PCDD/Fs and PCBs in seafood species from Moreton Bay, Queensland, Australia

https://doi.org/10.1016/j.marpolbul.2008.01.034Get rights and content

Abstract

Previous studies have identified elevated levels of polychlorinated dibenzo-p-dioxins (PCDDs) in sediments and megafauna (dugongs and green turtles) in the marine environment of southeast Queensland, Australia. Little information exists, however, regarding the levels of PCDDs, polychlorinated dibenzofurans (PCDFs) and related polychlorinated biphenyls (PCBs) in seafood from this area. This study aims to establish baseline information on PCDD/F and PCB contamination in a range of seafood species from Moreton Bay and to investigate contaminant variability due to harvesting season, size, habitat location and trophic level. In addition, different seafood extraction methods were tested to evaluate their impact on lipid yields and contaminant concentration. Overall, the median TEQDF&PCB levels in seafood from Moreton Bay were elevated compared to background levels in Australian marine/estuarine and retail fish. However, TEQDF&PCB levels of most seafood analysed were below the respective EU maximum limits. High inter- and intraspecies variability was observed, which could be partially attributed to differences in trophic level, season harvested and habitat location.

Introduction

Persistent organic pollutants (POPs), such as PCDD/Fs and PCBs, are ubiquitous in the environment due to their emission from numerous sources, high persistency and a propensity to be transported long distances. These compounds are well known to bioaccumulate in animal tissue, biomagnify through the food web and have been shown to elicit adverse effects at relatively low concentrations (US EPA, 2004). For the general population, dietary intake contributes approximately 90% of the total human exposure to POPs (Liem et al., 2000). The majority of this dietary exposure results from consumption of lipid rich products, including seafood. To date, very limited information exists on the levels of these contaminants in commonly consumed seafood species from Australia. An Australian national study on pooled seafood (of unknown origin) from supermarkets suggested that TEQDF&PCB levels are generally low in purchased seafood (0.023–80 pg/g lipid, median 1.35 pg/g lipid; n = 19) (FSANZ, 2004). The 80 pg/g lipid result represents an extreme outlier with all other retail samples TEQDF& PCB ranging from 0.023 to 5.1 pg/g lipid (FSANZ, 2004). For fish originating from the Australian marine system, a national dioxins survey in 2004 recorded similarly low TEQDF&PCB background levels ranging from 0.72 to 68 pg/g lipid (median 3.9 pg/g lipid; n = 20) (Mueller et al., 2004). An examination of PCB and organochlorine pesticide contamination in a range of foodstuffs from various metropolitan locations within Australia showed that fish sourced locally, including coastal waters, were generally the most contaminated, with PCBs ranging in total concentration from 18 to 130,000 ng/g lipid (average 6900 ng/g lipid; n = 37) (Kannan et al., 1994).

Previous studies in the Australian north-eastern state of Queensland have identified widespread and elevated levels of PCDDs, particularly OCDD, in marine sediments along the coastline (Gaus et al., 2001, Hermanussen et al., 2004) and elevated PCDD TEQ levels were observed in lower trophic, nearshore marine biota (dugong and green turtles) (Gaus et al., 2004, Hermanussen et al., 2006). These findings suggest that other marine biota from Queensland, and in particular higher trophic seafood sourced near the mainland, may contain considerably higher levels of PCDDs and/or other POPs compared to seafood purchased from supermarkets and fish caught from offshore locations. Local seafood may be consumed by individuals as part of recreational, subsistence and commercial fishing. Consequently, information on the levels of POPs in seafood caught from Queensland’s nearshore marine environment, together with seafood consumption data, will provide information on the contribution of such activities to human exposure levels with respect to the subpopulation groups involved.

Bioconcentration and biomagnification processes and the resulting tissue levels of POP contaminants are influenced by numerous and complex interactions between biological, seasonal, geographical and other factors (Porte and Albaiges, 1993, Mackay and Fraser, 2000, Kiviranta et al., 2003, Mormede and Davies, 2003). This results typically in high variability of contaminant levels within and between species which can span several orders of magnitude. Understanding the extent and cause of contaminant variability in seafood provides an important basis for evaluating their levels, as well as potential human exposure and risks.

This study represents a component of a broader investigation into the pathways and processes of seafood contamination in tropical marine systems and resulting human exposure from consumption of locally caught seafood. The key focus of this initial component presented here was to provide baseline information on the distribution of PCDD/Fs and PCBs in individual seafood within a marine nearshore environment. Various factors that may influence the tissue levels of these contaminants were considered in order to provide an initial insight into their significance and potential contribution to seafood contamination.

Section snippets

Sampling

This study was focused on Moreton Bay in southeast Queensland, Australia (Fig. 1), an area that sustains both commercial and recreational fishing. This bay is located directly adjacent to the city of Brisbane, which supports a population of approximately 1.77 million. Apart from urban land use, widespread agriculture and grazing and relatively low density tertiary industry are present in the bay’s catchments. Several major river systems enter the bay on the western side while on the eastern

Lipid extraction methods

Since many organic pollutants accumulate preferably in fat tissue, it is important to employ methods that allow efficient and reliable extraction of both lipids and contaminants from biological samples for evaluation of organic contaminant levels in these matrices. Fish and other marine biological tissues contain a range of lipids that differ in polarity and anatomical location, present either within or external to cells or in cell membranes (Kolakowska et al., 2003). Different seafood species

Acknowledgements

The authors would like to thank the Quandamooka community and John Page for assistance with sample collection and James McBroom for statistical analysis advice; their support for this study is greatly appreciated. Gratefully acknowledged is the continuous support and professional advice from staff at Eurofins-ERGO Forschungsgesellschaft, particularly Olaf Päpke and Peter Ebsen. This study is funded by the National Health and Medical Research Council (grant no: 351572). EnTox is a partnership

References (44)

  • D. Mackay et al.

    Bioaccumulation of persistent organic chemicals: mechanisms and models

    Environmental Pollution

    (2000)
  • P. Manirakiza et al.

    Comparative Study on Total Lipid Determination using Soxhlet, Roese-Gottlieb, Bligh & Dyer, and Modified Bligh & Dyer Extraction Methods

    Journal of Food Composition and Analysis

    (2001)
  • S. Mormede et al.

    Horizontal and vertical distribution of organic contaminants in deep-sea fish species

    Chemosphere

    (2003)
  • W. Naito et al.

    Dynamics of PCDDs/DFs and coplanar-PCBs in an aquatic food chain of Tokyo Bay

    Chemosphere

    (2003)
  • X. Nie et al.

    Distribution of polychlorinated biphenyls in the water, sediment and fish from the Pearl River estuary, China

    Marine Pollution Bulletin

    (2005)
  • A.J. Niimi

    Evaluation of PCBs and PCDD/Fs retention by aquatic organisms

    Science of The Total Environment

    (1996)
  • M. Simm et al.

    PCDD/Fs in sprat (Sprattus sprattus balticus) from the Gulf of Finland, the Baltic Sea

    Chemosphere

    (2006)
  • J. Zhang et al.

    Polychlorinated dibenzo-p-dioxin and dibenzofuran concentrations in common fish species in the Pearl River Delta area, China

    Chemosphere

    (2007)
  • European Commission, 2006. Amending regulation (EC) No 466/2001 setting maximum levels for certain contaminants in...
  • DIN, 1986. (Deutsches Institut fur Normung) Entwurf DIN 51 527 (Teil 1). Bestimmung des Gehaltes an polychlorierten...
  • FSANZ (2004). Dioxins in Food: Dietary Exposure Assessment and Risk Characterisation. Canberra, Food Standards...
  • C. Gaus et al.

    Exposure and potential risk of dioxins to the marine mammal dugong

    Organohalogen Compounds

    (2004)
  • Cited by (35)

    • Levels and patterns of polychlorinated dibenzo-p-dioxins and dibenzofurans and polychlorinated biphenyls in foodstuffs of animal origin from Chinese markets and implications of dietary exposure

      2021, Environmental Pollution
      Citation Excerpt :

      The aquatic animal food groups from coastal regions primarily consisted of sea species, which typically accumulate more PCDD/Fs and PCBs due to pollution in coastal waters (Shang et al., 2016; Wei et al., 2010). In addition, other factors, such as season (Matthews et al., 2008), feeding habits (Shang et al., 2016), metabolism (Phua et al., 2008) and biotransformation (Buckman et al., 2006; Kleeman et al., 1988) might also affect PCDD/Fs and PCBs concentrations. In contrast, fresh water species with lower accumulation levels of ∑PCDD/Fs and ∑PCBs were the primary components in the aquatic animal food groups from inland regions (Fu et al., 2018), which led to lower concentrations of PCDD/Fs and PCBs in these inland aquatic animal food groups.

    • Impact and Issues of Organic Pollutants

      2021, Management of Contaminants of Emerging Concern (CEC) in Environment
    • Relevance of current PCB concentrations in edible fish species from the Mediterranean Sea

      2020, Science of the Total Environment
      Citation Excerpt :

      The three species showed the same mono-ortho congener profile (118 > 105 > 156); however, a distinct abundance of non-ortho congeners was observed depending on the species. Sardine and bogue exhibited the same profile PCB-77 > 126 > 169 > 81, which is commonly found in other studies in the same and different species in the Mediterranean Sea and other parts of the world (Gómara et al., 2005; Matthews et al., 2008; Moon et al., 2009). Instead, the pattern of non-ortho-PCBs was quite different in anchovy (126 > 77 > 169) with a contribution of PCB-126 about 71% and no detection of PCB-81.

    View all citing articles on Scopus
    View full text