Member State report / Art8 / 2018 / D3 / Lithuania / Baltic Sea

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
Member State Lithuania
Region/subregion Baltic Sea
Reported by Environmental Protection Agency
Report date 2020-06-09
Report access msfd2018-ART8_GES_04-07-corrected_06-04.xml

BAL-LT-AA-03

GES component
D3
D3
D3
D3
D3
D3
D3
D3
D3
D3
D3
D3
D3
D3
Feature
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Element
Clupea harengus
Clupea harengus
Clupea harengus
Clupea harengus
Gadus morhua
Gadus morhua
Gadus morhua
Gadus morhua
Platichthys flesus
Platichthys flesus
Sprattus sprattus
Sprattus sprattus
Sprattus sprattus
Sprattus sprattus
Element code
126417
126417
126417
126417
126436
126436
126436
126436
127141
127141
126425
126425
126425
126425
Element code source
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Element 2
Herring (Clupea harengus) in subdivisions 25-29 and 32, excluding the Gulf of Riga (central Baltic Sea)
Herring (Clupea harengus) in subdivisions 25-29 and 32, excluding the Gulf of Riga (central Baltic Sea)
Herring (Clupea harengus) in subdivisions 25-29 and 32, excluding the Gulf of Riga (central Baltic Sea)
Herring (Clupea harengus) in subdivisions 25-29 and 32, excluding the Gulf of Riga (central Baltic Sea)
Cod (Gadus morhua) in subdivisions 24-32, eastern Baltic stock (eastern Baltic Sea)
Cod (Gadus morhua) in subdivisions 24-32, eastern Baltic stock (eastern Baltic Sea)
Cod (Gadus morhua) in subdivisions 24-32, eastern Baltic stock (eastern Baltic Sea)
Cod (Gadus morhua) in subdivisions 24-32, eastern Baltic stock (eastern Baltic Sea)
Flounder (Platichthys flesus) in subdivisions 26 and 28 (east of Gotland and Gulf of Gdansk)
Flounder (Platichthys flesus) in subdivisions 26 and 28 (east of Gotland and Gulf of Gdansk)
Sprat (Sprattus sprattus) in Subdivisions 22-32 (Baltic Sea)
Sprat (Sprattus sprattus) in Subdivisions 22-32 (Baltic Sea)
Sprat (Sprattus sprattus) in Subdivisions 22-32 (Baltic Sea)
Sprat (Sprattus sprattus) in Subdivisions 22-32 (Baltic Sea)
Element 2 code
her.27.25-2932
her.27.25-2932
her.27.25-2932
her.27.25-2932
cod.27.24-32
cod.27.24-32
cod.27.24-32
cod.27.24-32
fle.27.2628
fle.27.2628
spr.27.22-32
spr.27.22-32
spr.27.22-32
spr.27.22-32
Element 2 code source
Species (D3) http://vocab.ices.dk/?ref=357
Species (D3) http://vocab.ices.dk/?ref=357
Species (D3) http://vocab.ices.dk/?ref=357
Species (D3) http://vocab.ices.dk/?ref=357
Species (D3) http://vocab.ices.dk/?ref=357
Species (D3) http://vocab.ices.dk/?ref=357
Species (D3) http://vocab.ices.dk/?ref=357
Species (D3) http://vocab.ices.dk/?ref=357
Species (D3) http://vocab.ices.dk/?ref=357
Species (D3) http://vocab.ices.dk/?ref=357
Species (D3) http://vocab.ices.dk/?ref=357
Species (D3) http://vocab.ices.dk/?ref=357
Species (D3) http://vocab.ices.dk/?ref=357
Species (D3) http://vocab.ices.dk/?ref=357
Element source
ICES
ICES
ICES
ICES
ICES
ICES
ICES
ICES
ICES
ICES
ICES
ICES
ICES
ICES
Criterion
D3C1
D3C2
D3C3
D3C3
D3C1
D3C2
D3C3
D3C3
D3C3
D3C3
D3C1
D3C2
D3C3
D3C3
Parameter
Mortality rate / Mortality rate from fishing (F)
BIOM-SSB
Other
Size distribution
Mortality rate / Mortality rate from fishing (F)
BIOM-SSB
Other
Size distribution
Other
Size distribution
Mortality rate / Mortality rate from fishing (F)
BIOM-SSB
Other
Size distribution
Parameter other
SIZE distribution
SIZE distribution
SIZE distribution
SIZE distribution
Threshold value upper
0.22
600000.0
0.26
570000.0
Threshold value lower
Threshold qualitative
Statistically reliable positive trend or no trend
Statistically reliable positive trend or no trend
F
SSB> MSYBtrigger
Statistically reliable positive trend or no trend
Statistically reliable positive trend or no trend
Statistically reliable positive trend or no trend
Statistically reliable positive trend or no trend
Statistically reliable positive trend or no trend
Statistically reliable positive trend or no trend
Threshold value source
Threshold value source other
Value achieved upper
0.195
1341625.0
0.1
0.1
97284.0
0.13
0.66
0.1
0.42
0.22
1289000.0
0.74
0.27
Value achieved lower
Value unit
tonne
tonne
tonne
Value unit other
Proportion threshold value
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
Proportion value achieved
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
Proportion threshold value unit
% of population achieving threshold value
% of population achieving threshold value
% of population achieving threshold value
% of population achieving threshold value
% of population achieving threshold value
% of population achieving threshold value
% of population achieving threshold value
% of population achieving threshold value
% of population achieving threshold value
% of population achieving threshold value
% of population achieving threshold value
% of population achieving threshold value
% of population achieving threshold value
Trend
Improving
Improving
Deteriorating
Deteriorating
Deteriorating
Deteriorating
Stable
Stable
Stable
Stable
Improving
Improving
Stable
Stable
Parameter achieved
Yes
Yes
No
No
No
No
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Description parameter
For the values of the indicator “95th percentile of fish length distribution based on the records of research vessels: herring (Clupea harengus)” the trend is statistically significantly negative (p = 0.1), the condition is not good.
For the values of the indicator “Proportion of fish larger than the average rate of first sexual maturity: herring (Clupea harengus) (> 16 cm)” the trend is statistically significantly negative (p = 0.1), the condition is not good.
In recent years, for the cod stock in the Eastern Baltic (Subdivisions 25-32), the sustainable fishing mortality rate (MSY) has not been calculated. Cod stocks are significantly overexploited and in a critical state due to the negative effects of commercial fishing. Both the spawning stock biomass and fishing mortality did not comply with the GES during the period under review, and in the second half of 2019 commercial fishing for eastern Baltic cod was generally banned (FMSY = 0).
In recent years, for the cod stock in the Eastern Baltic (Subdivisions 25-32), the sustainable fishing mortality rate (MSY) has not been calculated. Cod stocks are significantly overexploited and in a critical state due to the negative effects of commercial fishing. Both the spawning stock biomass and fishing mortality did not comply with the GES during the period under review, and in the second half of 2019 commercial fishing for eastern Baltic cod was generally banned (FMSY = 0).
There was no statistically significant trend (p = 0.13) for the values of the indicator “95th percentile of fish length distribution based on the records of research vessels: cod (Gadus morhua)”, the condition is good.
There was no statistically significant trend (p = 0.66) for the values of the indicator “Proportion of fish larger than the average rate of first sexual maturity: cod (Gadus morhua) (> 35 cm)”, the condition is good.
For the indicators: "Proportion of fish above the average first sexual maturity rate: plaice (Platichthys flesus) (> 21.5 cm)" and "95th percentile of the length distribution based on research vessel records: plaice (Platichthys flesus)", the GES corresponds statistically. reliable positive trend or no trend. According to both indicators, there was no statistically significant trend for the values of flounder indicators, the condition by species of flounder (Platichthys flesus) was good.
For the indicators: "Proportion of fish above the average first sexual maturity rate: plaice (Platichthys flesus) (> 21.5 cm)" and "95th percentile of the length distribution based on research vessel records: plaice (Platichthys flesus)", the GES corresponds statistically. reliable positive trend or no trend. According to both indicators, there was no statistically significant trend for the values of flounder indicators, the condition by species of flounder (Platichthys flesus) was good.
For the indicators: “Proportion of fish above the average first sexual maturity rate: sprat (Sprattus sprattus) (> 12 cm)” and “95th percentile of fish length distribution based on research vessel records: sprat (Sprattus sprattus)”, the GES corresponds to a statistically significant positive trend or no trend. According to both indicators, a statistically reliable trend was not found for the values of sprat indicators, the condition is good. Overall condition by species of sprat (Sprattus sprattus) - good.
For the indicators: “Proportion of fish above the average first sexual maturity rate: sprat (Sprattus sprattus) (> 12 cm)” and “95th percentile of fish length distribution based on research vessel records: sprat (Sprattus sprattus)”, the GES corresponds to a statistically significant positive trend or no trend. According to both indicators, a statistically reliable trend was not found for the values of sprat indicators, the condition is good. Overall condition by species of sprat (Sprattus sprattus) - good.
Related indicator
Criteria status
Good
Good
Not good
Not good
Not good
Not good
Good
Good
Good
Good
Good
Good
Good
Good
Description criteria
For the indicators: “Proportion of fish above the average first sexual maturity rate: herring (Clupea harengus) (> 16 cm)” and “95th percentile of fish length distribution based on research vessel records: herring (Clupea harengus)”, the GES corresponds to a statistically significant positive trend or no trend. The trends of the values of both indicators were statistically significantly negative (p = 0.01), the condition is not good according to the indicators of the D3C3 criterion.
For the indicators: “Proportion of fish above the average first sexual maturity rate: herring (Clupea harengus) (> 16 cm)” and “95th percentile of fish length distribution based on research vessel records: herring (Clupea harengus)”, the GES corresponds to a statistically significant positive trend or no trend. The trends of the values of both indicators were statistically significantly negative (p = 0.01), the condition is not good according to the indicators of the D3C3 criterion.
For the indicators: “Proportion of fish above the average first sexual maturity rate: cod (Gadus morhua) (> 35 cm)” and “95th percentile of the length distribution based on research vessel records: cod (Gadus morhua)”, the GES corresponds to a statistically significant positive trend or no trend. According to both indicators, there is no statistically significant trend for the values of cod indicators, the condition is good. However, the overall condition by species of cod (Gadus morhua) is poor.
For the indicators: “Proportion of fish above the average first sexual maturity rate: cod (Gadus morhua) (> 35 cm)” and “95th percentile of the length distribution based on research vessel records: cod (Gadus morhua)”, the GES corresponds to a statistically significant positive trend or no trend. According to both indicators, there is no statistically significant trend for the values of cod indicators, the condition is good. However, the overall condition by species of cod (Gadus morhua) is poor.
For the indicators: “Proportion of fish above the average first sexual maturity rate: sprat (Sprattus sprattus) (> 12 cm)” and “95th percentile of fish length distribution based on research vessel records: sprat (Sprattus sprattus)”, the GES corresponds to a statistically significant positive trend or no trend. According to both indicators, a statistically reliable trend was not found for the values of sprat indicators, the condition is good. Overall condition by species of sprat (Sprattus sprattus) - good.
For the indicators: “Proportion of fish above the average first sexual maturity rate: sprat (Sprattus sprattus) (> 12 cm)” and “95th percentile of fish length distribution based on research vessel records: sprat (Sprattus sprattus)”, the GES corresponds to a statistically significant positive trend or no trend. According to both indicators, a statistically reliable trend was not found for the values of sprat indicators, the condition is good. Overall condition by species of sprat (Sprattus sprattus) - good.
For the indicators: “Proportion of fish above the average first sexual maturity rate: sprat (Sprattus sprattus) (> 12 cm)” and “95th percentile of fish length distribution based on research vessel records: sprat (Sprattus sprattus)”, the GES corresponds to a statistically significant positive trend or no trend. According to both indicators, a statistically reliable trend was not found for the values of sprat indicators, the condition is good. Overall condition by species of sprat (Sprattus sprattus) - good.
For the indicators: “Proportion of fish above the average first sexual maturity rate: sprat (Sprattus sprattus) (> 12 cm)” and “95th percentile of fish length distribution based on research vessel records: sprat (Sprattus sprattus)”, the GES corresponds to a statistically significant positive trend or no trend. According to both indicators, a statistically reliable trend was not found for the values of sprat indicators, the condition is good. Overall condition by species of sprat (Sprattus sprattus) - good.
Element status
Not good
Not good
Not good
Not good
Not good
Not good
Not good
Not good
Good
Good
Good
Good
Good
Good
Description element
For herring (Clupea harengus) stocks, the SSB-compliant GES corresponds to the MSYBtrigger and the fishing mortality F corresponds to the FMSY. Given that herring stocks are exploited at a lower rate than FMSY, it can be assumed that herring stocks and their SSBs will increase or remain stable in the long run. For the indicators: “Proportion of fish above the average first sexual maturity rate: herring (Clupea harengus) (> 16 cm)” and “95th percentile of fish length distribution based on research vessel records: herring (Clupea harengus)”, the GES corresponds to a statistically significant positive trend or no trend. The trends of the values of both indicators were statistically significantly negative (p = 0.01), the condition is not good according to the indicators of the D3C3 criterion.
For herring (Clupea harengus) stocks, the SSB-compliant GES corresponds to the MSYBtrigger and the fishing mortality F corresponds to the FMSY. Given that herring stocks are exploited at a lower rate than FMSY, it can be assumed that herring stocks and their SSBs will increase or remain stable in the long run. For the indicators: “Proportion of fish above the average first sexual maturity rate: herring (Clupea harengus) (> 16 cm)” and “95th percentile of fish length distribution based on research vessel records: herring (Clupea harengus)”, the GES corresponds to a statistically significant positive trend or no trend. The trends of the values of both indicators were statistically significantly negative (p = 0.01), the condition is not good according to the indicators of the D3C3 criterion.
For herring (Clupea harengus) stocks, the SSB-compliant GES corresponds to the MSYBtrigger and the fishing mortality F corresponds to the FMSY. Given that herring stocks are exploited at a lower rate than FMSY, it can be assumed that herring stocks and their SSBs will increase or remain stable in the long run. For the indicators: “Proportion of fish above the average first sexual maturity rate: herring (Clupea harengus) (> 16 cm)” and “95th percentile of fish length distribution based on research vessel records: herring (Clupea harengus)”, the GES corresponds to a statistically significant positive trend or no trend. The trends of the values of both indicators were statistically significantly negative (p = 0.01), the condition is not good according to the indicators of the D3C3 criterion.
For herring (Clupea harengus) stocks, the SSB-compliant GES corresponds to the MSYBtrigger and the fishing mortality F corresponds to the FMSY. Given that herring stocks are exploited at a lower rate than FMSY, it can be assumed that herring stocks and their SSBs will increase or remain stable in the long run. For the indicators: “Proportion of fish above the average first sexual maturity rate: herring (Clupea harengus) (> 16 cm)” and “95th percentile of fish length distribution based on research vessel records: herring (Clupea harengus)”, the GES corresponds to a statistically significant positive trend or no trend. The trends of the values of both indicators were statistically significantly negative (p = 0.01), the condition is not good according to the indicators of the D3C3 criterion.
In recent years, for the cod stock in the Eastern Baltic (Subdivisions 25-32), the sustainable fishing mortality rate (MSY) has not been calculated. Cod stocks are significantly overexploited and in a critical state due to the negative effects of commercial fishing. Both the spawning stock biomass and fishing mortality did not comply with the GES during the period under review, and in the second half of 2019 commercial fishing for eastern Baltic cod was generally banned (FMSY = 0). For the other indicators: "Proportion of fish above the average first sexual maturity rate: cod (Gadus morhua) (> 35 cm)" and "95th percentile of the length distribution based on research vessel records: cod (Gadus morhua)", the GES corresponds to a statistically significant positive trend or no trend. According to both indicators, there is no statistically significant trend for the values ​​of cod indicators, the condition is good. However, the overall condition by species of cod (Gadus morhua) is poor.
In recent years, for the cod stock in the Eastern Baltic (Subdivisions 25-32), the sustainable fishing mortality rate (MSY) has not been calculated. Cod stocks are significantly overexploited and in a critical state due to the negative effects of commercial fishing. Both the spawning stock biomass and fishing mortality did not comply with the GES during the period under review, and in the second half of 2019 commercial fishing for eastern Baltic cod was generally banned (FMSY = 0). For the other indicators: "Proportion of fish above the average first sexual maturity rate: cod (Gadus morhua) (> 35 cm)" and "95th percentile of the length distribution based on research vessel records: cod (Gadus morhua)", the GES corresponds to a statistically significant positive trend or no trend. According to both indicators, there is no statistically significant trend for the values ​​of cod indicators, the condition is good. However, the overall condition by species of cod (Gadus morhua) is poor.
In recent years, for the cod stock in the Eastern Baltic (Subdivisions 25-32), the sustainable fishing mortality rate (MSY) has not been calculated. Cod stocks are significantly overexploited and in a critical state due to the negative effects of commercial fishing. Both the spawning stock biomass and fishing mortality did not comply with the GES during the period under review, and in the second half of 2019 commercial fishing for eastern Baltic cod was generally banned (FMSY = 0). For the other indicators: "Proportion of fish above the average first sexual maturity rate: cod (Gadus morhua) (> 35 cm)" and "95th percentile of the length distribution based on research vessel records: cod (Gadus morhua)", the GES corresponds to a statistically significant positive trend or no trend. According to both indicators, there is no statistically significant trend for the values ​​of cod indicators, the condition is good. However, the overall condition by species of cod (Gadus morhua) is poor.
In recent years, for the cod stock in the Eastern Baltic (Subdivisions 25-32), the sustainable fishing mortality rate (MSY) has not been calculated. Cod stocks are significantly overexploited and in a critical state due to the negative effects of commercial fishing. Both the spawning stock biomass and fishing mortality did not comply with the GES during the period under review, and in the second half of 2019 commercial fishing for eastern Baltic cod was generally banned (FMSY = 0). For the other indicators: "Proportion of fish above the average first sexual maturity rate: cod (Gadus morhua) (> 35 cm)" and "95th percentile of the length distribution based on research vessel records: cod (Gadus morhua)", the GES corresponds to a statistically significant positive trend or no trend. According to both indicators, there is no statistically significant trend for the values ​​of cod indicators, the condition is good. However, the overall condition by species of cod (Gadus morhua) is poor.
For the indicators: "Proportion of fish above the average first sexual maturity rate: plaice (Platichthys flesus) (> 21.5 cm)" and "95th percentile of the length distribution based on research vessel records: plaice (Platichthys flesus)", the GES corresponds statistically. reliable positive trend or no trend. According to both indicators, there was no statistically significant trend for the values of flounder indicators, the condition by species of flounder (Platichthys flesus) was good.
For the indicators: "Proportion of fish above the average first sexual maturity rate: plaice (Platichthys flesus) (> 21.5 cm)" and "95th percentile of the length distribution based on research vessel records: plaice (Platichthys flesus)", the GES corresponds statistically. reliable positive trend or no trend. According to both indicators, there was no statistically significant trend for the values of flounder indicators, the condition by species of flounder (Platichthys flesus) was good.
The SSB corresponding to sprat (Sprattus sprattus) stocks corresponds to MSYBtrigger and the fishing mortality rate F corresponds to FMSY. The status of the indicator is in line with the GES and has improved compared to the results of the JSPD cycle I (2006-2011). The sprat stock has long been exploited at a higher rate than the FMSY regime, but fishing mortality has declined at the end of the assessment period. Given that F is currently in line with the GES, it can be assumed that sprat stocks and their SSBs will increase or remain stable in the long run. On the other hand, declining cod abundance can have a positive effect on sprat stocks. For the indicators: “Proportion of fish above the average first sexual maturity rate: sprat (Sprattus sprattus) (> 12 cm)” and “95th percentile of fish length distribution based on research vessel records: sprat (Sprattus sprattus)”, the GES corresponds to a statistically significant positive trend or no trend. According to both indicators, a statistically reliable trend was not found for the values ​​of sprat indicators, the condition is good. Overall condition by species of sprat (Sprattus sprattus) - good.
The SSB corresponding to sprat (Sprattus sprattus) stocks corresponds to MSYBtrigger and the fishing mortality rate F corresponds to FMSY. The status of the indicator is in line with the GES and has improved compared to the results of the JSPD cycle I (2006-2011). The sprat stock has long been exploited at a higher rate than the FMSY regime, but fishing mortality has declined at the end of the assessment period. Given that F is currently in line with the GES, it can be assumed that sprat stocks and their SSBs will increase or remain stable in the long run. On the other hand, declining cod abundance can have a positive effect on sprat stocks. For the indicators: “Proportion of fish above the average first sexual maturity rate: sprat (Sprattus sprattus) (> 12 cm)” and “95th percentile of fish length distribution based on research vessel records: sprat (Sprattus sprattus)”, the GES corresponds to a statistically significant positive trend or no trend. According to both indicators, a statistically reliable trend was not found for the values ​​of sprat indicators, the condition is good. Overall condition by species of sprat (Sprattus sprattus) - good.
The SSB corresponding to sprat (Sprattus sprattus) stocks corresponds to MSYBtrigger and the fishing mortality rate F corresponds to FMSY. The status of the indicator is in line with the GES and has improved compared to the results of the JSPD cycle I (2006-2011). The sprat stock has long been exploited at a higher rate than the FMSY regime, but fishing mortality has declined at the end of the assessment period. Given that F is currently in line with the GES, it can be assumed that sprat stocks and their SSBs will increase or remain stable in the long run. On the other hand, declining cod abundance can have a positive effect on sprat stocks. For the indicators: “Proportion of fish above the average first sexual maturity rate: sprat (Sprattus sprattus) (> 12 cm)” and “95th percentile of fish length distribution based on research vessel records: sprat (Sprattus sprattus)”, the GES corresponds to a statistically significant positive trend or no trend. According to both indicators, a statistically reliable trend was not found for the values ​​of sprat indicators, the condition is good. Overall condition by species of sprat (Sprattus sprattus) - good.
The SSB corresponding to sprat (Sprattus sprattus) stocks corresponds to MSYBtrigger and the fishing mortality rate F corresponds to FMSY. The status of the indicator is in line with the GES and has improved compared to the results of the JSPD cycle I (2006-2011). The sprat stock has long been exploited at a higher rate than the FMSY regime, but fishing mortality has declined at the end of the assessment period. Given that F is currently in line with the GES, it can be assumed that sprat stocks and their SSBs will increase or remain stable in the long run. On the other hand, declining cod abundance can have a positive effect on sprat stocks. For the indicators: “Proportion of fish above the average first sexual maturity rate: sprat (Sprattus sprattus) (> 12 cm)” and “95th percentile of fish length distribution based on research vessel records: sprat (Sprattus sprattus)”, the GES corresponds to a statistically significant positive trend or no trend. According to both indicators, a statistically reliable trend was not found for the values ​​of sprat indicators, the condition is good. Overall condition by species of sprat (Sprattus sprattus) - good.
Integration rule type parameter
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
Integration rule description parameter
Integration rule type criteria
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
Integration rule description criteria
GES extent threshold
100.00
100.00
100.00
100.00
100.00
100.00
100.00
100.00
100.00
100.00
100.00
100.00
100.00
100.00
GES extent achieved
50.00
50.00
50.00
50.00
50.00
50.00
50.00
50.00
50.00
50.00
50.00
50.00
50.00
50.00
GES extent unit
Proportion of populations in good status
Proportion of populations in good status
Proportion of populations in good status
Proportion of populations in good status
Proportion of populations in good status
Proportion of populations in good status
Proportion of populations in good status
Proportion of populations in good status
Proportion of populations in good status
Proportion of populations in good status
Proportion of populations in good status
Proportion of populations in good status
Proportion of populations in good status
Proportion of populations in good status
GES achieved
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
GES expected to be achieved later than 2020, no Article 14 exception reported
Description overall status
The environmental status of the marine area (BAL-LT-AA-03) according to D3 was assessed according to three criteria (D3C1, D3C2, D3C3) described by the indicators for four commercial fisheries (cod, herring, sprat and plaice): 1) Fishing mortality rate ( D3C1), 2) Spawning stock biomass (D3C2), 3) 95th percentile of fish length distribution based on records from research vessels (D3C3), 4) Proportion of fish above the average first sexual maturity rate (D3C3). Indicator values were calculated for each species (element). After integrating the indicators, the condition of the sea area was assessed for each element (species). Based on the 2009-2017 According to the values of the indicators calculated from the data of the period, the environmental condition of the marine area was not good according to the indicators of cod (Gadus morhua) and herring (Clupea harengus), according to the indicators of sprat (Sprattus sprattus) and flounder (Platichthys flesus).
The environmental status of the marine area (BAL-LT-AA-03) according to D3 was assessed according to three criteria (D3C1, D3C2, D3C3) described by the indicators for four commercial fisheries (cod, herring, sprat and plaice): 1) Fishing mortality rate ( D3C1), 2) Spawning stock biomass (D3C2), 3) 95th percentile of fish length distribution based on records from research vessels (D3C3), 4) Proportion of fish above the average first sexual maturity rate (D3C3). Indicator values were calculated for each species (element). After integrating the indicators, the condition of the sea area was assessed for each element (species). Based on the 2009-2017 According to the values of the indicators calculated from the data of the period, the environmental condition of the marine area was not good according to the indicators of cod (Gadus morhua) and herring (Clupea harengus), according to the indicators of sprat (Sprattus sprattus) and flounder (Platichthys flesus).
The environmental status of the marine area (BAL-LT-AA-03) according to D3 was assessed according to three criteria (D3C1, D3C2, D3C3) described by the indicators for four commercial fisheries (cod, herring, sprat and plaice): 1) Fishing mortality rate ( D3C1), 2) Spawning stock biomass (D3C2), 3) 95th percentile of fish length distribution based on records from research vessels (D3C3), 4) Proportion of fish above the average first sexual maturity rate (D3C3). Indicator values were calculated for each species (element). After integrating the indicators, the condition of the sea area was assessed for each element (species). Based on the 2009-2017 According to the values of the indicators calculated from the data of the period, the environmental condition of the marine area was not good according to the indicators of cod (Gadus morhua) and herring (Clupea harengus), according to the indicators of sprat (Sprattus sprattus) and flounder (Platichthys flesus).
The environmental status of the marine area (BAL-LT-AA-03) according to D3 was assessed according to three criteria (D3C1, D3C2, D3C3) described by the indicators for four commercial fisheries (cod, herring, sprat and plaice): 1) Fishing mortality rate ( D3C1), 2) Spawning stock biomass (D3C2), 3) 95th percentile of fish length distribution based on records from research vessels (D3C3), 4) Proportion of fish above the average first sexual maturity rate (D3C3). Indicator values were calculated for each species (element). After integrating the indicators, the condition of the sea area was assessed for each element (species). Based on the 2009-2017 According to the values of the indicators calculated from the data of the period, the environmental condition of the marine area was not good according to the indicators of cod (Gadus morhua) and herring (Clupea harengus), according to the indicators of sprat (Sprattus sprattus) and flounder (Platichthys flesus).
The environmental status of the marine area (BAL-LT-AA-03) according to D3 was assessed according to three criteria (D3C1, D3C2, D3C3) described by the indicators for four commercial fisheries (cod, herring, sprat and plaice): 1) Fishing mortality rate ( D3C1), 2) Spawning stock biomass (D3C2), 3) 95th percentile of fish length distribution based on records from research vessels (D3C3), 4) Proportion of fish above the average first sexual maturity rate (D3C3). Indicator values were calculated for each species (element). After integrating the indicators, the condition of the sea area was assessed for each element (species). Based on the 2009-2017 According to the values of the indicators calculated from the data of the period, the environmental condition of the marine area was not good according to the indicators of cod (Gadus morhua) and herring (Clupea harengus), according to the indicators of sprat (Sprattus sprattus) and flounder (Platichthys flesus).
The environmental status of the marine area (BAL-LT-AA-03) according to D3 was assessed according to three criteria (D3C1, D3C2, D3C3) described by the indicators for four commercial fisheries (cod, herring, sprat and plaice): 1) Fishing mortality rate ( D3C1), 2) Spawning stock biomass (D3C2), 3) 95th percentile of fish length distribution based on records from research vessels (D3C3), 4) Proportion of fish above the average first sexual maturity rate (D3C3). Indicator values were calculated for each species (element). After integrating the indicators, the condition of the sea area was assessed for each element (species). Based on the 2009-2017 According to the values of the indicators calculated from the data of the period, the environmental condition of the marine area was not good according to the indicators of cod (Gadus morhua) and herring (Clupea harengus), according to the indicators of sprat (Sprattus sprattus) and flounder (Platichthys flesus).
The environmental status of the marine area (BAL-LT-AA-03) according to D3 was assessed according to three criteria (D3C1, D3C2, D3C3) described by the indicators for four commercial fisheries (cod, herring, sprat and plaice): 1) Fishing mortality rate ( D3C1), 2) Spawning stock biomass (D3C2), 3) 95th percentile of fish length distribution based on records from research vessels (D3C3), 4) Proportion of fish above the average first sexual maturity rate (D3C3). Indicator values were calculated for each species (element). After integrating the indicators, the condition of the sea area was assessed for each element (species). Based on the 2009-2017 According to the values of the indicators calculated from the data of the period, the environmental condition of the marine area was not good according to the indicators of cod (Gadus morhua) and herring (Clupea harengus), according to the indicators of sprat (Sprattus sprattus) and flounder (Platichthys flesus).
The environmental status of the marine area (BAL-LT-AA-03) according to D3 was assessed according to three criteria (D3C1, D3C2, D3C3) described by the indicators for four commercial fisheries (cod, herring, sprat and plaice): 1) Fishing mortality rate ( D3C1), 2) Spawning stock biomass (D3C2), 3) 95th percentile of fish length distribution based on records from research vessels (D3C3), 4) Proportion of fish above the average first sexual maturity rate (D3C3). Indicator values were calculated for each species (element). After integrating the indicators, the condition of the sea area was assessed for each element (species). Based on the 2009-2017 According to the values of the indicators calculated from the data of the period, the environmental condition of the marine area was not good according to the indicators of cod (Gadus morhua) and herring (Clupea harengus), according to the indicators of sprat (Sprattus sprattus) and flounder (Platichthys flesus).
The environmental status of the marine area (BAL-LT-AA-03) according to D3 was assessed according to three criteria (D3C1, D3C2, D3C3) described by the indicators for four commercial fisheries (cod, herring, sprat and plaice): 1) Fishing mortality rate ( D3C1), 2) Spawning stock biomass (D3C2), 3) 95th percentile of fish length distribution based on records from research vessels (D3C3), 4) Proportion of fish above the average first sexual maturity rate (D3C3). Indicator values were calculated for each species (element). After integrating the indicators, the condition of the sea area was assessed for each element (species). Based on the 2009-2017 According to the values of the indicators calculated from the data of the period, the environmental condition of the marine area was not good according to the indicators of cod (Gadus morhua) and herring (Clupea harengus), according to the indicators of sprat (Sprattus sprattus) and flounder (Platichthys flesus).
The environmental status of the marine area (BAL-LT-AA-03) according to D3 was assessed according to three criteria (D3C1, D3C2, D3C3) described by the indicators for four commercial fisheries (cod, herring, sprat and plaice): 1) Fishing mortality rate ( D3C1), 2) Spawning stock biomass (D3C2), 3) 95th percentile of fish length distribution based on records from research vessels (D3C3), 4) Proportion of fish above the average first sexual maturity rate (D3C3). Indicator values were calculated for each species (element). After integrating the indicators, the condition of the sea area was assessed for each element (species). Based on the 2009-2017 According to the values of the indicators calculated from the data of the period, the environmental condition of the marine area was not good according to the indicators of cod (Gadus morhua) and herring (Clupea harengus), according to the indicators of sprat (Sprattus sprattus) and flounder (Platichthys flesus).
The environmental status of the marine area (BAL-LT-AA-03) according to D3 was assessed according to three criteria (D3C1, D3C2, D3C3) described by the indicators for four commercial fisheries (cod, herring, sprat and plaice): 1) Fishing mortality rate ( D3C1), 2) Spawning stock biomass (D3C2), 3) 95th percentile of fish length distribution based on records from research vessels (D3C3), 4) Proportion of fish above the average first sexual maturity rate (D3C3). Indicator values were calculated for each species (element). After integrating the indicators, the condition of the sea area was assessed for each element (species). Based on the 2009-2017 According to the values of the indicators calculated from the data of the period, the environmental condition of the marine area was not good according to the indicators of cod (Gadus morhua) and herring (Clupea harengus), according to the indicators of sprat (Sprattus sprattus) and flounder (Platichthys flesus).
The environmental status of the marine area (BAL-LT-AA-03) according to D3 was assessed according to three criteria (D3C1, D3C2, D3C3) described by the indicators for four commercial fisheries (cod, herring, sprat and plaice): 1) Fishing mortality rate ( D3C1), 2) Spawning stock biomass (D3C2), 3) 95th percentile of fish length distribution based on records from research vessels (D3C3), 4) Proportion of fish above the average first sexual maturity rate (D3C3). Indicator values were calculated for each species (element). After integrating the indicators, the condition of the sea area was assessed for each element (species). Based on the 2009-2017 According to the values of the indicators calculated from the data of the period, the environmental condition of the marine area was not good according to the indicators of cod (Gadus morhua) and herring (Clupea harengus), according to the indicators of sprat (Sprattus sprattus) and flounder (Platichthys flesus).
The environmental status of the marine area (BAL-LT-AA-03) according to D3 was assessed according to three criteria (D3C1, D3C2, D3C3) described by the indicators for four commercial fisheries (cod, herring, sprat and plaice): 1) Fishing mortality rate ( D3C1), 2) Spawning stock biomass (D3C2), 3) 95th percentile of fish length distribution based on records from research vessels (D3C3), 4) Proportion of fish above the average first sexual maturity rate (D3C3). Indicator values were calculated for each species (element). After integrating the indicators, the condition of the sea area was assessed for each element (species). Based on the 2009-2017 According to the values of the indicators calculated from the data of the period, the environmental condition of the marine area was not good according to the indicators of cod (Gadus morhua) and herring (Clupea harengus), according to the indicators of sprat (Sprattus sprattus) and flounder (Platichthys flesus).
The environmental status of the marine area (BAL-LT-AA-03) according to D3 was assessed according to three criteria (D3C1, D3C2, D3C3) described by the indicators for four commercial fisheries (cod, herring, sprat and plaice): 1) Fishing mortality rate ( D3C1), 2) Spawning stock biomass (D3C2), 3) 95th percentile of fish length distribution based on records from research vessels (D3C3), 4) Proportion of fish above the average first sexual maturity rate (D3C3). Indicator values were calculated for each species (element). After integrating the indicators, the condition of the sea area was assessed for each element (species). Based on the 2009-2017 According to the values of the indicators calculated from the data of the period, the environmental condition of the marine area was not good according to the indicators of cod (Gadus morhua) and herring (Clupea harengus), according to the indicators of sprat (Sprattus sprattus) and flounder (Platichthys flesus).
Assessments period
2009-2017
2009-2017
2009-2017
2009-2017
2009-2017
2009-2017
2009-2017
2009-2017
2009-2017
2009-2017
2009-2017
2009-2017
2009-2017
2009-2017
Related pressures
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
Related targets
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