Member State report / Art9 / 2018 / D3 / Baltic

Report type Member State report to Commission
MSFD Article Art. 9 Determination of GES (and Art. 17 updates)
Report due 2018-10-15
GES Descriptor D3 Commercial fish and shellfish
Region/subregion Baltic
Reported by Member state
Member state
Finland
Estonia
Latvia
Lithuania
Poland
Germany
Denmark
Sweden
Member state report
Marine reporting units MRUs used
  • BAL-FI
  • BAL-FI-AS
  • BAL-FI-BB
  • BAL-FI-BS
  • BAL-FI-GF
  • BAL-FI-NB
  • BAL-FI-QK
  • BAL-EE-AA
  • BAL-EE-EGB
  • BAL-EE-GF
  • BAL-EE-GR
  • BAL-EE-NBP
  • BAL-GR-EE-EEEE_13
  • BAL-LV-AAA-006
  • BAL-LT-AA-03
  • BAL-POL-FAO27-3D24
  • BAL-POL-FAO27-3D25
  • BAL-POL-FAO27-3D26
  • BALDE_MS
  • DK-TOTAL-part-BAL
  • BAL-SE-RG-Ostersjon
Structure, functions and processes of marine ecosystems: Species All fish
  • D3 (1)
Structure, functions and processes of marine ecosystems: Species Commercially exploited fish and shellfish
  • D3C1 (10)
  • D3C2 (20)
  • D3C3 (1)
  • D3C1 (6)
  • D3C2 (6)
  • D3C3 (2)
  • D3 (1)
  • D3C1 (1)
  • D3C2 (1)
  • D3C3 (1)
  • D3 (3)
  • D3C1 (3)
  • D3C2 (3)
  • D3C1 (1)
  • D3C2 (1)
  • D3C3 (1)
  • D3C1 (1)
  • D3C2 (1)
Anthropogenic pressures on the marine environment: Biological Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • D3 (1)
GES description D3 Commercial fish and shellfish
D3C1 Fishing mortality
D3C2 Spawning stock biomass
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
GES for the descriptor "Condition of commercial fish and shellfish stocks" is achieved "when the fishing mortality rate is not higher for all commercially exploited fish and shellfish populations in the North Sea than the corresponding FMSY target, the spawning stock biomass (SSB) is above BMSY trigger, and the populations of harvested species have an age and size structure in which all age and size classes continue to be represented resembling natural conditions."

The criteria for assessing GES for D3 set out in Commission Decision (EU) 2017/848 are as follows: D3C1, D3C2, D3C3.

Explanation: Germany does not update the general description of good environmental status (GES) from 2012 at descriptor level in this reporting exercise. During the reporting period, Germany has worked with the countries bordering the Baltic Sea in the framework of the EU?s MSC CIS process and in HELCOM to develop methodological standards (indicators, evaluation procedures). Specific aspects of criteria and indicators that contribute to a quantitative assessment of good environmental status are reported in the reporting scheme Art. 8_GES. For the assessment of the criteria set out in Commission Decision (EU) 2017/848, the relevant assessments under other EU directives shall be taken into account under Article 8_GES, taking into account, as far as possible, the regional assessments that have been coordinated so far and, on a case-by-case basis, supplemented by national assessments.
GES description D3C1 Fishing mortality rate (F) (3.1, 3.1.1, 3.1.2)
Cod: ICES recommended FMSY level (not defined in 2018). Commercial fish stocks are first assessed by species and then the total estimate for the Finnish marine area as an average of the status of each species.


Herring: ICES recommended FMSY level (0.21 in the Gulf of 2018, 0.22 in other marine areas). Commercial fish stocks are first assessed by species and then the total estimate for the Finnish marine area as an average of the status of each species.


Sprat: ICES recommended Fmsy level (0.26 in 2018). Commercial fish stocks are first assessed by species and then the total estimate for the Finnish marine area as an average of the status of each species.
GES is achieved if subpopulation of spring spawning baltic herring (Clupea harengus membras) and Baltic sprat (Sprattus sprattus balticus) actual fishing mortality (F) is lower than the fishing mortality level that would provide maximum sustainable yield (Fmsy). GES = F<Fmsy.

In case of flounder (Platichthys flesus), perch (Perca fluviatilis) and pikeperch (Sander lucioperca), GES is determined via ratio between annual commercial catch and biomass index (WPUE in monitoring area). GES is achieved if the index values are stable in time. GES = annual commercial catch/WPUE >0,6.
Fishing mortality rates for populations of commercial species are equal to or lower than the maximum sustainable yield (MSY). The indicator “Fishing Mortality Rate” is used to assess the status of three elements: fish species (Gadus morhua), herring (Clupea harengus) and sprat (Sprattus sprattus).
The Fishing mortality rate of populations of commercially-exploited species is at or below levels which can produce the maximum sustainable yield (MSY).
The fishing mortality rate for populations of commercially exploited species is at or below levels that can produce the maximum sustainable yield (MSY).
D3C1 Fiskeridödligheten för populationer av kommersiellt nyttjade arter ligger under nivåer som garanterar en maximal hållbar avkastning (MSY).
God miljöstatus: När alla populationer i respektive bedömningsområde klarar de populationsspecifika tröskelvärdena.
Bedömningen sker per population utifrån det kriterium som visar sämst status.
D3C1 The fishing mortality rate of populations of commersially-exploited species are below levels which can produce maximum sustainable yield (MSY).
GES:When all populations in the assessment area achieve the population specific threshold values.Each species is assessed on the basis of the criterion which show the worst status.
GES description D3C2 Spawning stock biomass (SSB) (3.2, 3.2.1, 3.2.2)
Cod: MSY Btrigger level recommended by ICES (not defined in 2018). Commercial fish stocks are first assessed by species and then the total estimate for the Finnish marine area as an average of the status of each species.


Herring: MSY Btrigger level recommended by ICES (283 180 t in the Gulf of 2018 and 600 000 t in other sea areas). Commercial fish stocks are first assessed by species and then the total estimate for the Finnish marine area as an average of the status of each species.


Salmon smolt production is > 75% of the spawning river production potential: in the Tornionjoki and Simojoki. Commercial fish stocks are first assessed by species and then the total estimate for the Finnish marine area as an average of the status of each species.


Sprat: MSY Btrigger level recommended by ICES (570,000 t in 2018). Commercial fish stocks are first assessed by species and then the total estimate for the Finnish marine area as an average of the status of each species.


The perch population size indicator is above the regional threshold for the area: 0.07 in the Gulf of Bothnia, no negative trend in the Bothnian Sea, trend in the Archipelago Sea of 0,18, an increasing trend in the Gulf of Finland. Commercial fish stocks are first assessed by species and then the total estimate for the Finnish marine area as an average of the status of each species.
GES is achieved if spawning stock biomass (SSB) of subpopulation of spring spawning Baltic herring (Clupea harengus membras) and Baltic sprat (Sprattus sprattus balticus) is equal or higher than minimum value of spawning stock biomass (Btrigger) which would ensure fishing mortality level that would provide maximum sustainable yield (Fmsy). GES = SSB ≥ Btrigger.

In case of flounder (Platichthys flesus), perch (Perca fluviatilis) and pikeperch (Sander lucioperca), GES is determined via abundance index of sexually mature flounder, perch and female pikeperch in monitoring catches. GES is achieve if index value is >0,6.

In case of Baltic salmon (Salmo salar), GES is determined via indicator smolt production of Baltic salmon relative to the level of natural smolt production capacity on a riverby river basis. GES is achieved if the smolt production of Baltic salmon is 75% of the potential Smolt Production Capacity of the riverby river basin.
The biomass of spawning stocks in populations of commercial species exceeds the biomass levels that can ensure the maximum sustainable yield. The indicator “Spawning stock biomass” is used to assess the status of three elements: fish species: cod (Gadus morhua), herring (Clupea harengus) and sprat (Sprattus sprattus).
The Spawning Stock Biomass of populations of commercially-exploited species are above biomass levels capable of producing maximum sustainable yield.
The spawning biomass for populations of species exploited by industry is above the levels that can produce the maximum sustainable yield.
D3C2 Lekbeståndets biomassa för populationer av kommersiellt nyttjade arter ligger över nivåer för biomassa som kan ge maximal hållbar avkastning.
God miljöstatus:se under D3C1.
D3C2 The spawning stock biomass of populations of commersially-exploited species are above biomass levels that can produce maximum sustainable yield.
GES:See under D3C1
GES description D3C3 Population age/size distribution (3.3, 3.3.1, 3.3.3, 3.3.4)
Habitat in the Bothnian Bay: The average growth rate of spawning parent fish is decreasing and the proportion of small individuals in spawning fish is decreasing. Commercial fish stocks are first assessed by species and then the total estimate for the Finnish marine area as an average of the status of each species. Commercial fish stocks are first assessed by species and then the total estimate for the Finnish marine area as an average of the status of each species.
GES for flounder (Platichthys flesus) is determined via indicator 95 % percentile of the length distribution of flounder (Platichthys flesus) in monitoring catches. GES is achieved if the indicator value is >0,6.

GES for perch (Perca fluviatilis) is determined via abundance index of large (TL>250 mm) perch (Perca fluviatilis) in monitoring catches. GES is achieved if the indicator value is >0,6.

GES for pikeperch (Sander lucioperca) is determined via indicator 95 % percentile of the length distribution of pikeperch (Sander lucioperca) in monitoring catches. GES is achieved if the indicator value is >0,6.
The age and size distribution of individuals in populations of commercial species indicates that they are in good condition. Older / large individuals must make up a large proportion and the negative impact of resource use on genetic diversity must be small. Indicators to be assessed: 1) 95th percentile of fish length distribution based on records from research vessels: cod (Gadus morhua), herring (Clupea harengus), sprat (Sprattus sprattus), flounder (Platichthys flesus). 2) Proportion of fish above the average first sexual maturity rate: Gadus morhua (> 35 cm), Clupea harengus (> 16 cm), Sprattus sprattus (> 12 cm), Platichthys flesus (> 21.5 cm).
The age and size distribution of individuals in the populations of species exploited for occupational use is indicative of a healthy population. This includes a high proportion of old / large individuals and limited negative effects on genetic diversity as a result of exploitation.
GES description 3.3.2 Mean maximum length across all fish species found in research vessel
Determination date
  • 2017-07 (D3C2, D3C1)
  • 2018-07 (D3C3, D3C2, D3C1)
  • 2018-07 (D3C3, D3C2, D3C1)
  • 2019-02 (D3)
  • 2013-04 (D3C3, D3C1)
  • 2020-02 (D3C2)
  • 2018-09 (D3C2, D3, D3C1)
  • 2018-10 (D3)
  • 2019-04 (D3C3, D3C2, D3C1)
  • 2018-12 (D3C2, D3C1)
Update type
  • Modified from reported determination (D3C2, D3C1)
  • New determination (D3C2, D3C3)
  • Same as last reported determination (D3C2)
  • New determination (D3C3, D3C2, D3C1)
  • New determination (D3)
  • New determination (D3C2)
  • Same as last reported determination (D3C3, D3C1)
  • Same as last reported determination (D3C2, D3, D3C1)
  • Same as last reported determination (D3)
  • Modified from reported determination (D3C3, D3C2, D3C1)
  • Modified from reported determination (D3C2, D3C1)
Justification for non-use of criterion
D3C1: Baltic salmon: data about Baltic salmon (Salmo salar) in Estonian marine area does not enable to assess directly fishing mortality rate under criteria D3C1. However it can be assumed that if the spawning stock status is good enough to ensure the smolt production of Baltic salmon in 75% of the potential Smolt Production Capacity of the riverby river basin, then the fishing mortality can not be higher than the fishing mortality level that would provide maximum sustainable yield (Fmsy).


D3C3: GES has not been determined for subpopulation of spring spawning Baltic herring (Clupea harengus membras) and Baltic sprat (Sprattus sprattus balticus) due to 3 reasons: 1) those two species have short lifespan due to which population age and size distribution is not of primary importance; 2) assessing the population of the two species using virtual population assessment methods, the age and size data has been added to the virtual population modelling and 3) for assessing the population age and size distribution, there is no regionally agreed threshold value.

Baltic salmon (Salmo salar): current datasets does not enable to determine GES for Baltic salmon due to short data series. There is only three year data (2015-2017) available about the sizes of spawning Baltic salmon which is not enough to develop reliable indicator for assessing Baltic salmon population age and size distribution.
Justification for delay in setting EU/regional requirements
D3: During the reporting period, regional cooperation focused on the development of methodological standards to assess the various aspects of stress and resilience on the basis of Commission Decision 2010/477/EU. The indicators vary in their level of maturity and require further development or testing. Commission Decision (EU) 2017/848 gives, for the first time, an explicit obligation on the part of the EU Member States to agree on evaluation elements, thresholds and integration rules in the framework of the EU MSFD CIS process and through regional or subregional cooperation. Germany is actively working with the countries bordering the Baltic Sea in the framework of the ongoing work programmes of the EU MSFD and the HELCOM bodies to establish where a coordinated definition is still missing.
D3C1: The regulation of fisheries and the setting of maximum levels for maximum fishing pressure and minimum spawning biomass are carried out through the EU's Common Fisheries Policy on the basis of advice from ICES.


D3C2: The regulation of fisheries and the setting of maximum levels for maximum fishing pressure and minimum spawning biomass is done through the EU's Common Fisheries Policy on the basis of advice from ICES.


D3C3: There is insufficient knowledge of age and size distribution (D3C3) among the commercially exploited species, and therefore there is not a sufficient basis for assessing when good environmental status is achieved. Furthermore, the regulation of fisheries and the setting of limit values for maximum fishing pressure and minimum spawning biomass are carried out through the EU's Common Fisheries Policy on the basis of advice from ICES.
D3C3: All Swedish determinations of GES are implemented in a regulation (HVMFS 2012:18) issued from the Swedish Agency for Marine and Water Management. From the update made in 2018 only criteria supported with at least one indicator are included in the regulation. Furthermore, only indicators underpinned with a regular monitoring programme are included.

Reference levels and tools for a quantitative assessment of age and size distribution at population level is still missing, and development from ICES is needed.
The article 8 assessment include some descriptions on society level.