Condition Factor (CF) of fishޥᅈࡋ Hepatosomatic Index (HSI) of fish طᡏКࡰኧ Gonadosomatic Index (GSI) of fish ғဏࡰኧ Fin erosion of fish ങ៧ᆭឳำࡋ Body burden of heavy metals and trace organics in mussels ຢنᡏϣख़ߎឦᆶ༾ໆԖᐒނ
ኻ࿉:ᅕǺᔮങᜪၗྍໆ ीᆉБ;ݤᙖҗКၨਔ໔ϣΕబǵᒃങғނໆǵڕങໆᆶԝΫ ޑᖿ༈ǶԶقǴԝΫຬຫΕబᆶԋߏǴԜၗྍё ຎࣁຬၸӼӄғނज़ڋǶӦύੇБय़ޑၗྍຑЬाϩڕങ ໆᖿ༈ǵғނໆፓǵDQVFޑኧᏵǶ Fig. 1: Status of fish stocks in the International Council for the Exploration of the Sea (ICES) and General Fisheries Commission for the Mediterranean (GFCM) fishing regions of Europe, 2006
蓂Note: The chart shows the proportion of assessed stocks which are overfished (red) and stocks within safe biological limits (blue): In the Baltic Sea, 12 stocks were assessed and 20% of them are overfished.
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اǵੇࢩߥៈ୯ϣѦԖࡰ ୯ϣ (Ҟ٬Ҕޑȑ MPA՞य़ᑈКٯ (ՉБਢᕮਏࡰȑ a) ԖਏᅕэMPAय़ᑈК b) MPAسߥៈભᆶᆅྗ ߾ c) ुڋӚࡹ۬ǵޗǵᅕ ቚMPAϐႴᓰࡼ (୯ϣࠄБѤ҉ុวࡰ)٩ ᏵғᄊǵޗᔮǵݯΟቫय़ วӵނᅿᙦࡋǵճიᡏӧ MPAᆅಔᙃ܌՞КٯǵMPA࣬ ᜢࡓݤࡰǶ
ߥៈᆅԋਏຑ (PAME) 2005 ‒ 2010Ǵ 140ঁ୯ৎǴ9,000ঁ ຑ Average scores for 31 headline indicators from 'most recent' studies. Indicators with < 500 entries have been deleted from 4,151 assessments. Colors used to indicate the element of the IUCN-WCPA Framework: Black indicates ‘context’ factors, aqua: planning, Red : inputs, brown : process, yellow : 38 outputs, and green : outcome
Extent of Mangrove and Seagrass, and Coral Condition Source: Adapted with permission from Butchart et al. 2010 41
ມǵ ǵۓӦ ᐞࢪ:εൕᕛੇ۞ݮᅱෳ ෳໆБԄ:ੇဂᆫރᄊᆶН፦ᕉნёᙖҗੇޑᙦǵ ғոΚǵғ่ᄬǵߕғᝯᜪᆶੇယТಔᙃϐ C:N:PϡનКෳໆѐຑǶ 蓂The patterns of seagrass abundance have also differed between habitat types since long-term monitoring was established (Fig. 3).
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