Member State report / Art8 / 2018 / D3 / Mediterranean
Report type | Member State report to Commission |
MSFD Article | Art. 8 Initial assessment (and Art. 17 updates) |
Report due | 2018-10-15 |
GES Descriptor | D3 Commercial fish and shellfish |
Region/subregion | Mediterranean |
Reported by | Member state |
Member state | United Kingdom |
Spain |
France |
Italy |
Malta |
Slovenia |
Croatia |
Greece |
Cyprus |
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Member state report | ||||||||||
Marine reporting units | MRUs used |
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Features | Species |
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Element | Anguilla anguilla |
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Element | Aristaeomorpha foliacea |
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Element | Aristeus antennatus |
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Element | Aristeus antennatus_ GFCM GSA5 |
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Element | Aristeus antennatus_ GFCM GSA6 |
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Element | Auxis rochei rochei |
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Element | Boops boops |
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Element | Centrophorus granulosus |
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Element | Chelidonichthys cuculus |
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Element | Coryphaena hippurus |
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Element | Dentex dentex |
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Element | Dicentrarchus labrax |
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Element | Diplodus annularis |
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Element | Diplodus sargus |
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Element | Eledone cirrhosa |
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Element | Eledone moschata |
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Element | Engraulis encrasicolus |
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Element | Epinephelus aeneus |
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Element | Epinephelus caninus |
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Element | Epinephelus marginatus |
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Element | Hexanchus griseus |
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Element | Illex coindetii |
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Element | Lepidopus caudatus |
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Element | Lithognathus mormyrus |
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Element | Loligo vulgaris |
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Element | Lophius budegassa |
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Element | Lophius piscatorius |
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Element | Merluccius merluccius |
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Element | Mullus barbatus |
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Element | Mullus surmuletus |
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Element | Mustelus mustelus |
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Element | Nephrops norvegicus |
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Element | Octopodidae |
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Element | Octopus vulgaris |
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Element | Pagellus acarne |
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Element | Pagellus bogaraveo |
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Element | Pagellus erythrinus |
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Element | Pagrus pagrus |
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Element | Palinurus elephas |
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Element | Parapenaeus longirostris |
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Element | Pecten jacobeus |
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Element | Penaeus kerathurus |
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Element | Polyprion americanus |
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Element | Prionace glauca |
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Element | Raja clavata |
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Element | Raja montagui |
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Element | Sarda sarda |
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Element | Sardina pilchardus |
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Element | Sardinella aurita |
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Element | Scomber japonicus |
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Element | Scomber scombrus |
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Element | Scorpaena scrofa |
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Element | Scyliorhinus canicula |
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Element | Sepia officinalis |
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Element | Seriola dumerili |
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Element | Serranus cabrilla |
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Element | Solea solea (sin. vulgaris) |
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Element | Sparisoma cretense |
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Element | Sparus aurata |
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Element | Spicara maena |
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Element | Spicara smaris |
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Element | Squalus acanthias |
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Element | Squalus blainville |
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Element | Squilla mantis |
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Element | Thunnus alalunga |
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Element | Thunnus thynnus |
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Element | Trachurus mediterraneus |
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Element | Trachurus trachurus |
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Element | Xiphias gladius |
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Element2 |
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Element sources | No. of elements per level |
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Criteria and parameters used (number of parameters) | D3 Commercial fish and shellfish | |||||||||
Criteria and parameters used (number of parameters) | D3C1 Fishing mortality rate (F) (3.1, 3.1.1, 3.1.2) |
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Criteria and parameters used (number of parameters) | D3C2 Spawning stock biomass (SSB) (3.2, 3.2.1, 3.2.2) |
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Criteria and parameters used (number of parameters) | D3C3 Population age/size distribution (3.3, 3.3.1, 3.3.3, 3.3.4) |
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Criteria and parameters used (number of parameters) | 3.3.2 Mean maximum length across all fish species found in research vessel | |||||||||
Threshold values | % of parameters with values (no. of parameters) | 52% (19) |
100% (7) |
89% (43) |
33% (48) |
0% (0) |
0% (0) |
0% (0) |
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Threshold value sources | D3 Commercial fish and shellfish | |||||||||
Threshold value sources | D3C1 Fishing mortality rate (F) (3.1, 3.1.1, 3.1.2) |
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Threshold value sources | D3C2 Spawning stock biomass (SSB) (3.2, 3.2.1, 3.2.2) |
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Threshold value sources | D3C3 Population age/size distribution (3.3, 3.3.1, 3.3.3, 3.3.4) |
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Threshold value sources | 3.3.2 Mean maximum length across all fish species found in research vessel | |||||||||
Value achieved upper | % of parameters with values (no. of parameters) | 52% (19) |
100% (7) |
100% (48) |
0% (0) |
80% (8) |
0% (0) |
0% (0) |
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Value achieved lower | % of parameters with values (no. of parameters) | 2% (1) |
0% (0) |
0% (0) |
0% (0) |
80% (8) |
0% (0) |
0% (0) |
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Value unit/Value unit other (count of use per criterion) | D3 Commercial fish and shellfish | |||||||||
Value unit/Value unit other (count of use per criterion) | D3C1 Fishing mortality rate (F) (3.1, 3.1.1, 3.1.2) |
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Value unit/Value unit other (count of use per criterion) | D3C2 Spawning stock biomass (SSB) (3.2, 3.2.1, 3.2.2) |
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Value unit/Value unit other (count of use per criterion) | D3C3 Population age/size distribution (3.3, 3.3.1, 3.3.3, 3.3.4) |
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Value unit/Value unit other (count of use per criterion) | 3.3.2 Mean maximum length across all fish species found in research vessel | |||||||||
Proportion threshold values | Range of % values (no. of parameters) | Range: 100-100% (47 of 48 parameters) |
Range: 100-100% (144 of 144 parameters) |
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Proportion values achieved | Range of % values (no. of parameters) | Range: 1-3% (19 of 144 parameters) |
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Proportion threshold value units | % of population achieving threshold value |
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Trends | No. of trends per category |
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Parameters achieved | No. of parameters per category |
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Related indicators |
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Criteria status | No. of criteria per category |
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Element status | No. of elements per category |
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Integration rule type for parameters | OTH (24 or 100.0%) |
Not relevant (190 or 100.0%) |
Not relevant (41 or 100.0%) |
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Integration rule description for parameters |
The evaluation obtained by calculating the parameter directly informs the corresponding criterion, for a given stock, without an integration rule.
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Integration rule type for criteria | OOAO (54 or 100.0%) |
OOAO (24 or 100.0%) |
TREE (97 or 100.0%) |
Not relevant (41 or 100.0%) |
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Integration rule description for criteria | D3C1 and D3C2 must be both in GOOD in 100% of the elements assessed. |
The condition of the stock is evaluated by integrating the evaluations of criterion D3C1 and/or criterion D3C2 obtained for this stock. The integration method used is the "One Out All Out" (OOAO) method. This means that all criteria assessed must be within values describing maximum sustainable yield.
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To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. under development |
The integration method used for the criteria was the following: If 2/2 criteria assessed were ‘good’, the overall status of the species was determined to be ‘good’; if one criterion was determined to be ‘good’ and the other as ‘not good’, the overall status of the species was determined to be as ‘not assessed’; if 2/2 criteria assessed were ‘not good’, the overall status of the species was determined to be ‘not good’. In accordance with the ‘Guidance for Assessments Under Article 8 of the Marine Strategy Framework Directive’ there is no integration at species level; however, since the majority of the species were found to be in ‘not good’ status, on the basis of expert judgement, GES for commercially exploited species is expected to be achieved later than 2020. |
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GES extent threshold |
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GES extent achieved |
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GES extent unit |
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GES achieved | Commercially exploited fish and shellfish |
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Assessment period | 2012-2017 (54 or 100.0%) |
2011-2016 (24 or 100.0%) |
2012-2017 (190 or 100.0%) |
2012-2018 (144 or 100.0%) |
2011-2018 (10 or 100.0%) |
2013-2018 (24 or 100.0%) |
2012-2018 (41 or 100.0%) |
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Related pressures |
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Related targets | 29 |
5 |
1 |
1 |
1 |