The Davis Strait - DCE - Nationalt Center for Miljø og Energi
The Davis Strait - DCE - Nationalt Center for Miljø og Energi
The Davis Strait - DCE - Nationalt Center for Miljø og Energi
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glaucous gulls, great black-backed gulls, killer whales, pilot whales, Arctic<br />
fox, and polar bears). This is particularly true in relation to biomagnification<br />
of PCBs and DDT. AMAP activities have also shown a decrease in the levels<br />
of some POPs (e.g. PCBs and DDT), resulting from introduction of bans and<br />
restrictions relating to their use in other parts of the world (AMAP 2004,<br />
Muir & de Wit 2010). At the same time, however, use of new persistent pollutants,<br />
currently produced in large quantities, is on the increase (AMAP<br />
2004, Muir & de Wit 2010). <strong>The</strong>se substances have also been detected in animals<br />
from Greenland; such as the brominated flame retardants hexabromocyclododecane<br />
(HBCD) or tetrabromobisphenol (TBBPA), chemicals which<br />
are produced in high volumes. In recent years their presence has been reported<br />
in sediment and biota from the marine environment (Frederiksen et<br />
al. 2007), with concentrations of HBCDs in animals from West Greenland<br />
generally being lower than in the same species from East Greenland. <strong>The</strong><br />
same effect has previously been described <strong>for</strong> other hal<strong>og</strong>enated compounds<br />
such as polybrominated diphenyl ethers (PBDEs) (Vorkamp et al. 2007).<br />
Another, more localised source of pollution is mining activity, e.g. the olivine<br />
mine at Seqi in Niaqunngunaq (Fiskefjord) north of Nuuk. <strong>The</strong> nearest<br />
settlement is Atammik, at the inlet of the fjord. <strong>The</strong> mine was in operation<br />
between 2005 and 2010. Since 2004, environmental monitoring has been<br />
conducted every year in order to assess any impact from mining. During operation<br />
increased levels of some elements, particularly chromium and nickel,<br />
were measured in lichens, blue mussels and seaweed. Generation and<br />
spread of metal-contaminated dust from the roads and the ore-crushing facility<br />
was considered the main source of this contamination. Since closure of<br />
the mine in 2010, the environmental impact has decreased and is presently<br />
considered as being insignificant <strong>for</strong> the Niaquungunaq fjord system (Søndergaard<br />
& Asmund 2011).<br />
7.1.1 Tributyltin (TBT)<br />
<strong>The</strong> antifouling agent, tributyltin (TBT) can be found in many coastal waters<br />
in both industrial and developing countries with the highest levels in harbours<br />
and shipping lanes (Sousa et al. 2009). In remote areas such as the Arctic<br />
environment, TBT levels are usually low, except close to harbours, e. g.<br />
Sisimiut (Villumsen & Ottosen 2006) and shipping lanes (Strand & Asmund<br />
2003, AMAP 2004, Berge et al. 2004). <strong>The</strong> presence of TBT residues in harbour<br />
porpoises from Greenland documents that organotin compounds have<br />
also spread to the Arctic region, though the concentrations are rather low<br />
(Jacobsen & Asmund 2000, Strand et al. 2005).<br />
7.1.2 Petroleum hydrocarbons and Polycyclic Aromatic Hydrocarbons<br />
(PAH)<br />
Petroleum hydrocarbons represent several hundred chemical compounds<br />
originating from crude oil e.g. gasoline, kerosene, and diesel fuel. Of primary<br />
interest <strong>for</strong> assessment of the environmental impacts are the aromatic hydrocarbons<br />
(i.e., benzene, ethylbenzene, toluene, and xylenes). Another important<br />
group is the polycyclic aromatic hydrocarbons (PAHs), which originate<br />
from two main sources: combustion (pyr<strong>og</strong>enic) and crude oil (petr<strong>og</strong>enic).<br />
PAHs represent the most toxic fraction of oil and are released to the<br />
environment through oil spills and discharge of produced water (see also<br />
chapter 10 and 11). Twentythree PAHs are included on the lists of priority<br />
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