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Marine områder 2011 - DCE - Nationalt Center for Miljø og Energi

Marine områder 2011 - DCE - Nationalt Center for Miljø og Energi

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Registrations from the Great Belt and Kalundborg Fjord showed that the<br />

porpoises are present all year round, but that the abundance is highest in<br />

the Great Belt during summer and in Kalundborg Fjord during winter. In<br />

addition, there was a distinct diurnal variation in sound signals with<br />

most detection during night and fewest during daytime.<br />

Hazardous substances and biol<strong>og</strong>ical effects<br />

In 20 % of the common mussel samples and 86 % of the fish samples the<br />

content of heavy metals were higher than Environmental Quality Standards<br />

<strong>for</strong> biota (EQS) due to mercury (Hg) but no metals were above the<br />

EU criteria <strong>for</strong> content in food. Only the content of nickel (Ni) and copper<br />

(Cu) in the soft clams Mya arenaria from Ringkøbing Fjord were above the<br />

‘good ecol<strong>og</strong>ical status’ limit according to Norwegian assessment criteria.<br />

Concentrations of metals in seawater from Skive Fjord in 2010/<strong>2011</strong> were<br />

within the EU limits <strong>for</strong> nickel (Ni), lead (Pb), and cadmium (Cd).<br />

The content of TBT in mussels is decreasing in the areas where time<br />

trends of significance are available due to the ban of antifouling paints.<br />

However, at more than 50 % of the stations, the concentrations are still<br />

above the ecotoxicol<strong>og</strong>ical assessment criteria (EAC) so an impact from<br />

TBT in the marine environment can still be expected.<br />

PAH in mussels were not above the EAC and in most cases corresponding<br />

to or below the ‘background’ criteria <strong>for</strong> the North Sea.<br />

Chlorinated compounds in fish were generally below the EAC except <strong>for</strong><br />

CB118 (50 % of fish above EAC) and HCB (25 % of fish above EAC), and<br />

also CB138 were above EAC in a few samples. Thus it cannot be ruled out<br />

that CB118 and HCB still have an impact in the marine environment.<br />

It is possible to identify the ge<strong>og</strong>raphic origin of flounder based on the<br />

composition of chlorinated compounds.<br />

Time trends <strong>for</strong> hazardous compounds are in general decreasing especially<br />

<strong>for</strong> the organic compounds under regulation (PCB, and TBT) –<br />

most evident in Langerak (the Limfjord).<br />

Imposex and intersex in sea snails due to exposure to TBT are still widespread<br />

and assessed as an environmental problem in Danish marine waters.<br />

Based on the OSPAR criteria <strong>for</strong> imposex and intersex, good ecol<strong>og</strong>ical<br />

status is only found in the North Sea and the Skagerrak.<br />

Levels of imposex and intersex are so high in the inner Danish marine<br />

waters that in relation to OSPAR and HELCOM criteria many areas have<br />

to be considered as not acceptable and even bad in certain contaminated<br />

harbours and marinas. However, the level has decreased markedly in recent<br />

years, which indicates that further improvements can be expected.<br />

Investigations of lysosomal membrane stability in common mussels indicated<br />

that approximately one third of the investigated coastal areas were<br />

affected by hazardous substances and especially PAH.<br />

Investigations of eelpout showed marked differences in the degree of effects<br />

between areas, both concerning presence of mal<strong>for</strong>mation in fry,<br />

CYP1A enzyme activity, and PAH metabolites in the gall. A correlation<br />

between the activity of CYP1A and the concentration of PAH and PCB<br />

was found, whereas this was not the case <strong>for</strong> mal<strong>for</strong>mation in fry and the<br />

measured hazardous substances.<br />

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