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The Davis Strait - DCE - Nationalt Center for Miljø og Energi

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focus should improve our understanding and allow the distribution and recruitment<br />

<strong>for</strong> fish and shellfish to be predicted.<br />

Vulnerability of plankton to anthrop<strong>og</strong>enic impacts should be linked even<br />

more to local environmental conditions that influence the pelagic food web,<br />

such as temperature, water circulation and ice occurrence in order <strong>for</strong> the<br />

ecol<strong>og</strong>ical impact of future environmental disturbances associated with climate<br />

change and increased human activities (e.g. oil exploration) to be understood.<br />

4.2.7 Zooplankton sensitivity to oil<br />

In connection with hydrodynamic discontinuities, i.e. spring blooms, fronts,<br />

upwelling areas or the marginal ice zone, high biol<strong>og</strong>ical activity in the surface<br />

waters can be expected. Anthrop<strong>og</strong>enic impacts, e.g. oil pollution, might<br />

also influence productivity.<br />

Exposure experiments per<strong>for</strong>med on natural plankton communities (Hjorth<br />

et al. 2007, Hjorth et al. 2008) and copepods (Hjorth & Dahllöf 2008, Jensen et<br />

al. 2008b, Hjorth & Nielsen 2011) with pyrene (as a proxy <strong>for</strong> crude oil) have<br />

shown reductions in primary production, copepod grazing and production<br />

and an indirect positive effect on bacterial growth due to substrate release.<br />

Effects of pyrene have been studied in relation to a wide range of variables<br />

and life stages of the calanoid copepods Calanus finmarchicus and C. glacialis<br />

held under three different temperatures (0, 5 and 10º C) (Hjorth & Nielsen<br />

2011, Grenvald et al. in prep.).<br />

Adult C. finmarchicus were affected the most by pyrene exposure and<br />

sensitivity increased in warmer water in contrast to C. Glacialis, which may<br />

be partly due to buffering from lipid stores. Pyrene had no effect on development<br />

time <strong>for</strong> the two first non-feeding nauplii stages but clearly prolonged<br />

development time from nauplii stage III onwards when they begin to<br />

graze on phytoplankton. This was most pronounced at the lowest temperature<br />

(0º C), which suggests that the effects of pyrene exposure would be<br />

more severe during a spring phytoplankton bloom (~0º C in the upper 50m),<br />

since reduced grazing on phytoplankton would potentially lead to lower incorporation<br />

of phytoplankton into lipids with more being left ungrazed to<br />

sedimentate to the benthic community. <strong>The</strong> different responses to pyrene<br />

exposure in relation to food uptake, production and development time of<br />

the two species and higher water temperatures will not only affect them on a<br />

species level but will affect the Arctic food chain through a regime-shift to a<br />

less lipid-rich energy flux. Temperature stimulates C. finmarchicus more than<br />

C. glacialis, but the <strong>for</strong>mer is also more sensitive to oil. Vulnerability of<br />

plankton to anthrop<strong>og</strong>enic impacts should be linked even more to local environmental<br />

conditions that influence the pelagic food web, such as temperature,<br />

water circulation and ice occurrence. <strong>The</strong> impacts of human activity<br />

are likely to vary according to season, location and biol<strong>og</strong>ical activity. High<br />

biol<strong>og</strong>ical activity in surface waters can be expected in connection with hydrodynamic<br />

discontinuities, i.e. spring blooms, fronts, upwelling areas and<br />

the marginal ice zone. In Arctic marine habitats, the most severe ecol<strong>og</strong>ical<br />

consequences of massive anthrop<strong>og</strong>enic impacts (such as oil spills) are to be<br />

expected in seasons with high biol<strong>og</strong>ical activity within the pelagic food web<br />

in the upper 50m. In late summer after Calanus have migrated down to<br />

where they overwinter above the seabed biomass of grazers in surface waters<br />

is low (Dünweber et al. 2010) and biol<strong>og</strong>ical activity is lower or concen-<br />

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