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Dioxin- and POP-contaminated sites—contemporary and future relevance and challenges

Overview on background, aims and scope of the series

  • DIOXIN AND POP-CONTAMINATED SITES • CHALLENGES • OVERVIEW
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Environmental Science and Pollution Research Aims and scope Submit manuscript

Abstract

Background, aim and scope

Once they have been generated, polychlorinated dibenzo-p-dioxins (PCDDs) and dibenzofurans (PCDFs) and other persistent organic pollutants (POPs) can persist in soils and sediments and in waste repositories for periods extending from decades to centuries. In 1994, the US EPA concluded that contaminated sites and other reservoirs are likely to become the major source of contemporary pollution problems with these substances. With this in mind, this article is the first in a new series in ESPR under the title ‘Case Studies on Dioxin and POP Contaminated Sites—Contemporary and Future Relevance and Challenges’, which will address this important issue. The series will document various experiences from sites contaminated with PCDD/F and other POPs. This article provides an overview of the content of the articles comprising the series. In addition, it provides a review of the subject in its own right and identifies the key issues arising from dioxin/POP-contaminated sites. Additionally, it highlights the important conclusions that can be drawn from these examples. The key aim of this article and of the series as a whole is to provide a comprehensive overview of the types of PCDD/F contaminated sites that exist as a result of historical activities. It details the various processes whereby these sites became contaminated and attempts to evaluate their contemporary relevance as sources of PCDD/Fs and other POPs. It also details the various strategies used to assess these historical legacies of contamination and the concepts developed, or which are under development, to effect their remediation.

Main features

Special sessions on ‘Contaminated sites—Cases, remediation, risk and policy’ were held at the DIOXIN conferences in 2006 and 2007, and this theme will be continued at DIOXIN 2008 to be held in Birmingham. Selected cases from the approximately 70 contributions made to these sessions, together with some additional invited case studies are outlined together with the key issues they raise. By evaluating these cases and adding details of experiences published in the current literature, an overview will be given of the different features and challenges of dioxin and POP-contaminated sites.

Results

This article provides a systematic categorisation of types of PCDD/F and POP-contaminated sites. These are categorised according to the chemical or manufacturing process, which generated the PCDD/Fs or POPs and also includes the use and disposal aspects of the product life cycle in question. The highest historical PCDD/F and dioxin-like polychlorinated biphenyl (PCB) contamination burdens have arisen as a result of the production of chlorine and of chlorinated organic chemicals. In particular, the production of chlorinated pesticides, PCBs and the related contaminated waste streams are identified being responsible for historical releases of toxic equivalents (TEQs) at a scale of many tonnes. Along with such releases, major PCDD/F contaminated sites have been created through the application or improper disposal of contaminated pesticides, PCBs and other organochlorine chemicals, as well through the recycling of wastes and their attempted destruction. In some extreme examples, PCDD/F contaminated sites have also resulted from thermal processes such as waste incinerators, secondary metal industries or from the recycling or deposition of specific waste (e.g. electronic waste or car shredder wastes), which often contain chlorinated or brominated organic chemicals. The examples of PCDD/F and dioxin-like PCB contamination of fish in European rivers or the impact of contaminated sites upon fishing grounds and upon other food resources demonstrate the relevance of these historical problems to current and future human generations. Many of the recent food contamination problems that have emerged in Europe and elsewhere demonstrate how PCDD/F and dioxin like PCBs from historical sources can directly contaminate human and animal feedstuffs and indeed highlight their considerable contemporary relevance in this respect. Accordingly, some key experiences and lessons learnt regarding the production, use, disposal and remediation of POPs from the contaminated sites are summarised.

Discussion

An important criterion for evaluating the significance and risks of PCDD/Fs and other POPs at contaminated sites is their present or future potential for mobility. This, in turn, determines to a large degree their propensity for off-site transport and environmental accessibility. The detailed evaluation of contaminated site cases reveals different site-specific factors, which influence the varied pathways through which poor water-soluble POPs can be mobilised. Co-contaminants with greater water solubility are also typically present at such sites. Hence, pumping of groundwater (pump and treat) is often required in addition to attempting to physically secure a site. At an increasing number of contaminated sites, securing measures are failing after relatively short time spans compared to the time horizon, which applies to persistent organic pollutant contamination. Due to the immense costs and challenges associated with remediation of contaminated sites ‘monitored natural attenuation’ is increasingly gaining purchase as a conceptual remediation approach. However, these concepts may well prove limited in their practical application to contaminated sites containing persistent organic pollutants and other key pollutants like heavy metals.

Conclusions

It is inevitable, therefore, that dioxin/POP-contaminated sites will remain of contemporary and future relevance. They will continue to represent an environmental issue for future generations to address. The securing and/or remediation of dioxin/POP-contaminated sites is very costly, generally in the order of tens or hundreds of millions of dollars. Secured landfills and secured production sites need to be considered as constructions not made for ‘eternity’ but built for a finite time scale. Accordingly, they will need to be controlled, supervised and potentially repaired/renewed. Furthermore, the leachates and groundwater impacted by these sites will require ongoing monitoring and potential further remediation. These activities result in high maintenance costs, which are accrued for decades or centuries and should, therefore, be compared to the fully sustainable option of complete remediation. The contaminated site case studies highlight that, while extensive policies and established funds for remediation exist in most of the industrialised western countries, even these relatively well-regulated and wealthy countries face significant challenges in the implementation of a remediation strategy. This highlights the fact that ultimately only the prevention of contaminated sites represents a sustainable solution for the future and that the Polluter Pays Principle needs to be applied in a comprehensive way to current problems and those which may emerge in the future.

Recommendations and perspectives

With the continuing shift of industrial activities in developing and transition economies, which often have poor regulation (and weak self-regulation of industries), additional global challenges regarding POPs and other contaminated sites may be expected. In this respect, a comprehensive application of the “polluter pays principle” in these countries will also be a key to facilitate the clean-up of contaminated areas and the prevention of future contaminated sites. The threats and challenges of contaminated sites and the high costs of securing/remediating the problems highlight the need for a comprehensive approach based upon integrated pollution prevention and control. If applied to all polluting (and potentially polluting) industrial sectors around the globe, such an approach will prove to be both the cheapest and most sustainable way to underpin the development of industries in developing and transition economies.

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Notes

  1. Currently, there are only four unintentionally produced POPs in the Stockholm Convention list. However, PentaCBz is currently in the POPRC and other compounds are proposed or discussed as being unintentionally produced POPs (see Table 1). Other unintentionally produced compound classes are proposed for the evaluation of the TEF concept (Van den Berg et al. 2006) and should to be considered as UPOPs (see Table 1).

  2. For a comprehensive overview on the chlorine industry and emissions from the chlorine industry, see Stringer and Johnston (2001).

  3. The contemporary release of PCDD/F via pesticide production, however, is not clear. Wenborn et al. (1999) estimated the release of PCDD/F from pesticide production in Germany alone to be 160 to 26,500 g/year. The wide range of the estimation is indicative for the lack of data required for a more clear determination of emission factors from chemical production.

  4. The production of the majority of the intentionally produced POPs was stopped in the 1980s, and today, only DDT is produced in commercially significant amounts. Destruction of the remaining stockpiles and wastes, however, is a managerial challenge and a financial burden. For example, many electrical transformers containing or contaminated with PCBs remain in use, and it is estimated that about 4 million tonnes of such equipment will need environmentally sound waste management (OECD 2007) as it is decommissioned. With current total treatment costs of US $2,000 to 5,000 (including packing, transport and destruction) this would amount to an estimated US $8 to 20 billion to manage transformer-associated PCBs alone. A comparison to the US $550 million allocated GEF funding for the Stockholm Convention from 2003 to 2010 demonstrates the magnitude of the financial challenge to implement the PCB obligations of the Stockholm Convention by the target date of 2028.

  5. For example, the contribution of coplanar PCBs to total TEQ in fish (Scientific Committee on Food 2000), dairy products (Fürst 2001) or butter (Weiss et al. 2001; Santillo et al. 2003) amount, on average, to more than 50% in the Northern Hemisphere, while the PCB contribution to total TEQ is less in the Southern Hemisphere.

  6. If the contamination was mainly via food chain to the mothers or stems from exposure of the grandmothers during the decades, PCP were applied (see Fig. 2) and passed on perinatally warrants further evaluation.

  7. The recent food contamination from PCDD/F resulted from the use of contaminated HCl from Tessenderlo for the production of gelatine (Hoogenboom et al. 2006; Wilm 2007). This case demonstrates that contemporary PCDD/F release from the chlorine industry can lead to direct food contamination with PCDD/F and needs to be better controlled.

  8. In this respect, it must be emphasised that increased or continued use of chlorinated pesticides is taking place, particularly in developing countries (Mansour 2004), e.g. Pakistan and India (Sankar et al. 2006; Tariq et al. 2007), leading to increased risk of PCDD/F contamination of environment and food as, e.g. revealed by the recent PCDD/F contamination of guar gum from India by PCP (Community Reference Laboratory for Dioxins and PCBs in Feed and Food 2007a, b). Regulations limiting the formation and release of PCDD/Fs from chlorinated pesticide manufacture and products and concomitant upgrades and control technologies are not applied and/or enforced in all countries (Mansour 2004; Sankar et al. 2006; Tariq et al. 2007).

  9. Unintentionally produced POPs (PCDD, PCDF, PCB and HCB) are normally formed in parallel in thermal and chemical processes (Weber et al. 2001; Kannan et al. 2000), and therefore, unintentionally produced HCB waste can be expected to contain also the other unintentionally produced PCDDs, PCDFs and PCBs.

  10. The relevance of PCB conversion to PCDF can be seen, for example in the Belgium food crises (Covaci et al. 2002) and also for the Yusho and Yucheng incidents of high human exposure via contaminated oil in which PCDF from PCB contamination accounted for more than 50% of TEQ and today account for approximately 90% of the TEQ burdens of these populations (Masuda et al. 1986; Kajiwara et al. 2007).

  11. Another important contemporary waste management challenge with a high risk of PCDD/F release is the destruction of global POPs stockpiles (PCB and POPs pesticides) as required under the framework of the Stockholm Convention (www.pops.int). The destruction of such high chlorine and dioxin precursor containing waste will require comprehensive monitoring with respect to PCDD/F formation and emission from destruction facilities (Weber 2007b).

  12. In this process, 8% sodium chloride was added before roasting.

  13. A good overview on DNAPLs topics can be found on the website of the DNAPL group at Sheffield University http://www.dnapl.group.shef.ac.uk/main.htm

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Correspondence to Roland Weber.

Appendix

Appendix

Table 3 Overview on the contaminated site cases to be presented within this series. (The cases are compiled according to the chronology of the ‘chlorine cycle’ and/or the origin of contamination)

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Weber, R., Gaus, C., Tysklind, M. et al. Dioxin- and POP-contaminated sites—contemporary and future relevance and challenges. Environ Sci Pollut Res 15, 363–393 (2008). https://doi.org/10.1007/s11356-008-0024-1

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