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Last ned - Direktoratet for naturforvaltning

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Klimaendringer, hav<strong>for</strong>suring og langtransportert <strong>for</strong>urensning<br />

Ocean acidification<br />

Carbon dioxide concentrations both in the atmosphere and in the oceans have risen due to<br />

anthropogenic greenhouse gas emissions. As a result, the average pH of ocean surface water is now<br />

about 0.1 pH units lower than the pre-industrial level. It is estimated that pH may drop by almost 0.4<br />

units in Norway’s sea areas in the period up to 2100, although no modelling studies have been<br />

carried out in the Norwegian part of the North Sea and Skagerrak. Monitoring of acidification in the<br />

North Sea has recently been started, and the results so far show large diurnal and seasonal variations<br />

caused by biological activity.<br />

Five pressures and impacts have been defi<strong>ned</strong> <strong>for</strong> ocean acidification. Changes in pH and the carbon<br />

system are expected to have the greatest effects on ecosystem components. These changes may<br />

result in lower saturation levels of calcium minerals that organisms such as diatoms, crustaceans,<br />

molluscs and corals use to build calcium shells and skeletons. Food supplies <strong>for</strong> other organisms<br />

could be affected as a result, with repercussions along food chains. Lower pH in itself may also have<br />

direct effects on certain ecosystem components.<br />

There is also concern about whether ocean acidification may result in changes in the nutrient and<br />

organic material content of seawater, <strong>for</strong> example by affecting the nitrogen cycle. It could also result<br />

in changes in the bioavailability of micronutrients. The future effects of these two factors are<br />

assessed as moderate and minor respectively, but the knowledge base is very inadequate.<br />

Ocean acidification could also result in changes in the transport, mobilisation and metabolism of<br />

hazardous substances. The very limited knowledge we have at present makes it impossible to draw<br />

any conclusions about the effects on the ecosystem components that have been assessed.<br />

The final factor considered was a decrease in low-frequency ocean sound absorption. The assessment<br />

concluded that this will have no effect in the management plan area.<br />

It is expected that ocean acidification will have major cumulative effects in the management plan<br />

area in the future.<br />

Long-range pollution<br />

The cumulative effects of long-range pollution have been assessed both <strong>for</strong> the current situation and<br />

<strong>for</strong> the two scenarios <strong>for</strong> 2030, with most emphasis on the current situation.<br />

Four different pressures and impacts have been defi<strong>ned</strong> under the theme of long-range pollution.<br />

Long-range transport of hazardous substances (excluding radioactivity) is the factor that is assessed<br />

to have the greatest effect in the management plan area today. Pollution levels are generally low in<br />

the North Sea and Skagerrak, but higher than in the Norwegian and Barents Seas. The content of<br />

hazardous substances in sediments is low, but somewhat higher near the coast. Levels in biota are<br />

also low, but show wider geographical variation and variation between species, sampling media and<br />

pollutants. However, since many of the pollutants in question are bioaccumulative, they may be<br />

present at relatively high levels in species at the top of food chains. It is of particular concern that<br />

levels of dioxins and dioxin-like PCBs in the liver of a large proportion of the gadids sampled in the<br />

open sea exceeded the maximum levels permitted in foodstuffs. Moreover, levels of mercury in cod<br />

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