Member State report / Art8 / 2018 / D5 / 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 D5 Eutrophication
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

Coastal waters (including transitional waters regarding descriptors and associated indicators that is not covered by WFD) (BAL-LT-AA-01)

GES component
D5
D5
D5
D5
D5
D5
Feature
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Element
TN
TP
Chlorophyll-a
Transparency
Benthic habitats - macrophyte communities
Benthic habitats - macrobenthic communities
Element code
NTOT
PTOT
EEA_3164-01-0
QE3-1-1
QE1-2-2
QE1-3
Element code source
Contaminants (D8-D9) http://seadatanet.maris2.nl/v_bodc_vocab_v2/vocab_relations.asp?lib=P02
Contaminants (D8-D9) http://seadatanet.maris2.nl/v_bodc_vocab_v2/vocab_relations.asp?lib=P02
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view
Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view
Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view
Element 2
Element 2 code
Element 2 code source
Element source
National
National
National
National
National
National
Criterion
D5C1
D5C1
D5C2
D5C4
D5C7
D5C8
Parameter
Concentration in water
Concentration in water
Concentration in water
Transparency in water
Extent
Other
Parameter other
BQI index
Threshold value upper
0.25
0.026
4.8
5.0
15.0
3.2
Threshold value lower
Threshold qualitative
Threshold value source
National
National
National
National
National
National
Threshold value source other
Value achieved upper
0.411
0.022
5.82
3.4
15.0
3.7
Value achieved lower
Value unit
Other
Other
microgram per litre
metre
Other
Other
Value unit other
mg N/l
mg P/l
maximum depth of the cultivated area, m
index
Proportion threshold value
100.0
100.0
100.0
100.0
100.0
100.0
Proportion value achieved
75.0
50.0
100.0
100.0
Proportion threshold value unit
% of stations achieving threshold value
% of stations achieving threshold value
% of stations achieving threshold value
% of stations achieving threshold value
% area of MRU achieving threshold value
% of stations achieving threshold value
Trend
Deteriorating
Improving
Stable
Stable
Stable
Improving
Parameter achieved
No
No
No
No
Yes
Yes
Description parameter
In the BAL-AA-01 study area, the GES value of total phosphorus was reached in 75% of the study sites (not in all), therefore the condition of the area was assessed as not good according to the TP. However, it should be noted that the mean summer (06-09 months) TP concentration in the BAL-AA-01 study area was 0.022 ± 0.016 mg P / l, and it corresponded to the GES value (0.026 mg P / l) and was lower than in the previous MSFD. In the first evaluation period 2006-2011 (0.035 ± 0.016 mg P / l). A decreasing trend of TP concentrations is observed. The indicator and its values are used to assess the ecological status of the coast according to the WFD.
Related indicator
Criteria status
Not good
Not good
Not good
Not good
Good
Good
Description criteria
Element status
Not good
Not good
Not good
Not good
Good
Good
Description element
According to the data of the period of 2012-2017, the average summer (06-09 months) TN concentration (0.411 mg N / l) in coastal waters (BAL-LT-AA-01) always exceeded the GES value (0.25 mg N / l), except in 2012. The indicator and its values are used to assess the ecological status of the coast according to the WFD.
The mean summer (06-09 months) TP concentration in the BAL-AA-01 study area was 0.022 ± 0.016 mg P / l and corresponded to the GES value (0.026 mg P / l) and was lower than in the previous MSFD I assessment period 2006-2011. (0.035 ± 0.016 mg P / l). However, not all study sites, but only 75% of stations TP reached the GES value, so the overall condition of the BAL-AA-01 study area in terms of TP concentrations remains poor. The indicator and its values are used to assess the ecological status of the coast according to the WFD.
Average warm period chlorophyll-a concentration in the coastal zone (BAL-LT-AA-01) in 2012-2017. was 5.82 ± 3.74 μg / l and showed poor environmental status. A similar (5.24 ± 3.51 μg / l) average warm-period chlorophyll-a concentration was determined in 2006-2011. period. The indicator and its values are used to assess the ecological status of the coast according to the WFD.
Secchi disk depth in the coastal zone (BAL-LT-AA-01) 2012-2017. was 3.40 ± 0.95 m during the period and showed poor environmental condition. A slightly higher (3.94 ± 0.62 m) average warm-up Secchi disk depth was found in 2006-2011. period. The indicator and its values are used to assess the ecological status of the coast according to the WFD.
The maximum depth of the red alga Furcellaria lumbricalis habitat in coastal waters was up to 15 m. The EQS obtained was 0.93, which corresponds to a very good ecological status. The latter has not changed since 2013. The indicator and its values are used to assess the ecological status of the coast according to the WFD.
2012-2017 The average value of the Benthos Quality Index (BQI) in coastal waters (BAL-LT-AA-01) was 3.7 and showed good environmental status (GES> 3.2). The indicator and its values are used to assess the ecological status of the coast according to the WFD.
Integration rule type parameter
Integration rule description parameter
Integration rule type criteria
Integration rule description criteria
GES extent threshold
100.00
100.00
100.00
100.00
100.00
100.00
GES extent achieved
GES extent unit
Proportion of area in good status
Proportion of area in good status
Proportion of area in good status
Proportion of area in good status
Proportion of area in good status
Proportion of area in good status
GES achieved
GES expected to be achieved later than 2020, Article 14 exception reported
GES expected to be achieved later than 2020, Article 14 exception reported
GES expected to be achieved later than 2020, Article 14 exception reported
GES expected to be achieved later than 2020, Article 14 exception reported
GES expected to be achieved later than 2020, Article 14 exception reported
GES expected to be achieved later than 2020, Article 14 exception reported
Description overall status
According to the data of the period of 2012-2017, the average summer (06-09 months) TN concentration (0.411 mg N / l) in coastal waters (BAL-LT-AA-01) always exceeded the GES value (0.25 mg N / l), except in 2012. The mean summer (06-09 months) TP concentration was 0.022 ± 0.016 mg P / l, corresponded to the GES value (0.026 mg P / l) and was lower than in the previous MSFD I assessment period 2006-2011 (0.035 ± 0.016 mg P / l). l). However, the TN GES value was not reached in all, but only in 75% of the research stations, therefore the condition according to TP is not good. Average warm period chlorophyll-a concentration in the coastal zone (BAL-LT-AA-01) in 2012-2017. was 5.82 ± 3.74 μg / l and showed poor environmental status. A similar (5.24 ± 3.51 μg / l) average warm-period chlorophyll-a concentration was determined in 2006-2011. period. Average warm period Secchi disk depth in the coastal zone (BAL-LT-AA-01) in 2012-2017. was 3.40 ± 0.95 m during the period and showed poor environmental condition. A slightly higher (3.94 ± 0.62 m) average warm-up Secchi disk depth was found in 2006-2011. period. The maximum depth of the red alga Furcellaria lumbricalis habitat in coastal waters was up to 15 m. The EQS obtained was 0.93, which corresponds to a very good ecological status. The latter has not changed since 2013. The average value of the Benthic Quality Index (BQI) in coastal waters (BAL-LT-AA-01) was 3.7 and indicated good environmental status (GAB> 3.2). In summary, of the 6 indicators used to assess eutrophication in coastal waters (BAL-LT-AA-01), two (F. lumbricalis depth of distribution and BQI index) reached GAB values. By integrating indicators at the level of criteria and applying the OOAO rule, the sea area in 2012-2017. did not achieve good environmental status.
According to the data of the period of 2012-2017, the average summer (06-09 months) TN concentration (0.411 mg N / l) in coastal waters (BAL-LT-AA-01) always exceeded the GES value (0.25 mg N / l), except in 2012. The mean summer (06-09 months) TP concentration was 0.022 ± 0.016 mg P / l, corresponded to the GES value (0.026 mg P / l) and was lower than in the previous MSFD I assessment period 2006-2011 (0.035 ± 0.016 mg P / l). l). However, the TN GES value was not reached in all, but only in 75% of the research stations, therefore the condition according to TP is not good. Average warm period chlorophyll-a concentration in the coastal zone (BAL-LT-AA-01) in 2012-2017. was 5.82 ± 3.74 μg / l and showed poor environmental status. A similar (5.24 ± 3.51 μg / l) average warm-period chlorophyll-a concentration was determined in 2006-2011. period. Average warm period Secchi disk depth in the coastal zone (BAL-LT-AA-01) in 2012-2017. was 3.40 ± 0.95 m during the period and showed poor environmental condition. A slightly higher (3.94 ± 0.62 m) average warm-up Secchi disk depth was found in 2006-2011. period. The maximum depth of the red alga Furcellaria lumbricalis habitat in coastal waters was up to 15 m. The EQS obtained was 0.93, which corresponds to a very good ecological status. The latter has not changed since 2013. The average value of the Benthic Quality Index (BQI) in coastal waters (BAL-LT-AA-01) was 3.7 and indicated good environmental status (GAB> 3.2). In summary, of the 6 indicators used to assess eutrophication in coastal waters (BAL-LT-AA-01), two (F. lumbricalis depth of distribution and BQI index) reached GAB values. By integrating indicators at the level of criteria and applying the OOAO rule, the sea area in 2012-2017. did not achieve good environmental status.
According to the data of the period of 2012-2017, the average summer (06-09 months) TN concentration (0.411 mg N / l) in coastal waters (BAL-LT-AA-01) always exceeded the GES value (0.25 mg N / l), except in 2012. The mean summer (06-09 months) TP concentration was 0.022 ± 0.016 mg P / l, corresponded to the GES value (0.026 mg P / l) and was lower than in the previous MSFD I assessment period 2006-2011 (0.035 ± 0.016 mg P / l). l). However, the TN GES value was not reached in all, but only in 75% of the research stations, therefore the condition according to TP is not good. Average warm period chlorophyll-a concentration in the coastal zone (BAL-LT-AA-01) in 2012-2017. was 5.82 ± 3.74 μg / l and showed poor environmental status. A similar (5.24 ± 3.51 μg / l) average warm-period chlorophyll-a concentration was determined in 2006-2011. period. Average warm period Secchi disk depth in the coastal zone (BAL-LT-AA-01) in 2012-2017. was 3.40 ± 0.95 m during the period and showed poor environmental condition. A slightly higher (3.94 ± 0.62 m) average warm-up Secchi disk depth was found in 2006-2011. period. The maximum depth of the red alga Furcellaria lumbricalis habitat in coastal waters was up to 15 m. The EQS obtained was 0.93, which corresponds to a very good ecological status. The latter has not changed since 2013. The average value of the Benthic Quality Index (BQI) in coastal waters (BAL-LT-AA-01) was 3.7 and indicated good environmental status (GAB> 3.2). In summary, of the 6 indicators used to assess eutrophication in coastal waters (BAL-LT-AA-01), two (F. lumbricalis depth of distribution and BQI index) reached GAB values. By integrating indicators at the level of criteria and applying the OOAO rule, the sea area in 2012-2017. did not achieve good environmental status.
According to the data of the period of 2012-2017, the average summer (06-09 months) TN concentration (0.411 mg N / l) in coastal waters (BAL-LT-AA-01) always exceeded the GES value (0.25 mg N / l), except in 2012. The mean summer (06-09 months) TP concentration was 0.022 ± 0.016 mg P / l, corresponded to the GES value (0.026 mg P / l) and was lower than in the previous MSFD I assessment period 2006-2011 (0.035 ± 0.016 mg P / l). l). However, the TN GES value was not reached in all, but only in 75% of the research stations, therefore the condition according to TP is not good. Average warm period chlorophyll-a concentration in the coastal zone (BAL-LT-AA-01) in 2012-2017. was 5.82 ± 3.74 μg / l and showed poor environmental status. A similar (5.24 ± 3.51 μg / l) average warm-period chlorophyll-a concentration was determined in 2006-2011. period. Average warm period Secchi disk depth in the coastal zone (BAL-LT-AA-01) in 2012-2017. was 3.40 ± 0.95 m during the period and showed poor environmental condition. A slightly higher (3.94 ± 0.62 m) average warm-up Secchi disk depth was found in 2006-2011. period. The maximum depth of the red alga Furcellaria lumbricalis habitat in coastal waters was up to 15 m. The EQS obtained was 0.93, which corresponds to a very good ecological status. The latter has not changed since 2013. The average value of the Benthic Quality Index (BQI) in coastal waters (BAL-LT-AA-01) was 3.7 and indicated good environmental status (GAB> 3.2). In summary, of the 6 indicators used to assess eutrophication in coastal waters (BAL-LT-AA-01), two (F. lumbricalis depth of distribution and BQI index) reached GAB values. By integrating indicators at the level of criteria and applying the OOAO rule, the sea area in 2012-2017. did not achieve good environmental status.
According to the data of the period of 2012-2017, the average summer (06-09 months) TN concentration (0.411 mg N / l) in coastal waters (BAL-LT-AA-01) always exceeded the GES value (0.25 mg N / l), except in 2012. The mean summer (06-09 months) TP concentration was 0.022 ± 0.016 mg P / l, corresponded to the GES value (0.026 mg P / l) and was lower than in the previous MSFD I assessment period 2006-2011 (0.035 ± 0.016 mg P / l). l). However, the TN GES value was not reached in all, but only in 75% of the research stations, therefore the condition according to TP is not good. Average warm period chlorophyll-a concentration in the coastal zone (BAL-LT-AA-01) in 2012-2017. was 5.82 ± 3.74 μg / l and showed poor environmental status. A similar (5.24 ± 3.51 μg / l) average warm-period chlorophyll-a concentration was determined in 2006-2011. period. Average warm period Secchi disk depth in the coastal zone (BAL-LT-AA-01) in 2012-2017. was 3.40 ± 0.95 m during the period and showed poor environmental condition. A slightly higher (3.94 ± 0.62 m) average warm-up Secchi disk depth was found in 2006-2011. period. The maximum depth of the red alga Furcellaria lumbricalis habitat in coastal waters was up to 15 m. The EQS obtained was 0.93, which corresponds to a very good ecological status. The latter has not changed since 2013. The average value of the Benthic Quality Index (BQI) in coastal waters (BAL-LT-AA-01) was 3.7 and indicated good environmental status (GAB> 3.2). In summary, of the 6 indicators used to assess eutrophication in coastal waters (BAL-LT-AA-01), two (F. lumbricalis depth of distribution and BQI index) reached GAB values. By integrating indicators at the level of criteria and applying the OOAO rule, the sea area in 2012-2017. did not achieve good environmental status.
According to the data of the period of 2012-2017, the average summer (06-09 months) TN concentration (0.411 mg N / l) in coastal waters (BAL-LT-AA-01) always exceeded the GES value (0.25 mg N / l), except in 2012. The mean summer (06-09 months) TP concentration was 0.022 ± 0.016 mg P / l, corresponded to the GES value (0.026 mg P / l) and was lower than in the previous MSFD I assessment period 2006-2011 (0.035 ± 0.016 mg P / l). l). However, the TN GES value was not reached in all, but only in 75% of the research stations, therefore the condition according to TP is not good. Average warm period chlorophyll-a concentration in the coastal zone (BAL-LT-AA-01) in 2012-2017. was 5.82 ± 3.74 μg / l and showed poor environmental status. A similar (5.24 ± 3.51 μg / l) average warm-period chlorophyll-a concentration was determined in 2006-2011. period. Average warm period Secchi disk depth in the coastal zone (BAL-LT-AA-01) in 2012-2017. was 3.40 ± 0.95 m during the period and showed poor environmental condition. A slightly higher (3.94 ± 0.62 m) average warm-up Secchi disk depth was found in 2006-2011. period. The maximum depth of the red alga Furcellaria lumbricalis habitat in coastal waters was up to 15 m. The EQS obtained was 0.93, which corresponds to a very good ecological status. The latter has not changed since 2013. The average value of the Benthic Quality Index (BQI) in coastal waters (BAL-LT-AA-01) was 3.7 and indicated good environmental status (GAB> 3.2). In summary, of the 6 indicators used to assess eutrophication in coastal waters (BAL-LT-AA-01), two (F. lumbricalis depth of distribution and BQI index) reached GAB values. By integrating indicators at the level of criteria and applying the OOAO rule, the sea area in 2012-2017. did not achieve good environmental status.
Assessments period
2012-2017
2012-2017
2012-2017
2012-2017
2012-2017
2012-2017
Related pressures
  • Changes to hydrological conditions
  • Input of nutrients - diffuse sources, point sources, atmospheric deposition
  • Changes to hydrological conditions
  • Input of nutrients - diffuse sources, point sources, atmospheric deposition
  • Changes to hydrological conditions
  • Input of nutrients - diffuse sources, point sources, atmospheric deposition
  • Changes to hydrological conditions
  • Input of nutrients - diffuse sources, point sources, atmospheric deposition
  • Changes to hydrological conditions
  • Input of nutrients - diffuse sources, point sources, atmospheric deposition
  • Changes to hydrological conditions
  • Input of nutrients - diffuse sources, point sources, atmospheric deposition
Related targets
  • 3
  • 3
  • 3
  • 3
  • 3
  • 3

Transitional waters (BAL-LT-AA-02)

GES component
D5
D5
D5
D5
D5
Feature
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Element
TN
TP
Chlorophyll-a
Benthic habitats - macrophyte communities
Benthic habitats - macrobenthic communities
Element code
NTOT
PTOT
EEA_3164-01-0
QE1-2-2
QE1-3
Element code source
Contaminants (D8-D9) http://seadatanet.maris2.nl/v_bodc_vocab_v2/vocab_relations.asp?lib=P02
Contaminants (D8-D9) http://seadatanet.maris2.nl/v_bodc_vocab_v2/vocab_relations.asp?lib=P02
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view
Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view
Element 2
Element 2 code
Element 2 code source
Element source
National
National
National
National
National
Criterion
D5C1
D5C1
D5C2
D5C7
D5C8
Parameter
Concentration in water
Concentration in water
Concentration in water
Extent
Other
Parameter other
BQI index
Threshold value upper
0.25
0.026
4.8
14.0
3.2
Threshold value lower
Threshold qualitative
Threshold value source
National
National
National
National
National
Threshold value source other
Value achieved upper
0.539
0.033
7.42
10.0
3.3
Value achieved lower
Value unit
Other
Other
microgram per litre
microgram per litre
Other
Value unit other
mg N/l
mg P/l
index
Proportion threshold value
100.0
100.0
100.0
100.0
100.0
Proportion value achieved
50.0
Proportion threshold value unit
% of stations achieving threshold value
% of stations achieving threshold value
% of stations achieving threshold value
% of stations achieving threshold value
% of stations achieving threshold value
Trend
Deteriorating
Improving
Stable
Stable
Improving
Parameter achieved
No
No
No
No
No
Description parameter
Good status according to the average BQI value is registered for one of the two monitoring stations (50%), but according to the average BQI value (3.3) the environmental status of the BAL-AA-02 marine area reached the GAB value (3.2).
Related indicator
Criteria status
Not good
Not good
Not good
Not good
Not good
Description criteria
Element status
Not good
Not good
Not good
Not good
Not good
Description element
2012-2017 In the period of distribution of the Curonian Lagoon waters in the Baltic Sea (BAL-LT-AA-02), the average summer (06-09 months) TN concentration (0.54 mg N / l) exceeded the GAB value (0.25 mg N / l). twice. Compared to 2006–2011, the concentration of TN in 2012–2017. increased by an average of 12% over the period, from 0.48 ± 0.14 to 0.54 ± 0.18 mg N / l. The indicator and its values are used to assess the ecological status of intermediate waters type 3 according to the WFD.
The mean summer (06-09 months) TP concentration (0.033 mg P / l) exceeded the established GAB threshold value (0.026 mg P / l). During the assessment period, the concentration of TP was lower compared to the period of 2006-2011 (0.041 ± 0.02 mg P / l). The indicator and its values are used to assess the ecological status of intermediate waters type 3 according to the WFD.
2012-2017 the average concentration of chlorophyll-a in the sea during the warm period (06-09 months) (BAL-LT-AA-02) was 7.42 μg / l and did not reach the GAB value. Good environmental status was observed only in 2014 and 2017. 2006-2011 The average value of the indicator was also not in good condition and was similar - 7.70 μg / l. The indicator and its values are used to assess the ecological status of intermediate waters type 3 according to the WFD.
During the period covered by the study, the maximum depth of the production area of the branched whale Furcellaria lumbricalis in the waters of BAL-LT-AA-02 was until 10. The ecological quality ratio (EQF) reached 0.71, which corresponds to the average ecological status of transitional waters, i.e. below good. The indicator and its values shall be used to measure the type 3 ecological status of transitional waters under the WFD.
Between 2012 and 2017, the average value of the Bentos Quality Index (BQI) for intermediate waters (BAL-LT-AA-02) was 3.3, indicating good environmental status (GAB > 3.2). However, good status is recorded on the basis of the average BQI value for one of the two monitoring stations (50 %) and therefore the area is below good status.
Integration rule type parameter
Integration rule description parameter
Integration rule type criteria
Integration rule description criteria
GES extent threshold
100.00
100.00
100.00
100.00
100.00
GES extent achieved
GES extent unit
Proportion of area in good status
Proportion of area in good status
Proportion of area in good status
Proportion of area in good status
Proportion of area in good status
GES achieved
GES expected to be achieved later than 2020, Article 14 exception reported
GES expected to be achieved later than 2020, Article 14 exception reported
GES expected to be achieved later than 2020, Article 14 exception reported
GES expected to be achieved later than 2020, Article 14 exception reported
GES expected to be achieved later than 2020, Article 14 exception reported
Description overall status
Between 2012 and 2017, the average summer TN concentration (between 06 and 09 months) in the area of distribution of Curonian Lagoon waters in the Baltic Sea (BAL-LT-AA-02) was twice as high as the GEC value (06,09 mg N/l).Compared to the period 2006-2011, the TN concentration increased on average between 2012 and 2017 by 12 %, from 0.48 ± 0.14 to 0.54 ± 0.18 mg N/l. The average summer (between 06 and 09 months) TP concentration (0.033 mg P/l) exceeded the GAB threshold (0.026 mg P/l). During the assessment period the TP concentration was lower than in the period 2006-2011 (0,041± 0,02 mg P/l). Between 2012 and 2017, the average concentration of chlorophyll-a at sea (BAL-LT-AA-02) in the warm period (06 to 09 months) was 7.42 μg/l below the GEC value. Good environmental status was observed only in 2014 and 2017. During the period 2006-2011, the average value of the indicator was also below good status and similar to 7.70 μg/l. In the area of distribution of the Curonian Lagoon waters in the Baltic Sea, saltwater and freshwater of the Curonian Lagoon are mixed. Therefore, the GEC for TN, TP and chlorophyll-a is based on the salinity of the water (>4 PSU (applies to coastal criteria), 2-4 PSU, <2 psu (applies to the indicator criteria for the northern part of the Curonian Lagoon)). During the study period, the average salinity was above PSU 4 and the GEC values of the coastal zone were used for the assessment of the status. During the period covered by the study, the maximum depth of the production area of the branched whale Furcellaria lumbricalis in the waters of BAL-LT-AA-02 was until 10. The ecological quality ratio (EQF) reached 0.71, which corresponds to the average ecological status of transitional waters, i.e. below good. Between 2012 and 2017, the average value of the Bentos Quality Index (BQI) for intermediate waters (BAL-LT-AA-02) was 3.3, indicating good environmental status (GAB > 3.2). However, good status is recorded on the basis of the average BQI value for one of the two monitoring stations (50 %) and therefore the area is below good status. By integrating indicators at criterion level and applying the OOAO rule, according to Descriptor D5, the sea area was below good environmental status between 2012 and 2017.
Between 2012 and 2017, the average summer TN concentration (between 06 and 09 months) in the area of distribution of Curonian Lagoon waters in the Baltic Sea (BAL-LT-AA-02) was twice as high as the GEC value (06,09 mg N/l).Compared to the period 2006-2011, the TN concentration increased on average between 2012 and 2017 by 12 %, from 0.48 ± 0.14 to 0.54 ± 0.18 mg N/l. The average summer (between 06 and 09 months) TP concentration (0.033 mg P/l) exceeded the GAB threshold (0.026 mg P/l). During the assessment period the TP concentration was lower than in the period 2006-2011 (0,041± 0,02 mg P/l). Between 2012 and 2017, the average concentration of chlorophyll-a at sea (BAL-LT-AA-02) in the warm period (06 to 09 months) was 7.42 μg/l below the GEC value. Good environmental status was observed only in 2014 and 2017. During the period 2006-2011, the average value of the indicator was also below good status and similar to 7.70 μg/l. In the area of distribution of the Curonian Lagoon waters in the Baltic Sea, saltwater and freshwater of the Curonian Lagoon are mixed. Therefore, the GEC for TN, TP and chlorophyll-a is based on the salinity of the water (>4 PSU (applies to coastal criteria), 2-4 PSU, <2 psu (applies to the indicator criteria for the northern part of the Curonian Lagoon)). During the study period, the average salinity was above PSU 4 and the GEC values of the coastal zone were used for the assessment of the status. During the period covered by the study, the maximum depth of the production area of the branched whale Furcellaria lumbricalis in the waters of BAL-LT-AA-02 was until 10. The ecological quality ratio (EQF) reached 0.71, which corresponds to the average ecological status of transitional waters, i.e. below good. Between 2012 and 2017, the average value of the Bentos Quality Index (BQI) for intermediate waters (BAL-LT-AA-02) was 3.3, indicating good environmental status (GAB > 3.2). However, good status is recorded on the basis of the average BQI value for one of the two monitoring stations (50 %) and therefore the area is below good status. By integrating indicators at criterion level and applying the OOAO rule, according to Descriptor D5, the sea area was below good environmental status between 2012 and 2017.
Between 2012 and 2017, the average summer TN concentration (between 06 and 09 months) in the area of distribution of Curonian Lagoon waters in the Baltic Sea (BAL-LT-AA-02) was twice as high as the GEC value (06,09 mg N/l).Compared to the period 2006-2011, the TN concentration increased on average between 2012 and 2017 by 12 %, from 0.48 ± 0.14 to 0.54 ± 0.18 mg N/l. The average summer (between 06 and 09 months) TP concentration (0.033 mg P/l) exceeded the GAB threshold (0.026 mg P/l). During the assessment period the TP concentration was lower than in the period 2006-2011 (0,041± 0,02 mg P/l). Between 2012 and 2017, the average concentration of chlorophyll-a at sea (BAL-LT-AA-02) in the warm period (06 to 09 months) was 7.42 μg/l below the GEC value. Good environmental status was observed only in 2014 and 2017. During the period 2006-2011, the average value of the indicator was also below good status and similar to 7.70 μg/l. In the area of distribution of the Curonian Lagoon waters in the Baltic Sea, saltwater and freshwater of the Curonian Lagoon are mixed. Therefore, the GEC for TN, TP and chlorophyll-a is based on the salinity of the water (>4 PSU (applies to coastal criteria), 2-4 PSU, <2 psu (applies to the indicator criteria for the northern part of the Curonian Lagoon)). During the study period, the average salinity was above PSU 4 and the GEC values of the coastal zone were used for the assessment of the status. During the period covered by the study, the maximum depth of the production area of the branched whale Furcellaria lumbricalis in the waters of BAL-LT-AA-02 was until 10. The ecological quality ratio (EQF) reached 0.71, which corresponds to the average ecological status of transitional waters, i.e. below good. Between 2012 and 2017, the average value of the Bentos Quality Index (BQI) for intermediate waters (BAL-LT-AA-02) was 3.3, indicating good environmental status (GAB > 3.2). However, good status is recorded on the basis of the average BQI value for one of the two monitoring stations (50 %) and therefore the area is below good status. By integrating indicators at criterion level and applying the OOAO rule, according to Descriptor D5, the sea area was below good environmental status between 2012 and 2017.
Between 2012 and 2017, the average summer TN concentration (between 06 and 09 months) in the area of distribution of Curonian Lagoon waters in the Baltic Sea (BAL-LT-AA-02) was twice as high as the GEC value (06,09 mg N/l).Compared to the period 2006-2011, the TN concentration increased on average between 2012 and 2017 by 12 %, from 0.48 ± 0.14 to 0.54 ± 0.18 mg N/l. The average summer (between 06 and 09 months) TP concentration (0.033 mg P/l) exceeded the GAB threshold (0.026 mg P/l). During the assessment period the TP concentration was lower than in the period 2006-2011 (0,041± 0,02 mg P/l). Between 2012 and 2017, the average concentration of chlorophyll-a at sea (BAL-LT-AA-02) in the warm period (06 to 09 months) was 7.42 μg/l below the GEC value. Good environmental status was observed only in 2014 and 2017. During the period 2006-2011, the average value of the indicator was also below good status and similar to 7.70 μg/l. In the area of distribution of the Curonian Lagoon waters in the Baltic Sea, saltwater and freshwater of the Curonian Lagoon are mixed. Therefore, the GEC for TN, TP and chlorophyll-a is based on the salinity of the water (>4 PSU (applies to coastal criteria), 2-4 PSU, <2 psu (applies to the indicator criteria for the northern part of the Curonian Lagoon)). During the study period, the average salinity was above PSU 4 and the GEC values of the coastal zone were used for the assessment of the status. During the period covered by the study, the maximum depth of the production area of the branched whale Furcellaria lumbricalis in the waters of BAL-LT-AA-02 was until 10. The ecological quality ratio (EQF) reached 0.71, which corresponds to the average ecological status of transitional waters, i.e. below good. Between 2012 and 2017, the average value of the Bentos Quality Index (BQI) for intermediate waters (BAL-LT-AA-02) was 3.3, indicating good environmental status (GAB > 3.2). However, good status is recorded on the basis of the average BQI value for one of the two monitoring stations (50 %) and therefore the area is below good status. By integrating indicators at criterion level and applying the OOAO rule, according to Descriptor D5, the sea area was below good environmental status between 2012 and 2017.
Between 2012 and 2017, the average summer TN concentration (between 06 and 09 months) in the area of distribution of Curonian Lagoon waters in the Baltic Sea (BAL-LT-AA-02) was twice as high as the GEC value (06,09 mg N/l).Compared to the period 2006-2011, the TN concentration increased on average between 2012 and 2017 by 12 %, from 0.48 ± 0.14 to 0.54 ± 0.18 mg N/l. The average summer (between 06 and 09 months) TP concentration (0.033 mg P/l) exceeded the GAB threshold (0.026 mg P/l). During the assessment period the TP concentration was lower than in the period 2006-2011 (0,041± 0,02 mg P/l). Between 2012 and 2017, the average concentration of chlorophyll-a at sea (BAL-LT-AA-02) in the warm period (06 to 09 months) was 7.42 μg/l below the GEC value. Good environmental status was observed only in 2014 and 2017. During the period 2006-2011, the average value of the indicator was also below good status and similar to 7.70 μg/l. In the area of distribution of the Curonian Lagoon waters in the Baltic Sea, saltwater and freshwater of the Curonian Lagoon are mixed. Therefore, the GEC for TN, TP and chlorophyll-a is based on the salinity of the water (>4 PSU (applies to coastal criteria), 2-4 PSU, <2 psu (applies to the indicator criteria for the northern part of the Curonian Lagoon)). During the study period, the average salinity was above PSU 4 and the GEC values of the coastal zone were used for the assessment of the status. During the period covered by the study, the maximum depth of the production area of the branched whale Furcellaria lumbricalis in the waters of BAL-LT-AA-02 was until 10. The ecological quality ratio (EQF) reached 0.71, which corresponds to the average ecological status of transitional waters, i.e. below good. Between 2012 and 2017, the average value of the Bentos Quality Index (BQI) for intermediate waters (BAL-LT-AA-02) was 3.3, indicating good environmental status (GAB > 3.2). However, good status is recorded on the basis of the average BQI value for one of the two monitoring stations (50 %) and therefore the area is below good status. By integrating indicators at criterion level and applying the OOAO rule, according to Descriptor D5, the sea area was below good environmental status between 2012 and 2017.
Assessments period
2012-2017
2012-2017
2012-2017
2012-2017
2012-2017
Related pressures
  • Changes to hydrological conditions
  • Input of nutrients - diffuse sources, point sources, atmospheric deposition
  • Physical disturbance to seabed
  • Changes to hydrological conditions
  • Input of nutrients - diffuse sources, point sources, atmospheric deposition
  • Physical disturbance to seabed
  • Changes to hydrological conditions
  • Input of nutrients - diffuse sources, point sources, atmospheric deposition
  • Physical disturbance to seabed
  • Changes to hydrological conditions
  • Input of nutrients - diffuse sources, point sources, atmospheric deposition
  • Physical disturbance to seabed
  • Changes to hydrological conditions
  • Input of nutrients - diffuse sources, point sources, atmospheric deposition
  • Physical disturbance to seabed
Related targets
  • 5
  • 5
  • 5
  • 5
  • 5

BAL-LT-AA-03

GES component
D5
D5
D5
D5
D5
D5
D5
D5
D5
Feature
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Element
DIN
DIP
TN
TP
Chlorophyll-a
Chlorophyll-a
Transparency
Transparency
Benthic habitats - macrobenthic communities
Element code
TDIN
PHOS
NTOT
PTOT
EEA_3164-01-0
EEA_3164-01-0
QE3-1-1
QE3-1-1
QE1-3
Element code source
Contaminants (D8-D9) http://seadatanet.maris2.nl/v_bodc_vocab_v2/vocab_relations.asp?lib=P02
Contaminants (D8-D9) http://seadatanet.maris2.nl/v_bodc_vocab_v2/vocab_relations.asp?lib=P02
Contaminants (D8-D9) http://seadatanet.maris2.nl/v_bodc_vocab_v2/vocab_relations.asp?lib=P02
Contaminants (D8-D9) http://seadatanet.maris2.nl/v_bodc_vocab_v2/vocab_relations.asp?lib=P02
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view
Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view
Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view
Element 2
Element 2 code
Element 2 code source
Element source
HELCOM
HELCOM
HELCOM
HELCOM
HELCOM
HELCOM
HELCOM
HELCOM
HELCOM
Criterion
D5C1
D5C1
D5C1
D5C1
D5C2
D5C2
D5C4
D5C4
D5C8
Parameter
Concentration in water
Concentration in water
Concentration in water
Concentration in water
Concentration in water
Other
Other
Transparency in water
Other
Parameter other
Concentration in water (summer mean)
Transparency of water (summer mean)
BQI index
Threshold value upper
0.04
0.01
0.225
0.014
0.99
1.9
7.0
8.8
2.9
Threshold value lower
Threshold qualitative
Threshold value source
MS(sub)region
MS(sub)region
MS(sub)region
MS(sub)region
MS(sub)region
MS(sub)region
MS(sub)region
MS(sub)region
National
Threshold value source other
Value achieved upper
0.084
0.017
0.371
0.018
3.35
3.55
5.16
5.88
3.0
Value achieved lower
Value unit
Other
Other
Other
Other
microgram per litre
microgram per litre
metre
metre
Other
Value unit other
MGN/l
MGP/l
MGN/l
MGP/l
index
Proportion threshold value
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
50.0
Proportion value achieved
17.0
100.0
Proportion threshold value unit
% of stations achieving threshold value
% of stations achieving threshold value
% of stations achieving threshold value
% of stations achieving threshold value
% of stations achieving threshold value
% of stations achieving threshold value
% of stations achieving threshold value
% of stations achieving threshold value
% area of MRU achieving threshold value
Trend
Improving
Stable
Deteriorating
Improving
Stable
Stable
Stable
Stable
Stable
Parameter achieved
No
No
No
No
No
No
No
No
Yes
Description parameter
The average annual chlorophyll-a concentration in open waters (BAL-LT-AA-03) was 3.35 μg/l below good environmental status (<0.99 μg/l).
Between 2012 and 2017, the average concentration of chlorophyll-a in the warm period in open waters (BAL-LT-AA-03) was 3.55 μg/l below good environmental status (< 1.90 μg/l).
The average depth of Secchi during the warm period in open waters (BAL-LT-AA-03) was 5.16 metres below the GEC value (>7 metres). A similar value (5.15 metres) was established for the period 2006-2011.
The average annual depth of the Secchi disc was 5.88 metres below the GEC value (>8.8 metres).
During the period 2012-2017, good status according to BQI mean values was achieved in all high seas waters (subsequently halocline, approximately 3000 km²), except for the debarking area (23.2 km², approximately 1 % of the area) affected by the physical disturbance effects assessed in accordance with D6. There is no further assessment of the status of the halocline area due to the lack of sufficient data. The environment is stable compared to 2006-2011.
Related indicator
Criteria status
Not good
Not good
Not good
Not good
Not good
Not good
Not good
Not good
Good
Description criteria
During the period 2012-2017, good status according to BQI mean values was achieved in all high seas waters (subsequently halocolin, about 3000 km²), except for the ground burial area (23.2 km², about 1 % of the site). There is no further assessment of the status of the halocolin area due to the lack of sufficient data. There are no objectives under the benthic quality indicator for soil burial as the area is exposed to other physical disturbances. The environment is stable compared to 2006-2011.
Element status
Not good
Not good
Not good
Not good
Not good
Not good
Not good
Not good
Good
Description element
The average concentration of dissolved inorganic nitrogen (DIN) in the winter part of BAL-LT-AA-03 was 0.084 mg N/l and the GES (0.04 mg N/l) was twice as high.
The concentration of dissolved inorganic phosphorus (DIP) in the winter part of BAL-LT-AA-03 was 0.017 mg P/l and almost twice the GES value (0.01 mg P/l).
Based on data from 2012 to 2017, in the territorial sea (BAL-LT-AA-03), the annual average nitrogen concentration (0,37 mg N/l) was 1,7 times higher than the GES value (0,225 mg N/l). The TN concentration was slightly higher than that observed between 2006 and 2011 (0.35 mg N/l).
The average annual concentration of TP varied between 0.016 mg P/l and 0.024 mg P/l, exceeding the GES value (0.014 mg P/l), except for 2014 years. In the period 2012-2017, the average TP concentration was twice as low (0.018 mg P/l) as in 2006-2011 (0.033 mg P/l).
Between 2012 and 2017, the average concentration of chlorophyll-a in the warm period in open waters (BAL-LT-AA-03) was 3.55 μg/l below good environmental status (< 1.90 μg/l). The average annual chlorophyll-a concentration in open waters (BAL-LT-AA-03) was 3.35 μg/l and was also below good environmental status (<0.99 μg/l).
Between 2012 and 2017, the average concentration of chlorophyll-a in the warm period in open waters (BAL-LT-AA-03) was 3.55 μg/l below good environmental status (< 1.90 μg/l). The average annual chlorophyll-a concentration in open waters (BAL-LT-AA-03) was 3.35 μg/l and was also below good environmental status (<0.99 μg/l).
The average warm-up Secchi disc depth in open water (BAL-LT-AA-03) was 5.16 meters and did not reach the GES value (> 7 meters). A similar value (5.15 meters) was found for the 2006-2011 period. The average annual depth of the Secchi disk was 5.88 meters, and also below the GES value (> 8.8 meters).
The average warm-up Secchi disc depth in open water (BAL-LT-AA-03) was 5.16 meters and did not reach the GES value (> 7 meters). A similar value (5.15 meters) was found for the 2006-2011 period. The average annual depth of the Secchi disk was 5.88 meters, and also below the GES value (> 8.8 meters).
During the period 2012-2017, good status according to BQI mean values was achieved in all high seas waters (subsequently halocline, approximately 3000 km²), except for the debarking area (23.2 km², approximately 1 % of the area) affected by the physical disturbance effects assessed in accordance with D6. There is no further assessment of the status of the halocline area due to the lack of sufficient data. The environment is stable compared to 2006-2011.
Integration rule type parameter
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
OOAO
Integration rule description parameter
Integration rule type criteria
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
GES extent achieved
GES extent unit
Proportion of area in good status
Proportion of area in good status
Proportion of area in good status
Proportion of area in good status
Proportion of area in good status
Proportion of area in good status
Proportion of area in good status
Proportion of area in good status
Proportion of area in good status
GES achieved
GES expected to be achieved later than 2020, Article 14 exception reported
GES expected to be achieved later than 2020, Article 14 exception reported
GES expected to be achieved later than 2020, Article 14 exception reported
GES expected to be achieved later than 2020, Article 14 exception reported
GES expected to be achieved later than 2020, Article 14 exception reported
GES expected to be achieved later than 2020, Article 14 exception reported
GES expected to be achieved later than 2020, Article 14 exception reported
GES expected to be achieved later than 2020, Article 14 exception reported
GES expected to be achieved later than 2020, Article 14 exception reported
Description overall status
Based on data from 2012 to 2017, in the territorial sea (BAL-LT-AA-03), the annual average nitrogen concentration (0,37 mg N/l) was 1,7 times higher than the GES value (0,225 mg N/l). The TN concentration was slightly higher than that observed between 2006 and 2011 (0.35 mg N/l). The average annual concentration of TP varied between 0.016 mg P/l and 0.024 mg P/l, exceeding the GES value (0.014 mg P/l), except for 2014 years. In the period 2012-2017, the average TP concentration was twice as low (0.018 mg P/l) as in 2006-2011 (0.033 mg P/l). The average concentration of dissolved inorganic nitrogen (DIN) in the winter part of BAL-LT-AA-03 was 0.084 mg N/l and the GES (0.04 mg N/l) was twice as high. The concentration of dissolved inorganic phosphorus (DIP) in the winter part of BAL-LT-AA-03 was 0.017 mg P/l and almost twice the GES value (0.01 mg P/l). Between 2012 and 2017, the average concentration of chlorophyll-a in the warm period in open waters (BAL-LT-AA-03) was 3.55 μg/l below good environmental status (< 1.90 μg/l). The average annual chlorophyll-a concentration (3,35 μg/l) also exceeded the GES value (<0,99 μg/l). The average depth of Secchi during the warm period in open waters (BAL-LT-AA-03) was 5.16 metres below the GEC value (>7 metres). A similar value (5.15 metres) was established for the period 2006-2011. The average annual depth of the Secchi disc was 5.88 metres and was also below the GES value (>8.8 metres). During the period 2012-2017, good status according to BQI mean values was achieved in all high seas waters (subsequently halocolin, about 3000 km²), except for the ground burial zone (23.2 km²). The environment is stable compared to 2006-2011. In summary, of the 9 indicators used to measure eutrophication in high seas (BAL-LT-AA-03), only one (BQI-index) reached the GES value. By integrating indicators at criterion level and applying the OOAO rule, according to Descriptor D5, the sea area was below good environmental status between 2012 and 2017.
Based on data from 2012 to 2017, in the territorial sea (BAL-LT-AA-03), the annual average nitrogen concentration (0,37 mg N/l) was 1,7 times higher than the GES value (0,225 mg N/l). The TN concentration was slightly higher than that observed between 2006 and 2011 (0.35 mg N/l). The average annual concentration of TP varied between 0.016 mg P/l and 0.024 mg P/l, exceeding the GES value (0.014 mg P/l), except for 2014 years. In the period 2012-2017, the average TP concentration was twice as low (0.018 mg P/l) as in 2006-2011 (0.033 mg P/l). The average concentration of dissolved inorganic nitrogen (DIN) in the winter part of BAL-LT-AA-03 was 0.084 mg N/l and the GES (0.04 mg N/l) was twice as high. The concentration of dissolved inorganic phosphorus (DIP) in the winter part of BAL-LT-AA-03 was 0.017 mg P/l and almost twice the GES value (0.01 mg P/l). Between 2012 and 2017, the average concentration of chlorophyll-a in the warm period in open waters (BAL-LT-AA-03) was 3.55 μg/l below good environmental status (< 1.90 μg/l). The average annual chlorophyll-a concentration (3,35 μg/l) also exceeded the GES value (<0,99 μg/l). The average depth of Secchi during the warm period in open waters (BAL-LT-AA-03) was 5.16 metres below the GEC value (>7 metres). A similar value (5.15 metres) was established for the period 2006-2011. The average annual depth of the Secchi disc was 5.88 metres and was also below the GES value (>8.8 metres). During the period 2012-2017, good status according to BQI mean values was achieved in all high seas waters (subsequently halocolin, about 3000 km²), except for the ground burial zone (23.2 km²). The environment is stable compared to 2006-2011. In summary, of the 9 indicators used to measure eutrophication in high seas (BAL-LT-AA-03), only one (BQI-index) reached the GES value. By integrating indicators at criterion level and applying the OOAO rule, according to Descriptor D5, the sea area was below good environmental status between 2012 and 2017.
Based on data from 2012 to 2017, in the territorial sea (BAL-LT-AA-03), the annual average nitrogen concentration (0,37 mg N/l) was 1,7 times higher than the GES value (0,225 mg N/l). The TN concentration was slightly higher than that observed between 2006 and 2011 (0.35 mg N/l). The average annual concentration of TP varied between 0.016 mg P/l and 0.024 mg P/l, exceeding the GES value (0.014 mg P/l), except for 2014 years. In the period 2012-2017, the average TP concentration was twice as low (0.018 mg P/l) as in 2006-2011 (0.033 mg P/l). The average concentration of dissolved inorganic nitrogen (DIN) in the winter part of BAL-LT-AA-03 was 0.084 mg N/l and the GES (0.04 mg N/l) was twice as high. The concentration of dissolved inorganic phosphorus (DIP) in the winter part of BAL-LT-AA-03 was 0.017 mg P/l and almost twice the GES value (0.01 mg P/l). Between 2012 and 2017, the average concentration of chlorophyll-a in the warm period in open waters (BAL-LT-AA-03) was 3.55 μg/l below good environmental status (< 1.90 μg/l). The average annual chlorophyll-a concentration (3,35 μg/l) also exceeded the GES value (<0,99 μg/l). The average depth of Secchi during the warm period in open waters (BAL-LT-AA-03) was 5.16 metres below the GEC value (>7 metres). A similar value (5.15 metres) was established for the period 2006-2011. The average annual depth of the Secchi disc was 5.88 metres and was also below the GES value (>8.8 metres). During the period 2012-2017, good status according to BQI mean values was achieved in all high seas waters (subsequently halocolin, about 3000 km²), except for the ground burial zone (23.2 km²). The environment is stable compared to 2006-2011. In summary, of the 9 indicators used to measure eutrophication in high seas (BAL-LT-AA-03), only one (BQI-index) reached the GES value. By integrating indicators at criterion level and applying the OOAO rule, according to Descriptor D5, the sea area was below good environmental status between 2012 and 2017.
Based on data from 2012 to 2017, in the territorial sea (BAL-LT-AA-03), the annual average nitrogen concentration (0,37 mg N/l) was 1,7 times higher than the GES value (0,225 mg N/l). The TN concentration was slightly higher than that observed between 2006 and 2011 (0.35 mg N/l). The average annual concentration of TP varied between 0.016 mg P/l and 0.024 mg P/l, exceeding the GES value (0.014 mg P/l), except for 2014 years. In the period 2012-2017, the average TP concentration was twice as low (0.018 mg P/l) as in 2006-2011 (0.033 mg P/l). The average concentration of dissolved inorganic nitrogen (DIN) in the winter part of BAL-LT-AA-03 was 0.084 mg N/l and the GES (0.04 mg N/l) was twice as high. The concentration of dissolved inorganic phosphorus (DIP) in the winter part of BAL-LT-AA-03 was 0.017 mg P/l and almost twice the GES value (0.01 mg P/l). Between 2012 and 2017, the average concentration of chlorophyll-a in the warm period in open waters (BAL-LT-AA-03) was 3.55 μg/l below good environmental status (< 1.90 μg/l). The average annual chlorophyll-a concentration (3,35 μg/l) also exceeded the GES value (<0,99 μg/l). The average depth of Secchi during the warm period in open waters (BAL-LT-AA-03) was 5.16 metres below the GEC value (>7 metres). A similar value (5.15 metres) was established for the period 2006-2011. The average annual depth of the Secchi disc was 5.88 metres and was also below the GES value (>8.8 metres). During the period 2012-2017, good status according to BQI mean values was achieved in all high seas waters (subsequently halocolin, about 3000 km²), except for the ground burial zone (23.2 km²). The environment is stable compared to 2006-2011. In summary, of the 9 indicators used to measure eutrophication in high seas (BAL-LT-AA-03), only one (BQI-index) reached the GES value. By integrating indicators at criterion level and applying the OOAO rule, according to Descriptor D5, the sea area was below good environmental status between 2012 and 2017.
Based on data from 2012 to 2017, in the territorial sea (BAL-LT-AA-03), the annual average nitrogen concentration (0,37 mg N/l) was 1,7 times higher than the GES value (0,225 mg N/l). The TN concentration was slightly higher than that observed between 2006 and 2011 (0.35 mg N/l). The average annual concentration of TP varied between 0.016 mg P/l and 0.024 mg P/l, exceeding the GES value (0.014 mg P/l), except for 2014 years. In the period 2012-2017, the average TP concentration was twice as low (0.018 mg P/l) as in 2006-2011 (0.033 mg P/l). The average concentration of dissolved inorganic nitrogen (DIN) in the winter part of BAL-LT-AA-03 was 0.084 mg N/l and the GES (0.04 mg N/l) was twice as high. The concentration of dissolved inorganic phosphorus (DIP) in the winter part of BAL-LT-AA-03 was 0.017 mg P/l and almost twice the GES value (0.01 mg P/l). Between 2012 and 2017, the average concentration of chlorophyll-a in the warm period in open waters (BAL-LT-AA-03) was 3.55 μg/l below good environmental status (< 1.90 μg/l). The average annual chlorophyll-a concentration (3,35 μg/l) also exceeded the GES value (<0,99 μg/l). The average depth of Secchi during the warm period in open waters (BAL-LT-AA-03) was 5.16 metres below the GEC value (>7 metres). A similar value (5.15 metres) was established for the period 2006-2011. The average annual depth of the Secchi disc was 5.88 metres and was also below the GES value (>8.8 metres). During the period 2012-2017, good status according to BQI mean values was achieved in all high seas waters (subsequently halocolin, about 3000 km²), except for the ground burial zone (23.2 km²). The environment is stable compared to 2006-2011. In summary, of the 9 indicators used to measure eutrophication in high seas (BAL-LT-AA-03), only one (BQI-index) reached the GES value. By integrating indicators at criterion level and applying the OOAO rule, according to Descriptor D5, the sea area was below good environmental status between 2012 and 2017.
Based on data from 2012 to 2017, in the territorial sea (BAL-LT-AA-03), the annual average nitrogen concentration (0,37 mg N/l) was 1,7 times higher than the GES value (0,225 mg N/l). The TN concentration was slightly higher than that observed between 2006 and 2011 (0.35 mg N/l). The average annual concentration of TP varied between 0.016 mg P/l and 0.024 mg P/l, exceeding the GES value (0.014 mg P/l), except for 2014 years. In the period 2012-2017, the average TP concentration was twice as low (0.018 mg P/l) as in 2006-2011 (0.033 mg P/l). The average concentration of dissolved inorganic nitrogen (DIN) in the winter part of BAL-LT-AA-03 was 0.084 mg N/l and the GES (0.04 mg N/l) was twice as high. The concentration of dissolved inorganic phosphorus (DIP) in the winter part of BAL-LT-AA-03 was 0.017 mg P/l and almost twice the GES value (0.01 mg P/l). Between 2012 and 2017, the average concentration of chlorophyll-a in the warm period in open waters (BAL-LT-AA-03) was 3.55 μg/l below good environmental status (< 1.90 μg/l). The average annual chlorophyll-a concentration (3,35 μg/l) also exceeded the GES value (<0,99 μg/l). The average depth of Secchi during the warm period in open waters (BAL-LT-AA-03) was 5.16 metres below the GEC value (>7 metres). A similar value (5.15 metres) was established for the period 2006-2011. The average annual depth of the Secchi disc was 5.88 metres and was also below the GES value (>8.8 metres). During the period 2012-2017, good status according to BQI mean values was achieved in all high seas waters (subsequently halocolin, about 3000 km²), except for the ground burial zone (23.2 km²). The environment is stable compared to 2006-2011. In summary, of the 9 indicators used to measure eutrophication in high seas (BAL-LT-AA-03), only one (BQI-index) reached the GES value. By integrating indicators at criterion level and applying the OOAO rule, according to Descriptor D5, the sea area was below good environmental status between 2012 and 2017.
Based on data from 2012 to 2017, in the territorial sea (BAL-LT-AA-03), the annual average nitrogen concentration (0,37 mg N/l) was 1,7 times higher than the GES value (0,225 mg N/l). The TN concentration was slightly higher than that observed between 2006 and 2011 (0.35 mg N/l). The average annual concentration of TP varied between 0.016 mg P/l and 0.024 mg P/l, exceeding the GES value (0.014 mg P/l), except for 2014 years. In the period 2012-2017, the average TP concentration was twice as low (0.018 mg P/l) as in 2006-2011 (0.033 mg P/l). The average concentration of dissolved inorganic nitrogen (DIN) in the winter part of BAL-LT-AA-03 was 0.084 mg N/l and the GES (0.04 mg N/l) was twice as high. The concentration of dissolved inorganic phosphorus (DIP) in the winter part of BAL-LT-AA-03 was 0.017 mg P/l and almost twice the GES value (0.01 mg P/l). Between 2012 and 2017, the average concentration of chlorophyll-a in the warm period in open waters (BAL-LT-AA-03) was 3.55 μg/l below good environmental status (< 1.90 μg/l). The average annual chlorophyll-a concentration (3,35 μg/l) also exceeded the GES value (<0,99 μg/l). The average depth of Secchi during the warm period in open waters (BAL-LT-AA-03) was 5.16 metres below the GEC value (>7 metres). A similar value (5.15 metres) was established for the period 2006-2011. The average annual depth of the Secchi disc was 5.88 metres and was also below the GES value (>8.8 metres). During the period 2012-2017, good status according to BQI mean values was achieved in all high seas waters (subsequently halocolin, about 3000 km²), except for the ground burial zone (23.2 km²). The environment is stable compared to 2006-2011. In summary, of the 9 indicators used to measure eutrophication in high seas (BAL-LT-AA-03), only one (BQI-index) reached the GES value. By integrating indicators at criterion level and applying the OOAO rule, according to Descriptor D5, the sea area was below good environmental status between 2012 and 2017.
Based on data from 2012 to 2017, in the territorial sea (BAL-LT-AA-03), the annual average nitrogen concentration (0,37 mg N/l) was 1,7 times higher than the GES value (0,225 mg N/l). The TN concentration was slightly higher than that observed between 2006 and 2011 (0.35 mg N/l). The average annual concentration of TP varied between 0.016 mg P/l and 0.024 mg P/l, exceeding the GES value (0.014 mg P/l), except for 2014 years. In the period 2012-2017, the average TP concentration was twice as low (0.018 mg P/l) as in 2006-2011 (0.033 mg P/l). The average concentration of dissolved inorganic nitrogen (DIN) in the winter part of BAL-LT-AA-03 was 0.084 mg N/l and the GES (0.04 mg N/l) was twice as high. The concentration of dissolved inorganic phosphorus (DIP) in the winter part of BAL-LT-AA-03 was 0.017 mg P/l and almost twice the GES value (0.01 mg P/l). Between 2012 and 2017, the average concentration of chlorophyll-a in the warm period in open waters (BAL-LT-AA-03) was 3.55 μg/l below good environmental status (< 1.90 μg/l). The average annual chlorophyll-a concentration (3,35 μg/l) also exceeded the GES value (<0,99 μg/l). The average depth of Secchi during the warm period in open waters (BAL-LT-AA-03) was 5.16 metres below the GEC value (>7 metres). A similar value (5.15 metres) was established for the period 2006-2011. The average annual depth of the Secchi disc was 5.88 metres and was also below the GES value (>8.8 metres). During the period 2012-2017, good status according to BQI mean values was achieved in all high seas waters (subsequently halocolin, about 3000 km²), except for the ground burial zone (23.2 km²). The environment is stable compared to 2006-2011. In summary, of the 9 indicators used to measure eutrophication in high seas (BAL-LT-AA-03), only one (BQI-index) reached the GES value. By integrating indicators at criterion level and applying the OOAO rule, according to Descriptor D5, the sea area was below good environmental status between 2012 and 2017.
Based on data from 2012 to 2017, in the territorial sea (BAL-LT-AA-03), the annual average nitrogen concentration (0,37 mg N/l) was 1,7 times higher than the GES value (0,225 mg N/l). The TN concentration was slightly higher than that observed between 2006 and 2011 (0.35 mg N/l). The average annual concentration of TP varied between 0.016 mg P/l and 0.024 mg P/l, exceeding the GES value (0.014 mg P/l), except for 2014 years. In the period 2012-2017, the average TP concentration was twice as low (0.018 mg P/l) as in 2006-2011 (0.033 mg P/l). The average concentration of dissolved inorganic nitrogen (DIN) in the winter part of BAL-LT-AA-03 was 0.084 mg N/l and the GES (0.04 mg N/l) was twice as high. The concentration of dissolved inorganic phosphorus (DIP) in the winter part of BAL-LT-AA-03 was 0.017 mg P/l and almost twice the GES value (0.01 mg P/l). Between 2012 and 2017, the average concentration of chlorophyll-a in the warm period in open waters (BAL-LT-AA-03) was 3.55 μg/l below good environmental status (< 1.90 μg/l). The average annual chlorophyll-a concentration (3,35 μg/l) also exceeded the GES value (<0,99 μg/l). The average depth of Secchi during the warm period in open waters (BAL-LT-AA-03) was 5.16 metres below the GEC value (>7 metres). A similar value (5.15 metres) was established for the period 2006-2011. The average annual depth of the Secchi disc was 5.88 metres and was also below the GES value (>8.8 metres). During the period 2012-2017, good status according to BQI mean values was achieved in all high seas waters (subsequently halocolin, about 3000 km²), except for the ground burial zone (23.2 km²). The environment is stable compared to 2006-2011. In summary, of the 9 indicators used to measure eutrophication in high seas (BAL-LT-AA-03), only one (BQI-index) reached the GES value. By integrating indicators at criterion level and applying the OOAO rule, according to Descriptor D5, the sea area was below good environmental status between 2012 and 2017.
Assessments period
2012-2017
2012-2017
2012-2017
2012-2017
2012-2017
2012-2017
2012-2017
2012-2017
2012-2017
Related pressures
  • Changes to hydrological conditions
  • Input of nutrients - diffuse sources, point sources, atmospheric deposition
  • Physical disturbance to seabed
  • Changes to hydrological conditions
  • Input of nutrients - diffuse sources, point sources, atmospheric deposition
  • Physical disturbance to seabed
  • Changes to hydrological conditions
  • Input of nutrients - diffuse sources, point sources, atmospheric deposition
  • Physical disturbance to seabed
  • Changes to hydrological conditions
  • Input of nutrients - diffuse sources, point sources, atmospheric deposition
  • Physical disturbance to seabed
  • Changes to hydrological conditions
  • Input of nutrients - diffuse sources, point sources, atmospheric deposition
  • Physical disturbance to seabed
  • Changes to hydrological conditions
  • Input of nutrients - diffuse sources, point sources, atmospheric deposition
  • Physical disturbance to seabed
  • Changes to hydrological conditions
  • Input of nutrients - diffuse sources, point sources, atmospheric deposition
  • Physical disturbance to seabed
  • Changes to hydrological conditions
  • Input of nutrients - diffuse sources, point sources, atmospheric deposition
  • Physical disturbance to seabed
  • Changes to hydrological conditions
  • Input of nutrients - diffuse sources, point sources, atmospheric deposition
  • Physical disturbance to seabed
Related targets
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  • 3
  • 3
  • 3
  • 3
  • 3
  • 3
  • 3