Skip to main content
International Journal of Circumpolar Health logoLink to International Journal of Circumpolar Health
. 2024 Oct 3;83(1):2408057. doi: 10.1080/22423982.2024.2408057

Key recommendations and research priorities of the 2021 AMAP human health assessment

Cheryl Khoury a,, Pál Weihe b
PMCID: PMC11451291  PMID: 39360677

ABSTRACT

Over the last three decades, the Arctic Monitoring and Assessment Programme has published five human health assessments. These assessments have summarised the current state of the science regarding environmental contaminants and human health in the Arctic. The 2021 Human Health Assessment Report had a particular focus on dietary transitions, in addition to human biomonitoring levels and trends, health effects, risk assessment methodologies, risk communication and multi-disciplinary approaches to contaminants research. The recommendations and research priorities identified in the latest assessment are summarised here to assist decision- and policy-makers in understanding and addressing the impacts of contaminants on human populations in the Arctic.

KEYWORDS: Arctic, contaminants, biomonitoring, risk, dietary transition

Introduction

The Arctic Monitoring Assessment Programme (AMAP) was established in 1991 as a Working Group of the Arctic Council. It is mandated to document, monitor and assess pollution and climate change issues and trends in the Arctic and to produce sound evidence-based assessments for use by policy- and decision-makers. Human Health Assessment reports summarise contaminant exposures and health effects associated with these exposures, in addition to risk assessment methodologies, risk communication activities and multi-disciplinary approaches to contaminants research in Arctic populations.

Diet is a primary source of human exposure to contaminants in the Arctic. This is the result of long-range transport of these pollutants by air and water currents from other parts of the world to northern latitudes. Once contaminants reach the Arctic many can persist and bioaccumulate in the food chain. Consumption of marine species and wildlife can contribute to higher levels of contaminants in humans. Contextualising the adverse effects of exposure to these contaminants is complicated by the fact that dietary sources of contaminants also have nutritional, spiritual and cultural importance. This is referred to as the Arctic Dilemma.

The terms “traditional food”, “country food”, “traditional country food”, “subsistence foods” and “local foods” are used to describe food such as hunted animals and plants gathered from the land. These terms may be interchangeable in some regions, but have distinct meanings in others. Even within regions, different definitions may be preferred by different groups. AMAP [1] uses all of theses phrases depending on the context of the results being described.

The 2021 Arctic Monitoring and Assessment Programme (AMAP) Human Health Assessment follows four previous assessments [2–5]. It includes an update on the science regarding contaminants and human health with a focus on dietary transitions in the Arctic. Here, we summarise the recommendations of this assessment and priorities for research, in the context of the findings of all five AMAP assessments by describing the relationship of these conclusions to those from previous AMAP assessments.

Recommendations1

Building on the recommendations of previous assessments and new evidence, the 2021 AMAP Human Health Assessment report made four key recommendations. These are presented in this section, with a high-level summary and supporting examples. The reader is referred to the full report [1] for complete details.

Reduce or eliminate contaminants at the source

  • Arctic States and all parties to the Stockholm and Minamata Conventions should strengthen and accelerate measures to eliminate POPs and human-made mercury emissions globally.

  • Arctic States should take steps to reduce or eliminate chemicals of emerging Arctic concern such as non-regulated PFAS through national policies and international agreements.

It is crucial that international efforts to regulate chemicals in the environment continue and that these regulations are implemented effectively. Given the global sources of much of the pollution that reaches the Arctic, international cooperation on chemicals management is important in reducing exposures to populations in the Arctic. This can be achieved by reducing and controlling regional industrial emissions [2,5], controlling production and use of POPs [3] and supporting international conventions [2–5]. Global assessments of health and the environment can highlight linkages between health and the environment to support international regulatory efforts [3].

Previous recommendations aimed to strengthen international chemicals management. These included recommending that polybrominated compounds and fluorinated compounds be added to the Stockholm Convention and included in future routine monitoring [4]; recommending that a global agreement on mercury be established [4]; and recommending a precautionary approach to the chemicals management of contaminants of emerging concern [5]. As reported succinctly in AMAP [5], risk communication is not the solution to the contaminant crisis and continued chemicals risk management efforts at the international level are required to reduce levels of contaminants in the Arctic.

The value of monitoring programmes in documenting trends can be seen in the ways data from these programmes have been used as evidence for the need to establish and adopt global conventions (e.g. Stockholm Convention, Minamata Convention). There are now limits in place on more than 30 POPs under the Stockholm Convention. Since 2009, new POPs have been added including some perfluorinated compounds, such as PFOS and PFOA. Data suggesting increasing trends of some PFAS such as PFNA (Lemire and Blanchette pers comm 2019, as reported in AMAP [1]; [6]) may support further regulatory efforts of this class of chemicals. Evidence of the effects of mercury on humans and the environment in the Arctic played a significant role in the development of the Minamata Convention [7]. The time trends established through on-going work provide evidence of the need for, and evaluation of, international chemicals management, which is the only true solution to reducing exposure to contaminants in Arctic populations.

The collection of evidence for the reduction of contaminants and effectiveness evaluation of international conventions benefits from harmonised approaches. These can encourage high-quality data and comparability of results. The need to develop uniform methods to allow for comparisons of studies across the Arctic was identified in 1998 and confirmed in subsequent assessments [2–5]. Standard laboratory practices are not the only uniform methods required. One mechanism for achieving harmonised results is through the use of existing biobanks. The creation and management of tissue/specimen banks was promoted in early AMAP assessments [2,3]. In future studies, samples from multiple biobanks may be analysed using the same, or complimentary, methods to produce comparable human biomonitoring data across regions. Harmonised results may also be encouraged through the reporting of health outcomes using uniform indicators and similar reporting structures to help understand trends and make meaningful comparisons [4]. In 2015, it was recommended that guidance on harmonised study designs, statistical methodologies and reporting of results would make it possible to carry out strong meta-analyses and enhance the ability to compare results across all regions [5].

The use of harmonised approaches has been highlighted in the 2021 Assessment. While the establishment and maintenance of biobanks are huge undertakings, projects in many regions have biobanked samples. A successful example of the use of biobanks is the MercuNorth project, which relied on biobanks from several regions to establish baseline levels of mercury in Arctic populations [8]. Results provide evidence for the value of these long-term investments, as samples from pregnant women recruited from across the circumpolar Arctic into different studies were analysed by laboratories to provide comparable baseline levels of mercury in advance of ratification of the Minamata Convention. Participation by analytical laboratories in external quality assurance and control schemes provides confidence that comparisons between laboratories are valid and data are of a high quality. As contaminants of emerging Arctic concern are identified and included in monitoring programmes, the importance of harmonisation is even greater to ensure that emerging methodologies and new data are comparable.

Promote healthy food choices by promoting foods low in contaminants

  • To get the best out of country, local and traditional foods and store-bought Western diets, governments can, for example, promote consumption of foods low in contaminants. Effective communication can increase the use of healthy country, local and traditional foods (e.g. fish and terrestrial animals such as reindeer/caribou, musk ox, and sheep) and reduce intake of foods that are likely to have high levels of contaminants or that are otherwise unhealthy.

  • Vitamin D and iodine levels should be monitored in Arctic populations and the need for supplements and fortification should be evaluated.

Risk communication messaging should promote the nutritional value of foods while providing information on the risk of contaminants. Risk communication has always been identified as a necessary but challenging area. Early recommendations were to enhance the development of local information and advice for Indigenous peoples [2,3]. These recommendations were followed by further advice that regional health authorities should collaborate with communities to develop effective, culturally appropriate strategies to enhance messaging about the benefits of country foods, in addition to promoting the benefits of breast feeding and providing balanced advice that includes the benefits of country foods with the risks concerning contaminants [4,5]. In 2009, it was recommended that communication efforts should be evaluated with respect to their impact on the intended audience [4]. Since the first assessments, the need for relevant and up-to-date guidance values has been noted that would help to interpret and, in turn, communicate risk-benefits [2,3].

There are several examples in the 2021 Assessment Report that provide evidence that work is being done in these areas to improve risk communication messaging. For example, consumption guidance has been published for various food items, such as fish [9,10]; [11–13] and pilot whale [14]. There are also examples of messaging co-developed with communities (e.g. [15]) and evaluation studies that can help to inform future messaging (e.g. [16]) [17,18]). Some groups have worked to make meaningful data accessible to the appropriate audience, while attempting to minimise misuse of information (e.g. Local Environmental Observer LEO network) [19]. Positive research findings have been incorporated into messaging (e.g. advice given in Greenland that include information about the nutritional qualities of fish that are low in contaminants) [20]. However, trusted relationships are crucial to the success of communication. This trust is difficult to build and very easily damaged or destroyed. While risk communication is key to educating and empowering communities to make the best food choices, experience has shown that this is a very complex undertaking and is not a sustainable solution to ensure low levels of contaminant exposures in human populations. It is therefore crucial that regulations to lower contaminants in the environment are implemented effectively.

Studies of the interactions between nutrients and contaminants will help to provide balanced advice on reducing risks from contaminants with the nutritional benefits of country, local and traditional foods, and imported foods. In the second AMAP assessment it was recommended that studies on the nutrient content of traditional food items should be promoted [3]. Promoting improved access to country foods that have lower levels of contaminants and higher levels of nutrients was recommended [4], as well as the importance of studying the interactions between different contaminants and between contaminants and nutrients [4,5]. It was also noted that more research was needed on determinants of food choice and availability, including age and gender differences to inform dietary advice. Studies that include both biomonitoring and total diet components were highlighted as necessary to better characterise exposure estimates and provide dietary advice [4].

Dietary transitions across the circumpolar Arctic are described in AMAP [1]. In some areas, the dietary transition is well documented, such as in Greenland [13,21,22], the Faroe Islands [23–25], Iceland [26,27], Norway [28–30] and Sweden [31]. However, information is lacking in other areas, including Russia and the Sápmi area, the traditional homeland area of the Saami people.

In general, there has been a change towards more imported or store-bought foods. However, country food consumption has been consistent over the past 25 years in some areas (e.g. fish and terrestrial foods consumption in Northwest Territories, Canada) [18] and fish consumption in Chukotka, Russia ([32,33]). Whether positive effects (e.g. decline in mercury levels; increases in dietary fibre or decreases in trans fatty acid intake) [27,34,35]; or negative effects (e.g. increases in obesity and diabetes) [36–40]; are observed depends on which food components are adopted from a new diet and to what extent components of the local diet are changed and/or continue to be consumed. Documented declines in nutrients differ substantially by country. Reduced country food consumption has been linked to declines in Vitamin D [41], omega-3 fatty acids [34] and iodine [42] The links between country foods and nutrients is supported by the finding that vitamin D levels were higher in Russian ethnic groups with a more traditional lifestyle [43]. Understanding dietary transitions helps inform advice on the risk-benefits of country, local and traditional foods.

Initiatives to increase awareness of the benefits of country foods, the best kinds of country foods to consume (low in contaminants, high in nutrients), the development of programmes to increase access to foods and education around food handling and preparation have been undertaken in Canada and Greenland [44,45]. Efforts to improve vitamin D levels have been made through supplementation of dairy products and margarine and use of cod liver oil [46,47]. Finland has also addressed iodine levels through fortification of cow fodder and table salt [48]. Results from on-going studies and analyses in different regions will provide additional information on diet and health for Indigenous Peoples in the Arctic [49,50,51].

Monitor and address food insecurity in Arctic communities

  • Food insecurity is a growing problem in some Arctic Indigenous populations as diets transition toward expensive store-bought food and environmental factors such as climate change affect the availability of country, local and traditional foods. Governments and non-governmental organizations should take an active role in monitoring food insecurity in Arctic communities and collaboratively develop proactive approaches to address it, building on and learning from existing best practices and models.

The impact of contaminants on the health of human populations in the Arctic is influenced by food availability. Food security can be defined as physical and economic access to sufficient, safe and nutritious food that meets the dietary needs and food preferences for an active and health life [52]. Food insecurity can be described as poor food security. While AMAP has a role in documenting trends and issues related to contaminants, a discussion of contaminants cannot disregard food insecurity and how it intersects with exposure to, and health effects associated with, contaminants, as well as how risks are assessed, communicated and contextualized. The 2021 AMAP assessment makes clear that food security continues to be a high priority for many Arctic populations. [53–56]

Expand efforts to collect data on exposure, dietary transitions, and health impacts

  • Arctic States and research funding bodies should work to fill information gaps, such as the need for more data on lifelong human health impacts in the Arctic related to exposure to contaminants, dietary transitions, and nutrition. There are also geographical gaps in Arctic data on contaminant levels and trends in humans: the need to expand monitoring and research is especially evident in Russia, where only a few dietary studies have evaluated Arctic Indigenous populations.

  • Research should continue to focus on the effects of contaminants on pregnant women and women of childbearing age whose diets involve significant consumption of marine mammals. New, collaborative studies are required to study levels of chemicals of emerging Arctic concern, routes of exposure, health effects, lifestyle implications, and interactions with influences outside the field of contaminants for these specific groups. There should be more focus on mixtures of POPs to which people are exposed and their effects on reproductive health and the immune system.

On-going cohort and biomonitoring programmes are needed to support time trends, follow populations with elevated levels of contaminants, study health effects and identify contaminants of emerging Arctic concern. The importance of establishing temporal trends in contaminant levels was identified in 1998 [2] and reiterated in each subsequent AMAP assessment [3–5]. Even as declines in many POPs were observed, high exposure levels and new contaminants in some regions warranted continued monitoring in Arctic populations [4,5].

Since 2015, biomonitoring studies have documented exposure to POPs and metals, as well as other contaminants, some of which were identified in the Chemicals of Emerging Arctic Concern report [57]. While there is a rich database for some contaminants, more data are needed for other contaminants to establish regiothere are still limitednal and temporal trends. For example, the 2021 Assessment presents more data on PFAS than previous reports, but there are still limited temporal PFAS data available and gaps across regions [6,58–74].

The importance of health studies, in particular cohort studies, was acknowledged in the first AMAP assessment [2]. The importance of establishing on-going studies in the Arctic to better understand health effects and risk associated with current levels of exposure in the Arctic was recommended in subsequent assessments [3–5]. Cohort studies not only provide a means to study contaminant-related effects on sensitive endpoints, but they can also be used to study the effects of changing conditions on these associations (e.g. climate change, dietary transitions). These studies are expensive, resource intensive and invaluable to the study of contaminants in the Arctic. Results reported in the 2021 Assessment included studies of endpoints identified as knowledge gaps in earlier assessments, including genetic variability and health outcomes associated with contaminant exposures [75–86] and the effects of contaminants and diet on the cardiovascular system [87–93]. Furthermore, health effects research also included the effects of contaminant exposure on the central nervous system [94–98]; immune system [70,99–106], reproductive system [61,65,107–122] as well as endocrine disruption [123–144] and cancer incidence [145–151].

Multidisciplinary efforts and cooperation between researchers and organisations with different mandates are required to address the complexities of contaminants research and to study contaminants within a holistic perspective. In 1998, multi-disciplinary cooperation was recommended to combine expertise from multiple disciplines such as biomarker research, epidemiology and monitoring programmes [2]. A recommendation of 2002 AMAP report [3] was to pursue a more holistic health impact assessment of the influences of environmental pollution on the health of Arctic peoples and the associated risk factors affecting them, coordinated with related public health work initiated through the AMAP Sustainable Development Working Group. Later, it was suggested that specific studies could support our understanding of genetic variability and susceptibility among Arctic populations, the toxicology of emerging substances (e.g. polybrominated compounds, perfluorinated compounds), the relationship between mercury and cardiovascular disease in Arctic populations, as well as research on climate change impacts on contaminants [4]. This was followed by a Climate Change and POPs assessment which included input from human health experts [152]. The need for climate-contaminant work was reiterated in the 2015 AMAP assessment [5] along with the need to understand contaminants in wildlife and the availability of country foods as a result of climate change.

The 2021 Assessment describes the need to recognise the interaction between contaminants and other stressors. In 2015 [5] results of the ArcRisk study (Arctic Health: Impacts on health in the Arctic and Europe owing to climate-induced changes in contaminant cycling 2009–14) were reported. These included that the impact of climate change on exposure risk will depend on the properties of any given contaminant and climate-mediated changes in food availability and resource exploitation may influence human exposure to contaminants more than direct climate mediated effects. The study authors also highlighted the need for more data to model and characterise sources and exposures to contaminants, as well as the need for epidemiological research that is accompanied by detailed reporting of results. More information on the outcomes of this project were presented in the 2021 Assessment [153,154]. With respect to dietary transitions, the influence of climate change will depend on the types of food being consumed. Dietary transitions away from traditional and local foods may overshadow other climate-mediated effects on human exposures to contaminants.

There is growing recognition of the usefulness of the One Health paradigm (e.g [155–157]). Greater uptake of this paradigm will improve the ability of residents, public health agencies, and wildlife resource managers to deal with existing environmental threats, and early recognition of emerging threats. Epidemiological zoonotic/human disease models are needed, as well as new approaches to integrate existing and future data. The models will enable estimates of the risk and magnitude of human and wildlife health impacts and changes in disease and contaminant exposure in response to different climate change scenarios. Trends in population migration from smaller to larger communities and urban centres may be accompanied by changes in exposure to contaminants and zoonotic diseases. Understanding contaminants in a holistic context will help to address interconnected environmental health risks.

Research priorities

Following from the key findings and knowledge gaps presented in the 2021 AMAP Assessment [1], priorities for future research were proposed. These are outlined in Table 1. Specific activities are grouped by the following themes: international cooperation on chemicals management, harmonised approaches, risk communication messaging, interactions between nutrients and contaminants, cohort studies and biomonitoring programmes, and multidisciplinary efforts and cooperations.

Table 1.

Priorities for future research of the impact of contaminants on human populations in the Arctic.

Research Priority Activities to address priority
International cooperation on chemicals management
  • Advocate for reducing or eliminating contaminants at the source

  • Support the Stockholm and Minamata Conventions

  • Contribute to the identification of chemicals of concern to human health in the Arctic

Harmonized approaches
  • Participation in QA/QC programs as a requirement of all labs submitting data to AMAP assessments

  • Guidance on harmonised study designs, statistical methodologies and results reporting, including harmonised methods for assessing dietary intake, food security, health outcomes, and northern food environments to enable comparisons that are more accurate across populations and over time and that consider season, gender- and age-based differences in consumption.

  • The creation and maintenance of biobanks for as many projects as is possible.

  • A systematic update on the general health status of Arctic inhabitants.

Risk communication messaging
  • Balanced messaging that appropriately presents the risks and benefits of local, traditional and country foods.

  • Promote increased consumption of species low in contaminants to increase dietary consumption of nutrients.

  • Evaluation studies, including follow-up on policy recommendations to evaluate reception and awareness of the communication to ensure the success of the messages, and studies of the effectiveness of social media in risk communication. As well, the evaluation of the combinations of medium and messenger for a variety of health messages is important to improve understanding of optimal communication strategies for different communities.

  • Data on health communication and risk perception to compare results to those from other regions and across Arctic countries that would help identify best practices, including cultural appropriateness that could be used and adapted to specific regional and community needs.

  • Collaborative communication projects done with affected communities that take into consideration aspects such as social, economic, and cultural factors to ensure that they are culturally appropriate.

  • The development of tools (e.g. guidance values) and models to help reduce uncertainties in the estimates of health risks from exposure to contaminants.

Interactions between nutrients and contaminants
  • Understanding modern dietary changes and reasons behind dietary choices. Dietary intakes should be continuously followed in Arctic populations, especially in Russia, where there is a lack of dietary studies.

  • Risk-benefit analyses to compare traditional foods with store-bought Western foods while considering health, economics, local contexts, cultural resilience, and sustainability.

  • Study of the effects of low nutrient levels on health status.

  • Studies of the influence of sex, age, socio-economic status and geographical location on dietary intakes and dietary transition patterns.

  • Promotion of knowledge of the healthiest local and country foods.

  • Studies of the interactions of chemicals and nutrients and the benefits and risks associated with country foods.

  • Monitoring of Vitamin D and iodine levels in Arctic populations, and consideration of the need for dietary enrichment.

  • Partnerships among academics and Arctic Indigenous communities and organisations conducting dietary research using an approach based on co-production of knowledge.

Cohort studies and and biomonitoring programs
  • Regularly conducted biomonitoring studies (e.g. every 5 years) to obtain data to support time trends, with the inclusion of contaminants of emerging concern, particularly new PFAS.

  • Support for, and expansion, of the use of cohort studies, which are important for making links between exposures and health outcomes in Arctic populations.

  • Studies to identify the mechanisms through which exposure can lead to health impacts, to support the findings of epidemiological studies.

  • A continued focus on exposure and health effects studies of pregnant women and women of child-bearing age whose diets involve significant consumption of marine mammals. This should include identification of prenatal and postnatal windows of vulnerability – the periods in which the foetus and infant are most vulnerable to impacts from exposure.

  • Research on mixtures of POPs and their effects on reproductive health and cardiovascular outcomes and the immune system.

Multidisciplinary efforts and cooperation
  • Collaborations with experts in zoonoses and climate change using a holistic approach like the One Health model.

  • Acknowledgement of the importance of Indigenous knowledge and equitable engagement of Indigenous Peoples.

  • An improved understanding of the health impacts of contaminants on wildlife, including possible immunosuppressive effects that could lead to increased active zoonotic infections in exposed wildlife and increased risk to human consumers. The warming Arctic climate and permafrost thaw may influence contaminant exposure as well as an increase in the spread of zoonotic infectious diseases in the Arctic.

  • Research on critical questions related to lifetime contaminant accumulation, lifetime exposure to zoonotic pathogens, and the health consequences to wildlife and human consumers.

  • Collaborative studies to investigate lifestyle implications (e.g. smoking), and interactions with influences (e.g. climate change) outside the field of contaminants.

  • Work to integrate research with other disciplines through support for other AMAP expert groups.

Conclusions

AMAP Human Health Assessment reports include comprehensive coverage of available data from across the Arctic. They include reporting on not just contaminant levels, but health effects, dietary transitions and the ways in which contaminants are assessed, communicated and placed in context of overall health and well-being.

Central to the 2021 Assessment was a review of dietary transitions. Many Arctic populations are experiencing a transition towards imported foods. While these transitions may lead to positive reductions in levels of contaminants, they can also have negative outcomes, such as reduced connection to the land, increased obesity, impaired dental status and declining vitamin D and iodine levels. Overall, contaminant levels are decreasing in many Arctic populations; however, these declines are not uniform or consistent across regions. Developing messaging around the risks and benefits of traditional, local and country foods is essential, but complex. Unfortunately, how risks of contaminant exposure are identified and assessed differs by jurisdiction, and studies of the interactions between nutrients and contaminants are needed to provide balanced advice on reducing risks from contaminants in food while maintaining the nutritional benefits of country, local and traditional foods and imported foods.

It is crucial that international efforts to regulate chemicals in the environment continue and that these regulations are implemented effectively. Use of harmonised approaches helps to support regulations by ensuring high-quality data and comparability of results. This is necessary during the collection and reporting of biomonitoring and health data.

There is growing awareness and use of multi-disciplinary approaches such as the One Health paradigm, to address environmental health issues, including lifetime contaminant accumulation, lifetime exposure to zoonotic pathogens, and health consequences for wildlife and human consumers. For reasons that include dietary change, a warming Arctic may not greatly change contaminant exposure. Population migration towards urban centres and larger communities in the Arctic may be accompanied by changes in exposure to contaminants and zoonotic diseases. Future work may include links between contaminants, health and response to rapid changes, especially those that impact diet and food availability, such as zoonotic diseases, climate change and other stressors.

After review and assessment of the available evidence, four key recommendations were made in the 2021 Assessment Report. These are (1) reduce or eliminate contaminants at the source, (2) promote healthy food choices by promoting foods low in contaminants, (3) monitor and address food insecurity in Arctic communities, and, (4) expand efforts to collect data on exposure, dietary transitions, and health impacts. Regular assessments provide up-to-date, evidence-based recommendations for policy and decision makers. These recommendations are intended to assist in understanding and addressing the impact of contaminants on Arctic populations.

Acknowledgments

This article is based on Chapter 8 “Key findings, research priorities and recommendations” of the AMAP Assessment 2021: Human Health in the Arctic, which was completed prior to February 2022. We would like to acknowledge the AMAP Secretariat for their support of this work.

Footnotes

1

AMAP: Arctic Monitoring and Assessment Programme; POPs: persistent organic pollutants; PFAS: per-/polyfluoroalkyl substances; PFOS: perfluorooctane sulphonate; PFOA: perfluorooctanoic acid; PFHxs: perfluorohexane sulphonate; SAMINOR study: The Population-based Study on Health and Living Conditions in Regions with Sami and Norwegian Populations; HALDI study: health and living conditions in Sápmi, Sweden; HHAG: Human Health Assessment Group

Disclosure statement

No potential conflict of interest was reported by the author(s).

References

  • [1].AMAP . AMAP assessment 2021: human health in the Arctic. In: Arctic monitoring and assessment programme (AMAP). Tromsø, Norway; 2021. p. 240. [Google Scholar]
  • [2].AMAP . AMAP assessment report: arctic pollution issues. Arctic monitoring and assessment programme (AMAP). Oslo, Norway; 1998. [Google Scholar]
  • [3].AMAP . AMAP assessment 2002: human health in the Arctic. In: Arctic monitoring and assessment programme (AMAP). Oslo, Norway; 2003. p. xiv+137. [Google Scholar]
  • [4].AMAP . Assessment 2009: human health in the Arctic. Arctic monitoring and assessment programme (AMAP). Oslo, Norway; 2009. p. xiv+254. [Google Scholar]
  • [5].AMAP . AMAP assessment 2015: human health in the Arctic. In: Arctic monitoring and assessment programme (AMAP). Oslo, Norway; 2015. p. vii + 165. [Google Scholar]
  • [6].Donat-Vargas C, Bergdahl I, Tornevi A, et al. Associations between repeated measure of plasma perfluoroalkyl substances and cardiometabolic risk factors. Environ Int. 2019;124:58–13. doi: 10.1016/j.envint.2019.01.007 [DOI] [PubMed] [Google Scholar]
  • [7].Platjouw FM, Hovland Steindal E, Borch T.. From arctic science to International Law: the road towards the minamata convention and the role of the arctic council. Arct Rev Law Polit. 2018;9:226–243. doi: 10.23865/arctic.v9.1234 [DOI] [Google Scholar]
  • [8].Adlard B, Lemire M, Bonefeld-Jørgensen EC, et al. MercuNorth – monitoring mercury in pregnant women from the Arctic as a baseline to assess the effectiveness of the minamata convention. Int J Circumpolar Health. 2021;80(1):1881345. doi: 10.1080/22423982.2021.1881345 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [9].State of Alaska . Fish facts & consumption guidelines. 2020. Available from: http://dhss.alaska.gov/dph/Epi/eph/Pages/fish/default.aspx
  • [10].Finnish Food Authority . Safe use of fish. 2019. Available from: www.ruokavirasto.fi/en/private-persons/information-on-food/instructions-forsafe-use-of-foodstuffs/safe-use-of-foodstuffs/safe-use-of-fish/1
  • [11].Government of the NWT . Site specific fish consumption advice. 2016. Available from: www.hss.gov.nt.ca/en/services/recommandations-sur-la-consommation-de-poisson/site-specific-fish-consumption-advice
  • [12].Icelandic Directorate of Health . Diet during pregnancy, information for women of childbearing age. 2018. Available from: www.ruokavirasto.fi/en/private-persons/information-on-food/instructions-forsafe-use-of-foodstuffs/safe-use-of-foodstuffs/safe-use-of-fish/2
  • [13].Larsen CVL, Hansen CB, Ingemann C, et al. Befolkningsundersøgelsen i Grønland 2018. Levevilkår, livsstil og helbred [Population Health Survey in Greenland 2018. Living conditions, lifestyle, and health. In Danish]. Copenhagen. SIF’s Grønlandsskrifter no. 30. Available National Institute of Public Health; 2019. Available from: www.sdu.dk/sif [Google Scholar]
  • [14].Weihe P, Joensen HD. Dietary recommendations regarding pilot whale meat and blubber in the Faroe Islands. Int J Circumpolar Health. 2012;71(1):18594. doi: 10.3402/ijch.v71i0.18594 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [15].Boyd AD, Furgal CM. Towards a participatory approach to risk communication: the case of contaminants and Inuit health. J Risk Res. 2022;25(7):892–910. doi: 10.1080/13669877.2022.2061035 [DOI] [Google Scholar]
  • [16].Desiré-Tesar C, Furgal C, Friendship K, et al. Understanding communications on contaminants: lessons learned from northern Canada. Project report (draft). Ottawa (ON): Clive Tesar Consulting; 2010. [Google Scholar]
  • [17].Furgal C, Boyd A. Risk perception and message evaluation of the Inuit health survey contaminants assessment in Nunavut. Peterborough, Canada: Results from Iqaluit, Nunavut. Trent University; 2014. [Google Scholar]
  • [18].Ratelle M, Skinner K, Brandow D, et al. Results report: contaminant biomonitoring in the Northwest Territories Mackenzie Valley: investigating the links between contaminant exposure, nutritional status, and country food use. Waterloo (ON): University of Waterloo; 2019. Available from: https://uwaterloo.ca/human-exposure-and-toxicology-research-group/sites/default/files/uploads/files/community_report_-_mackenzie_final_review_1.pdf [Google Scholar]
  • [19].Brubaker M, Berner J, Tcheripanoff M. LEO, the local environmental observer network: a community-based system for surveillance of climate, environment, and health events. 2017. Available from: https://arctichealth.org/media/pubs/284409/pg513.pdf
  • [20].Bjerregaard P, Mulvad G. The best of two worlds: how the Greenland board of nutrition has handled conflicting evidence about diet and health. Int J Circumpolar Health. 2012;71(1):18588. doi: 10.3402/ijch.v71i0.18588 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [21].Knudsen A-KS, Long M, Henning S, et al. Lifestyle, reproductive factors and food intake in Greenlandic pregnant women: the ACCEPT – sub-study. Int J Circumpolar Health. 2015;74(1):29469. doi: 10.3402/ijch.v74.29469 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [22].Terkelsen AS, Long M, Hounsgaard L, et al. Reproductive factors, lifestyle and dietary habits among pregnant women in Greenland: the ACCEPT sub-study 2013–2015. Scand J Public Health. 2018;46(2):252–261. doi: 10.1177/1403494817714188 [DOI] [PubMed] [Google Scholar]
  • [23].Veyhe AS, Andreassen J, Halling J, et al. Prevalence of type 2 diabetes and prediabetes in the Faroe Islands. Diabetes Res Clin Pract. 2018;140:162–173. doi: 10.1016/j.diabres.2018.03.036 [DOI] [PubMed] [Google Scholar]
  • [24].Veyhe AS, Andreassen J, Halling J, et al. Prevalence of prediabetes and type 2 diabetes in two non-random populations aged 44–77 years in the Faroe Islands. J Clin Transl Endocrinol. 2019;16:100187. doi: 10.1016/j.jcte.2019.100187 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [25].Veyhe AS. Færøske kvinders kostvanter i graviditetens tredje trimester [Dietary survey with pregnant women from the Faroe Islands during their third trimester] [thesis]. Gothenburg, Sweden: Master of Public Health. Nordic School of Public Health; 2006. [Google Scholar]
  • [26].Steingrimsdottir L, Thorkelsson G, Eythorsdottir E. Food, nutrition and health in Iceland. In: Andersen V, Bar E, and Wirtanen G, editors. Nutritional and health aspects of food in Nordic countries. Elsevier; 2018. p. 145–177. https://iris.rais.is/en/publications/food-nutrition-and-health-in-iceland-in-nutritional-and-health-as. [Google Scholar]
  • [27].Steingrimsdottir L, Valgeirsdottir H, Halldorsson TI, et al. [National nutrition surveys and dietary changes in Iceland. Economic differences in healthy eating]. Læknablađiđ. 2014;100(12):659–664. doi: 10.17992/lbl.2014.12.571 [DOI] [PubMed] [Google Scholar]
  • [28].Johansson L. NORKOST 1993-94 Landsomfattende kostholdsundersøkelse blant menn og kvinner i alderen 16-79 år. (National dietary survey among men and women aged 16-79 years). Oslo: Norwegian Directorate of Health; 1997. [Google Scholar]
  • [29].Johansson L, Solvoll K. NORKOST 1997 Landsomfattende kostholdsundersøkelse blant menn og kvinner i alderen 16-79 år [National dietary survey among men and women aged 16-79 years]. Oslo: Norwegian Directorate of Health; 1999. [Google Scholar]
  • [30].Totland TH, Melnæs BK, Lundberg-Hallén N, et al. Norkost 3. En landsomfattende kostholdsundersøkelse blant menn og kvinner i Norge i alderen 18-70 år, 2010-11 [Norkost 3. A nationwide dietary survey among men and women in Norway aged 18-70 years, 2010-11]. Report no. IS-2000. Oslo: Norwegian Directorate of Health; 2012. [Google Scholar]
  • [31].Johansson I, Nilsson LM, Stegmayr B, et al. Associations among 25-year trends in diet, cholesterol and BMI from 140,000 observations in men and women in Northern Sweden. Nutr J. 2012;11:40. doi: 10.1186/1475-2891-11-40 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [32].Dudarev AA. Dietary exposure to persistent organic pollutants and metals among Inuit and Chukchi in Russian Arctic Chukotka. Int J Circumpolar Health. 2012;71(1):18592. doi: 10.3402/ijch.v71i0.18592 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [33].Dudarev AA, Yamin-Pasternak S, Pasternak I, et al. Traditional diet and environmental contaminants in coastal Chukotka I: study design and dietary patterns. Int J Environ Res Public Health. 2019;16(5):702. doi: 10.3390/ijerph16050702 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [34].Jeppesen C, Bjerregaard P. Consumption of traditional food and adherence to nutrition recommendations in Greenland. Scand J Public Health. 2012;40(5):475–481. doi: 10.1177/1403494812454467 [DOI] [PubMed] [Google Scholar]
  • [35].Weihe P. Department of Public Health and Occupational Medicine, Tórshavn, Faroe Islands. Personal Communication. 2014. As reported in AMAP (2021a).
  • [36].Bjerregaard P, Young TK, Dewailly E, et al. Indigenous health in the Arctic: an overview of the circumpolar Inuit population. Scand J Public Health. 2004;32(5):390–395. doi: 10.1080/14034940410028398 [DOI] [PubMed] [Google Scholar]
  • [37].Galloway T, Young TK, Egeland GM. Emerging obesity among preschool-aged Canadian Inuit children: results from the Nunavut Inuit Child Health Survey. Int J Circumpolar Health. 2010;69(2):151–157. doi: 10.3402/ijch.v69i2.17437 [DOI] [PubMed] [Google Scholar]
  • [38].IBIS . Diabetes and Obesity Prevalence. Alaska Department Health Soc Serv, Indicator-Based Inf System Public Health (AkIBIS) website 2019. Available from: http://ibis.dhss.alaska.gov
  • [39].Matthiessen J, Andersen LF, Barbieri HE, et al. The Nordic Monitoring System 2011–2014: Status and development of diet, physical activity, smoking, alcohol and overweight. Denmark: Nordic Council of Ministers; 2016. [Google Scholar]
  • [40].Reeds J, Mansuri S, Mamakeesick M, et al. Dietary patterns and type 2 diabetes mellitus in a First Nations Community. Can J Diabetes. 2016;40(4):304–310. doi: 10.1016/j.jcjd.2016.05.001 [DOI] [PubMed] [Google Scholar]
  • [41].Singleton R, Lescher R, Gessner BD, et al. Rickets and vitamin D deficiency in Alaska Native children. J Pediatr Endocrinol Metab. 2015;28(7–8):815–823. doi: 10.1515/jpem-2014-0446 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [42].Adalsteinsdottir S, Tryggvadottir EA, Hrolfsdottir L, et al. Insufficient iodine status in pregnant women as a consequence of dietary changes. Food Nutr Res. 2020;64:3653. doi: 10.29219/fnr.v64.3653 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [43].Kozlov A, Khabarova Y, Vershubsky G, et al. Vitamin D status of northern Indigenous people of Russia leading traditional and “modernized” way of life. Int J Circumpolar Health. 2014;73:26038. doi: 10.3402/ijch.v73.26038 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [44].Nerisa . Erhvervsområdet i Kommuneqarfik Sermersooq [The business area in Kommuneqarfik Sermersooq]. 2020. Available from: www.nerisa.gl
  • [45].Nunavut Food Security Coalition . Guidelines for Serving Country Food in Government-funded Facilities and Community Programs. 2016. Available from: www.nunavutfoodsecurity.ca/node/928
  • [46].Amcoff E. Riksmaten vuxna 2010-2011. Food and nutrient intake among adults in Sweden. Report from the Swedish National Food Agency. [In Swedish]. 2012. Available from: www.livsmedelsverket.se/globalassets/publikationsdatabas/rapporter/2011/riksmaten_2010_20111.pdf
  • [47].Raulio S, Erlund I, Männistö S, et al. Successful nutrition policy: improvement of vitamin D intake and status in Finnish adults over the last decade. Eur J Public Health. 2017;27:268–273. doi: 10.1093/eurpub/ckw154 [DOI] [PubMed] [Google Scholar]
  • [48].Nyström HF, Brantsæter AL, Erlund I, et al. Iodine status in the Nordic countries – past and present. Food Nutr Res. 2016;60(1):31969. doi: 10.3402/fnr.v60.31969 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [49].Brustad M, Hansen KL, Broderstad AR, et al. A population-based study on health and living conditions in areas with mixed Sami and Norwegian settlements – the SAMINOR 2 questionnaire study. Int J Circumpolar Health. 2014;73(1):23147. doi: 10.3402/ijch.v73.23147 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [50].Nunavik Regional Board of Health and Social Services . What is Qanuilirpitaa? 2020. https://nrbhss.ca/en/what-qanuilirpitaa-2017
  • [51].Umeå University . HALDI - health and living conditions in Sápmi. Sweden; 2021. Available from: www.umu.se/forskning/projekt/haldi–halsaoch-levnadsvilkor-i-sapmi-sverige-/ [Google Scholar]
  • [52].Shaw DJ. World Food Summit, 1996. In: World Food Security. London: Palgrave Macmillan; 2007. p. 347–360. doi: 10.1057/9780230589780_35 [DOI] [Google Scholar]
  • [53].Fillion M, Laird BD, Douglas V, et al. Development of a strategic plan for food security and safety in the Inuvialuit Settlement Region, Canada. Int J Circumpolar Health. 2014;73(1):25091. doi: 10.3402/ijch.v73.25091 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [54].Furgal C, McTavish K, Martin R, et al. The importance of scale in understanding and addressing Arctic food security. In: Arctic Change, International Conference, December 2017; (QC) City, Canada; 2017. Presentation, Abstract. [Google Scholar]
  • [55].St-Germain A-AF, Galloway T, Tarasuk V. Food insecurity in Nunavut following the introduction of Nutrition North Canada. Can Med Assoc J. 2019;191(20):E552–E558. doi: 10.1503/cmaj.181617 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [56].Walch A, Bersamin A, Loring PA, et al. A scoping review of traditional food security in Alaska. Int J Circumpolar Health. 2018;77(1):1419678. doi: 10.1080/22423982.2017.1419678 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [57].AMAP . AMAP Assessment 2016: Chemicals of Emerging Arctic Concern. In: Arctic Monitoring and Assessment Programme (AMAP). Oslo, Norway; 2017. p. xvi+353. [Google Scholar]
  • [58].Averina M, Brox J, Huber S, et al. Perfluoroalkyl substances in adolescents in northern Norway: Lifestyle and dietary predictors. The Tromsø study, Fit Futures 1. Environ Int. 2018;114:123–130. doi: 10.1016/j.envint.2018.02.031 [DOI] [PubMed] [Google Scholar]
  • [59].Byrne S, Seguinot-Medina S, Miller P, et al. Exposure to polybrominated diphenyl ethers and perfluoroalkyl substances in a remote population of Alaska Natives. Environ Pollut. 2017;231:387–395. doi: 10.1016/j.envpol.2017.08.020 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [60].Dassuncao C, Hu XC, Nielsen F, et al. Shifting global exposures to poly- and perfluoroalkyl substances (PFAS) evident in longitudinal birth cohorts from a seafood-consuming population. Environ Sci Technol. 2018;52(6):3738–3747. doi: 10.1021/acs.est.7b06044 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [61].Hjermitslev MH, Long M, Wielsøe M, et al. Persistent organic pollutants in Greenlandic pregnant women and indices of foetal growth: the ACCEPT study. Sci Total Environ. 2020;698:134118. doi: 10.1016/j.scitotenv.2019.134118 [DOI] [PubMed] [Google Scholar]
  • [62].Laird B, Ratelle M. Personal communication. In: School of Public Health and Health Systems, Faculty of Applied Health. Waterloo, Canada: University of Waterloo; 2019. As reported in AMAP (2021). [Google Scholar]
  • [63].Lemire M, Blanchette C. Personal communication. Axe santé des populations et pratiques optimales en santé, Centre de recherche du CHU de Québec –. Université Laval, Canada; 2019. As reported in AMAP (2021a). [Google Scholar]
  • [64].Lemire M, Blanchette C. Personal communication. Axe santé des populations et pratiques optimales en santé, Centre de recherche du CHU de Québec –. Université Laval, Canada; 2020. As reported in AMAP (2021a). [Google Scholar]
  • [65].Lenters V, Portengen L, Rignell-Hydbom A, et al. Prenatal phthalate, perfluoroalkyl acid, and organochlorine exposures and term birth weight in three birth cohorts: multi-pollutant models based on elastic net regression. Environ Health Perspect. 2016;124(3):365–372. doi: 10.1289/ehp.1408933 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [66].Lindh CH, Rylander L, Toft G, et al. Blood serum concentrations of perfluorinated compounds in men from Greenlandic Inuit and European populations. Chemosphere. 2012;88(11):1269–1275. doi: 10.1016/j.chemosphere.2012.03.049 [DOI] [PubMed] [Google Scholar]
  • [67].Livsmedelsverket and Naturvårdsverket . Contaminants in blood and urine from adolescents in Sweden. Results from the national dietary survey Riksmaten Adolescents 2016–17. 2020. Livsmedelsverket, Naturvårdsverket. S 2020 nr 01.
  • [68].Mogensen UB, Grandjean P, Nielsen F, et al. Breastfeeding as an exposure pathway for perfluorinated alkylates. Environ Sci Technol. 2015;49(17):10466–10473. doi: 10.1021/acs.est.5b02237 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [69].Ólafsdóttir K. Personal communication. Department of Pharmacology and Toxicology. Reykjavik, Iceland: University of Iceland; 2019. As reported in AMAP (2021a). [Google Scholar]
  • [70].Oulhote Y, Shamin Z, Kielsen K, et al. Children’s white blood cell counts in relation to developmental exposures to methylmercury and persistent organic pollutants. Reprod Toxicol. 2017;68:207–214. doi: 10.1016/j.reprotox.2016.08.001 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [71].Papadopoulou E, Haug LS, Sabaredzovic A, et al. Reliability of perfluoroalkyl substances in plasma of 100 women in two consecutive pregnancies. Environ Res. 2015;140:421–429. doi: 10.1016/j.envres.2015.04.022 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [72].Petersen MS. Personal communication. Department of Occupational Medicine and Public Health, The Faroese Hospital System. 2019, Tórshavn, Faroe Islands. As reported in AMAP (2021a).
  • [73].Poothong S, Thomsen C, Padilla-Sanchez JA, et al. Distribution of novel and well-known poly- and perfluoroalkyl substances (PFAS) in human serum, plasma, and whole blood. Environ Sci Technol. 2017;51(22):13388–13396. doi: 10.1021/acs.est.7b03299 [DOI] [PubMed] [Google Scholar]
  • [74].Timmermann CAG, Pedersen HS, Budtz-JØrgensen E, et al. Environmental chemical exposures among Greenlandic children in relation to diet and residence. Int J Circumpolar Health. 2019;78(1):1642090. doi: 10.1080/22423982.2019.1642090 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [75].Brokken LJ, Lundberg PJ, Spanò M, et al. Interactions between polymorphisms in the aryl hydrocarbon receptor signalling pathway and exposure to persistent organochlorine pollutants affect human semen quality. Reprod Toxicol. 2014;49:65–73. doi: 10.1016/j.reprotox.2014.07.073 [DOI] [PubMed] [Google Scholar]
  • [76].Consales C, Toft G, Leter G, et al. Exposure to persistent organic pollutants and sperm DNA methylation changes in Arctic and European populations. Environ Mol Mutagen. 2016;57(3):200–209. doi: 10.1002/em.21994 [DOI] [PubMed] [Google Scholar]
  • [77].Fumagalli M, Moltke I, Grarup N, et al. Greenlandic Inuit show genetic signatures of diet and climate adaptation. Science. 2015;349(6254):1343–1347. doi: 10.1126/science.aab2319 [DOI] [PubMed] [Google Scholar]
  • [78].Goldman SM, Tanner CM, Trimble B, et al. Genetic and gene-environment associations with Parkinson’s disease (PD) in an Alaska native population. Mov Disord. 2015;30(Suppl. 1):S435–S436. [Google Scholar]
  • [79].Goldman S, Kamel F, Meng C, et al. Polychlorinated biphenyls (PCBs) and Parkinson’s disease (PD): Effect modification by membrane transporter variants. Neurology. 2016;86(16 Supplement):S32.004. doi: 10.1212/WNL.86.16_supplement.S32.004 [DOI] [Google Scholar]
  • [80].Kummu M, Sieppi E, Koponen J, et al. Organic anion transporter 4 (OAT 4) modifies placental transfer of perfluorinated alkyl acids PFOS and PFOA in human placental ex vivo perfusion system. Placenta. 2015;36(10):1185–1191. doi: 10.1016/j.placenta.2015.07.119 [DOI] [PubMed] [Google Scholar]
  • [81].Leter G, Consales C, Eleuteri P, et al. Exposure to perfluoroalkyl substances and sperm DNA global methylation in Arctic and European populations. Environ Mol Mutagen. 2014;55(7):591–600. doi: 10.1002/em.21874 [DOI] [PubMed] [Google Scholar]
  • [82].Leung YK, Ouyang B, Niu L, et al. Identification of sex-specific DNA methylation changes driven by specific chemicals in cord blood in a Faroese birth cohort. Epigenetics. 2018;13(3):290–300. doi: 10.1080/15592294.2018.1445901 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [83].Parajuli RP, Goodrich JM, Chan LHM, et al. Genetic polymorphisms are associated with exposure biomarkers for metals and persistent organic pollutants among Inuit from the Inuvialuit Settlement Region, Canada. Sci Total Environ. 2018;634:569–578. doi: 10.1016/j.scitotenv.2018.03.331 [DOI] [PubMed] [Google Scholar]
  • [84].Pilsner JR, Shershebnev A, Medvedeva YA, et al. Peripubertal serum dioxin concentrations and subsequent sperm methylome profiles of young Russian adults. Reprod Toxicol. 2018;78:40–49. doi: 10.1016/j.reprotox.2018.03.007 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [85].Skotte L, Koch A, Yakimov V, et al. CPT1A missense mutation associated with fatty acid metabolism and reduced height in Greenlanders. Circ, Cardiovasc Genet. 2017;10(3):e001618. doi: 10.1161/CIRCGENETICS.116.001618 [DOI] [PubMed] [Google Scholar]
  • [86].Wielsøe M, Eiberg H, Ghisari M, et al. Genetic variations, exposure to persistent organic pollutants and breast cancer risk - a Greenlandic case-control study. Basic Clin Pharmacol Toxicol. 2018;123:335–346. [DOI] [PubMed] [Google Scholar]
  • [87].Hu XF, Laird BD, Chan HM. Mercury diminishes the cardiovascular protective effect of omega-3 polyunsaturated fatty acids in the modern diet of Inuit in Canada. Environ Res. 2017;152:470–477. doi: 10.1016/j.envres.2016.06.001 [DOI] [PubMed] [Google Scholar]
  • [88].Larsen TJ, Jørgensen ME, Larsen CVL, et al. Whole blood mercury and the risk of cardiovascular disease among the Greenlandic population. Environ Res. 2018;164:310–315. doi: 10.1016/j.envres.2018.03.003 [DOI] [PubMed] [Google Scholar]
  • [89].Tajik B, Kurl S, Tuomainen TP, et al. Associations of the serum long-chain omega-3 polyunsaturated fatty acids and hair mercury with heart rate-corrected QT and JT intervals in men: the Kuopio Ischaemic Heart Disease Risk Factor Study. Eur J Nutr. 2017;56(7):2319–2327. doi: 10.1007/s00394-016-1272-3 [DOI] [PubMed] [Google Scholar]
  • [90].Tajik B, Kurl S, Tuomainen TP, et al. Associations of the serum long-chain n-3 PUFA and hair mercury with resting heart rate, peak heart rate during exercise and heart rate recovery after exercise in middle-aged men. Br J Nutr. 2018;119(1):66–73. doi: 10.1017/S0007114517003191 [DOI] [PubMed] [Google Scholar]
  • [91].Turunen AW, Jula A, Suominen AL, et al. Fish consumption, omega-3 fatty acids, and environmental contaminants in relation to low-grade inflammation and early atherosclerosis. Environ Res. 2013;120:43–54. doi: 10.1016/j.envres.2012.09.007 [DOI] [PubMed] [Google Scholar]
  • [92].Valera B, Dewailly E, Poirier P. Association between methylmercury and cardiovascular risk factors in a native population of Quebec (Canada): a retrospective evaluation. Environ Res. 2013;120:102–108. doi: 10.1016/j.envres.2012.08.002 [DOI] [PubMed] [Google Scholar]
  • [93].Valera B, Jørgensen ME, Jeppesen C, et al. Exposure to persistent organic pollutants and risk of hypertension among Inuit from Greenland. Environ Res. 2013;122:65–73. doi: 10.1016/j.envres.2012.12.006 [DOI] [PubMed] [Google Scholar]
  • [94].Caspersen IH, Asse H, Biele G, et al. The influence of maternal dietary exposure to dioxins and PCBs during pregnancy on ADHD symptoms and cognitive functions in Norwegian preschool children. Environ Int. 2016;94:649–660. doi: 10.1016/j.envint.2016.06.033 [DOI] [PubMed] [Google Scholar]
  • [95].Høyer BB, Ramlau-Hansen CH, Obel C, et al. Pregnancy serum concentrations of perfluorinated alkyl substances and offspring behaviour and motor development at age 5–9 years – a prospective study. Environ Health. 2015;14(1):069X-14–2. doi: 10.1186/1476-069X-14-2 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [96].Høyer BB, Ramlau-Hansen CH, Pedersen HS, et al. Motor development following in utero exposure to organochlorines: a follow-up study of children aged 5–9 years in Greenland, Ukraine and Poland. BMC Public Health. 2015;15(1):146. doi: 10.1186/s12889-015-1465-3 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [97].Høyer BB, Bonde JP, Tøttenborg SS, et al. Exposure to perfluoroalkyl substances during pregnancy and child behaviour at 5 to 9 years of age. Horm Behav. 2018;101:105–112. doi: 10.1016/j.yhbeh.2017.11.007 [DOI] [PubMed] [Google Scholar]
  • [98].Oulhote Y, Steuerwald U, Debes F, et al. Behavioral difficulties in 7-year old children in relation to developmental exposure to perfluorinated alkyl substances. Environ Int. 2016;97:237–245. doi: 10.1016/j.envint.2016.09.015 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [99].Grandjean P, Heilmann C, Weihe P, et al. Serum vaccine antibody concentrations in adolescents exposed to perfluorinated compounds. Environ Health Perspect. 2017;125(7):077018. doi: 10.1289/EHP275 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [100].Grandjean P, Heilmann C, Weihe P, et al. Estimated exposures to perfluorinated compounds in infancy predict attenuated vaccine antibody concentrations at age 5-years. J Immunotoxicol. 2017;14(1):188–195. doi: 10.1080/1547691X.2017.1360968 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [101].Hansen S, Strøm M, Olsen SF, et al. Prenatal exposure to persistent organic pollutants and offspring allergic sensitization and lung function at 20 years of age. Clin Exp Allergy. 2016;46(2):329–336. doi: 10.1111/cea.12631 [DOI] [PubMed] [Google Scholar]
  • [102].Hansen S, Strøm M, Olsen SF, et al. Maternal concentrations of persistent organochlorine pollutants and the risk of asthma in offspring: results from a prospective cohort with 20 years of follow-up. Environ Health Perspect. 2014;122(1):93–99. doi: 10.1289/ehp.1206397 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [103].Osuna CE, Grandjean P, Weihe P, et al. Autoantibodies associated with prenatal and childhood exposure to environmental chemicals in Faroese children. Toxicological Sci. 2014;142(1):158–166. doi: 10.1093/toxsci/kfu163 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [104].Schaebel LK, Bonefeld-Jørgensen EC, Laurberg P, et al. Vitamin D-rich marine Inuit diet and markers of inflammation - a population-based survey in Greenland. J Nutr Sci. 2015;4:e40. doi: 10.1017/jns.2015.33 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [105].Schaebel LK, Bonefeld-Jørgensen EC, Vestergaard H, et al. The influence of persistent organic pollutants in the traditional Inuit diet on markers of inflammation. PLOS ONE. 2017;12(5):e0177781. doi: 10.1371/journal.pone.0177781 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [106].Timmermann CA, Budtz-Jørgensen E, Jensen TK, et al. Association between perfluoroalkyl substance exposure and asthma and allergic disease in children as modified by MMR vaccination. J Immunotoxicol. 2017;14(1):39–49. doi: 10.1080/1547691X.2016.1254306 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [107].Bank-Nielsen PI, Long M, Bonefeld-JØrgensen EC. Pregnant Inuit Women’s Exposure to Metals and Association with Fetal Growth Outcomes: ACCEPT 2010–2015. Int J Environ Res Public Health. 2019;16(7):1171. doi: 10.3390/ijerph16071171 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [108].Criswell R, Lenters V, Mandal S, et al. Persistent environmental toxicants in breast milk and rapid infant growth. Ann Nutr Metab. 2017;70(3):210–216. doi: 10.1159/000463394 [DOI] [PubMed] [Google Scholar]
  • [109].Jørgensen KT, Specht IO, Lenters V, et al. Perfluoroalkyl substances and time to pregnancy in couples from Greenland, Poland and Ukraine. Environ Health. 2014;13(1):116. doi: 10.1186/1476-069X-13-116 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [110].Kvist L, Giwercman A, Weihe P, et al. Exposure to persistent organic pollutants and sperm sex chromosome ratio in men from the Faroe Islands. Environ Int. 2014;73:359–364. doi: 10.1016/j.envint.2014.09.001 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [111].Lenters V, Portengen L, Smit LA, et al. Phthalates, perfluoroalkyl acids, metals and organochlorines and reproductive function: a multipollutant assessment in Greenlandic, Polish and Ukrainian men. Occup Environ Med. 2015;72(6):385–393. doi: 10.1136/oemed-2014-102264 [DOI] [PubMed] [Google Scholar]
  • [112].Minguez-Alarcon L, Sergeyev O, Burns JS, et al. A longitudinal study of peripubertal serum organochlorine concentrations and semen parameters in young men: the Russian children’s study. Environ Health Perspect. 2017;125(3):460–466. doi: 10.1289/EHP25 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [113].Perry MJ, Young HA, Grandjean P, et al. Sperm aneuploidy in Faroese men with lifetime exposure to dichlorodiphenyldichloroethylene (p,p´-DDE) and polychlorinated biphenyl (PCB) pollutants. Environ Health Perspect. 2016;124(7):951–956. doi: 10.1289/ehp.1509779 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [114].Petersen MS, Halling J, Weihe P, et al. Spermatogenic capacity in fertile men with elevated exposure to polychlorinated biphenyls. Environ Res. 2015;138:345–351. doi: 10.1016/j.envres.2015.02.030 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [115].Petersen MS, Halling J, Jørgensen N, et al. Reproductive function in a population of young Faroese men with elevated exposure to polychlorinated biphenyls (PCBs) and perfluorinated alkylate substances (PFAS). Int J Environ Res Public Health. 2018;15(9):1880. doi: 10.3390/ijerph15091880 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [116].Specht IO, Toft G, Hougaard KS, et al. Associations between serum phthalates and biomarkers of reproductive function in 589 adult men. Environ Int. 2014;66:146–156. doi: 10.1016/j.envint.2014.02.002 [DOI] [PubMed] [Google Scholar]
  • [117].Specht IO, Bonde JPE, Toft G, et al. Environmental hexachlorobenzene exposure and human male reproductive function. Reprod Toxicol. 2015;58:8–14. doi: 10.1016/j.reprotox.2015.07.074 [DOI] [PubMed] [Google Scholar]
  • [118].Stigum H, Iszatt N, Polder A, et al. A novel model to characterize postnatal exposure to lipophilic environmental toxicants and application in the study of hexachlorobenzene and infant growth. Environ Int. 2015;85:156–162. doi: 10.1016/j.envint.2015.08.011 [DOI] [PubMed] [Google Scholar]
  • [119].Timmermann CAG, Choi AL, Petersen MS, et al. Secondary sex ratio in relation to exposures to polychlorinated biphenyls, dichlorodiphenyl dichloroethylene and methylmercury. Int J Circumpolar Health. 2017;76(1):1406234. doi: 10.1080/22423982.2017.1406234 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [120].Toft G, Lenters V, Vermeulen R, et al. Exposure to polybrominated diphenyl ethers and male reproductive function in Greenland, Poland and Ukraine. Reprod Toxicol. 2014;43:1–7. doi: 10.1016/j.reprotox.2013.10.002 [DOI] [PubMed] [Google Scholar]
  • [121].Vesterholm Jensen D, Christensen J, Virtanen HE, et al. No association between exposure to perfluorinated compounds and congenital cryptorchidism: a nested case–control study among 215 boys from Denmark and Finland. Reproduction. 2014;147(4):411–417. doi: 10.1530/REP-13-0444 [DOI] [PubMed] [Google Scholar]
  • [122].Whitworth KW, Haug LS, Sabaredzovic A, et al. Brief report: Plasma concentrations of perfluorooctane sulfonamide and time-to-pregnancy among primiparous women. Epidemiology. 2016;27(5):712–715. doi: 10.1097/EDE.0000000000000524 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [123].Berg V, Nøst TH, Pettersen RD, et al. Persistent organic pollutants and the association with maternal and infant thyroid homeostasis: a multipollutant assessment. Environ Health Perspect. 2017;125(1):127–133. doi: 10.1289/EHP152 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [124].Berg V, Nøst TH, Skeie G, et al. Thyroid homeostasis in mother–child pairs in relation to maternal iodine status: the MISA study. Eur J Clin Nutr. 2017;71(8):1002–1007. doi: 10.1038/ejcn.2017.83 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [125].Berg V, Nøst TH, Hansen S, et al. Assessing the relationship between perfluoroalkyl substances, thyroid hormones and binding proteins in pregnant women; a longitudinal mixed effects approach. Environ Int. 2015;77:63–69. doi: 10.1016/j.envint.2015.01.007 [DOI] [PubMed] [Google Scholar]
  • [126].Byrne SC, Miller P, Seguinot-Medina S, et al. Exposure to perfluoroalkyl substances and associations with serum thyroid hormones in a remote population of Alaska Natives. Environ Res. 2018;166:537–543. doi: 10.1016/j.envres.2018.06.014 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [127].Byrne SC, Miller P, Seguinot-Medina S, et al. Associations between serum polybrominated diphenyl ethers and thyroid hormones in a cross sectional study of a remote Alaska Native population. Sci Rep. 2018;8(1):2198. doi: 10.1038/s41598-018-20443-9 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [128].de Cock M, de Boer MR, Govarts E, et al. Thyroid-stimulating hormone levels in newborns and early life exposure to endocrine-disrupting chemicals: analysis of three European mother–child cohorts. Pediatr Res. 2017;82(3):429–437. doi: 10.1038/pr.2017.50 [DOI] [PubMed] [Google Scholar]
  • [129].Engel SM, Villanger GD, Nethery RC, et al. Prenatal phthalates, maternal thyroid function, and risk of attention deficit hyperactivity disorder in the Norwegian Mother and Child Cohort. Environ Health Perspect. 2018;126(5):057004. doi: 10.1289/EHP2358 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [130].Hansen AF, Simić A, Åsvold BO, et al. Trace elements in early phase type 2 diabetes mellitus-A population-based study. The HUNT study in Norway. J Trace Elem Med Biol. 2017;40:46–53. doi: 10.1016/j.jtemb.2016.12.008 [DOI] [PubMed] [Google Scholar]
  • [131].Høyer BB, Ramlau-Hansen CH, Vrijheid M, et al. Anthropometry in 5- to 9-year-old Greenlandic and Ukrainian children in relation to prenatal exposure to perfluorinated alkyl substances. Environ Health Perspect. 2015;123(8):841–846. doi: 10.1289/ehp.1408881 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [132].Høyer BB, Ramlau-Hansen CH, Henriksen TB, et al. Body mass index in young school-age children in relation to organochlorine compounds in early life: a prospective study. Int J Obes. 2014;38(7):919–925. doi: 10.1038/ijo.2014.58 [DOI] [PubMed] [Google Scholar]
  • [133].Iszatt N, Stigum H, Govarts E, et al. Perinatal exposure to dioxins and dioxin-like compounds and infant growth and body mass index at seven years: A pooled analysis of three European birth cohorts. Environ Int. 2016;94:399–407. doi: 10.1016/j.envint.2016.04.040 [DOI] [PubMed] [Google Scholar]
  • [134].Jeppesen C, Valera B, Nielsen NO, et al. Association between whole blood mercury and glucose intolerance among adult Inuit in Greenland. Environ Res. 2015;143(Pt A):192–197. doi: 10.1016/j.envres.2015.10.013 [DOI] [PubMed] [Google Scholar]
  • [135].Jeppesen C, Bjerregaard P, Jørgensen ME. Dietary patterns in Greenland and their relationship with type 2 diabetes mellitus and glucose intolerance. Public Health Nutr. 2014;17(2):462–470. doi: 10.1017/S136898001300013X [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [136].Karlsen M, Grandjean P, Weihe P, et al. Early-life exposures to persistent organic pollutants in relation to overweight in preschool children. Reprod Toxicol. 2017;68:145–153. doi: 10.1016/j.reprotox.2016.08.002 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [137].Lauritzen HB, Larose TL, Øien T, et al. Prenatal exposure to persistent organic pollutants and child overweight/obesity at 5-year follow-up: a prospective cohort study. Environ Health. 2018;17(1):9. doi: 10.1186/s12940-017-0338-x [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [138].Rantakokko P, Männistö V, Airaksinen R, et al. Persistent organic pollutants and non-alcoholic fatty liver disease in morbidly obese patients: a cohort study. Environ Health. 2015;14(1):79. doi: 10.1186/s12940-015-0066-z [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [139].Tang-Péronard JL, Jensen TK, Andersen HR, et al. Associations between exposure to persistent organic pollutants in childhood and overweight up to 12 years later in a low exposed Danish population. Obes Facts. 2015;8(4):282–292. doi: 10.1159/000438834 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [140].Tang-Péronard JL, Heitmann BL, Jensen TK, et al. Prenatal exposure to persistent organochlorine pollutants is associated with high insulin levels in 5-year-old girls. Environ Res. 2015;142:407–413. doi: 10.1016/j.envres.2015.07.009 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [141].Tang-Péronard JL, Heitmann BL, Andersen HR, et al. Association between prenatal polychlorinated biphenyl exposure and obesity development at ages 5 and 7 y: a prospective cohort study of 656 children from the Faroe Islands. Am J Clin nutr. 2014;99(1):5–13. doi: 10.3945/ajcn.113.066720 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [142].Valvi D, Oulhote Y, Weihe P, et al. Gestational diabetes and offspring birth size at elevated environmental pollutant exposures. Environ Int. 2017;107:205–215. doi: 10.1016/j.envint.2017.07.016 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [143].Virtanen JK, Mursu J, Voutilainen S, et al. Serum omega-3 polyunsaturated fatty acids and risk of incident type 2 diabetes in men: the Kuopio Ischemic Heart Disease Risk Factor study. Diabetes Care. 2014;37(1):189–196. doi: 10.2337/dc13-1504 [DOI] [PubMed] [Google Scholar]
  • [144].Yary T, Virtanen JK, Ruusunen A, et al. Serum zinc and risk of type 2 diabetes incidence in men: The Kuopio Ischaemic Heart Disease Risk Factor Study. J Trace Elem Med Biol. 2016;33:120–124. doi: 10.1016/j.jtemb.2015.11.001 [DOI] [PubMed] [Google Scholar]
  • [145].Ali I, Julin B, Glynn A, et al. Exposure to polychlorinated biphenyls and prostate cancer: population-based prospective cohort and experimental studies. Carcinogenesis. 2016;37:1144–1151. doi: 10.1093/carcin/bgw105 [DOI] [PubMed] [Google Scholar]
  • [146].Gaudet MM, Deubler EL, Kelly RS, et al. Blood levels of cadmium and lead in relation to breast cancer risk in three prospective cohorts. Int J Cancer. 2019;144(5):1010–1016. doi: 10.1002/ijc.31805 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [147].Holmes AK, Koller KR, Kieszak SM, et al. Case–control study of breast cancer and exposure to synthetic environmental chemicals among Alaska Native women. Int J Circumpolar Health. 2014;73(1):25760. doi: 10.3402/ijch.v73.25760 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [148].Koutros S, Langseth H, Grimsrud TK, et al. Prediagnostic Serum Organochlorine Concentrations and Metastatic Prostate Cancer: A Nested Case–Control Study in the Norwegian Janus Serum Bank Cohort. Environ Health Perspect. 2015;123(9):867–872. doi: 10.1289/ehp.1408245 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [149].Tsyrlov I, Konenkov V. HBV-linked chronic inflammation and hepatocellular carcinomas in Arctic natives might be triggered by elevated body burden dioxin. J Viral Hepat. 2015;22(Suppl. S3):39–40. [Google Scholar]
  • [150].Wielsøe M, Bjerregaard-Olesen C, Kern P, et al. Receptor activities of persistent pollutant serum mixtures and breast cancer risk. Endocr Relat Cancer. 2018;25(3):201–215. doi: 10.1530/ERC-17-0366 [DOI] [PubMed] [Google Scholar]
  • [151].Wielsøe M, Kern P, Bonefeld-Jørgensen EC. Serum levels of environmental pollutants is a risk factor for breast cancer in Inuit: a case control study. Environ Health. 2017;16(1):56. doi: 10.1186/s12940-017-0269-6 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [152].UNEP/AMAP . Climate change and POPs: predicting the impacts. Report of the UNEP/AMAP expert group. Secretariat of the stockholm convention. U Nations Environ Programme (UNEP) / Arct Monit and Assess Programme (AMAP). 2011. [Google Scholar]
  • [153].Carlsson P, Breivik K, Brorström-Lundén E, et al. Polychlorinated biphenyls (PCBs) as sentinels for the elucidation of Arctic environmental change processes: a comprehensive review combined with ArcRisk project results. Environ Sci Pollut Res Int. 2018;25(23):22499–22528. doi: 10.1007/s11356-018-2625-7 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [154].Sundseth K, Pacyna JM, Banel A, et al. Climate change impacts on environmental and human exposure to mercury in the Arctic. Int J Environ Res Public Health. 2015;12(4):3579–3599. doi: 10.3390/ijerph120403579 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [155].ACIA . Impacts of a Warming Arctic: Arctic Climate Impact Assessment. ACIA Overview report. Cambridge University Press; 2004. [Google Scholar]
  • [156].Parkinson JA, Bruce MG, Zulz Y. International circumpolar surveillance, an Arctic network for the surveillance of infectious diseases. Emerg Infect Dis. 2008;14(1):18–24. doi: 10.3201/eid1401.070717 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [157].Vesterinen HM, Cutcher TV, Errecaborde KM, et al. Strengthening multi-sectoral collaboration on critical health issues: One Health Systems Mapping and Analysis Resource toolkit (OH-SMART) for operationalizing One health. PLOS ONE. 2019;14(7):e0219197. doi: 10.1371/journal.pone.0219197 [DOI] [PMC free article] [PubMed] [Google Scholar]

Articles from International Journal of Circumpolar Health are provided here courtesy of Taylor & Francis

RESOURCES