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Interim report of the HELCOM CORESET project

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11. Temporal considerations<br />

Frequency: ideally as <strong>of</strong>ten as possible, but realistically perhaps every fi fth year<br />

12. Current monitoring<br />

Monitoring done in all <strong>the</strong> Contracting States. Measured parameters must be compared and <strong>the</strong> indicator<br />

species agreed and included in <strong>the</strong> monitoring.<br />

13. Proposed or perceived target setting approach with a short justifi cation.<br />

The reference level for each seabird population should be set at a population size that is considered<br />

desirable for each individual species within each geographical area. This should be set for each species<br />

based on expert judgement <strong>of</strong> when population levels were subject to low impact by human activities.<br />

In <strong>the</strong> OSPAR EcoQO <strong>the</strong> target level was set to <strong>the</strong> level <strong>of</strong> standard deviation from <strong>the</strong> reference level.<br />

The lower target depended, however, partly on <strong>the</strong> species; species laying one egg were given stricter<br />

target (being more sensitive) than species laying more eggs.<br />

The proportion <strong>of</strong> species reaching <strong>the</strong>ir target is <strong>the</strong> “integrated indicator”. The target level could be<br />

75% as in <strong>the</strong> OSPAR EcoQO.<br />

Additional indicators for <strong>the</strong> breeding seabird populations<br />

The abundance <strong>of</strong> breeding seabirds is a good indicator for following long-term changes, whereas it is not<br />

feasible for detecting short-term changes. Short-term responses to environmental changes can be better<br />

followed by reproductive parameters, such as breeding success or brood size. The OSPAR EcoQO (under<br />

development) for <strong>the</strong> breeding success <strong>of</strong> <strong>the</strong> kittiwake is an example <strong>of</strong> such an indicator. It may be used<br />

as an indicator for <strong>the</strong> abundance <strong>of</strong> sandeel that also serves as a major food source for many o<strong>the</strong>r bird,<br />

fi sh and marine mammal species. Sandeel availability may be low because <strong>of</strong> natural reasons, or through<br />

industrial fi shing that competes with seabirds. When <strong>the</strong> breeding success <strong>of</strong> kittiwake is low over a threeyear<br />

period, this is likely to be triggered by low abundance <strong>of</strong> sandeel in coastal areas. The indicator thus<br />

shows <strong>the</strong> status <strong>of</strong> sandeel and kittiwake populations and <strong>the</strong> need to reduce industrial fi shing.<br />

In <strong>the</strong> Baltic Sea, <strong>the</strong> availability <strong>of</strong> data on brood size and breeding success needs to be clarifi ed.<br />

The national monitoring programmes to monitor <strong>the</strong> breeding populations <strong>of</strong> sea birds can be also used to<br />

develop a distribution indicator. The indicator would require sub-basin wise species selection and setting<br />

<strong>of</strong> GES boundaries. In addition, it should be decided which density threshold is used to determine <strong>the</strong><br />

margin <strong>of</strong> distribution.<br />

4.6. Proportion <strong>of</strong> seabirds being oiled<br />

1. Working team<br />

Sea birds<br />

2. Name <strong>of</strong> candidate indicator<br />

Proportion <strong>of</strong> seabirds being oiled<br />

3. Unit <strong>of</strong> <strong>the</strong> candidate indicator<br />

Number <strong>of</strong> oiled seabirds per species<br />

4. Description <strong>of</strong> proposed indicator<br />

Proportion <strong>of</strong> oiled seabirds found in <strong>the</strong> winter-time population counts are being used for <strong>the</strong> estimate<br />

<strong>of</strong> this indicator.<br />

In addition, proportion <strong>of</strong> oiled seabirds among those found dead or dying on beaches can be used as<br />

an additional information.<br />

5. Functional group or habitat type<br />

Mainly <strong>of</strong>fshore benthic feeders and <strong>of</strong>fshore pelagic and surface feeding birds<br />

6. Policy relevance<br />

Descriptor 1<br />

Descriptor 4<br />

165

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