BSEP116B Biodiversity in the Baltic Sea - Helcom
BSEP116B Biodiversity in the Baltic Sea - Helcom
BSEP116B Biodiversity in the Baltic Sea - Helcom
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<strong>Baltic</strong> <strong>Sea</strong>, most of <strong>the</strong> 105 recorded by-caught<br />
porpoises <strong>in</strong> <strong>the</strong> years 1990 to 2001 were<br />
reported from bottom-set gillnet fisheries or were<br />
stranded with characteristic net-marks (Siebert<br />
et al. 2006). While <strong>the</strong>se numbers are considered<br />
to be m<strong>in</strong>imum figures, Rubsch & Kock (2004)<br />
estimated <strong>the</strong> annual by-catch <strong>in</strong> <strong>the</strong> German<br />
set-net fishery to be 57 <strong>in</strong>dividuals <strong>in</strong> <strong>the</strong> western<br />
<strong>Baltic</strong> <strong>Sea</strong> and 25 <strong>in</strong> <strong>the</strong> German part of <strong>the</strong> <strong>Baltic</strong><br />
Proper. A total of 45 by-caught animals were<br />
reported from Polish waters between 1990 and<br />
1999 (Skóra & Kuklik 2003). In Latvia, two porpoises<br />
were found entangled <strong>in</strong> fish<strong>in</strong>g nets <strong>in</strong><br />
<strong>the</strong> Gulf of Riga <strong>in</strong> October 2003 and <strong>in</strong> January<br />
2004, respectively (ASCOBANS 2004). A modell<strong>in</strong>g<br />
study by Berggren et al. (2002) estimated<br />
<strong>the</strong> potential limits to anthropogenic mortality<br />
for harbour porpoises. To achieve <strong>the</strong> goal of a<br />
population recovery to more than 80% of carry<strong>in</strong>g<br />
capacity, by-catch limits of two <strong>in</strong>dividuals<br />
per year <strong>in</strong> <strong>the</strong> <strong>Baltic</strong> Proper and three <strong>in</strong>dividuals<br />
per year <strong>in</strong> <strong>the</strong> Kiel Bight–Mecklenburg Bight area<br />
should not be exceeded.<br />
<strong>Sea</strong>birds<br />
Several studies from different parts of <strong>the</strong> <strong>Baltic</strong><br />
<strong>Sea</strong> have shown that set-net (gillnet) fisheries <strong>in</strong><br />
<strong>the</strong> <strong>Baltic</strong> <strong>Sea</strong> cause <strong>the</strong> death of tens of thousands<br />
of birds every year. The by-catch problem is of<br />
special relevance where gillnet fisheries are practiced<br />
<strong>in</strong> areas with high concentrations of rest<strong>in</strong>g,<br />
moult<strong>in</strong>g or w<strong>in</strong>ter<strong>in</strong>g seabirds. The conflicts are<br />
usually seasonal.<br />
F<strong>in</strong>land, especially eider, black guillemot (Cepphus<br />
grylle), razorbill (Alca torda) and red-throated and<br />
black-throated divers (G. stellata and G. arctica)<br />
are <strong>the</strong> species most affected (Hario 1998). The<br />
most recent Swedish by-catch study cover<strong>in</strong>g <strong>the</strong><br />
Swedish fishery as a whole (Lunneryd et al. 2004)<br />
showed that <strong>the</strong> cormorant was <strong>the</strong> species predom<strong>in</strong>antly<br />
affected, followed by eider, guillemot,<br />
merganser, and long-tailed duck. The threat of<br />
drown<strong>in</strong>g <strong>in</strong> fish<strong>in</strong>g gear is larger for piscivorous<br />
species than for benthophagic ducks, although <strong>in</strong><br />
most areas <strong>the</strong> total number of piscivorous birds<br />
drowned is lower ow<strong>in</strong>g to <strong>the</strong>ir smaller populations.<br />
The studies available ma<strong>in</strong>ly <strong>in</strong>vestigated<br />
bird by-catches <strong>in</strong> near-coastal waters. Information<br />
about <strong>the</strong> by-catch on fish<strong>in</strong>g grounds<br />
fur<strong>the</strong>r offshore is scarce, although it is known<br />
that high densities of birds and high fish<strong>in</strong>g <strong>in</strong>tensity<br />
may overlap seasonally <strong>in</strong> <strong>the</strong>se areas also.<br />
Ano<strong>the</strong>r effect of fisheries on birds is related to<br />
<strong>the</strong> discard<strong>in</strong>g of unwanted catch and offal at<br />
sea. Gulls especially benefit from this food source.<br />
Fur<strong>the</strong>rmore, <strong>the</strong> <strong>in</strong>crease <strong>in</strong> sprat stocks as a consequence<br />
of cod overfish<strong>in</strong>g is expected to have a<br />
positive effect on piscivorous birds, especially auks.<br />
Abiotic environment<br />
In general, <strong>the</strong> effects of bottom-towed gears on<br />
abiotic habitats are primarily (i) removal of physical<br />
features, (ii) reduction <strong>in</strong> complexity, and (iii)<br />
alteration of <strong>the</strong> physical structure of <strong>the</strong> seafloor<br />
(ICES 2005b).<br />
Piscivorous birds (divers, grebes, mergansers,<br />
auks, cormorants) and benthophagic ducks may<br />
become entangled and die <strong>in</strong> fish<strong>in</strong>g gear. At<br />
<strong>the</strong> sou<strong>the</strong>rn coast of <strong>the</strong> <strong>Baltic</strong> <strong>Sea</strong>, <strong>the</strong> longtailed<br />
duck (Clangula hyemalis) is <strong>the</strong> most<br />
numerous species caught <strong>in</strong> gillnets, followed by<br />
black scoter (Melanitta nigra), common scoter<br />
(Melanitta fusca) and red-throated diver (Gavia<br />
stellata), while <strong>in</strong> some areas, eider (Somateria<br />
mollissima), greater scaup (Aythya marila), guillemot<br />
(Uria alge) and cormorant (Phalacrocorax<br />
carbo) are also found <strong>in</strong> large numbers (I.L.N.<br />
& IfAÖ 2005, Schirmeister 2003, Stempniewicz<br />
1994, Kirchoff 1982, Kowalski & Manikowski<br />
1982). In <strong>the</strong> coastal waters of Lithuania, losses<br />
of Steller’s eiders are of concern ow<strong>in</strong>g to <strong>the</strong><br />
rareness of this species (Dagys & Žydelis 2002). In<br />
Towed demersal fish<strong>in</strong>g gear can also substantially<br />
affect <strong>the</strong> abiotic environment <strong>in</strong> <strong>the</strong> <strong>Baltic</strong><br />
<strong>Sea</strong> area, where this fish<strong>in</strong>g practice is applied.<br />
For example, <strong>in</strong> <strong>the</strong> <strong>in</strong>tensely fished Kiel Bight, <strong>the</strong><br />
total area disturbed was estimated at 630 km 2<br />
per year caus<strong>in</strong>g a mobilization of nutrients<br />
estimated to be 0.6–2.5 tonnes silicate, 0.3–1.3<br />
tonnes nitrogen and 0.1–0.5 tonnes phosphorus<br />
per km 2 and year (Krost 1990). The <strong>in</strong>crease<br />
<strong>in</strong> nutrient concentrations was followed by an<br />
<strong>in</strong>crease <strong>in</strong> oxygen consumption of 1.5–7.8 tonnes<br />
per km 2 and year. This po<strong>in</strong>ts to a considerable<br />
impact of fish<strong>in</strong>g activities on <strong>the</strong> mar<strong>in</strong>e environment<br />
(Krost 1990). There is no documented<br />
evidence that traditional coastal fisheries (e.g., by<br />
means of trapnets and gillnets) have affected <strong>the</strong><br />
abiotic environment.<br />
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