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Widening the Scope of Responses to Environmental Concerns in the High North: Arctic Countries' Policies and the Role of China

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With the progressing exploration of the Arctic as a resource base and trade corridor between the continents, the region is experiencing changes that fundamentally affect the environment, biodiversity, and people. The once established patterns are transforming and bringing new potential risks to the sustainable development of the region. Due to the industrialization in many northern territories, air, water, and soil pollution have been emerging as threats to ecosystems and public health. For those countries that now launch industrial projects in the Arctic, there is a challenge of how to converge the economic benefits with the urgent need for environmental protection. In this chapter, the authors review current policies and potential responses to environmental challenges contained in the national development strategies of Canada, Denmark, Finland, Iceland, Norway, Russia, Sweden, and the USA. Among non-Arctic countries, China has emerged as one of the prominent actors in the region, including in the spheres of industrial development and shipping. Other countries also show ever-deeper environmental concerns, but progressing climate change in the High North is not an issue to be solved by any country acting alone. It is of emerging global concern with the broader community of Arctic and non-Arctic countries having a mutual interest in cooperation to ensure the protection of fragile ecosystems and sustainable development of the region. Using China as an example, the authors discuss how non-Arctic states may contribute to the solution of environmental problems in the High North. The study analyses existing international and national approaches to environmental protection and climate change issues in the Arctic. It discusses how varying interests of Arctic states, from one side, and China, from the other, could be translated into effective international policies for the benefit of sustainable development of the region.
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Gao Tianming is a Professor at the School of Economics and Management, and the Director and Chief
Expert at the Arctic Blue Economy Research Center, and Vasilii Erokhin is an Associate Professor, School
of Economics and Management, and a Researcher at the Arctic Blue Economy Research Center, both at
Harbin Engineering University, China.
Widening the Scope of Responses to Environmental
Concerns in the High North:
Arctic Countries’ Policies and the Role of China
Gao Tianming & Vasilii Erokhin
With the progressing exploration of the Arctic as a resource base and trade corridor between the continents, the region is
experiencing changes that fundamentally affect the environment, biodiversity, and people. The once established patterns are
transforming and bringing new potential risks to the sustainable development of the region. Due to the industrialization in
many northern territories, air, water, and soil pollution have been emerging as threats to ecosystems and public health. For
those countries that now launch industrial projects in the Arctic, there is a challenge of how to converge the economic benefits
with the urgent need for environmental protection. In this chapter, the authors review current policies and potential responses to
environmental challenges contained in the national development strategies of Canada, Denmark, Finland, Iceland, Norway,
Russia, Sweden, and the USA. Among non-Arctic countries, China has emerged as one of the prominent actors in the region,
including in the spheres of industrial development and shipping. Other countries also show ever-deeper environmental concerns,
but progressing climate change in the High North is not an issue to be solved by any country acting alone. It is of emerging
global concern with the broader community of Arctic and non-Arctic countries having a mutual interest in cooperation to ensure
the protection of fragile ecosystems and sustainable development of the region. Using China as an example, the authors discuss
how non-Arctic states may contribute to the solution of environmental problems in the High North. The study analyses existing
international and national approaches to environmental protection and climate change issues in the Arctic. It discusses how
varying interests of Arctic states, from one side, and China, from the other, could be translated into effective international
policies for the benefit of sustainable development of the region.
Introduction
The Arctic is changing in many ways with the climate being one of the most dramatic
transformations in the past years. According to the Arctic Monitoring and Assessment Programme
[AMAP] (2019), the annual average Arctic surface air temperature has increased by 2.7°C since
1971 (AMAP, 2019: 3), while the September average volume of sea ice has declined by 75% since
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1979 (AMAP, 2019: 4). Climate change in the Arctic is largely related to global warming, the latter
being triggered by air pollution (Norkina & Van Canegem, 2020). In terms of various
anthropogenic emissions, the world’s biggest contributor to climate change is China with 27% of
global emissions of greenhouse gas (Olivier & Peters, 2018) and about 20-24% of global emissions
of black carbon (United Nations Environment Programme [UNEP], 2015).
Although it is difficult to assess the amount of pollution coming to the Arctic specifically from
China (Kopra et al., 2020), it is clear that progressing warming may result in a reduction in the area
and thickness of sea ice, melting of permafrost, shifting boundaries of the forest zone,
transformation of ecosystems, and degradation of landscapes. Due to excessive air pollution,
chemicals accumulate intensively in the trophic chains of terrestrial and aquatic Arctic ecosystems
and are concentrated in the bodies of long-lived carnivorous mammals, birds, and fish. This creates
prerequisites for the long-term effects of chemical pollution in Arctic ecosystems, including the
death of offspring, the reduction or extinction of populations, and the depletion of fauna.
Currently, the critical pollutants in the trophic chains of the Arctic ecosystems are organochlorine
hydrocarbons. They are herbicides, insecticides, fungicides, and industrial chemicals (carbon,
chlorine, and other products of transformations occurring in technological processes and side
reactions in the environment) that disrupt the hormone balance of animals, birds, and aquatic
organisms (Rosińska, 2019; Macías-Zamora, 2011). Bioaccumulation of such contaminants is
associated with ocean pollution, long-range transboundary air pollution, aerosol deposition, as well
as bird migrations. Arctic ecosystems are highly susceptible to global and regional transport of
substances. Global pollution is primarily associated with the Gulf Stream, river flow, and
atmospheric transport. Regional ones have their specifics in each country, but in general, they are
the consequences of toxicant emissions by industrial enterprises, shipping, military and industrial
waste, oil and gas production in coastal areas, as well as the exploration and development of oil
and gas fields.
For over a decade by now, China has been actively implementing various domestic policies to
reduce the growth of emissions of greenhouse gases and other pollutants. The Greenhouse Gas
Emission Reduction Plan (China Briefing, 2012) aimed to reduce the amount of carbon emitted
per unit of GDP by 17% by 2015 compared with 2010. China has taken part in a variety of
international negotiations and partnerships on climate change, including the United Nations
Framework Convention on Climate Change, the Kyoto Protocol, and the Paris Agreement
(Koivurova et al., 2019). In 2016, China ratified the Kigali Amendment to the Montreal Protocol
aiming to reduce the climate impact of hydrofluorocarbon gases (Science Daily, 2020). In 2018,
China introduced an action plan to meet “ultra-low emission” standards in steel production (China
Power, 2020). The power grid system has been actively transitioning to the use of natural gas
instead of coal. Furthermore, China has made serious efforts to develop its renewable energy
sector. As a result of these actions, by 2018, China had managed to reduce carbon intensity by
45% and raise the share of non-fossil fuel energy sources to 15% compared to 2005 levels (China
Power, 2020).
Despite the efforts on reducing emissions of greenhouse gases, persistent organic pollutants, and
other climate change forcers, Chinese companies have been blamed for negatively affecting Arctic
habitats, including in Greenland, Russia, northern Europe, and Canada (Sidorov, 2018; Lajeunesse,
2018; Erokhin et al., 2019; Kopra et al., 2020). The increasing shipping activities of Chinese
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operators in the Arctic Ocean are also viewed as a threat to marine ecosystems and air quality in
the Arctic (Kopra et al., 2020). Among the risks are oil spills, emissions of pollutants into the air
and water, oil spills during loading, unloading, bunkering, or as a result of emergencies. In its Arctic
policy, China advocates stronger international cooperation in environmental protection, energy
conservation, emissions reduction, low-carbon development, and tackling climate change in the
Arctic (State Council of the People’s Republic of China, 2018: article IV.4). However, the
development and implementation of such cooperation should take into account both the global
challenges of controlling climate change in the Arctic and individual priorities of Arctic countries
(as well as China itself) in concentrating their efforts and resources in certain areas of the
environmental agenda. This chapter aims to address major environmental problems in the Arctic
across the spheres of climate change, industrial pollution, shipping, living resources, and habitats
and populations of various species of flora and fauna. The authors explore how the international
community in general and Arctic countries in particular approach to responding to the above-
mentioned environmental problems in their strategies, policies, and regulations. The article
concludes with an analysis of intersections between China’s and Arctic countries’ priorities in
environmental protection and climate change responses in the Arctic.
Major environmental challenges in the Arctic
According to the United Nations Environment Program (UNEP) (n.d.), the environmental
problems of the Arctic are grouped into several main areas: oil pollution of the Arctic seas; climate
change leading to ice melting; extensive fishing and seafood production; changes in the habitat of
flora and fauna and reduction of animals’ populations; and intensive shipping. These five points
are detailed in the following sections.
Oil spills and industrial pollution
Arctic territories and offshore waters of the Arctic Ocean seas are increasingly being developed by
oil-and-gas and other resource companies (Blaauw, 2013; Batin et al., 2015). In many regions,
especially in the Russian sector of the Arctic as the most developed in industrial terms, negative
environmental processes lead to the transformation of the natural geochemical background,
atmospheric pollution, degradation of vegetation, soil pollution, and introduction of harmful
substances in food chains. Industrial pollution in the Arctic affects the safety of the river and
marine ecosystems, as well as the health of Indigenous populations. Only with river runoff, several
hundred thousand tons of oil products are taken out to the Arctic Ocean annually. This problem
is particularly critical in Russia, where intensive resource development projects are being carried
out. Air masses from the continent are transported to the High North, bringing nitrogen and sulfur
oxides. Acid rains negatively affect the health of people and animals.
In a cold climate, the risk of accidents increases significantly whereas the possibilities for the
elimination of consequences decrease (Fadeev, 2012). On the Arctic Ocean shelf, even a small leak
of hydrocarbons into ice-covered water areas can lead to significant environmental damage. On
May 29, 2020, in Norilsk, Russia, there occurred a spill of over 20,000 tons of diesel fuel, with part
of it flowing into the Ambarnaya and Daldykan rivers. According to Greenpeace (2020), this is
one of the most massive environmental disasters in the Arctic in the past few decades. It is
comparable in scale and consequences with the accident that occurred in 1989 off the coast of
Alaska when the wreck of the Exxon Valdez tanker spilled 37,000 tons of fuel into the ocean. In
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Norilsk, the pollution covered the total area of 180,000 square meters. The damage is estimated at
$86 million, while it is still difficult to assess the long-term impact caused to the soil and air. Diesel
fuel is more toxic than oil and contains chemical compounds that are not captured by treatment
facilities. According to Knizhnikov (RBC, 2020), Blokov (Greenpeace, 2020), and some Russian
environmental experts working at the site of the accident, the diesel will dissolve in the water,
remaining there for a long time. In a cold climate, where nature is slower to respond to oil spills,
the effects of the latter on the environment may be observed for years, causing permanent losses
of fish and other aquatic organisms and thus degrading traditional sources of the food supply in
Indigenous communities in the long run.
There is growing evidence of contamination from industrial pollution in the Arctic (Davis, 1996;
Macdonald et al., 2000; Kurgankina et al., 2020). The ecosystems are affected by the emissions and
effluents from industrial enterprises and public utilities (Arnold et al., 2016; Law et al., 2017; Recio-
Garrido et al., 2018), products of hydrocarbon processing (Fang et al., 2018), heavy metals and
other wastes from metallurgical production (Caputo et al., 2019; Khan et al., 2019), microplastics
and marine litter (Abate et al., 2020; Martinez et al., 2020), certain toxic substances (phenol,
ammonia, and others) (Lee et al., 2019; Skaar et al., 2019), numerous pollutants from military sites
(Koch et al., 2005; Brown et al., 2014; Hird, 2016), and waste from nuclear-powered vessels
(Sarkisov, 2019; Karcher et al., 2017; Huang et al., 2020). In conditions of ultra-low temperatures
and the shielding effect of permafrost, pollutants can have a long-term negative impact on peoples,
fauna, and flora.
Ice Melting
Climate changes observed in the Arctic in recent decades may lead to the reduction of the ice cover
and the expansion of the navigation window. According to the Intergovernmental Panel on
Climate Change (IPCC) (2013), the global average temperature increased by 0.85°C during 1880-
2012. In the polar regions, however, the increase has been much more noticeable, especially in
recent decades, reflecting new prospects for commercial cargo shipping and research due to
climate change (Cavalieri & Parkinson, 2012; Stroeve & Notz, 2015; Ng et al., 2018). Observations
show significant fluctuations in the ice cover across the Arctic Ocean (Landy et al., 2016; Tschudi
et al., 2016). In 1979-2019, the September minimum ice spread decreased significantly by 87.2
km2 or 13.3% every decade (National Snow and Ice Data Center [NSIDC], 2016). The record low
in September 2012 was 3.41 million km2, or just 54% of the average low in 1981-2010 (Liu et al.,
2016). In addition to the reduction of the spread of ice, Lindsay and Schweiger (2015) report an
increase in the proportion of thinner and younger ice in the overall structure of the Arctic Ocean
ice cover (Figure 1).
The average annual temperature in the Arctic is increasing, which affects the processes of ice
formation, growth, constancy, and movement throughout the year. Side processes are also
triggered, which have an equally noticeable and non-linear growing influence on the ice cover. For
example, melting ice increases the area of open water, which has a lower coefficient of reflection
of sunlight compared to ice. As a result, the absorption of solar heat in open water zones increases,
the surface water temperature increases, which causes a cyclical process of ice melting (Parkinson,
2014). This effect of global warming works both in seasonal and long-term perspectives: warming
of surface water layers postpones autumn freezing, thereby reducing the period of ice growth. As
a result, the next year, the ice layer is thinner and more prone to early splitting (Serreze & Barry,
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2011). However, despite the apparent relief of the ice situation occurring in the Arctic, it should
not be unambiguously identified with the improvement of conditions for shipping.
Figure 1. Ice distribution in the central part of the Arctic Ocean during peak periods (March) in 2009-2019
Note: light blue open water, bluenilas ice (0-10 cm), purplenewly-formed ice (10-30 cm), greenfirst-year ice
(30-200 cm), brown multi-year ice, gray fast ice.
Source: Authors’ development based on the Arctic and Antarctic Research Institute [AARI] (n.d.)
Dynamic forces affecting the ice or icebergs breaking off from glaciers pose serious risks to the
establishment of stable and secure shipping routes. In some zones of the Arctic Ocean,
dynamically deformed annual ice can reach 5-7 meters in thickness (Landy et al., 2016). This
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complicates or completely blocks the passage of vessels, especially in narrow straits. To the north
of Greenland and in the waters of the Canadian Arctic Archipelago, currents press ice, and the
thickness of the ice cover reaches the world’s maximums (Melling, 2002). Drifting ice is also a
danger. Due to the decrease in the thickness of the ice cover and its area, the ice becomes more
mobile, the speed of drift increases, and the behavior of the ice becomes more dynamic and less
predictable (Rampal et al., 2009).
Increase in marine fisheries
Ice melting frees up a significant part of the Arctic Ocean for fishing. During warmer seasons, fish
and other marine populations increase in the Barents, Norwegian, and Greenland seas. This applies
primarily to cod, haddock, perch, halibut, herring, whiting, and other species. At the same time,
their range is expanding in eastern and northern directions (Zilanov, 2015). Rayfuse (2019) warns
that an expansion of unregulated fishing may wipe out particular fish species or entire fish stock.
The extensive removal of fish from food chains may harm many species, including marine
mammals and birds. Improper monitoring and lack of international research may result in
overfishing of harvested species and may undermine the economic integrity of the ecosystem.
Diminishing fish stock in the Arctic seas may have a negative consequence for Indigenous peoples,
for whom fish and marine mammals are subjects of subsistence harvesting (Muir, 2010).
Regularly, fishing is carried out by Norway, Russia, Iceland, the Faroe Islands, Greenland, and
some of the EU countries. The central part of the Arctic Ocean is located outside the exclusive
economic zones of the five Arctic states (Canada, Denmark, Norway, Russia, and the USA) and is
thus considered as an open sea where any country can fish. In 2015, Canada, Denmark, Norway,
Russia, and the USA signed the Agreement to Prevent Unregulated High Seas Fisheries in the
Central Arctic Ocean (CAOFA). In 2018, the agreement was extended to include China, Japan,
South Korea, Iceland, and EU countries (EUR-Lex, 2018). According to the CAOFA, each signing
party allows vessels under its flag to conduct commercial fishing in the Central Arctic only in
accordance with measures for sustainable management of fish stocks taken by regional or sub-
regional fisheries management organizations. Taking into account the current lack of commercial
fishing in the central part of the Arctic Ocean (Schatz et al., 2019), there is no clear indication yet
as to the immediate success of the agreement. Moreover, the likelihood of the rapid growth of
commercial fisheries in the Central Arctic is low even in 2034 until when the CAOFA is valid.
Vylegzhanin et al. (2020) underline the reliance of the CAOFA on a precautionary approach, while
Rayfuse (2019) considers the agreement as “an initial framework for environmentally sound
decision making regarding the potential for future fisheries”. In a few years, it remains to be seen
whether the CAOFA is applied correctly by all signing parties and allowed to ensure the
conservation and sustainable use of fish stocks.
Habitat change and population decline
Rising sea level as a result of climate warming and ice melting leads to the desalination of surface
water and an increase in primary productivity of the Arctic seas. Besides, global warming triggers
the invasion of alien species into the northern ecosystems. As a result, the characteristics of the
habitats of both marine and land animals change. According to the Organization for Economic
Cooperation and Development (OECD) (2016), there are seven critical environmental threats to
marine ecosystems in the Arctic (Table 1).
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Table 1. Main environmental threats to Arctic marine ecosystems until 2050
Environmental threat
Impacts on ecosystems and potential economic losses
Sea level rise as a result of
climate change and ice
melting
Flooding of low-lying coastal areas and wetlands, erosion of coastal areas,
increased flooding in other areas, increased salinity of rivers, bays, and aquifers.
The threat of damage to harbors and ports due to rising sea levels. According to
the OECD (2016), total economic losses could reach $111.6 billion by 2050 and
$367.2 billion by 2100.
Increase in temperature and
freshening of surface waters
due to glaciers melting
Significant changes in the lower/middle trophic chains and fluctuations of the
quantity and quality of food resources at higher trophic levels.
Increase in primary
productivity of the Arctic
Ocean and the North Atlantic
seas
Reduced proportion of stocks of valuable commercial species in the structure of
biodiversity, significant modification of technologies for extraction of biological
resources.
Invasion of alien species
Loss of marine biodiversity
Currently, 550 species of fish are endangered. The rate of biodiversity loss will
continue to increase.
Marine pollution
Marine ecosystems are under pressure from more than 300 chemicals classified
as the most dangerous, as well as plastics and microplastics. They cause changes
in the physical, chemical, and biological characteristics of marine and coastal
zones that affect the quality, productivity, and sustainability of marine
ecosystems. Pollutants can undermine the immune system and reproduction
capacity of marine species, their resistance to other anthropogenic stressors, and
contribute to the shifts in the ecosystems.
Acidification of the world’s
ocean waters
The increase in carbon dioxide emissions and climate warming causes an increase
in the acidity of ocean waters, a gradual increase in the concentration of
inorganic carbon, a decrease in the pH of waters, and their saturation with
calcium carbonate.
Source: Authors’ development based on OECD (2016)
With the current rates of pollution and climate change remaining constant, the OECD (2016)
predicts the increased pressure on Arctic ecosystems from chemical pollution, affecting their
health, productivity, and sustainability. Pollution undermines the immune system and reproduction
of all Arctic animal species. There are changes in the functioning of ecosystems, the consequences
of which are global and long-term (Titova, 2016). One of the major threats is the expected increase
in acidification of marine waters, a factor of physical and biological changes in ecosystems. The
extinction of entire populations of animals, birds, and fish is also a significant environmental
problem. To a certain extent, this is due to a sharp change in climate and habitat conditions.
According to the Conservation of Arctic Flora and Fauna (CAFF) (n.d.), mammals, birds, and fish
living in the High Arctic experienced an average 26% drop in their populations between 1970 and
2004 due to the loss of sea ice. Arctic grazing species have declined by 20% between 1985 and
2004 (CAFF, n.d.). For many bird species, widespread and accelerating declines in population have
been observed by Smith et al. (2020), Fuglei et al. (2020), Goyert et al. (2018), and Amundson et
al. (2019). According to Taylor et al. (2020), 57% of bird species in the Arctic had at least one
population in decline, while for 21% of species, all populations were declining. In the case of
mammals, Cuyler et al. (2020) found that six muskoxen populations had been declining since the
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2000s. The two of six with steepest declines used to be the largest endemic populations in the
world as recently as two decades ago (Taylor et al., 2020). Lemming populations declined in Russia
and outside Fennoscandia at the southern edge of their distribution (Loarie et al., 2009; Ehrich et
al., 2020) due to more frequent melt and freeze events in winter caused by climate change (Kausrud
et al., 2008; Berteaux et al., 2017). The occurrence of irregular winter conditions is recognized as
one of the major reasons for the Peary caribou population decline (Langlois et al., 2017; Kaluskar
et al., 2019), as well as habitat shifts in polar bears populations (Watson et al., 2019). Other
important factors of habitat change and biodiversity loss in the Arctic are poaching, industrial
development, urbanization, and increased shipping (Peck et al., 2018; Yurkowski et al., 2019).
Intensification of shipping
Currently, most ships operating in the Arctic use heavy fuel (up to 75% of all fuel), which is
dangerous for the environment (Cariou & Faury, 2015). As a result of its combustion, soot gets
into the air and then condensates on ice and snow thus contributing to greater absorption of solar
energy and ice melting. As the reflectivity of water and ice surfaces decreases, they absorb more
and more energy, which contributes to the strengthening of the greenhouse effect and progressing
warming. In the case of Norilsk and other catastrophes, we see that fuel spills cause serious damage
to the entire ecosystem, including people. Because of its viscous consistency, fuel oil is practically
insoluble in water and has a detrimental effect on birds and marine mammals.
Since the 2010s, there has been a search for ways to restrict and ban the use of heavy fuel in Arctic
shipping. The Arctic Council’s Working Group on the Protection of Arctic Marine Environment
(PAME) conducted a comprehensive assessment of the impact of shipping on Arctic ecosystems
and the threat of accidental oil spills in 2009 (Arctic Council, 2009). Further, the comprehensive
three-staged PAME study on the use and carriage of heavy fuel in Arctic shipping in 2011-2016
(PAME, 2011, 2013a, 2013b, 2016a, 2016b), has resulted in the IMO’s proposal to ban the use of
heavy fuel in the Arctic. According to the IMO’s Sub-Committee on Pollution Prevention and
Response, the ban is expected to be adopted in 2020 and will come into force on July 1, 2024.
However, some vessels, especially those with a double hull, will be able to continue using heavy
fuel until 2029. Also, for the Arctic littoral states, it will be possible to issue special permits for
individual vessels using heavy fuel also until 2029.
Responses to environmental problems in the Arctic
To unify approaches to solving the above-mentioned environmental problems, the issues of
conservation and protection of the Arctic ecosystems are addressed at the international, bilateral,
and national levels (Khludeneva, 2016).
International legislation in the sphere of environmental protection
At the international level, environmental challenges in the Arctic have been addressed since the
1960s. Since then, a comprehensive framework of multilateral agreements has been established,
including:
International Convention on Civil Liability for Oil Pollution Damage 1969
(International Maritime Organization [IMO], 1969).
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Convention on Wetlands of International Importance Especially as Waterfowl Habitat
1971 (International Union for Conservation of Nature [IUCN], 1971).
Convention on the Prevention of Marine Pollution by Dumping of Wastes and Other
Matter 1972 (IMO, 1972).
Declaration of the United Nations Conference on the Human Environment 1972
(United Nations [UN], 1972).
Convention on Long-Range Transboundary Air Pollution 1979 (United Nations
Economic Commission for Europe, 1979).
United Nations Convention on the Law of the Sea 1982 (UN, 1982).
Convention on Biological Diversity 1992 (UN, 1992a).
United Nations Framework Convention on Climate Change 1992 (UN, 1992c).
The Rio Declaration on Environment and Development 1992 (UN, 1992b).
Kyoto Protocol to the United Nations Framework Convention on Climate Change
1992 (UN, 1997).
Stockholm Convention on Persistent Organic Pollutants 2001 (UN, 2001).
International conventions set out the general requirements applicable to the protection of Arctic
ecosystems. These are, in particular, the measures for the protection of wetlands established by
the Convention on Wetlands of International Importance Especially as Waterfowl Habitat (IUCN,
1971), the measures to combat pollution of the marine environment from waste discharges, as set
out in the Convention on the Prevention of Marine Pollution by Dumping of Wastes and Other
Matter (IMO, 1972), and the measures for the conservation and sustainable use of biological
diversity envisaged by the Convention on Biological Diversity (UN 1992a).
The international framework for the protection of the Arctic environment is supplemented by the
measures stipulated in legal acts and agreements concluded between the Arctic states, for example:
The 1973 Agreement on the Conservation of Polar Bears between Canada, Denmark,
Norway, the USSR, and the USA (Polar Bear Range States, 1973).
Arctic Environmental Protection Strategy 1991 (Arctic Council, 1991).
Declaration on Environment and Development in the Arctic between Arctic Council
member countries (Arctic Portal, 1993).
Agreement on Cooperation on Marine Oil Pollution Preparedness and Response in
the Arctic between Arctic Council member countries (Government of Canada, 2013).
These agreements develop and specify the provisions of universal international treaties to ensure
that the natural and other features of the Arctic region are taken into account. As a rule, they are
concluded within the framework of the Arctic Council between all member countries, and then
implemented under the supervision of the relevant working groups. During its existence, working
groups of the Arctic Council have prepared many guidelines and reports on such areas as
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biodiversity, development of offshore oil and gas fields, safe transportation of oil in Arctic waters,
and spills of oil and other dangerous and toxic substances.
Environment-related policies and strategies of Arctic states
The recommendations made by the Arctic Council are not binding. Therefore, the key role in
shaping responses to environmental concerns in the Arctic is played by national environmental
policies. They address various aspects of both international and country-specific activities,
including prevention of pollution of the Arctic marine environment from various sources, creation
of Arctic marine and coastal specially protected natural territories, prevention of negative impact
on Arctic natural resources, and promotion of effective participation of indigenous people in the
rational use and protection of the Arctic environment. Given the above outlined five major
environmental concerns, the following sections discuss policies and responses to current
environmental challenges contained in the Arctic-related development strategies and documents
of eight Arctic Council states.
Canada
Canada’s Arctic legislation has changed significantly over the past decades. In 1985, the approval
of the Arctic Water Pollution Prevention Act (Government of Canada, 1985) meant to create a
legal framework for regulating shipping, economic activities, and marine pollution and for
protecting the Arctic marine environment. The Act provides for administrative and civil liability,
and economic sanctions against entities that pollute the marine environment. The Act also contains
a clause that regulates and controls activities in all Arctic territories of the country. Canada’s Arctic
strategy has been updated since the early 2000s. In 2019, Canada’s Arctic and Northern Policy
Framework (ANPF) (Government of Canada, 2019) was approved. Similar to previous Arctic-
related documents, it emphasizes the importance of climate change responses, environmental
protection, environmental management, and biodiversity conservation in the vast northern
territories of the country. In the Canadian Arctic, the annual temperature is rising 2-3 times faster
compared to the global average (Bush & Lemmen, 2019), which poses a significant threat to the
population, infrastructure, and ecosystems (Government of Canada, 2019). Najafi et al. (2015) and
Zhang et al. (2019b) attribute at least half of the observed warming to the anthropogenic activity,
particularly, to human-caused emissions of greenhouse gases. Climate change is projected to affect
northern parts of Canada more than southern ones, thus increasing the likelihood of extreme
events in the Canadian Arctic such as wildfires, droughts, and floods (Zhang et al., 2019b). Future
warming may have adverse effects on terrestrial and marine ecosystems, as well as on the economy.
These include risks to freshwater supply (Sturm et al., 2017), unpredictable seasonal and spatial
variations in ice situation for marine shipping (Laliberté et al., 2016; Pizzolato et al., 2016),
interruption of overland transportation due to the unstable lake and river ice conditions (Furgal &
Prowse, 2008), and the impacts of thawing permafrost on greenhouse gases release (Olefeldt et al.,
2016) and degradation of northern infrastructure (Prowse et al., 2009).
Increasing the resilience and ensuring a healthy state of the northern ecosystems are among the
strategic goals of Canada. To achieve this goal, the following tasks are provided (Government of
Canada, 2019):
“accelerate and intensify national and international reductions of greenhouse gas
emissions and short-lived climate pollutants;
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ensure the conservation, restoration, and sustainable use of ecosystems and species;
support sustainable use of species by Indigenous peoples;
approach the planning, management, and development of Arctic and northern
environments in a holistic and integrated manner;
partner with territories, provinces, and Indigenous peoples to recognize, manage and
conserve culturally and environmentally significant areas;
facilitate greater understanding of climate change impacts and adaptation options
through monitoring and research, including Indigenous-led and community-based
approaches;
enhance support for climate adaptation and resilience efforts;
enhance understanding of the vulnerabilities of ecosystems and biodiversity and the
effects of environmental change;
ensure safe and environmentally-responsible shipping;
decommission or remediate all contaminated sites;
strengthen pollution prevention and mitigation regionally, nationally and
internationally”.
The ANPF specifies no tools adjusted individually to the achievement of the environmental tasks,
but it outlines government mechanisms that will be developed to accomplish Canada’s overall
goals in the Arctic. These include renewed federal-provincial-territorial-Indigenous relationships,
involvement of the Inuit Crown Partnership Committee, the Yukon Forum, and the
Intergovernmental Council of the Northwest Territories, investment plan to define and attract
new investments to the region, and economic and regulatory levers to align funding initiatives with
the objectives of the Framework (Government of Canada, 2019). The ANPF declares Canada’s
commitment to international efforts to reduce the negative impact of environmental issues on the
population and Arctic ecosystems. Again, no specific environment-related agreements are
mentioned, but among the institutions and international formats, the ANPF underscores the
Arctic Council, the Arctic Coast Guard Forum, the Arctic Economic Council, the International
Maritime Organization (IMO), and the United Nations Convention on the Law of the Sea
(UNCLOS) (Government of Canada, 2019).
Denmark (Greenland and the Faroe Islands)
Denmark has a common strategy for the development of its circumpolar territories taking into
account the interests of Greenland and the Faroe Islands (Government of Denmark, Government
of the Faroes, & Government of Greenland [Kingdom of Denmark Strategy], 2011). The 2011
Arctic strategy is expected to be revised before it expires at the end of 2020 (McGwin, 2020). Since
the new text was unavailable at the time of writing, we analyze the 2011 version.
Both Greenland and the Faroe Islands are important migration routes for birds, whales, polar
bears, and other polar animals, as well as the conventional habitats of various species of flora and
fauna (Lyngs, 2003; Boertmann et al., 2006; Merkel et al., 2019). Over the past years, the evidence
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that migratory species have declined in the North Atlantic has accumulated (Ganter & Gaston,
2013; CAFF, 2017). Adverse effects of climate change on the terrestrial and marine ecosystems
across Arctic territories of Denmark were found by many scholars, including Irons et al. (2008),
Canini et al. (2019), Fortune et al. (2020), and Burgos et al. (2020). The 2011 Strategy recognizes
that a negative impact on the environment is caused by economic activities in Denmark,
Greenland, and the Faroe Islands, including the extractive and energy industries (Kingdom of
Denmark Strategy, 2011: 26). Intensive shipping is attributed to becoming a threat to marine
ecosystems as a source of pollution and a potential transfer route for invasive alien species
(Kingdom of Denmark Strategy, 2011: 45). In light of the increased maritime activities, oil
exploration, marine studies, fishing, and passenger transport, both Greenland and the Faroe
Islands “have entirely or in part been responsible for the monitoring of the marine environment
and pollution control in territorial waters” (Kingdom of Denmark Strategy, 2011: 18). Denmark
supports the surveying of territorial waters and promotes maritime safety and marine protection.
The Strategy claims that although a certain amount of pollutants is generated domestically, the
majority of greenhouse gases, heavy metals, persistent organic pollutants, petroleum products, and
mercury still comes from outside (Kingdom of Denmark Strategy, 2011: 45). Such influx of
transboundary pollutants negatively affects the health of the population and food chains
(Snodgrass, 2020; Foguth et al., 2020), as well as triggers Greenland Ice Sheet melt (Lamarche-
Gagnon et al., 2018; Williamson et al., 2020).
Due to the impacts of rapid global warming and greater pressure of anthropogenic activities on
fragile biodiversity, Danish Arctic policy expresses particular concern for protecting the
environment through improved understanding of climate change in the Arctic (Kingdom of
Denmark Strategy, 2011: 43), monitoring of the Greenland ice sheet (Kingdom of Denmark
Strategy, 2011: 45), monitoring and study of migratory species and migration routes, and tracking
of transboundary pollutants and understanding of their effects on the health of the people and the
biodiversity loss (Kingdom of Denmark Strategy, 2011: 46). The country plans to reduce
greenhouse gas emissions by 50% by 2050 in accordance with the EU guideline, increase the share
of renewable energy sources to 30% by 2020, and achieve full independence from hydrocarbon
fuels by 2050 (Kingdom of Denmark Strategy, 2011: 46).
Environmental protection efforts are focused on the national implementation of international
agreements (Kingdom of Denmark Strategy, 2011: 46) and are made in accordance with
international obligations based on the best international experience and scientific knowledge to
ensure the health, productivity, and sustainability of northern communities (Kingdom of Denmark
Strategy, 2011: 10). The two treaties that Denmark focuses on in its environmental policy in the
Arctic are the Convention on Wetlands of International Importance Especially as Waterfowl
Habitat (IUCN, 1971) and the Convention on Biological Diversity (UN, 1992a). In the sphere of
pollutants control, Denmark calls for a proactive application of the UNEP’s global mercury
convention (today, it is the Minamata Convention on Mercury signed in 2013 (UNEP, 2013)) and
the Stockholm Convention on Persistent Organic Pollutants (UN, 2001) (Kingdom of Denmark
Strategy, 2011: 46). In the sphere of marine environment protection, Denmark participates in the
International Convention on Liability and Compensation for Damage in Connection with the
Carriage of Hazardous and Noxious Substances by Sea (IMO, 2010) and the International
Convention for the Control and Management of Ships’ Ballast Water and Sediments (IMO, 2004)
(Kingdom of Denmark Strategy, 2011: 46). Under a bilateral agreement with Canada, Denmark
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and Greenland share information on oil spills and other marine pollution. Denmark also
collaborates with the IMO in the field of environmental regulation of shipping and oil spills.
Finland
Finland’s Strategy for the Arctic Region 2013 (Government of Finland, 2013) is largely focused on
environmental protection and climate issues. It states that the efforts are focused on the following
areas (Government of Finland, 2013: 38):
developing an understanding of the impact of climate change and transboundary
transport of pollutants;
sustainable use of natural resources in the Arctic;
identification of environmental limitations of Arctic development;
implementation of environmental protection measures in all spheres of activity in the
Arctic.
To some extent, this vision conflicts with the economic interests in the northern territories of the
country. Finnish legislation, particularly, the Environmental Protection Act (Ministry of the
Environment of Finland, 2014), the Waste Act (Finlex, 2011a), and the Water Act (Finlex, 2011b)
require the use of best available sustainable economic practices to reduce harmful impacts of
exploration of natural and mineral resources. The 2013 Strategy emphasizes that an
environmentally-oriented approach allows taking into account the impact of the use of natural
resources in a broad perspective. Environmental objectives are “the key considerations in the
efforts to promote economic activity and cooperation, while at the same time ensuring sustainable
use of natural resources” (Government of Finland, 2013: 7).
The fundamental parts of Finland’s environmental program in the Arctic are the creation of
conservation zones and the conservation of biodiversity (Heininen et al., 2020). One of the
Strategy’s objectives related to the Arctic environment is “the development of the network of
nature conservation areas in order to improve the standard of environmental protection and
clarify the framework for economic activity” (Government of Finland, 2013: 57). The expansion
of a network of nature reserves and protected areas in the north of Finland is seen as a pragmatic
way to improve environmental protection and to facilitate economic activity. In terms of
biodiversity, the main focus is on the conservation of various species of flora and fauna, especially
migrating birds. Since the development of economic development can negatively affect the
conservation of biodiversity, there is a need for careful planning of those activities that involve the
use of resources or land.
Finland recognizes pollution from various types of domestic and outer sources as one of the main
environmental threats (Government of Finland, 2013: 39). The main pollutants are greenhouse
gases, black carbon, methane, carbon dioxide, oil, waste from military production and military
bases, radioactive waste, waste from the mining industry, household garbage from settlements, as
well as pollution from the shipbuilding industry and shipping. To address the existing pollution
problems, Finland relies on the Arctic Council countries' compliance with the regulations of the
Agreement on Cooperation on Marine Oil Pollution Preparedness and Response in the Arctic
(Government of Finland, 2013: 58). Finland also calls on all Arctic states to responsibly reduce
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emissions of greenhouse gases and non-persistent pollutants (Government of Finland, 2013: 13,
39).
Iceland
Iceland has long been known to be one of the critical regions in the Arctic for preserving
biodiversity (primarily, in marine ecosystems) and global circulation of air and water masses
(Meissner et al., 2018). An increasing number of studies have been reporting a human-driven
climate change in Iceland in recent decades due to deep-sea resource extraction, mining operations,
fishing, shipping, and other anthropogenic activities (Halfar & Fujita 2007; Mengerink et al., 2014;
Van Jochumsen et al., 2016). Many of these concerns are addressed in the Parliamentary Resolution
on Iceland’s Arctic Policy (Ministry for Foreign Affairs of Iceland, 2011), which, as noted by
Heininen et al. (2020), has the most pronounced focus on climate change and environment among
the policies of other Arctic countries. The Resolution states that “Iceland will concentrate its
efforts fully on ensuring that increased economic activity in the Arctic region will contribute to
sustainable utilisation of resources and observe responsible handling of the fragile ecosystem and
the conservation of biota” (Ministry for Foreign Affairs of Iceland, 2011: 2).
An intensification of shipping activities in the waters around Iceland is considered to be one of
the major sources of increased greenhouse gases emission. Heininen et al. (2020) note that
although the Resolution hardly identifies other sources and types of pollution, it nevertheless
suggests measures to reduce the negative impact of pollutants on the environment. First, it calls
for the compliance with the provisions of such international agreements as the United Nations
Convention on the Law of the Sea (UN, 1982) and the United Nations Framework Convention
on Climate Change (UN, 1992c), as well as with the regulations established by the IMO. Second,
environmental pollution is considered a national security issue in terms of the establishment of
adequate capacity for response to “environmental accidents, accidents at sea and maritime activity
in connection with oil extraction and other resource utilization” (Ministry for Foreign Affairs of
Iceland, 2011: 10).
Various approaches are being implemented concerning climate change adaptation, including
research activities. Many states and their associations, including China, Japan, and the EU, are
invited to participate in the activities related to inter-state aspects of climate change. Iceland also
proclaims its collaboration with the UN in implementing the provisions of the Framework
Convention on Climate Change (UN, 1992c) and its commitment to the principles of sustainable
development, including reducing greenhouse gas emissions and developing renewable energy
opportunities.
Norway
The updated version of Norway’s Arctic Strategy has been in effect since 2017 (Norwegian
Ministries, 2017). It names environmental protection and preparedness for natural and man-made
emergencies among priority areas of the country in the Arctic, along with international
cooperation, business development, knowledge, and infrastructure development (Norwegian
Ministries, 2017: 15). In the sphere of environmental protection, Norway aims to “safeguard
threatened and valuable species and habitats and achieve good ecological status in ecosystems;
ensure sustainable use and the conservation of a representative selection of Norwegian nature
covering the whole range of habitats and ecosystems; reduce greenhouse gas emissions and
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pollution in line with national targets and international commitments; and strengthen emergency
preparedness and response related to increased activity in the north” (Norwegian Ministries, 2017:
35).
As pointed by Heininen et al. (2020), the Norwegian Arctic Strategy is particularly focused on
establishing a balance between environmental and economic activities. The Strategy underscores
that “all business activity in the Arctic is to be economically, environmentally and socially
sustainable” (Norwegian Ministries, 2017: 23), while main industries (fishing, mining, marine
biotechnology, energy, shipping, and tourism) have to be based on “even better utilisation of the
region’s natural and human resources” (Norwegian Ministries, 2017: 23-24).
Among the main pollutants in the Norwegian Arctic, the Strategy recognizes greenhouse gases
emissions, primarily, from the transport sector (Norwegian Ministries, 2017: 10, 32) and articulates
a goal to reduce the emissions by at least 40% by 2030 and to becoming a low-carbon society by
2050 (Norwegian Ministries, 2017: 12). Apart from road transport, other sources of pollution
include shipping and infrastructure development. The Government aims “to reduce the
environmental and climate impacts of ferry traffic and domestic shipping”, as well as “to ensure
that adequate attention continues to be given to climate change and environmental considerations
in connection with land-use decisions concerning infrastructure development” (Norwegian
Ministries, 2017: 33).
In the sphere of environmental protection, Norway announced several ambitious projects. The
Strategy mentions the creation of a center for oil spill preparedness and response, as well as the
collection of plastic debris (Norwegian Ministries, 2017: 37). Norway has high hopes for the
contribution of the Arctic Council states to the development of the seed storage facility in Svalbard
to preserve genetic diversity and promote global food security. The Agreement on Cooperation
on Marine Oil Pollution Preparedness and Response in the Arctic is seen as one of the principal
tools for combating pollution (Norwegian Ministries, 2017: 36).
Climate change impacts on the environment are one of the greatest challenges for the Norwegian
Arctic recognized by the 2017 Strategy (Norwegian Ministries, 2017: 3), ministerial reports
(Norwegian Ministry of Climate and Environment, 2015; The Research Council of Norway, 2012),
and individual scholars (Benestad & Haugen, 2007; Pall et al., 2019; Poschlod et al., 2020; Ward,
2020). The climate in Norway has become warmer and precipitation has increased by about 20%
since 1900. The Norwegian Ministry of Climate and Environment (2015) forecasts the annual
mean temperature in Norway to rise by between 2.3°C and 4.6°C by 2100. According to Heininen
et al. (2020), the Norwegian Arctic Strategy views global warming from two sides. Norway expects
that ice melting may soon have a positive impact on the development of economic activity in the
Arctic in terms of the emergence of new opportunities for shipping and resource extraction
(Norwegian Ministries, 2017: 3). On the other side, climate change is considered as a threat to
Arctic species and ecosystems (Norwegian Ministries, 2017: 35). For instance, rising temperatures
can lead to a northward shift in the distribution of habitats of terrestrial animals and plants, while
changing ocean currents along with the retreat of the sea ice can allow more southerly fish species
to move into Arctic sea areas. When such shifts happen, purely Arctic species of flora and fauna
will meet growing competition, greater predation pressure, and a higher risk of an influx of diseases
and parasites into the region (Norwegian Ministry of Climate and Environment, 2015).
Establishing a balance between economic opportunities and environmental considerations could
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be a challenging task for the Norwegian Government. Among the prospective tools to achieve a
balance, the Strategy outlines integrated management that pulls local, regional, and international
policies in the same direction.
Russia
In Russian legislation, the issues of environmental protection and rational use of natural resources
are covered at various levels. In the Foundations of the State Policy of the Russian Federation in
the Arctic till 2035 (President of the Russian Federation, 2020), environmental protection and
environmental security are mentioned among the main directions of the national policy in the
region. The lack of preparedness of the environmental monitoring system to contemporary
ecological challenges is recognized among the threats to national security in the Arctic. Following
this vision, the 2020 Policy identifies the tasks in the field of environmental protection and
environmental safety (President of the Russian Federation, 2020: article 15):
development of a network of specially protected natural territories and water areas to
preserve ecosystems and to adapt them to climate change;
ensurance of conservation of Arctic fauna and flora, protection of rare and
endangered plants, animals, and other organisms;
permanent work on the elimination of accumulated environmental damage;
improvement of the environmental monitoring system, usage of modern information
and communication technologies and communication systems for satellite
monitoring, development of sea and ice platforms, research vessels, and observatories;
introduction of the best available technologies, ensuring minimization of air
emissions, discharges of pollutants into water bodies, and reduction of other types of
negative impact on the environment in the course of economic and other activities;
ensurance of the rational use of natural resources, including in locations of traditional
residence and economic activities of indigenous peoples;
development of a comprehensive waste management system of all hazard classes,
construction of modern environmentally friendly waste processing complexes;
implementation of a set of measures to prevent toxic substances, infectious agents,
and radioactive substances from entering Russia’s Arctic zone.
The 2020 Policy’s vision of environmental protection tasks in the Russian Arctic is detailed in the
Strategy of Development of the Arctic Zone of the Russian Federation and Ensurance of National
Security till 2020 (Government of the Russian Federation, 2013). The update of the 2013 Strategy
is expected by the end of 2020 until when it is currently valid. The 2013 Strategy points out the
increase of technological and man-made burdens on the environment in some of Russia’s northern
coastal territories (Government of the Russian Federation, 2013: 3). It also emphasizes risks of
radioactive contamination along with a high level of accumulated environmental damage in many
inland areas of the Arctic zone (Government of the Russian Federation, 2013: 3). Therefore, the
2013 Strategy prioritizes the improvement of environmental security as a means of development
of the Arctic and the ensurance of national security (Government of the Russian Federation, 2013:
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3). Rational use of natural resources is recognized as a key to improving the quality of life of the
population in the Arctic, as well as ensuring positive demographic processes and socioeconomic
conditions in the region (Government of the Russian Federation, 2013: 7, 11, 13, 19).
To protect the environment and ensure environmental safety in the Arctic zone of Russia, the
2013 Strategy provides for (Government of the Russian Federation, 2013: 12-13).
ensuring the conservation of the biological diversity of Arctic flora and fauna in the
context of expanding economic activity and global climate change;
development and expansion of the network of specially protected natural territories
and water areas at both federal and regional levels;
elimination of environmental damage caused as a result of past economic, military,
and other activities, including assessment of the environmental damage and
implementation of measures to clean up land and water areas from pollution;
development, justification, and implementation of measures to reduce environmental
threats caused by the expansion of economic activity in the Arctic, including on the
continental shelf;
increasing the responsibility of enterprises for environmental pollution, encouraging
the development and implementation of new technologies that reduce a negative
impact on the environment, reduce the risks of occurrence and minimize the
consequences of man-made emergencies;
improving the system of state environmental monitoring to assess environmental
parameters, the establishment of a system to monitor environmental pollution, air,
and space-based observations of ecosystems and climate;
development and implementation of economic mechanisms that stimulate the
reproduction and rational use of mineral and biological resources, energy and resource
conservation, and utilization of fossil gas in oil production areas.
Along with the fundamental principles set out in the strategic documents, environmental
protection activities are regulated by industry-specific legislation. Within the Arctic zone of Russia,
continental shelf, and exclusive economic zone, it covers environmental requirements for any
activity that has or may harm the environment. The 2013 Strategy also defines the tools of
environmental regulation, environmental expertise, environmental impact assessment, payment
for negative impact on the environment, environmental insurance, state environmental
monitoring, state environmental supervision, industrial and public control in the field of
environmental protection (Government of the Russian Federation, 2013: 12-13).
Sweden
Among Arctic Council countries, Sweden was the first to elaborate comprehensive environmental
legislation by adopting the Environmental Protection Act in 1969 (Lidskog & Elander, 2000). Since
that time, environmental issues have always stood high in the national political agenda (Granberg
& Elander, 2007). Sweden’s Strategy for the Arctic Region addresses climate change and the
environment among major concerns of the country in the Arctic (Government Offices of Sweden,
2011: 23). There is also the Environmental Policy for the Arctic (Government Offices of Sweden,
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2016) which particularly emphasizes the focus on environmental and ecological activities in the
High North. As the 2016 Policy directly addresses Sweden’s priorities in the sphere of the Arctic
environment, we consider this document in our study.
The 2016 Policy declares three priorities for protecting the environment in its northern territories:
strengthening measures to prevent the negative effects of climate change, improving the protection
of biodiversity and ecosystems, and sustainable use of resources (Government Offices of Sweden,
2016: 2).
According to the first priority, international cooperation to prevent global warming above 2°C is
considered a fundamental element of curbing climate change in the Arctic (Government Offices
of Sweden, 2016: 2). Sweden's approach to this task is expressed in the climate strategy developed
in the run-up to the Paris agreement in 2015. Sweden aims “to strengthen the Arctic Council’s
climate and renewable energy measures” (Government Offices of Sweden, 2016: 2). One of the
main goals is to reduce “emissions of emissions of short-lived climate forcers such as soot and
methane” (Government Offices of Sweden, 2016: 2). In this area, Sweden operates within the
framework of the agreement on reducing harmful emissions concluded in 2015 between Arctic
countries, which involves improving national measures and joint actions to reduce soot and
methane emissions (Government Offices of Sweden, 2016: 2).
The second priority also highlights the need for international efforts to protect valuable natural
habitats of animals and plants. In its 2016 Policy, Sweden “supports the process under way in the
Arctic Council to implement the recommendations of the Arctic Biodiversity Assessment,
including efforts to establish networks of protected areas” (Government Offices of Sweden, 2016:
3). Protection of habitats in the Arctic meets the guidelines of the Convention on Biological
Diversity (UN, 1992a) on the conservation of at least 10% of inland territories and water areas and
up to 17% of inland water reservoirs by 2020 (Government Offices of Sweden, 2016: 3). The
UNCLOS (UN, 1982) is considered as an instrument for the protection and conservation of
marine biodiversity in the areas beyond national jurisdiction (Government Offices of Sweden,
2016: 3). However, Sweden recognizes that it takes “many years before such an implementing
agreement can enter into force” (Government Offices of Sweden, 2016: 3). In the meantime,
operational environmental measures can be implemented based on the Convention for the
Protection of the Marine Environment of the North-East Atlantic (OSPAR Commission, 1992).
Concerning the sustainable use of resources, the 2016 Policy recognizes the role of the UNCLOS
(United Nations, 1982) as the main international instrument for regulating the rights of littoral
states to explore mineral and other resources on the continental shelf (Government Offices of
Sweden, 2016: 4). At the same time, the extraction of oil and gas from the subsurface for
combustion and energy production must be limited to achieve the internationally approved target
of containing global warming within 2°C (Government Offices of Sweden, 2016: 4). Sweden is
committed to strict regulatory measures, particularly, in the areas with permanent or seasonal ice
cover, where the risks of oil spills and other pollutions to fragile Arctic ecosystems are higher
(Government Offices of Sweden, 2016: 4). Among the major sources of environmental risk, the
2016 Policy recognizes increased shipping activities (Government Offices of Sweden, 2016: 4). To
mitigate potential risks, Sweden follows the provisions of the Polar Code, which includes both
environmental regulations and technical requirements for marine and river vessels used in the
Arctic (Government Offices of Sweden, 2016: 4).
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USA
Similar to those in other Arctic territories, adverse impacts of climate change and environmental
disruptions on terrestrial and marine ecosystems in Alaska have been increasing in the previous
decades. The average temperature in Alaska has risen at twice the rate of the global average (Allen,
2020), while the Gulf of Alaska experienced extreme temperatures during 2014-2019, including
the four warmest years ever observed (Litzow et al., 2020). In response to warming and sea ice
reduction, Alaskan ecosystems are reacting by a decline and lower productivity in fish populations
(Jones et al., 2020), change of habitats of Arctic animals and birds (CAFF, 2017; Larson et al.,
2020), and decomposition of previously frozen carbon from tundra soils (Tao et al., 2020).
Many studies suggest that increasing and more fluctuant variabilities in the Alaskan climate, as well
as environmental pollution in the region, could be associated with more intensive anthropogenic
activities, including exploration of natural resources and development of industrial infrastructure
(Skjærseth & Skodvin, 2003; Jezierski et al., 2010a, 2010b; Litzow et al., 2020). An emerging
environmental problem in Alaska is the metal contamination of food and water resources due to
the emergence of mining and drilling activities (Perryman et al., 2020). The United States has
significantly developed its legislation related to the exploration of the continental shelf and
territorial waters. Outer Continental Shelf Lands Act (Cornell Law School, n.d.) is one of the
principal documents to regulate the activities of oil and gas companies on the Alaska shelf. The
Act states that the operations on the outer continental shelf should be concluded in a safe manner
to prevent or minimize the occurrence of damage to the environment (Cornell Law School, n.d.:
§1332). It also establishes liability for all types of environmental and economic damage is
established. There is a multi-stage system for planning of subsurface use, issuing licenses for
exploration, development of deposits, and production of minerals (Gladun, 2015).
The National Strategy for the Arctic Region states that the USA “will continue to protect the Arctic
environment and conserve its resources” (President of the United States, 2013: 2). Specific
objectives of the U.S. environmental efforts in the Arctic include conservation of natural resources,
assessment and monitoring of ecosystems and the risks of climate change, implementation of
integrated management practices to balance economic development and environmental
protection, studies on environment changes, and charting and mapping the ocean and waterways
(President of the United States, 2013: 9-10). Among critical concerns, the 2013 Strategy
underscores “land ice and its role in changing sea level; sea-ice and its role in global climate,
fostering biodiversity, and supporting Arctic peoples; and, the warming permafrost and its effects
on infrastructure and climate” (President of the United States, 2013: 9-10).
While the 2013 Strategy calls for a strengthening of international cooperation for “collaborative
efforts by nations seeking to explore emerging opportunities while emphasizing ecological
awareness and preservation” (President of the United States, 2013: 8), in recent years, the Arctic
has been turning into “an arena of global power and competition” (Pompeo, 2019). Two
documents released in 2019 articulate this new vision of the Arctic by the U.S. Coast Guard and
the U.S. Department of Defence. While the latter one, the DoD’s Arctic Strategy views
environmental changes in the High North as “specific operational challenges that limit
communications, including the harsh climate, vast distances, and atmospheric phenomena”
(United States Department of Defence, 2019: 10), the Coast Guard Arctic Strategic Outlook calls
for a deeper understanding of environmental processes through the development of pollution
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detection and tracking capabilities, weather and environmental observations, and assessment of
living marine resources activity (United States Coast Guard, 2019: 27).
Environmental focus of China’s Arctic policy
Since the contemporary environmental challenges faced by the Arctic countries are rapidly
becoming global, a broader international community has been attempting to contribute to their
solution. Among the non-Arctic states, China has become one of the most prominent and
important actors in the Arctic in recent years.
China’s active involvement in environmental studies in the Arctic dates back to 1996 when the
country entered the International Arctic Science Committee (IASC). In 1999, China organized its
first scientific expedition to the Arctic to study climate change and its impact on the country. Since
then, Chinese researchers have carried out eleven expeditions to various parts of the Arctic Ocean
to study the biological diversity of Arctic ecosystems and atmospheric, marine, and oceanic
processes associated with ice melt (Chistyakova, 2018; Filippova, 2019; Staalesen, 2020). Having
analyzed the results of China’s expeditions to the Arctic, Wang (2015) and Wei et al. (2020)
identified priority spheres in Arctic studies for China, i.e. environment, climate change, water and
ice, maritime routes, and sustainable development. Pan and Zhou (2010), Wu et al. (2013), and
Zhang et al. (2019a) emphasized environmental security and the need for scientific knowledge on
climate change as the premier interests explaining China’s research activities in the High North.
In 2017, China’s President Xi Jinping underscored the commitment of the country to “the
principles of prioritizing resource conservation and environmental protection” (Xi, 2017: 45) by
promoting low-carbon development, preventing and controlling pollution of air, water, and soils,
restoring ecosystems, and developing biodiversity protection networks (Xi, 2017: 45-46). Such a
vision of China’s role in building an “ecological civilization” (Xi, 2017: 47) is very much enshrined
in China’s Arctic Policy 2018 which states that “the Arctic situation now goes beyond its
regional nature, having a vital bearing on … the survival, the development, and the shared future
for mankind” (State Council of the People’s Republic of China, 2018: Foreword).
The 2018 Policy emphasizes that ice melting is associated with significant climate changes
throughout the planet and alerts the fact that progressing climate change in the Arctic can cause a
rise in the level of the Arctic Ocean and trigger natural disasters (State Council of the People’s
Republic of China, 2018: article I). Despite such threats to polar ecosystems, China acknowledges
the opportunities climate change could bring for the research and development of the Arctic, for
commercial use of maritime routes, and the exploration of natural and other resources in the region
(State Council of the People’s Republic of China, 2018: article I). A balance between economic
opportunities and environmental concerns may be established by integrating environmental
protection efforts and rational utilization of all kinds of natural resources the key areas of China’s
activities in the Arctic both prioritized in the 2018 Policy (State Council of the People’s Republic
of China, 2018: article IV). China recognizes the direct impact of the natural conditions of the
Arctic on China’s climate system (State Council of the People’s Republic of China, 2018: article
II) and calls for the enhancement of the environmental background investigation of Arctic
activities, evaluation of the interaction between the Arctic and global climate change, and
forecasting of potential risks posed by future climate change to the Arctic’s natural resources and
ecological environment (State Council of the People’s Republic of China, 2018: article IV.2). The
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2018 Policy states that “to protect the Arctic, China will actively respond to climate change in the
Arctic, protect its unique natural environment and ecological system, promote its own climatic,
environmental and ecological resilience” (State Council of the People’s Republic of China, 2018:
article III).
China’s role in shaping the common response to future environmental
challenges in the Arctic
Being a non-regional actor, China is particularly concerned with global implications and
international impacts of environmental management in the Arctic. To contribute to the protection
of the natural environment and Arctic ecosystems, China follows international law (the UN
Framework Convention on Climate Change, the Kyoto Protocol, the Paris Agreement, the
Agreement on Cooperation on Marine Oil Pollution Preparedness and Response in the Arctic, and
the IMO’s regulations) and participates in Arctic governance and international cooperation in the
sphere of environmental protection (Arctic Council, Arctic Science Ministerial Meeting, China-US
and China-Russia dialogues on polar issues, China-Iceland Framework Agreement on Arctic
Cooperation) (State Council of the People’s Republic of China, 2018: article IV.4). The country
takes an active part in addressing the challenges of environmental and climate change in several
ways, including environment protection, sustainable development and biodiversity protection,
emission reduction, utilization of Arctic resources in a rational manner, conservation and
utilization of living resources (State Council of the People’s Republic of China, 2018: article IV.3).
Such involvement of China in the Arctic environmental agenda provides a number of
opportunities for reshaping the existing approaches to addressing climate change and other global
ecological challenges in the region. To find potential areas for China and Arctic countries to
collaborate in the sphere of environmental protection in the High North, we viewed previously
discussed five environmental challenges through the lens of China’s priorities outlined in the 2018
Policy (State Council of the People’s Republic of China, 2018: articles IV.2, IV.3). These priorities
(namely, more efficient environmental protection, more resilient ecosystems, addressing climate
change, and conservation and utilization of fisheries and other living resources) were detailed in
24 activities derived from the text of articles IV.2 and IV.3 of the 2018 Policy. The activities were
then attributed to specific environmental challenges thus establishing five groups. For each activity,
we scanned the Arctic-related documents previously discussed in the Environment-Related
Policies section of the paper to identify intersections between China’s priorities and those of Arctic
countries.
As regards industrial pollution, oil spills, and intensification of shipping in the Arctic, China’s
interests correspond with those of Arctic countries in many areas, particularly, an assessment of
the environmental impact of Arctic activities, reduction of pollutants in the Arctic waters from
land-based sources, and control of the sources of marine pollution, including ship discharge,
offshore dumping, and air pollution (Table 2). China requires its enterprises to conduct
comprehensive risk assessments for resource exploration and encourages them to participate in
the exploitation of resources in the Arctic on the condition of properly protecting the environment
(State Council of the People’s Republic of China, 2018). To establish the foundations of stronger
cooperation, Chinese research institutions could also be engaged in enhancing the environmental
background investigation of economic, transport, resource extraction, and other activities.
Arctic Yearbook 2020
Gao & Erokhin
22
Table 2. Intersections between China’s and Arctic countries’ priorities in environmental protection and
climate change responses in the Arctic (challenges 1-3)
Activity
CAN
FIN
ICE
RUS1
RUS2
SWE1
SWE2
US1
US2
Challenge 1: Industrial pollution and oil spills
Environmental
background
investigation of Arctic
activities
+
+
Assessment of the
environmental impact
of Arctic activities
+
+
+
+
+
+
+
+
+
Reduction of
pollutants in the
Arctic waters from
land-based sources
+
+
+
+
Environmental
responsibility
awareness of citizens
and enterprises
+
+
+
+
+
Challenge 2: Intensification of shipping
Control of ship
discharge, offshore
dumping, air pollution
+
+
+
+
+
+
+
+
+
Challenge 3: Ice melting
Energy exchange
processes in the Arctic
+
+
+
+
+
Evaluation of the
impact on ecosystems
caused by climate and
human activities
+
+
+
+
+
+
Interaction between
the Arctic and global
climate change
+
+
+
+
+
+
Risks posed by climate
change to natural
resources and
ecosystems
+
+
+
+
+
+
+
+
+
Arctic cryospheric
sciences
+
+
+
Public awareness of
climate change
+
+
+
+
International projects
to address climate
change
+
+
+
+
+
+
+
+
+
Note: CAN = Canada’s Arctic and Northern Policy Framework (Government of Canada, 2019); DEN = Denmark,
Greenland, and the Faroe Islands: Kingdom of Denmark Strategy for the Arctic 2011-2020 (Kingdom of Denmark
Strategy, 2011); FIN = Finland’s Strategy for the Arctic Region 2013 (Government of Finland, 2013); ICE = A
Parliamentary Resolution on Iceland’s Arctic Policy (Ministry for Foreign Affairs of Iceland, 2011); NOR = Norway’s
Arctic Strategy between Geopolitics and Social Development (Norwegian Ministries, 2017); RUS1 = Strategy of
Development of the Arctic Zone of the Russian Federation and Ensurance of National Security till 2020 (Government
of the Russian Federation, 2013); RUS2 = Foundations of the State Policy of the Russian Federation in the Arctic till
2035 (President of the Russian Federation, 2020); SWE1 = Sweden’s Strategy for the Arctic Region (Government
Offices of Sweden, 2011); SWE2 = New Swedish Environmental Policy for the Arctic (Government Offices of
Sweden, 2016); US1 = National Strategy for the Arctic Region (President of the United States, 2013); US2 = Arctic
Strategic Outlook (United States Coast Guard, 2019); “+” = intersection with China’s Arctic Policy; -” = no
intersection with China’s Arctic Policy.
Source: Authors’ development
Arctic Yearbook 2020
Widening the Scope of Responses to Environmental Concerns in the High North
23
Water areas out of the national jurisdiction, where Chinese expeditions may carry out their research
activities without permission of the Arctic states, are considered as key areas for Arctic
environmental protection (Pilyasov, 2018). China proclaims the principle of unrestricted
navigation in the Arctic Ocean for all countries and recognizes the Polar Code to a greater extent
than national regulations of the Arctic countries (Erokhin et al., 2018). Nevertheless, China is
committed to collaborating with other countries in the Arctic to enhance control of the sources
of marine pollution such as ship discharge. Many Arctic states recognize shipping as one of the
sources of pollution. Because of the increasing activity of Chinese research and cargo vessels in
the Arctic Ocean, the reduction of ship discharge is one of the critical areas to collaborate. Due to
the ban on the use of heavy fuel in the Arctic, it will be necessary to ensure the transition to the
use of other types of fuel for cargo ships and tankers after 2024 and in some cases after 2029 (due
to the IMO’s ban of heavy fuel which will come into force in 2024 with specific extensions until
2029). It may have a major impact not only on Chinese vessels but also on resource-extraction
projects. China is one of the major consumers of liquefied natural gas (LNG) from Yamal LNG
and other facilities located in Russia’s Arctic sector. Knizhnikov and Klimentyev (2019) expect
that the use of LNG as an alternative to heavy fuel could become a solution for Chinese and other
vessels used in the Arctic. For Finnish and Norwegian companies, there is an opportunity to work
with China on the development of LNG technologies (Gao & Erokhin, 2019). In cooperation
with Russian oil-and-gas companies, Chinese research institutes and enterprises could be engaged
in the hydrographic surveys in the Northern Sea Route to improve the security of navigation and
reduce ship accidents (Erokhin & Gao, 2018; Gao & Erokhin, 2020b). The transition to the use
of LNG instead of heavy fuel can reduce air pollution, including carbon dioxide emissions.
The 2018 Policy underscores China’s commitment to “studying the substance and energy exchange
process and mechanisms of the Arctic” in relation to climate change (State Council of the People’s
Republic of China, 2018: article IV.2). Although none of the eleven documents contains this exact
term “energy exchange”, a need to study the impacts of melting ice sheet mass and permafrost on
elevated carbon dioxide levels in the atmosphere is prioritized by Denmark, Finland, Russia,
Sweden, and the USA. Denmark calls for the development of a model system “to study the inland
ice and its interaction with the surrounding seas, … the knowledge of permafrost conditions, and
the interplay between weather, sea and ice more generally” (Kingdom of Denmark Strategy, 2011:
45). Finland stands for deeper cooperation between countries which “must shoulder their
responsibility for reducing emissions of greenhouse gases and short-lived climate pollutants”
(Government of Finland, 2013: 41) in view that “the melting of the polar ice cover and permafrost
will further accelerate global warming” (Government of Finland, 2013: 15). Russia directly links
energy and climate and advocates the development of an international dialogue “for the exchange
of experience in the development of climate and energy policies” (Government of the Russian
Federation, 2013: article 15).
There are several areas for collaboration in the sphere of protection of Arctic ecosystems, including
habitat changes, declines of populations of mammals, fish, and birds, and rational use of fishery
resources (challenges 4 and 5). Such activities as biodiversity protection, ensurance of adaptability
and resilience of ecosystems, international cooperation in the sphere of protection of Arctic flora
and fauna, and environmental and ecosystem-based management are prioritized by most Arctic
countries (Table 3).
Arctic Yearbook 2020
Gao & Erokhin
24
Table 3. Intersections between China’s and Arctic countries’ priorities in environmental protection and
climate change responses in the Arctic (challenges 4 and 5)
Activity
CAN
FIN
ICE
RUS1
RUS2
SWE1
SWE2
US1
US2
Challenge 4: Increase in fisheries
Conservation and
rational use of fishery
resources
+
+
+
+
+
Survey on the fishery
resources and
exploratory fishing
+
+
+
International
management of
fisheries
+
+
+
+
Cooperation on
conservation and
utilization of fishery
resources
+
+
+
Challenge 5: Habitat change and population decline
Biodiversity
protection
+
+
+
+
+
+
+
+
Protection of
migratory birds and
their habitats
+
+
Study of migration
patterns of Arctic
migratory birds
+
Adaptability and
resilience of
ecosystems
+
+
+
+
+
+
International projects
to protect flora and
fauna
+
+
+
+
+
+
+
+
Transparent
exploration and
utilization of Arctic
genetic resources
Equitable sharing and
use of the benefits
generated by the
exploitation of living
resources
Environmental and
ecosystem-based
management
+
+
+
+
+
Note: CAN = Canada’s Arctic and Northern Policy Framework (Government of Canada, 2019); DEN = Denmark,
Greenland, and the Faroe Islands: Kingdom of Denmark Strategy for the Arctic 2011-2020 (Kingdom of Denmark
Strategy, 2011); FIN = Finland’s Strategy for the Arctic Region 2013 (Government of Finland, 2013); ICE = A
Parliamentary Resolution on Iceland’s Arctic Policy (Ministry for Foreign Affairs of Iceland, 2011); NOR =
Norway’s Arctic Strategy between Geopolitics and Social Development (Norwegian Ministries, 2017); RUS1 =
Strategy of Development of the Arctic Zone of the Russian Federation and Ensurance of National Security till 2020
(Government of the Russian Federation, 2013); RUS2 = Foundations of the State Policy of the Russian Federation
in the Arctic till 2035 (President of the Russian Federation, 2020); SWE1 = Sweden’s Strategy for the Arctic Region
(Government Offices of Sweden, 2011); SWE2 = New Swedish Environmental Policy for the Arctic (Government
Offices of Sweden, 2016); US1 = National Strategy for the Arctic Region (President of the United States, 2013);
US2 = Arctic Strategic Outlook (United States Coast Guard, 2019); “+” = intersection with China’s Arctic Policy; “-
” = no intersection with China’s Arctic Policy.
Source: Authors’ development
Arctic Yearbook 2020
Widening the Scope of Responses to Environmental Concerns in the High North
25
In its Arctic Policy, China underlines the importance of sustainable development and protection
of biodiversity in the Arctic (State Council of the People’s Republic of China, 2018: article IV.2).
In the coming years, the international collaboration agenda in the Arctic will be dominated by the
establishment of a special regime for the use of natural resources, monitoring the state of
ecosystem pollution, landscape restoration, creation of natural reserves, waste management,
conservation measures, increasing animal and bird populations, control of industrial fishing, and
fighting against poaching (Pilyasov, 2018; Heininen et al., 2020; Gao & Erokhin, 2020a; Titova,
2016). In contrast to China, few Arctic countries specify the protection of migratory birds and the
study of their flyways. In these areas, Chinese scholars could contribute to the Arctic research
agenda with their studies on the migration patterns of birds (for instance, in Finland and Greenland
which both prioritize studies of migratory birds), evaluation of the impact on the ecosystem caused
by the resource-extraction and other projects where Chinese companies participate (Russia, Nordic
countries), as well as with research on the adaptability and resilience of the ecosystems across the
Arctic. Most relevant topics: how to avoid a situation where ecosystem approaches and ecosystem
management do not create ecological borders in the Arctic in addition to the existing borders of
national jurisdiction; how to gradually transform the convention regime and adapt it to the new
international political and economic conditions; how to integrate the responses to these problems
in the national policies of the Arctic Council, China, and other observer states.
Conclusion
Taking into account progressing climatic and environmental changes in the Arctic along with the
growing influence of anthropogenic factors, risks to Arctic ecosystems are emerging due to
industrial pollution from land-based and offshore facilities, intensive shipping, and exploratory use
of living resources. In Arctic countries, the environmental component has long been an extremely
important part of development strategies. With the entry of non-Arctic actors into economic,
transport, and research activities in the High North, certain adjustments in the environmental
protection agenda are needed to efficiently integrate global responses to climate change with
individual priorities of the Arctic and non-Arctic countries in the region. The responses to the
existing environmental challenges with stronger involvement of China in international formats like
Arctic Council, Arctic Science Ministerial Meeting, and bilateral dialogue frameworks with Arctic
countries will depend on the integration of the environmental agenda in the international legal
framework. China is exactly committed to the existing framework of international law including
the UN Charter, UNCLOS, rules of the IMO, the Spitsbergen Treaty, and other treaties on climate
change and the environment that govern Arctic affairs (State Council of the People’s Republic of
China, 2018). Arguably, a comprehensive international treaty is needed to stress the importance of
environmental protection in the Arctic in the international legal context. The elaboration of an
umbrella environmentally-oriented agreement between the Arctic Council members, China, and
other non-Arctic countries is hardly likely shortly, especially when it comes to the exploration of
resources, exploitation of shipping routes, and benefiting from other economic opportunities in
the region. Nevertheless, the intersections of China’s and Arctic countries’ priorities demonstrate
the potential for establishing workable multilateral and bilateral cooperation frameworks in the
spheres of climate change, conservation and utilization of living resources, clean energy solutions,
and environmentally-friendly operation of the Arctic routes.
Arctic Yearbook 2020
Gao & Erokhin
26
Acknowledgment
The study is supported by the National Social Sciences Fund of China (grant no. 18BGJ004).
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... The increase in the average annual temperature in the Arctic is nearly four times higher than the global average (Rantanen et al., 2022). Climate-related processes have both positive and negative effects on the livelihoods and health of Indigenous peoples in the Russian Arctic, primarily on the food security status of Indigenous communities (Gao & Erokhin, 2020b). An increase in water temperature in the rivers of the Arctic zone along with an increase in the length of the off-season period may result in higher frequency of episodes of mass death of fish due to a lack of oxygen in organic-enriched water (Gao et al., 2021). ...
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The livelihoods and prosperity of Indigenous Peoples substantially depend on the quality of local ecosystems and biodiversity. Indigenous communities are particularly vulnerable to the detrimental effects of climate change. At the same time, Indigenous Peoples have extensive historical knowledge about the possibilities of responsible and environmentally friendly use of local resources, which allows them not only live in severe conditions, but also adapt to climate change. However, as the changes in the way of living have accelerated under the influence of progressing economic exploration and development of the Arctic, the adaption is becoming increasingly harder. Establishing food security is exacerbated by the cross-influence of climatic, environmental, economic, social, and cultural transformations that Indigenous communities are experiencing. In the cases of nine territories in the Russian Arctic, the chapter conceptualizes an approach to assessing the level of food and nutritional security with the differentiation of environmental, economic, and social factors that affect the security-related parameters in Indigenous communities. The authors make recommendations on how to improve the food security of Indigenous Peoples, mitigate the adverse effects of food insecurity on public health, boost self-sufficiency in food, and promote the use of traditional foods and related products in diets.
... Most recent studies, such as Luoto et al. (2019), Polvani et al. (2020), Cai et al. (2021), andMcCrystall et al. (2021), show that the climate change in the Arctic outpaces the global average. Although it is hardly possible to quantify the individual contribution of the energy sector in the Russian Arctic to the acceleration of climate change in the High North as a whole, the existence of such an influence is to be admitted (Southcott et al., 2018;Nuttall & Callaghan, 2019;Gao & Erokhin, 2020b;Morgunova & Kovalenko, 2021). ...
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This year’s theme, “The Russian Arctic: Economics, Politics & Peoples” was chosen, at the turn of 2021-2022 and prior to Russia’s invasion of Ukraine, due to the high relevance of the Russian Arctic in every aspect of Arctic politics. The region comprises over half of the Arctic’s land surface area, mostly covered by permafrost, and almost half of the coastline and the Exclusive Economic Zone of the Arctic Ocean. Its population consists of almost 70% of the total number of Arctic inhabitants. The volume of its economy with multiple fields of exploitation is 73% of that of the Arctic. Despite being largely covered by permafrost, the Russian part of the Arctic contains large cities and numerous towns and villages, as well as road networks and even railways. These populated centers, many of them ‘mono-towns’, are surrounded by advanced infrastructure – both old and new – and consist of mines, smelters and other factories, harbors, airports and other transportation means, research stations, as well as navel and other military bases. Since the time of tzardom, Russian scientists and scholars have explored the Arctic and conducted field work studying geography, Arctic ecosystems, climate, cryospheric sciences, glaciers, the Arctic Ocean, and sea-ice. The Russian Arctic is also home to diverse groups of Indigenous peoples with their unique languages, cultures and livelihoods. Research done by and with Russian scientists, scholars and academic institutions is an invaluable part of international Arctic research. The Russian Arctic is therefore an incredibly important part of the entire Arctic region to understand, not only because the Russian Federation is the biggest and largest of the eight Arctic states. And yet, the region is often either not known, and/or misunderstood to external audiences and stakeholders, with superficial characterizations proliferating due to a lack of up-to-date information. There is thus a need for sophisticated English-language scholarship on the Russian Arctic, especially from Russian authors themselves. That is the intent of the Arctic Yearbook 2022.
... Most recent studies, such as Luoto et al. (2019), Polvani et al. (2020), Cai et al. (2021), andMcCrystall et al. (2021), show that the climate change in the Arctic outpaces the global average. Although it is hardly possible to quantify the individual contribution of the energy sector in the Russian Arctic to the acceleration of climate change in the High North as a whole, the existence of such an influence is to be admitted (Southcott et al., 2018;Nuttall & Callaghan, 2019;Gao & Erokhin, 2020b;Morgunova & Kovalenko, 2021). ...
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The need to boost economic growth and develop high-tech energy-intensive industries requires an all-out effort to increase power generation. On the other hand, the human-induced carbon footprint has become so evident that radical actions are needed to reduce emissions and decarbonize the energy sector. Russia's attitude to the international carbon neutrality agenda is essential since the bulk of hydrocarbons and coal comes from the Russian Arctic, Siberia, and the Far East, where climate change is rapidly advancing. At the same time, Russia is facing a growing territorial imbalance between the demand for energy in the European part of the country and the extraction of fossil fuels which is shifting further to the northeast to the Arctic. Due to the abundance of local energy resources, most Russian Arctic regions prioritize further exploitation of oil, gas, and coal fields. Nevertheless, some territories have started turning to renewable energy in an attempt to overcome infrastructure gaps and to make local energy mixes more resilient to energy supply disruptions. Since the mid-2010s (the first international sanctions against Russia), part of Russia's energy supplies has been redirected to China (the Turn to the East policy), while Chinese companies have increased their share in Russia's energy sector. China is interested in expanding transboundary energy supply for domestic needs in the northern and northeastern provinces, making Russia's Far East and the Arctic zone particularly attractive to Chinese investors. However, the heated conflict in Ukraine has disrupted conventional collaboration formats with Russian energy companies, cut Russia from Western technologies and equipment, and forced the EU countries to embargo Russian oil. The chapter attempts to feel around for the new reality mechanisms of Russia-China collaboration which could contribute to bridging the spatial development gaps in the energy sector and address the contemporary challenges posed to the low-carbon transition in the Russian Arctic.
... Numerous human-made disasters and technological emergencies in the Russian Arctic over recent years (oil and fuel spills, fires, and soil degradation) have caused severe environmental consequences (Morgunova & Kovalenko, 2021). The common causes of disturbance include low diversification of the Arctic economy (too much stress on certain types of resources in certain territories), lack of access to advanced technologies (energy-saving, low-carbon, environmentally 87 3.5 Energy and sustainable development friendly), accumulation of industrial and municipal waste, high cost of economic activity and life support in extreme climate conditions, and weak control over anthropogenic activities in the Arctic by environmental authorities (Gao & Erokhin, 2020b). ...
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Economic activity is an important area in terms of innovation and sustainable development, and the instruments and mechanisms of the financial market are gaining new value for financing these particularly complex processes and with many challenges for stakeholders (Stancu & Iacovoiu, 2015; Iacovoiu & Stancu, 2017). Globally, the financial market is crucial to the smooth operation of capitalist economies, as it provides a regulated platform for trading all types of assets or securities, such as stocks, bonds, foreign currency, and derivatives (Johnson et al., 2003; Duffie, 2014). Financial market comprise banking, insurance, and capital markets. The capital market segment provides a platform for buyers and sellers (as individuals and institutions) to trade financial securities such as bonds and stocks (The Economic Times, 2021). The money market, by contrast, is the platform for trading in financial instruments, essentially commercial papers with high liquidity and short-term maturities (The Economic Times, 2021). The globalization and emergence of digitaltechnologies are disrupting all facets of the global economy, including financial market operations and instruments (Brezeanu et al., 2005; Stancu et al., 2017). Consequently, the financial market is one of the most attractive and constantly changing areas of economic life, continually pursuing the improvement and accessibility of instruments offered to investors, adapting these products to the needs of users through the emergence of new financial products, simplifying trading activities, reducing trading costs, and so on.
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Since the 1970s, the energy sector has become an increasingly important driver of economic growth in the Arctic. The exploration and exploitation of energy resources above the Arctic Circle are of vital concern to Russia. Its nine circumpolar territories accumulate vast reserves of hydrocarbons and minerals. While the Russian Arctic accounts for 80% and 17% of the country’s total output of natural gas and oil, respectively, it has also emerged as one of the planet-scale air and water pollution sources. Being a part of the global climate change mitigation agenda, Russia attempts to converge decarbonization efforts with industrial development priorities and energy security goals. This challenge is being addressed by implementing the sustainability-focused approach to the use of energy resources, allocation of power generating facilities, and support of local communities. In the chapter, the authors explore the opportunities for the sustainable environmental and spatial development of circumpolar territories through the modernization of conventional energy industries, promoting innovative low-emission and low-carbon energy technologies, and international collaboration in the energy sector.
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With the emergence of economic globalization, the concept of the blue economy has evolved from fisheries to a broader context that comprised all kinds of biological and mineral resources, maritime trade, shipping, energy, and tourism. Intensive economic exploration of water areas is changing ecosystems, affecting biodiversity, and threatening sustainability. The transformations are felt globally in the form of climate change and environmental degradation, but the Arctic has appeared to be particularly vulnerable. Using the case of China, this chapter attempts to contribute to the convergence of economic benefits of exploring the Arctic with the urgent need to protect a fragile Arctic environment. The authors discuss how China’s involvement in Arctic-related activities can benefit the sustainable development of the blue economy in the region.
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Coastal wetlands contain some of the largest stores of pedologic and biotic carbon pools, and climate change is likely to influence the ability of these ecosystems to sequester carbon. Recent studies have attempted to provide data on carbon sequestration in both temperate and tropical coastal wetlands. Alteration of Arctic wetland carbon sequestration rates is also likely where coastal forcing mechanisms interact directly with these coastal systems. At present there are no data available to provide a detailed understanding of present day and historical carbon sequestration rates within Arctic coastal wetlands. In order to address this knowledge gap, rates of carbon sequestration were assessed within five Arctic coastal wetland sites in Norway. This was undertaken using radiometric dating techniques (²¹⁰Pb and ¹³⁷Cs) to establish a geochronology for recent wetland development, and soil carbon stocks were estimated from cores. Average carbon sequestration rates were varied, both between sites and over time, ranging between 19 and 603 g C m² y⁻¹, and these were correlated with increases in the length of the growing season. Stocks ranged between 3.67 and 13.79 Mg C ha⁻¹, which is very low compared with global average estimations for similar coastal systems, e.g. 250 Mg C ha⁻¹ for temperate salt marshes, 280 Mg C ha⁻¹ for mangroves, and 140 Mg C ha⁻¹ for seagrasses. This is most likely due to isostatic uplift and sediment accretion historically outpacing sea level rise, which results in wetland progradation and thus a continuous formation of new marsh with thin organic soil horizons. However, with increasing rates of sea level rise it is uncertain whether this trend is set to continue or be reversed.
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The ecosystems supporting Pacific salmon (Oncorhynchus spp.) are changing rapidly as a result of climate change and habitat alteration. Understanding how—and how consistently—salmon populations respond to changes at regional and watershed scales has major implications for fisheries management and habitat conservation. Chinook salmon (O. tshawytscha ) populations across Alaska have declined over the past decade, resulting in fisheries closures and prolonged impacts to local communities. These declines are associated with large‐scale climate drivers, but uncertainty remains about the role of local conditions (e.g., precipitation, streamflow, and stream temperature) that vary among the watersheds where salmon spawn and rear. We estimated the effects of these and other environmental indicators on the productivity of 15 Chinook salmon populations in the Cook Inlet basin, southcentral Alaska, using a hierarchical Bayesian stock‐recruitment model. Salmon spawning during 2003–2007 produced 57% fewer recruits than the previous long‐term average, leading to declines in adult returns beginning in 2008. These declines were explained in part by density dependence, with reduced population productivity following years of high spawning abundance. Across all populations, productivity declined with increased precipitation during the fall spawning and early incubation period and increased with above‐average precipitation during juvenile rearing. Above‐average stream temperatures during spawning and rearing had variable effects, with negative relationships in many warmer streams and positive relationships in some colder streams. Productivity was also associated with regional indices of streamflow and ocean conditions, with high variability among populations. The cumulative effects of adverse conditions in freshwater, including high spawning abundance, heavy fall rains, and hot, dry summers may have contributed to the recent population declines across the region. Identifying both coherent and differential responses to environmental change underscores the importance of targeted, watershed‐specific monitoring and conservation efforts for maintaining resilient salmon runs in a warming world.
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The Gulf of Alaska experienced extreme temperatures during 2014-2019, including the four warmest years ever observed. The goal of this study is to evaluate the ecological consequences of that warming event, across multiple trophic levels and taxa. We tested for evidence that observed sea surface temperature (SST) anomalies were outside the envelope of natural climate variability in order to evaluate the risk of novel ecosystem configurations. We also tested for state changes in shared trends of climate (n = 11) and biology (n = 48) time series, using a Bayesian implementation of Dynamic Factor Analysis (DFA). And we tested for evidence of novel ecological relationships during 2014-2019. We found that 3-year running mean SST anomalies during 2014-2019 were outside the range of anomalies from preindustrial simulations in CMIP5 models, indicating that the combined magnitude and duration of the warming event was outside the range of natural variability. A DFA model of climate variability also returned a shared trend in climate time series that was at unprecedented levels during 2014-2019. However, DFA models fit to biology data did not show shared trends of variability at unprecedented levels, and Hidden Markov Models fit to shared trends from the climate and biology models failed to find evidence of shifts to a new ecosystem state during 2014-2019. Conversely, we did find preliminary indications that community responses to SST variability strengthened during 2014-2019 after decades of a mostly neutral relationship. Tests for nonstationary patterns of shared variability suggest that covariance between SST and other ecologically-important climate variables remained weaker than during the 1970s Pacific Decadal Oscillation shift, suggesting the potential for muted ecological responses to the 2014-2019 event. Finally, we found that recent patterns of community variability appear to be highly dissimilar to those associated with the 1970s event, suggesting the potential for novel community states with continued warming. In summary, we find no evidence for wholesale ecosystem reorganization during 2014-2019, though nonstationary relationships among climate and community variables suggest the ongoing possibility of novel patterns of ecosystem functioning with continued warming.
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Statistical analysis findings are presented for typical industrial waste accumulated in the Extreme North and the Arctic, as well as abandoned industrial regions. The analysis has been performed of industrial waste formation in regions exporting energy resources (coal, oil, and gas). A group of waste has been identified that is accumulated in the largest volumes. Advanced methods of its recycling are considered. Advantages and limitations of these methods are outlined. An approach is suggested that is based on preparing slurry fuels from industrial waste by adding water. Laboratory experiments with such slurry fuels have been conducted. Typical values of the following energy performance characteristics are determined: ignition delay times, minimum threshold temperature of combustion initiation, maximum combustion temperature, and heat of combustion. Anthropogenic emission concentrations have been measured (the most hazardous of them are sulfur and nitrogen oxides) from the combustion of slurry fuels under study. Economic, environmental, and energy performance indicators of slurry fuels have been compared with those of conventional energy resources. Graphic Abstract
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Background: In a warmer world, microbial decomposition of previously frozen organic carbon (C) is one of the most likely positive climate feedbacks of permafrost regions to the atmosphere. However, mechanistic understanding of microbial mediation on chemically recalcitrant C instability is limited; thus, it is crucial to identify and evaluate active decomposers of chemically recalcitrant C, which is essential for predicting C-cycle feedbacks and their relative strength of influence on climate change. Using stable isotope probing of the active layer of Arctic tundra soils after depleting soil labile C through a 975-day laboratory incubation, the identity of microbial decomposers of lignin and, their responses to warming were revealed. Results: The β-Proteobacteria genus Burkholderia accounted for 95.1% of total abundance of potential lignin decomposers. Consistently, Burkholderia isolated from our tundra soils could grow with lignin as the sole C source. A 2.2 °C increase of warming considerably increased total abundance and functional capacities of all potential lignin decomposers. In addition to Burkholderia, α-Proteobacteria capable of lignin decomposition (e.g. Bradyrhizobium and Methylobacterium genera) were stimulated by warming by 82-fold. Those community changes collectively doubled the priming effect, i.e., decomposition of existing C after fresh C input to soil. Consequently, warming aggravates soil C instability, as verified by microbially enabled climate-C modeling. Conclusions: Our findings are alarming, which demonstrate that accelerated C decomposition under warming conditions will make tundra soils a larger biospheric C source than anticipated. Video Abstract.
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Metal contamination of food and water resources is a known public health issue in Arctic and sub-Arctic communities due to the proximity of many communities to mining and drilling sites. In addition, permafrost thaw may release heavy metals sequestered in previously frozen soils, potentially contaminating food and water resources by increasing the concentration of metals in freshwater, plants, and wildlife. Here we assess the enrichment of selected heavy metals in Alaskan soils by synthesizing publicly available data of soil metal concentrations. We analyzed data of soil concentrations of arsenic, chromium, mercury, nickel, and lead from over 1,000 samples available through the USGS Alaskan Geochemical Database to evaluate 1) the spatial distribution of sampling locations for soil metal analysis, 2) metal concentrations in soils from different land cover types and depths, and 3) the occurrence of soils in Alaska with elevated metal concentrations relative to other soils. We found substantial clustering of sample sites in the southwestern portion of Alaska in discontinuous and sporadic permafrost, while the continuous permafrost zone in Northern Alaska and the more populous Interior are severely understudied. Metal concentration varied by land cover type but lacked consistent patterns. Concentrations of chromium, mercury, and lead were higher in soils below 10 cm depth, however these deeper soils are under-sampled. Arsenic, chromium, mercury, nickel and lead concentrations exceeded average values for US soils by one standard deviation or more in 3.7% to 18.7% of the samples in this dataset. Our analysis highlights critical gaps that impede understanding of how heavy metals in thawing permafrost soils may become mobilized and increase exposure risk for Arctic communities.
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The deep sea is a major sink for debris; however, temporal changes and underlying mechanisms of litter accumulation on the seafloor remain unclear. Photographic surveys at the long-term ecological research (LTER) observatory HAUSGARTEN, in the eastern Fram Strait, have enabled the assessment of spatial and temporal variability of seafloor litter in the Arctic. Previous studies of time-series data (2002–2014) reported an increase in litter quantities from the northernmost and central stations. Here, we extended the analysis by three years until 2017 and included data from the southernmost station. A total of 16,157 images covering 60.5 km² were analyzed and combined with previous studies, to determine litter density, type and size compositions. Moreover, the interaction of litter with epibenthic megafauna was evaluated. Indicators of local maritime traffic, fisheries activity and summer sea ice extent were examined as potential drivers. The mean annual litter density ranged between 813 ± 525 (SEM) and 6,717 ± 2,044 (SEM) items km–2. Litter density clearly increased over time, and the northernmost station experienced the strongest increase. Plastics dominated at two of the stations whereas the northern station harbored mainly glass. Small-sized items accounted for 63%. Interaction with epibenthic fauna was frequent, especially with sessile organisms. Litter densities correlated with fishing and tourism vessel abundance, but no correlation was found with summer sea ice extent. This 15-year record of marine litter shows that even secluded Arctic ecosystems become increasingly subject to plastic pollution and that it will likely continue in the face of growing global plastic production rates and ineffective waste management policies.
Article
In the past decades, climate change has been affecting the reduction of ice coverage in the Arctic Ocean and thus providing opportunities for the development of commercial navigation. Many countries are becoming increasingly interested in the exploration of opening maritime routes. Initiating the Polar Silk Road (PSR), China aims at the diversification of its trade routes and linking the markets of Asia and Europe within a network of transport and economic corridors. The initiative requires improvement of navigational safety and passability of the Northern Sea Route (NSR) and other major lanes in the Arctic seas. In this paper, the authors discuss how China may collaborate with Russia to ensure the development of secure navigable deep-water shipping routes in the Arctic and to partner in the engineering and construction of large-tonnage tankers and icebreakers. The paper presents an overview of the current condition of the shipbuilding industry in Russia in relation to the construction of vessels and marine equipment in such segments as icebreaking, transport, port, and dredging fleet. The authors conclude with a summary of the existing technological, engineering, and economic obstacles and opportunities for China in the light of the establishment of navigable maritime routes in the Arctic Ocean.
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The average temperature in Alaska and the North American Arctic has risen at twice the rate of the global average due to climate change, causing changes to the natural environment that affect the physical, social, and emotional well‐being of people and communities. Social workers must be prepared to respond. Using a non‐probability, convenience sample, this study surveyed 159 social workers in Alaska to assess their attitudes and their perceptions of the effects of climate change on their clients and constituents. Results indicate that social workers in Alaska believe that climate change is happening, that human activities are responsible, and that it is a large threat to people in Alaska. Over 75% believe that climate change is dangerous for their clients now or will be dangerous in 10 years. Social workers report that in the past year their clients or constituents have experienced multiple climate change‐related problems with community infrastructure, health, and mental health.
Article
The Central Arctic Ocean (CAO) has attracted increased attention since representatives of the five Arctic coastal states together with representatives of four other states and the European Union signed the Agreement to Prevent Unregulated High Seas Arctic Fisheries in October 2018. This article assesses the significance of this development as an element in the evolving governance complex for the Arctic Ocean. We begin with a discussion of the relevant legal framework, including universal treaties such as the UN Convention on the Law of the Sea (UNCLOS) and the Arctic lex specialis going back to the conventions of the Arctic coastal States in the 19th century and elaborated more recently under the terms of the 1996 Ottawa Declaration on the Establishment of the Arctic Council and ensuing arrangements. We then analyze the 2018 Agreement itself as an innovative arrangement including Arctic and non-Arctic states. This assessment leads to several conclusions. The agreement constitutes a progressive contribution to the evolving governance complex for the Arctic Ocean. Striking features of the agreement are (i) its reliance on a precautionary approach put in place before human activities get underway on a large scale and designed to ensure sustainability and (ii) the inclusion of non-Arctic states and the European Union as signatories. We consider whether the Central Arctic Ocean Fisheries Agreement will emerge as an important precedent with significant implications for the governance of the CAO as an area beyond national jurisdiction and for the Arctic Ocean governance complex more generally.