TY - JOUR T1 - Quantitative Analysis of Dioxins and Dioxin-like Polychlorinated Biphenyls in İnci Kefali (Alburnus tarichi, Güldenstädt, 1814): Implications for Public Health Risk Assessment TT - İnci Kefali (Alburnus tarichi, Güldenstädt, 1814)'nde Dioksin ve Dioksin Benzeri Poliklorlu Bifenillerin Kantitatif Analizi: Halk Sağlığı Risk Değerlendirmesi Açısından Sonuçları AU - Aydin, Funda PY - 2025 DA - August Y2 - 2025 DO - 10.52976/vansaglik.1726636 JF - Van Sağlık Bilimleri Dergisi JO - Van Sağ Bil Derg PB - Van Yüzüncü Yıl Üniversitesi WT - DergiPark SN - 2667-5072 SP - 131 EP - 138 VL - 18 IS - 2 LA - en AB - Objective: Polychlorinated dibenzo-p-dioxin and furans (PCDD/Fs) and dioxin-like polychlorinated biphenyls (dl-PCBs) classified as persistent organic pollutants can enter the human food chain, especially through animal-based products like fish, and pose significant toxicological risks. The inci kefali (Alburnus tarichi, Güldenstädt, 1814) an endemic species in Lake Van, is a widely consumed fish by the local population. Therefore, assessing the levels of these pollutants in inci kefali is of considerable importance for public health monitoring and risk assessment. Material and Method: In this study, a total of 30 inci kefali specimens were collected from ten different local fishers in Van Province. Sample preparation was performed in an accredited laboratory authorized by the Turkish Ministry of Agriculture, following EPA standard methods. PCDD/Fs, dl-PCBs, and indicator PCBs were analyzed by APGC-MS/MS using isotope dilution with ¹³C-labeled internal standards. Results: The mean concentrations of PCDD/Fs, PCDD/Fs + dl-PCBs and indicator PCBs in the analyzed samples were found to be 0.056 ± 0.008 pgWHO-TEQ/g wet weight, 0.220 ± 0.019 pgWHO-TEQ/g wet weight and 0.135 ± 0.010 ng/g wet weight, respectively. The Tolerable Daily Intake (TDI) and Tolerable Weekly Intake (TWI) were calculated as 0.063 pgWHO-TEQ/kg body weight/day and 0.440 pgWHO-TEQ/kg body weight/week, respectively. Conclusion: The results show that PCDD/Fs, PCDD/Fs + dl-PCBs, and indicator PCBs in inci kefali samples obtained from Lake Van are well below the legal limits set by the European Commission and the Turkish Food Codex. Furthermore, TDI and TWI values were also found to be below the limits set by the European Food Safety Authority. These findings show that inci kefali consumption does not currently pose a significant health risk to human health KW - Dioxins KW - Dioxin-like polychlorinated biphenyls KW - İnci kefali KW - APGC-MS/MS N2 - In this study, a total of 30 İnci Kefali (Alburnus tarichi Güldenstädt, 1814) specimens were collected from ten different local fishers in Van Province and analyzed for polychlorinated dibenzo-p-dioxins and furans (PCDD/Fs), dioxin-like polychlorinated biphenyls (dl-PCBs), and indicator PCBs (ICES-6: PCB28, PCB52, PCB101, PCB138, PCB153, PCB180) using APGC-MS/MS. The mean concentration of PCDD/Fs in the analyzed samples was determined as 0.056 ± 0.008 pg WHO-TEQ/g wet weight, while the total PCDD/F + dl-PCB concentration was 0.220 ± 0.019 pg WHO-TEQ/g wet weight. The total concentration of indicator PCBs (ICES-6) was measured as 0.135 ± 0.01 ng/g wet weight. When compared with the maximum permissible limits set by the European Commission (Commission Regulation (EU) 2023/915) and the Turkish Food Codex, the detected PCDD/F + dl-PCB levels correspond to only 3.4% of the legal limit. Similarly, the ICES-6 concentration represents approximately 0.2% of the maximum residue limits defined in the relevant regulations. Additionally, the estimated TDI (tolerable daily intake) and TWI (tolerable weekly intake) values were calculated as 0.01486 pg TEQ/kg/day and 0.104 pg TEQ/kg/week, respectively. These values are significantly below the limits recommended by EFSA (2018), which are 0.29 pg TEQ/kg/day for TDI and 2 pg TEQ/kg/week for TWI. The findings indicate that the levels of PCDD/F and dlPCBs, as persistent organic pollutants, in Alburnus tarichi pose no significant risk to public health and remain within safe limits. CR - Arıkan D, Yetim H, Sağdıç O, Kesmen Z (2009). Gıdalarda dioksin kontaminasyonu ve insan sağlığı üzerine etkileri. Gıda Teknolojisi Elektronik Dergisi, 12(2), 9-15. CR - Bartalini A, Muñoz-Arnanz J, Baini M, Panti C, Galli M, Giani D, et al. (2020). Relevance of current PCB concentrations in edible fish species from the Mediterranean Sea. Science of The Total Environment, 737, 139520. CR - Barone G, Storelli A, Busco A, Mallamaci R, Storelli MM. (2021). Polychlorinated dioxins, furans (PCDD/Fs) and dioxin-like polychlorinated biphenyls (dl-PCBs) in food from İtaly: Estimates of dietary intake and assessment. Journal of Food Science, 86, 4741-4753. CR - Barroso A, Mahler JV, Fonseca-Castro PH, Quintana FJ. (2021). The aryl hydrocarbon receptor and the gut-brain axis. Cellular & Molecular Immunology, 18, 259-268. CR - Çakıroğulları GÇ, Uçar Y, Oymael B, Bozkurt EN, Kılıç D. (2010). PCDD/F, dl-PCB and indicator PCBs in whiting, horse mackerel and anchovy in Black Sea in Turkey. Turkish Journal of Fisheries and Aquatic Sciences, 10, 357-362. CR - Çakıroğulları GÇ, Uçar Y, Kılıç D. (2010). Fileto levrek’te (Dicentrarchus labrax Linnaeus, 1758) dioksin, furan ve poliklorlu bifenillerin tespiti. Ege University Journal of Fisheries and Aquatic Sciences, 27(1), 15-18. CR - Çetintürk K, Güzel B, Canlı O. (2025). The development of a novel, green, efficient, and eco-friendly GC-MS/MS analytical method for the reliable and rapid determination of dl-PCBs, and PCDD/Fs using hydrogen as a carrier gas and a modified ion source. Talanta, 283, 127180. CR - De Mul A, Bakker MI, Zeilmaker MJ, Traag WA, van Leeuwen SPJ, et al. (2008). Dietary exposure to dioxins and dioxin-like PCBs in The Netherlands anno 2004. Regulatory Toxicology and Pharmacology, 51, 278-287. CR - Druga M, Moldovan C, Dumbrava DG, Velciov AB, Ştef DS. (2021). Polychlorinated dibenzodioxins, dibenzofurans and PCBs-a toxicological approach. Journal of Agroalimentary Processes and Technologies, 27(4), 437-445. CR - EFSA. (2018). European Food Safety Authority Contam Panel. Risk for human health related to the presence of dioxins and dioxin-like PCBs in food. EFSA Journal, 16(11), 5333. CR - EPA. (1994). United States Environmental Protection Agency. Method 1613: Tetra through octa-chlorinated dioxins and furans by isotopic dilution HRGC/HRMS. Erişim adresi: http://www.epa.gov/region3/1613.pdf. Erişim tarihi: 05.20.2025. CR - EU. (2023). European Commission Regulation 2023/915 of 25 April 2023 on maximum levels for certain contaminants in food and repealing Regulation (EC) No 1881/2006. Off J Eur Union. 2023. Erişim adresi: https://eur-lex.europa.eu/eli/reg/2023/915/2024-04-25/eng. Erişim tarihi: 06.20.2025. CR - Hişmioğulları ŞE, Hişmioğulları AA, Kontaş Aşkar T. (2012). Toxic effects of dioxin and dioxin-like chemicals. Balıkesir Sağlık Bilimleri Dergisi, 1(1), 23-27. CR - Kılıç D, Çakıroğulları GÇ, Uçar Y, Theelen R, Traag W. (2011). Comparison of PCDD/F and dl-PCB levels in Turkish foodstuffs: industrial versus rural, local versus supermarket products, and assessment of dietary intake. Food Additives & Contaminants: Part A, 28(7), 913-924. CR - Leeuwen SPJ van, Goeyens L, Loco J van, Carbonelle S, Overmeire I van, Beernaert H, et al. (2005). Dioxins in food and feed - Reference methods and new certified reference materials (DIFFERENCE). RIVO-75, Research no: C022/05 CR - Moon HB, Choi HG. (2009). Human exposure to PCDDs, PCDFs and dioxin-like PCBs associated with seafood consumption in Korea from 2005 to 2007. Environment International, 35, 279-284. CR - Nagyová S, Tölgyessy P. (2019). Validation including uncertainty estimation of a GC-MS/MS method for determination of selected halogenated priority substances in fish using rapid and efficient lipid removing sample preparation. Foods, 8(3), 101. CR - Öğretmen ÖY. (2022). Dondurulmuş olarak satışa sunulan hamsi balığının mikrobiyolojik kriter, radyoaktivite ve bazı kalıcı organik kirletici miktarlarının araştırılması. GIDA, 47(2), 359-371. CR - Pacini N, Abate V, Brambilla G, De Felip E, De Filippis SP, et al. (2013). Polychlorinated dibenzodioxins, dibenzofurans, and biphenyls in freshwater fish from Campania Region, southern Italy. Chemosphere, 90(1), 80-88. CR - TGK. (2023). Türk Gıda Kodeksi Bulaşanlar Yönetmeliği. Resmî Gazete No: 32360. Erişim adresi: https://resmigazete.gov.tr/eskiler/2023/11/20231105-1.htm. Erişim tarihi: 06.20.2025. CR - TÜİK. (2021). Türkiye İstatistik Kurumu Su ürünleri istatistikleri. 2021. Yayın No: 4637. Ankara. TÜİK. Erişim adresi: https://data.tuik.gov.tr. Erişim tarihi: 09.20.2025. CR - Türkmen A. (2011). Türkiye denizlerinden yakalanan dil balığı (Solea solea L., 1758) türünün kas ve karaciğer dokularında ağır metal düzeylerinin belirlenmesi. Karadeniz Fen Bilimleri Dergisi, 2(1), 139-151. CR - USEPA. (2008). United states environmental protection agency. Method 1668B: Chlorinated biphenyl congeners in water, soil, sediment, biosolids, and tissue by HRGC/HRMS. Erişim adresi: https://ntrl.ntis.gov/NTRL/dashboard/searchResults/titleDetail/PB2009105236.xhtml. Erişim tarihi: 09.20.2025. CR - Van den Berg M, Birnbaum LS, Denison M, De Vito M, Farland W, et al. (2006). The 2005 World Health Organization reevaluation of human and mammalian toxic equivalency factors (TEFs) for dioxins and dioxin-like compounds. Chemosphere, 67(9), 1739-1768. UR - https://doi.org/10.52976/vansaglik.1726636 L1 - https://dergipark.org.tr/tr/download/article-file/4988356 ER -