Member State report / Art9 / 2012 / D3 / Belgium / NE Atlantic: Greater North Sea
Report type | Member State report to Commission |
MSFD Article | Art. 9 Determination of GES (and Art. 17 updates) |
Report due | 2012-10-15 |
GES Descriptor | D3 Commercial fish and shellfish |
Member State | Belgium |
Region/subregion | NE Atlantic: Greater North Sea |
Reported by | FPS Health, Food Chain safety and Environment - Service Marine environment |
Report date | 2012-08-16 |
Report access | ANSBE_MSFD9GES_20130314.xml |
GES component |
D3
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3.1 Level of pressure of the fishing activity |
3.1.1 Fishing mortality |
3.1.2 Fish catch/biomass ratio |
3.2 Reproductive capacity of the stock |
3.2.1 Spawning stock biomass |
3.2.2 Biomass indices |
3.3 Population age and size distribution |
3.3.1 Proportion of larger fish |
3.3.3 Fish length distribution |
3.3.4 Fish size at sexual maturation |
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Method used |
ANS-BE-MS-1: Conform the Directive, GES and the environmental targets for the Belgian marine waters are defined on the basis of the eleven qualitative descriptors listed in Annex I of the Directive. The definition of GES is expressed in a qualitative description of what GES would look like when achieved for each of the descriptors. This is then underpinned by a set of more detailed quantitative environmental targets based on established environmental thresholds/limits for state, pressure or impact (Art. 10). Where quantitative environmental thresholds could not be set, trend-based or qualitative thresholds were used. The complete package of GES and environmental targets needs to give a complete and balanced overview. |
ANS-BE-MS-1: Conform the Directive, GES and the environmental targets for the Belgian marine waters are defined on the basis of the eleven qualitative descriptors listed in Annex I of the Directive. The definition of GES is expressed in a qualitative description of what GES would look like when achieved for each of the descriptors. This is then underpinned by a set of more detailed quantitative environmental targets based on established environmental thresholds/limits for state, pressure or impact (Art. 10). Where quantitative environmental thresholds could not be set, trend-based or qualitative thresholds were used. The complete package of GES and environmental targets needs to give a complete and balanced overview. |
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Marine reporting units |
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Feature |
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Criterion/indicator |
D3 |
3.1 |
3.1.1 |
3.1.2 |
3.2 |
3.2.1 |
3.2.2 |
3.3 |
3.3.1 |
3.3.3 |
3.3.4 |
GES description |
Populations of all commercially exploited fish and shellfish are within safe biological limits, exhibiting a population age and size distribution that is indicative of a healthy stock. |
o Situation 1 – FMSY known: the level of stock mortality generated by fishing activity (F) is equal to or lower than FMSY
o Situation 2 – FMSY not known, but Fpa known: the level of stock mortality generated by fishing activity (F) is equal to or lower than Fpa
o Situation 3 – FMSY & Fpa not known: a catch/biomass ratio that is consistent with a sustainable exploitation will be used as a proxy reference point
o Situation 4 – biomass not known: trends of survey CPUE (catch per unit of effort) will be evaluated as a proxy for fishery mortality |
Spawning stock biomass: the spawning stock biomass (SSB) is at a level capable of delivering MSY.
o Situation 1 - BMSY known: the level of spawning stock biomass (SSB) is equal to or higher than BMSY
o Situation 2 – BMSY not known, but Bpa known: the level of spawning stock biomass (SSB) is equal to or higher than Bpa
o Situation 3 – BMSY & Bpa not known: trends of survey abundance will be evaluated as a proxy of stock biomass |
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Threshold values |
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Threshold value unit |
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Proportion of area to achieve threshold value |
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Reference point type |
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Baseline |
ICES advice
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ICES advice
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Assessment method |
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Development status |