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BSEP116B Biodiversity in the Baltic Sea - Helcom

BSEP116B Biodiversity in the Baltic Sea - Helcom

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Recruitment (thousands)<br />

8000000<br />

7000000<br />

6000000<br />

5000000<br />

4000000<br />

3000000<br />

2000000<br />

1000000<br />

0<br />

1977<br />

1980<br />

hatch<strong>in</strong>g of cod eggs, has caused high cod egg<br />

mortality (Köster et al. 2003). This, toge<strong>the</strong>r with<br />

very high fish<strong>in</strong>g pressure, has resulted <strong>in</strong> historically<br />

low values of <strong>the</strong> cod stock s<strong>in</strong>ce <strong>the</strong> early<br />

1990s (ICES 2008b, Figure 3.5.1) altough <strong>the</strong>re<br />

has been an <strong>in</strong>crease <strong>in</strong> <strong>the</strong> eastern cod spawn<strong>in</strong>g<br />

stock biomass dur<strong>in</strong>g <strong>the</strong> past three years. This<br />

observed <strong>in</strong>crease s<strong>in</strong>ce 2005 has been a result<br />

of relatively strong year classes <strong>in</strong> 2003 and 2005<br />

(ICES 2008d). Release of <strong>the</strong> predation pressure<br />

by cod, accompanied by favourable hydrographic<br />

conditions, has allowed <strong>the</strong> sprat stock to <strong>in</strong>crease<br />

s<strong>in</strong>ce <strong>the</strong> late 1980s, which toge<strong>the</strong>r with herr<strong>in</strong>g<br />

has strongly dom<strong>in</strong>ated <strong>the</strong> <strong>Baltic</strong> fish communities<br />

s<strong>in</strong>ce <strong>the</strong>n (Figure 3.5.2 and Figure 3.5.3). This shift<br />

to dom<strong>in</strong>ation by a pelagic fish community represents<br />

a profound change <strong>in</strong> <strong>the</strong> mar<strong>in</strong>e ecosystem,<br />

also called a ’regime shift’ (e.g., Alheit et al. 2005).<br />

In addition, <strong>the</strong>re are several non-commercial<br />

mar<strong>in</strong>e fish present <strong>in</strong> <strong>the</strong> <strong>Baltic</strong> <strong>Sea</strong>, for example,<br />

gobies Pomatoschistus spp., three-sp<strong>in</strong>ed stickle-<br />

Recruitment<br />

SSB<br />

1983<br />

1986<br />

1989<br />

1992<br />

1995<br />

1998<br />

2001<br />

2004<br />

2007<br />

140000<br />

120000<br />

100000<br />

80000<br />

60000<br />

40000<br />

20000<br />

Figure 3.5.2. Recruitment (R, age 1 <strong>in</strong> thousands) and spawn<strong>in</strong>g<br />

stock biomass (SSB, <strong>in</strong> tonnes) of <strong>the</strong> Gulf of Riga herr<strong>in</strong>g dur<strong>in</strong>g<br />

1977–2007 (ICES 2008b).<br />

0<br />

SSB (tonnes)<br />

back (Gasterosteus aculeatus), n<strong>in</strong>e-sp<strong>in</strong>ed stickleback<br />

(Pungitius pungitus), and pipefish (Nerophis<br />

ophidion). These species are adapted ma<strong>in</strong>ly<br />

to low-sal<strong>in</strong>ity estuar<strong>in</strong>e areas and play several<br />

significant roles <strong>in</strong> <strong>the</strong> ecosystem. Despite <strong>the</strong>ir<br />

importance, <strong>the</strong> knowledge on <strong>the</strong> spatio-temporal<br />

population dynamics of <strong>the</strong>se fish species is relatively<br />

poor.<br />

Freshwater fish<br />

The most common freshwater species that are<br />

found <strong>in</strong> a majority of coastal areas of <strong>the</strong> <strong>Baltic</strong> <strong>Sea</strong><br />

are perch, roach, ruffe (Gymnocephalus cernuus),<br />

ide (Leuciscus idus), pike and whitebream (Blicca<br />

bjoerkna) (Ådjers et al. 2006). The most recent<br />

evidence suggests that freshwater species have<br />

exhibited different population dynamics <strong>in</strong> various<br />

parts of <strong>the</strong> <strong>Baltic</strong> <strong>Sea</strong> over <strong>the</strong> past 10–20 years for<br />

which monitor<strong>in</strong>g data are available. For example,<br />

coastal fish surveys show a significant <strong>in</strong>crease <strong>in</strong><br />

perch and roach abundance <strong>in</strong> <strong>the</strong> Archipelago <strong>Sea</strong><br />

(Figure 3.5.4, F<strong>in</strong>bo and Brunskär). This is thought<br />

to be caused by <strong>the</strong> ongo<strong>in</strong>g coastal eutrophication,<br />

because <strong>the</strong>se fish have been shown to be<br />

favoured by moderate eutrophication, as well as<br />

<strong>in</strong>creased water temperatures (HELCOM 2006b). In<br />

o<strong>the</strong>r areas, such as <strong>the</strong> west Estonian Archipelago<br />

<strong>Sea</strong> (Hiiumaa), Daugava, Curon<strong>in</strong>an Lagoon and<br />

Kvädöfjärden, <strong>the</strong> same species have decreased<br />

significantly or even collapsed (Figure 3.5.4). This,<br />

as well as <strong>the</strong> decl<strong>in</strong>e <strong>in</strong> pike and pikeperch stocks<br />

<strong>in</strong> <strong>the</strong> Curonian lagoon, Daugava estuary and Pärnu<br />

Bay which all are characterized as hav<strong>in</strong>g a high level<br />

of eutrophication, has occurred ow<strong>in</strong>g to a fish<strong>in</strong>g<br />

pressure that has been too high (Ådjers et al. 2006,<br />

HELCOM 2006b).<br />

56<br />

Recruitment (millions)<br />

300000<br />

250000<br />

200000<br />

150000<br />

100000<br />

50000<br />

0<br />

1974<br />

1977<br />

Recruitment<br />

SSB<br />

1980<br />

1983<br />

1986<br />

1989<br />

Figure 3.5.3. Recruitment (R, age 1 <strong>in</strong> millions) and spawn<strong>in</strong>g stock<br />

biomass (SSB, <strong>in</strong> thousand tonnes) of sprat <strong>in</strong> <strong>the</strong> <strong>Baltic</strong> <strong>Sea</strong> (ICES SD<br />

22–32) dur<strong>in</strong>g 1974–2007 (ICES 2008b).<br />

1992<br />

1995<br />

1998<br />

2001<br />

2004<br />

2007<br />

2000<br />

1800<br />

1600<br />

1400<br />

1200<br />

1000<br />

800<br />

600<br />

400<br />

200<br />

0<br />

SSB (thousand tonnes)<br />

A number of community-level (number of species,<br />

total biomass, species diversity, slope of size<br />

spectrum, and average trophic level of catch) and<br />

species-level (biomass, mean age, mortality, mean<br />

length, and slope of size spectrum) <strong>in</strong>dicators<br />

for coastal fish were recently developed with<strong>in</strong><br />

HELCOM. Some of <strong>the</strong>se <strong>in</strong>dicators have been used<br />

<strong>in</strong> <strong>the</strong> pilot studies us<strong>in</strong>g <strong>the</strong> <strong>Biodiversity</strong> Assessment<br />

Tool BEAT (see Chapter 5).<br />

Migratory species<br />

Several migratory species <strong>in</strong> <strong>the</strong> <strong>Baltic</strong> <strong>Sea</strong> are of<br />

commercial value. These <strong>in</strong>clude salmon (Salmo

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