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BSEP116B Biodiversity in the Baltic Sea - Helcom

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Mussel bed reef community, Jasmund, Germany<br />

86<br />

was fixed at 50% from <strong>the</strong> reference value, which<br />

also was used if no o<strong>the</strong>r acceptable deviation was<br />

specified by <strong>the</strong> case study authors.<br />

The BEAT matrix divides <strong>the</strong> range of possible<br />

values <strong>in</strong>to five classes: high, good, moderate,<br />

poor, and bad. In this system, ’high’ and ’good’<br />

are essentially equivalent to ’favourable conservation<br />

status’ (~ ‘good environmental status’) and<br />

’moderate’, ’poor’, and ’bad’ are equivalent to<br />

’unfavourable conservation status’ (~ impaired<br />

status). For technical details of <strong>the</strong> assessment<br />

approach and def<strong>in</strong>itions used for <strong>the</strong>se five<br />

classes, see Box 5.1.<br />

In order to create an overall assessment of <strong>the</strong> site,<br />

<strong>the</strong> reported <strong>in</strong>dicators were regrouped <strong>in</strong> <strong>the</strong> follow<strong>in</strong>g<br />

categories: Category I - Landscapes, Category<br />

II – Communities, and Category III – Species,<br />

follow<strong>in</strong>g <strong>the</strong> structure agreed <strong>in</strong> <strong>the</strong> HELCOM<br />

BSAP. In addition to <strong>the</strong>se three categories, an<br />

additional Category IV for supportive features was<br />

<strong>in</strong>cluded to cover o<strong>the</strong>r parameters of <strong>in</strong>terest (e.g.,<br />

nutrient concentrations, physical variables). The<br />

topics covered under each of <strong>the</strong>se categories are<br />

presented <strong>in</strong> Table 5.2. With<strong>in</strong> <strong>the</strong> Categories I–IV,<br />

weighted averages of <strong>the</strong> ratios between prist<strong>in</strong>e<br />

and present status, or Ecological Quality Ratios<br />

(EQRs), as well as <strong>the</strong> acceptable deviations of <strong>the</strong><br />

<strong>in</strong>dividual <strong>in</strong>dicators were calculated. If not specified<br />

o<strong>the</strong>rwise, <strong>the</strong> weight<strong>in</strong>g was kept neutral<br />

by giv<strong>in</strong>g each of <strong>the</strong> <strong>in</strong>dicators an equal weight.<br />

On <strong>the</strong> basis of <strong>the</strong> EQR and AcDev values, <strong>the</strong><br />

Categories I–IV were each given a quantitative<br />

assessment accord<strong>in</strong>g to <strong>the</strong> pr<strong>in</strong>ciples described<br />

above for a s<strong>in</strong>gle <strong>in</strong>dicator (rang<strong>in</strong>g from high to<br />

bad status).<br />

The overall assessment of <strong>the</strong> site or geographic<br />

unit, comb<strong>in</strong><strong>in</strong>g <strong>the</strong> results of <strong>the</strong> four categories,<br />

is conducted by apply<strong>in</strong>g <strong>the</strong> so-called ‘One<br />

out - All out’ pr<strong>in</strong>ciple to <strong>the</strong> Categories I–III. This<br />

implies that <strong>the</strong> worst-perform<strong>in</strong>g category of<br />

<strong>the</strong>se three def<strong>in</strong>es <strong>the</strong> overall status of <strong>the</strong> site.

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