BSEP116B Biodiversity in the Baltic Sea - Helcom
BSEP116B Biodiversity in the Baltic Sea - Helcom
BSEP116B Biodiversity in the Baltic Sea - Helcom
Create successful ePaper yourself
Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.
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.