
1.1 Microbial parameters
A selection of microbiological parameters was used to evaluate the safety and quality of seafood products and whether proper hygienic measures were applied during production or transport. To evaluate possible faecal contamination, analyses for common indicator organisms were conducted, including assays for coliforms, bacteria in the Enterobacteriaceae family, Escherichia coli and enterococci. In addition, examination for coagulase positive staphylococci and sulphite reducing clostridia were conducted on a selection of samples, either heat treated or under vacuum. Furthermore, samples were analysed for specific pathogens relevant for food safety, including norovirus, hepatitis A virus, and bacteria in the genera Salmonella, Listeria and Vibrio. The EU microbiological criteria for Salmonella spp. and Listeria monocytogenes (Commission Regulation 2073/2005), implemented by Norway has through the EEA agreement, formed a basis for the evaluation.
1.2 Antibiotic resistance
Antimicrobial resistance is a prevalent challenge to the global public health. Carbapenemase-producing and extended-spectrum β-lactamase (ESBL)-producing Enterobacteriaceae are priority pathogens for which research and urgent development of new antibiotics is needed (WHO 2017). Despite findings of carbapenem resistant Enterobacteriaceae in seafood imported from Southeast Asia (Janecko, Martz et al. 2016), there are currently no regulations in place for the screening for antibiotic resistant pathogens in imported seafood. As a preliminary survey with the goal of establishing a pipeline for the detection of antibiotic resistant pathogens, farmed fish and shellfish imported from Asia and South America were selected for analyses targeting carbapenem and/or third generation cephalosporin resistant Enterobacteriaceae.
1.3 Prohibited substances
Farmed seafood products were analysed for several prohibited veterinary medicinal products. Chloramphenicol is an antibiotic agent that exhibit activity against a broad spectrum of microorganisms. Due to a rare but serious dose-independent adverse effect (aplastic anaemia), this agent is not authorized in the treatment of food-producing animals, including fish. Nitrofurans were previously widely used in veterinary medicine as an antimicrobial agent. They were banned by the European Union (EU) in 1995 due to concerns about the carcinogenicity of possible residues in the edible tissue.
1.4 Chemical spoilage indicators
The survey also included the biogenic amine histamine, following Commission Regulation (EU) No 1019/2013 of 23 October 2013 amending Annex I to Regulation (EC) No 2073/2005 as regards histamine in fishery products.
1.5 Carbon monoxide
Carbon monoxide (CO) has been illegally used on fresh fish fillet and especially tuna to retain a fresh, red appearance for a longer storage period. It reacts with the oxy-myoglobin to form a cherry red carboxy-myoglobin complex. No direct health implications from eating CO-treated fish are known. However, the practice of food cosmetics is problematic, since the customer is misled regarding the product freshness. Potentially, CO could mask spoilage, as the CO-complex can be stable beyond the fish-fillet shelf life. As no official maximum level is provided, a sample was judged as CO treated if the analysed level was above 200 µg/kg, as described in Marrone et al. (2015).
1.6 Undesirable trace elements
Undesirable trace elements relevant for seafood safety occur naturally in the environment, with large geographical variations. The analysed levels reflect the geological presence, as well as anthropogenic sources. These compounds may accumulate in food chains and thus find their way into seafood. Farmed seafood can be affected via contaminated feed. The elements cadmium (Cd), mercury (Hg), and lead (Pb), were measured and the compliance of the values with the EU maximum levels (as listed in 1881/2006 (EC)) was evaluated. Arsenic (As), was also included, although there is no maximum level in seafood, in contrast to the maximum limits in terrestrial foods.
1.7 Persistent organic pollutants POPs' (PCDD/F, PCB, PBDE)
Persistent organic pollutants (POP’s) form a diverse group of substances with a range of chemical and toxicological characteristics. POPs are persistent in the environment and accumulate in food chains. Some classes of POPs are considered a human health dietary risk. The compliance of selected samples with established maximum levels for food stuffs (Commission Regulation (EC) 1259/2011) was evaluated for these contaminants: dioxins, furans, dioxin-like PCBs, and the EU selected “non-dioxin like-PCBs”. In addition, flame-retardant compounds in the polybrominated diphenyl ethers family (PBDEs) were measured. However, maximum levels in food have not yet been established for the BDEs. The EU recommends a monitoring of the BDE compounds in food (EU 2014). Seafood is considered a potential contributor to BDE-99 exposure, which is the BDE compound considered most relevant to food-safety (EFSA CONTAM Panel 2011).
1.8 Polycyclic aromatic hydrocarbons (PAH)
Polycyclic aromatic hydrocarbons (PAHs) are formed from incomplete combustion of organic matter. PAHs have been found to exhibit food safety issues, and maximum levels are established for smoked fishery products. The maximum levels are set for Benzo(a)pyrene (BaP) alone, as well as for the lower bound sum of four PAH compounds (PAH4): BaP, Benzo(a) anthracene, Benzo(b)fluoranthene and chrysene.
2 - Material and Methods
Sampling was carried out by NFSA at the Norwegian Border Inspection Posts (BIPs) while analytical examinations and the writing of this report was carried out by IMR. The sampling targeted hazards associated with different imported products, and took into account import volumes, compositional nature of the products, results from previous monitoring, geographical origin of samples, and information available in the RASFF (Rapid Alert System for Food and Feed).
Fresh samples were shipped without delay to IMR whereas frozen samples were stored frozen in the BIPs until shipment in the frozen state to IMR for analysis. Upon arrival, samples were registered at the IMR sample reception unit, each sample was photographed, and relevant information registered in a Laboratory Information Management System (LIMS). Microbiological assays were done prior to all other sample handling to prevent contamination. The samples were then further prepared for analyses and split in sub-samples (aliquots) for the different assays and analytical methods.
In general, the edible part was selected for analyses according to a manual specified for each type of sample. For undesirable chemical species where a legal maximum level is established, the tissue specified in the regulation was selected. The analytical methods and procedures used were quality assured and accredited according to the ISO 17025:2005 standard, unless otherwise specified (see Annex 1, Table 2 for details).
The evaluations of the analytical data in the report were based on the EU maximum levels and recommendations (Commission Regulation (EU) No. 2006/1881, Commission Regulation (EU) No. 2073/2005, 37/2010 and 1019/2013) and EU recommendations. The maximum levels provide a legal framework for trade. For undesirables with no established maximum level, interpretation of the analytical values was based on scientific expert opinions when available.
3 - Results and Discussion
A total of 100 samples from the NFSA at Norwegian BIPs, were examined by a selection of methods for microorganisms and undesirable chemical species (see Annex 1 for details on methods) as shown in Table 1. All samples were found to be compliant with EU regulations. Samples with detected microorganism levels or undesirable chemical species above detection limits are listed in Annex 2.
Table 1: Analyses performed on samples from different seafood categories. The “other” category includes all processed food items such as roe, crabsticks, fishcakes, battered, steamed, dried and salted, and marinated and canned food items.
Samples and assays included in the Norwegian veterinary border control of seafood 2021
|
|
Fish
|
Crustaceans
|
Cephalopods
|
Bivalves
|
Feed/Flour
|
Marine Oils
|
Other
|
Total number
|
Microbiology
|
33
|
16
|
8
|
3
|
|
6
|
18
|
84
|
Antibiotic resistance
|
7
|
12
|
|
|
|
|
|
19
|
Drug residues and dyes
|
6
|
8
|
|
1
|
|
|
6
|
21
|
Chemical spoilage indicators
|
6
|
|
|
|
|
2
|
12
|
20
|
Carbon monoxide
|
3
|
|
|
|
|
|
|
3
|
Undesirable trace elements
|
36
|
15
|
7
|
3
|
|
6
|
33
|
100
|
POPs’ (PCDD/F, PCB, PBDE)
|
7
|
|
2
|
|
|
6
|
15
|
30
|
PAH
|
|
|
|
3
|
|
|
1
|
4
|
3.1 Microbial parameters
Eighty-four samples were analysed for the presence of potential human pathogenic bacteria, spoilage bacteria and moulds/yeasts. All samples were compliant regarding the regulations. Details about samples exceeding the detection limit can be found in Annex II, Table 3.
Potential human pathogenic bacteria
Of the 84 samples, 64 were examined for the presence of coliform bacteria. Four samples had levels above or at the detection limit (10 cfu/g). Further, eighty-one samples were analysed for the presence of thermotolerant coliform bacteria, and two had levels above the method detection limit (10 cfu/g). Three samples were analysed for Enterobacteriaceae and all were below the detection limit of 10 cfu/g.
For enterococci, four of 68 samples examined were found above the detection limit of 100 cfu/g.
All 84 sample were analysed for the presence of Salmonella spp. and found negative. Listeria monocytogenes was not found in any of the 55 samples analysed.
Fourteen samples were analysed for the presence of coagulase positive staphylococci, and 16 samples were analysed for the presence of sulphite reducing clostridia. None of these samples had levels above the detection limit (100 cfu/g).
Twenty-five samples were analysed for the presence of potentially human pathogenic Vibrio spp., and three samples of whiteleg shrimp and scampi, all from Vietnam were positive. The isolated strains were identified using MALDI-TOF MS, and two were found to be V. parahaemolyticus and one was identified as V. lutrae.
Three samples were examined for the presence of Norovirus type I and II, Hepatitis A by RT-PCR in accordance with ISO 15216-1:2017 (Horizontal method for determination of hepatitis A virus and norovirus in food using real-time RT-PCR -Part 1: Method for quantification). One sample of Pacific oysters imported from South Korea was positive for the presence of Norovirus type II. Three samples were examined for the presence of Escherichia coli, and both had numbers below detection limit.
Mould and yeast
The presence of mould and yeast was examined in three samples, all were below the detection limit of 100 cfu/g.
3.2 Antibiotic resistance
A total of 19 samples were analyzed for the presence of carbapenemase-producing and extended-spectrum β-lactamase (ESBL)-producing Enterobacteriaceae. Five of the 19 samples tested showed presence of the members of the family Enterobacteriaceae. All five positive samples were whiteleg shrimps. Three of the samples carried Enterobacter spp and two of the samples carried Klebsiella pneumoniae. Enterobacter spp. carry AmpC betalactamase that confers resistance to cephalosporin, hence further analysis is needed to confirm the presence of ESBLs in these isolates (Jacoby, 2009). Klebsiella pneumoniae is an emerging threat to the human health and is known for causing several nosocomial infections, ESBL producing Klebsiella pneumoniae is a clinical problem in Norway (Fostervold et al, 2022). Thus, detection of these isolates in imported seafood is of concern from seafood safety point of view.
3.3 Prohibited substances
A selection of 21 samples of fish, crustaceans, processed seafood, and bivalves were examined with respect to antimicrobial agents and/or dyes (Table 1). None of these samples contained detectable residues of malachite green, leuco-malachite green, brilliant green, crystal violet or leuco-crystal violet. Furthermore, none of the samples contained chloramphenicol or any of the nitrofuran metabolites.
3.4 Chemical spoilage indicators
Histamine is a biogenic amine produced by bacterial degradation of the amino acid histidine, if scombroid fish species are exposed to improper storage or transport conditions. 20 relevant samples were selected for analysis, and all measured values were below the maximum permitted levels.
3.5 Carbon monoxide
Three samples of Yellowfin tuna were analysed for the presence of added carbon monoxide, and all showed levels below 200 µg/kg, which is the internationally accepted level for physiological CO content in muscle tissue (Marrone et al., 2015). The highest observed value was 171 µg/kg in a fillet of Kawakawa from Vietnam.
3.6 Undesirable trace elements
100 samples were analysed for undesirable trace elements. One sample of Pacific saury from Taiwan had cadmium values at 0.22 mg/kg, which is above the legal limit of 0.05 mg/kg for fish. However, this product was not meant for human consumption. Two samples of squid cut-offs including viscera from Argentina, not meant for human consumption, also contained high levels of cadmium with 43 and 33 mg/kg respectively. No further action was taken with these three samples. One sample of crushed lobster carapaces from Canada had a cadmium content of 1.4 mg/kg, which is above the legal limit of muscle from crustaceans of 0.5 mg/kg. However, there are no legal limits for carapaces, no further action was taken.
None of the other undesirable trace elements were measured at levels above legal limits.
3.7 Persistent organic pollutants - POP's (PCDD/F, PCB, PBDE)
Thirty samples, selected based on risk assessment-criteria, were analysed for three classes of organo-halogen compounds considered undesirable and relevant for seafood. The selected POPs’ classes were: The PCDD/Fs, the PCBs and the PBDEs. All analysed samples were compliant. Four samples were analysed for the presence of PAHs, and all were compliant according to the regulations.
3.8 Polycyclic aromatic hydrocarbons (PAH)
Four samples were analysed for the presence of PAH-compounds. None contained levels above legal limits.
4 - Conclusion
A total of 100 samples collected by the official staff at the Norwegian Border Inspection Posts of the Norwegian Food Safety Authority were examined for selected chemical and microbiological undesirables in 2021.
Selected microbiological analyses were performed on 84 samples, undesirable trace elements were measured in 100 samples and POPs’ were measured in 30 seafood samples. All samples were compliant with the current legislation. The chemical spoilage indicator histamine was examined in 20 relevant samples, all values were below the maximum permitted level.
One sample of Pacific saury from Taiwan and two samples of squid cut-offs were found with cadmium values above the legal limit. However, these products were not intended for human consumption. One sample of crushed lobster carapaces from Canada also had a high Cd value, but was deemed compliant as it was intended as a flavour enhancer, and not to be eaten whole.
Three samples contained potentially human pathogenic Vibrio spp., and five of the analysed samples carried cefotaxime resistant Enterobacteriaceae isolates. However, there are currently no regulations or limits regarding the presence of these bacteria in food items and they were deemed compliant.
None of the other samples examined were identified with undesirable microorganisms or had trace elements, POPs’ of PAH exceeding the respective maximum levels.
5 - Acknowledgements
The responsible technician for the import program in 2021 at IMR was Anne Margrethe Aase from the Sample Reception and Vessel Laboratory.
Five laboratories at IMR contributed with analyses in 2021: The Sample Reception and Vessel Laboratory, the Molecular Biology Laboratory, the Inorganic Chemistry Laboratory, the Nutrients Laboratory and the Chemistry and Undesirables Laboratory.
We wish to thank all laboratory leaders and everyone who contributed to this project for a good collaboration in 2021.
6 - References
Commission Regulation (EC) 2019/1871 of 7 November 2019 on reference points for action for non-allowed pharmacologically active substances present in food of animal origin and repealing Decision 2005/34/EC, 12 EFSA Journal (2014). https://doi.org/10.2903/j.efsa.2014.3907
Commission Regulation (EC) No 2073/2005 of 15 November 2005 "on microbiological criteria for foodstuffs", Official Journal of the European Union (2005). https://doi.org/10.1109/MACE.2010.5536537
Commission Regulation (EC) No 1881/2006 of 19 December 2006 "setting maximum levels for certain contaminants in foodstuffs." Official Journal of the European Union 49(L364): 5-24.
Commission Regulation (EC) No 37/2010 of 22 December 2009 "on pharmacologically active substances and their classification regarding maximum residue limits in foodstuffs of animal origin", Official Journal of the European Union (2010).
Commission Regulation (EC) No 1259/2011 of 2 December 2011 amending Regulation (EC) No 1881/2006 "as regards maximum levels for dioxins, dioxin-like PCBs and non dioxin-like PCBs in foodstuffs." Official Journal of the European Union 320(L320): 18-23.
Commission Regulation (EC) No 1019/2013 of 23 October 2013 amending Annex I to Regulation (EC) No 2073/2005 as regards histamine in fishery products, (2013).
Commission Recommendation of 3 March 2014 on the monitoring of traces of brominated flame retardants in food." Official Journal of the European Union 65(L65): 39-40.
EFSA CONTAM Panel (2011). "Scientific opinion on polybrominated diphenyl ethers (PBDEs) in food." EFSA Journal 9(5): 2156.
Fostervold, A., Hetland, M.A., Bakksjø, R., Bernhoff, E., Holt, K.E., Samuelsen, Ø., Simonsen, G.S., Sundsfjord, A., Wyres, K.L. and Löhr, I.H., 2022. A nationwide genomic study of clinical Klebsiella pneumoniae in Norway 2001–15: introduction and spread of ESBLs facilitated by clonal groups CG15 and CG307. Journal of Antimicrobial Chemotherapy, 77(3), pp.665-674.
Jacoby GA. AmpC beta-lactamases. Clin Microbiol Rev. 2009;22(1):161–82
Janecko, N., S.-L. Martz, B. P. Avery, D. Daignault, A. Desruisseau, D. Boyd, R. J. Irwin, M. R. Mulvey and R. J. Reid-Smith (2016). "Carbapenem-resistant Enterobacter spp. in retail seafood imported from Southeast Asia to Canada." Emerging infectious diseases 22(9): 1675.
Marrone, R., C. Mascolo, G. Palma, G. Smaldone, M. Girasole and A. Anastasio (2015). "Carbon monoxide residues in vacuum-packed yellowfin tuna loins (Thunnus Albacares)." Italian journal of food safety 4(3).
WHO. (2017). "WHO publishes list of bacteria for which new antibiotics are urgently needed." from http://www.who.int/news-room/detail/27-02-2017-who-publishes-list-of-bacteria-for-which-new-antibiotics-are-urgently-needed .
7 - Annex I
Table 2: Methods used for detection and quantification of microbial and chemical parameters.
Parameter
|
Method of detection/quantification
|
Accreditation/Validation
|
|
|
Microbial parameters
|
|
|
|
Salmonella
|
ISO 6579-1:2017
|
Accredited
|
|
Listeria monocytogenes
|
ISO 11290-1:2017
|
Accredited
|
|
Coliform bacteria
|
3M petrifilm CC*
|
Accredited
|
|
Thermotolerant coliform bacteria
|
3M petrifilm CC*
|
Accredited
|
|
Enterobacteriaceae
|
3M petrifilm Enterobacteaceae*
|
Accredited
|
|
Enterococci
|
ISO 7899-2:2000
|
Accredited
|
|
Coagulase positive staphylococci
|
3M petrifilm StaphExpress*
|
Accredited
|
|
Sulphite reducing clostridia
|
NMKL method nr.56 (2015)
|
Validated
|
|
Vibrio spp.
|
NMKL method nr.156 (1997)
|
Accredited
|
|
Norovirus and Hepatitis A
|
ISO 15216-1:2017
|
Validated
|
|
Mould and Yeast
|
NMKL method nr.98 (2005)
|
Accredited
|
|
Antibiotic resistance
|
|
|
|
Carbapenemase-producing and extended-spectrum
β-lactamase (ESBL)-producing Enterobacteriaceae
|
Internal method using selective growth media containing antibiotics
|
Currently under internal validation
|
|
Prohibited substances
|
|
|
|
Malachite green
|
LCMS/MS (QQQ)
|
Accredited
|
|
Leuco-malachite green
|
LCMS/MS (QQQ)
|
Accredited
|
|
Brilliant green
|
LCMS/MS (QQQ)
|
Accredited
|
|
Crystal violet
|
LCMS/MS (QQQ)
|
Accredited
|
|
Leuco-crystal violet
|
LCMS/MS (QQQ)
|
Accredited
|
|
Chloramphenicol
|
LCMS/MS (QQQ)
|
Accredited
|
|
Nitrofuran metabolites
|
LCMS/MS (QQQ)
|
Accredited
|
|
Chemical spoilage indicators
|
|
|
Histamin
|
HPLC
|
Accredited
|
|
Carbon monoxide
|
|
|
|
Carbon monoxide
|
GC-FID
|
Validated
|
|
Heavy metals
|
|
|
|
Cadmium (Cd)
|
Quantitative ICP-MS, (NMKL method nr.186, 2007)
|
Accredited after NMKL prosedure nr. 4 (2005)
|
|
Mercury (Hg)
|
Quantitative ICP-MS, (NMKL method nr.186, 2007)
|
Accredited after NMKL prosedure nr. 4 (2005)
|
|
Lead (Pb)
|
Quantitative ICP-MS, (NMKL method nr.186, 2007)
|
Accredited after NMKL prosedure nr. 4 (2005)
|
|
Arsenic (As)
|
Quantitative ICP-MS, (NMKL method nr.186, 2007)
|
Accredited after NMKL prosedure nr. 4 (2005)
|
|
Persistent organic pollutants
|
|
|
POPs
|
HRGC/HRMS, GC-MSMS or GC-MS (NCI)
|
Accredited
|
|
PAH
|
GC-MS/MS
|
Accredited
|
|
*AFNOR validated after ISO 16140
8 - Annex II
Table 3: Samples with measured values above detection limit. All samples were compliant according to current regulations.
Parameter
|
IMR sample No.
|
Samples above LOD/LOQ
|
Legal limit
|
Compliant/non compliant
|
Product
|
Country of origin
|
Measured value
|
Microbial parameters
|
|
|
|
|
|
|
Salmonella
|
-
|
-
|
|
-
|
0 cfu/g
|
Compliant
|
Listeria monocytogenes
|
-
|
-
|
|
-
|
100 cfu/g
|
Compliant
|
Coliform bacteria
|
2021-1094
|
Argentine shortfin squid
|
Argentina
|
90 cfu/g
|
No limit in seafood
|
Compliant
|
|
2021-1497
|
Whiteleg shrimp
|
Vietnam
|
60 cfu/g
|
|
Compliant
|
|
2021-1067
|
Scampi
|
Vietnam
|
80 cfu/g
|
|
Compliant
|
|
2021-1088
|
Marinated milkfish
|
Phillipines
|
10 cfu/g
|
|
Compliant
|
Thermotolerant coliform bacteria
|
2021-1094
|
Argentine shortfin squid
|
Argentina
|
30 cfu/g
|
No limit in seafood
|
Compliant
|
|
2021-1088
|
Marinated milkfish
|
Phillipines
|
30 cfu/g
|
|
Compliant
|
Enterobacteriaceae
|
-
|
-
|
-
|
-
|
No limit in seafood
|
|
Enterococci
|
|
Argentine shortfin squid
|
Argentina
|
100 cfu/g
|
No limit in seafood
|
Compliant
|
|
|
Yellowfin tuna
|
Vietnam
|
200 cfu/g
|
|
Compliant
|
|
2021-1497
|
Whiteleg shrimp
|
Vietnam
|
100 cfu/g
|
|
Compliant
|
|
2021-1498
|
Whiteleg shrimp
|
Vietnam
|
800 cfu/g
|
|
Compliant
|
Coagulase positive staphylococci
|
|
-
|
-
|
-
|
No limit in seafood
|
Compliant
|
Sulphite reducing clostridia
|
|
|
|
|
No limit in seafood
|
Compliant
|
Vibrio spp.
|
|
Whiteleg shrimp
|
Vietnam
|
Detected
|
No limit in seafood
|
Compliant
|
|
|
Whiteleg shrimp
|
Vietnam
|
Detected
|
|
Compliant
|
|
|
Scampi
|
Vietnam
|
Detected
|
|
Compliant
|
Norovirus and Hepatitis A virus
|
|
Pacific oyster
|
South Korea
|
Norovirus detected
|
No limit in seafood
|
Compliant
|
Mould and Yeast
|
|
-
|
-
|
-
|
No limit in seafood
|
Compliant
|
Antibiotic resistance
|
|
|
|
|
|
|
Multiresistant Klebsiella pneumoniae
|
2021-484
|
Battered Whiteleg Shrimp
|
Vietnam
|
Detected
|
No limit in seafood
|
Compliant
|
Resistant Enterobacter spp.
|
2021-559
|
Peeled Whiteleg Shrimp
|
Vietnam
|
Detected
|
|
Compliant
|
Resistant Enterobacter spp.
|
2021-1071
|
Battered Whiteleg Shrimp
|
Vietnam
|
Detected
|
|
Compliant
|
Multiresistent Klebsiella pneumoniae
|
2021-1081
|
Peeled Whiteleg Shrimp
|
Vietnam
|
Detected
|
|
Compliant
|
Resistant Enterobacter spp.
|
2021-1497
|
Whiteleg Shrimp
|
Vietnam
|
Detected
|
|
Compliant
|
Prohibited substances
|
|
|
|
|
|
|
Malachite green
|
|
-
|
-
|
-
|
Not allowed
|
Compliant
|
Leuco-malachite green
|
|
-
|
-
|
-
|
Not allowed
|
Compliant
|
Brilliant green
|
|
-
|
-
|
-
|
Not allowed
|
Compliant
|
Crystal violet
|
|
-
|
-
|
-
|
Not allowed
|
Compliant
|
Leuco-crystal violet
|
|
-
|
-
|
-
|
Not allowed
|
Compliant
|
Chloramphenicol
|
|
-
|
-
|
-
|
Not allowed
|
Compliant
|
Nitrofuran metabolites
|
|
-
|
-
|
-
|
Not allowed
|
Compliant
|
Chemical spoilage indicators
|
|
|
|
|
|
|
Histamin
|
2021-685
|
Tinned mackerel
|
United Kingdom
|
5.9 mg/kg ww
|
100-200 mg/kg ww
|
Compliant
|
|
2021-686
|
Tinned, chilifried mackerel
|
Thailand
|
9.3 mg/kg ww
|
|
Compliant
|
Carbon monoxide
|
|
|
|
|
|
|
Carbon monoxide
|
|
Kawakawa fillet
|
Vietnam
|
171 µg/kg
|
No maximum limit in seafood, values >200µg/kg indicate potential addition of CO to product
|
Compliant
|
Heavy metals
|
|
|
|
|
|
|
Cadmium (Cd)*
|
2021-2502
|
Pacific saury
|
Taiwan
|
0.22 mg/kg*
|
0.1-1.0 mg/kg ww depending on product
|
Compliant
|
|
2021-1569
|
Squid cut-off
|
Argentina
|
43 mg/kg*
|
|
Compliant
|
|
2021-1568
|
Squid-cut-off
|
Argentina
|
33 mg/kg*
|
|
Compliant
|
|
2021-2934
|
Lobster Carapaces
|
Canada
|
1.4 mg/kg*
|
|
Compliant
|
Mercury (Hg)#
|
|
|
-
|
-
|
0.5-1.0 mg/kg ww depending on product
|
Compliant
|
Lead (Pb) #
|
-
|
-
|
-
|
-
|
0.1-1.5 mg/kg ww depending on product
|
Compliant
|
Arsenic (As) #
|
-
|
-
|
-
|
-
|
No limit in seafood
|
Compliant
|
Persistent organic pollutants
|
|
|
|
|
|
Compliant
|
POPs#
|
-
|
-
|
-
|
-
|
Varies with matrix and analyte
|
Compliant
|
PAH#
|
-
|
-
|
-
|
-
|
Varies with matrix and analyte
|
Compliant
|
* Not for Human Consumption
# Most samples over LOD as the method is very sensitive, but all results were compliant with regulations
|