Member State report / Art11 / 2020 / D4 / Croatia / Mediterranean: Adriatic Sea

Report type Member State report to Commission
MSFD Article Art. 11 Monitoring programmes (and Art. 17 updates)
Report due 2020-10-15
GES Descriptor D4 Food webs/D1 Ecosystems
Member State Croatia
Region/subregion Mediterranean: Adriatic Sea
Reported by Institute of Oceanography and Fisheries
Report date 2020-10-15
Report access

Descriptor
D4/D1
D4/D1
D4/D1
D4/D1
D4/D1
D4/D1
D4/D1
D4/D1
D4/D1
D4/D1
D4/D1
D4/D1
D4/D1
D4/D1
D4/D1
Monitoring strategy description
Descriptor 4 address structural and functional changes in the food web according to main pressures including climatic variations and changes and anthropogenic impacts (eutrophication, pollution, alien species, fisheries). Primary (D4C1; D4C2) and secondary (D4C3; D4C4) criteria are applied to different trophic guilds using two indicators: (1) values are within natural range (NatRang) and (2) existence of trend (Trend).
Descriptor 4 address structural and functional changes in the food web according to main pressures including climatic variations and changes and anthropogenic impacts (eutrophication, pollution, alien species, fisheries). Primary (D4C1; D4C2) and secondary (D4C3; D4C4) criteria are applied to different trophic guilds using two indicators: (1) values are within natural range (NatRang) and (2) existence of trend (Trend).
Descriptor 4 address structural and functional changes in the food web according to main pressures including climatic variations and changes and anthropogenic impacts (eutrophication, pollution, alien species, fisheries). Primary (D4C1; D4C2) and secondary (D4C3; D4C4) criteria are applied to different trophic guilds using two indicators: (1) values are within natural range (NatRang) and (2) existence of trend (Trend).
Descriptor 4 address structural and functional changes in the food web according to main pressures including climatic variations and changes and anthropogenic impacts (eutrophication, pollution, alien species, fisheries). Primary (D4C1; D4C2) and secondary (D4C3; D4C4) criteria are applied to different trophic guilds using two indicators: (1) values are within natural range (NatRang) and (2) existence of trend (Trend).
Descriptor 4 address structural and functional changes in the food web according to main pressures including climatic variations and changes and anthropogenic impacts (eutrophication, pollution, alien species, fisheries). Primary (D4C1; D4C2) and secondary (D4C3; D4C4) criteria are applied to different trophic guilds using two indicators: (1) values are within natural range (NatRang) and (2) existence of trend (Trend).
Descriptor 4 address structural and functional changes in the food web according to main pressures including climatic variations and changes and anthropogenic impacts (eutrophication, pollution, alien species, fisheries). Primary (D4C1; D4C2) and secondary (D4C3; D4C4) criteria are applied to different trophic guilds using two indicators: (1) values are within natural range (NatRang) and (2) existence of trend (Trend).
Descriptor 4 address structural and functional changes in the food web according to main pressures including climatic variations and changes and anthropogenic impacts (eutrophication, pollution, alien species, fisheries). Primary (D4C1; D4C2) and secondary (D4C3; D4C4) criteria are applied to different trophic guilds using two indicators: (1) values are within natural range (NatRang) and (2) existence of trend (Trend).
Descriptor 4 address structural and functional changes in the food web according to main pressures including climatic variations and changes and anthropogenic impacts (eutrophication, pollution, alien species, fisheries). Primary (D4C1; D4C2) and secondary (D4C3; D4C4) criteria are applied to different trophic guilds using two indicators: (1) values are within natural range (NatRang) and (2) existence of trend (Trend).
Descriptor 4 address structural and functional changes in the food web according to main pressures including climatic variations and changes and anthropogenic impacts (eutrophication, pollution, alien species, fisheries). Primary (D4C1; D4C2) and secondary (D4C3; D4C4) criteria are applied to different trophic guilds using two indicators: (1) values are within natural range (NatRang) and (2) existence of trend (Trend).
Descriptor 4 address structural and functional changes in the food web according to main pressures including climatic variations and changes and anthropogenic impacts (eutrophication, pollution, alien species, fisheries). Primary (D4C1; D4C2) and secondary (D4C3; D4C4) criteria are applied to different trophic guilds using two indicators: (1) values are within natural range (NatRang) and (2) existence of trend (Trend).
Descriptor 4 address structural and functional changes in the food web according to main pressures including climatic variations and changes and anthropogenic impacts (eutrophication, pollution, alien species, fisheries). Primary (D4C1; D4C2) and secondary (D4C3; D4C4) criteria are applied to different trophic guilds using two indicators: (1) values are within natural range (NatRang) and (2) existence of trend (Trend).
Descriptor 4 address structural and functional changes in the food web according to main pressures including climatic variations and changes and anthropogenic impacts (eutrophication, pollution, alien species, fisheries). Primary (D4C1; D4C2) and secondary (D4C3; D4C4) criteria are applied to different trophic guilds using two indicators: (1) values are within natural range (NatRang) and (2) existence of trend (Trend).
Descriptor 4 address structural and functional changes in the food web according to main pressures including climatic variations and changes and anthropogenic impacts (eutrophication, pollution, alien species, fisheries). Primary (D4C1; D4C2) and secondary (D4C3; D4C4) criteria are applied to different trophic guilds using two indicators: (1) values are within natural range (NatRang) and (2) existence of trend (Trend).
Descriptor 4 address structural and functional changes in the food web according to main pressures including climatic variations and changes and anthropogenic impacts (eutrophication, pollution, alien species, fisheries). Primary (D4C1; D4C2) and secondary (D4C3; D4C4) criteria are applied to different trophic guilds using two indicators: (1) values are within natural range (NatRang) and (2) existence of trend (Trend).
Descriptor 4 address structural and functional changes in the food web according to main pressures including climatic variations and changes and anthropogenic impacts (eutrophication, pollution, alien species, fisheries). Primary (D4C1; D4C2) and secondary (D4C3; D4C4) criteria are applied to different trophic guilds using two indicators: (1) values are within natural range (NatRang) and (2) existence of trend (Trend).
Coverage of GES criteria
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Gaps and plans
Important difficulty is the lack of understanding the ecosystem consequences of the structural and functional changes in the food web, or the value that society should attribute to it. Indicators require further elaboration to become operational (definition of thresholds or limit reference points). In this moment two indicators (NatRang and Trend) are subject to an expert assessment.
Important difficulty is the lack of understanding the ecosystem consequences of the structural and functional changes in the food web, or the value that society should attribute to it. Indicators require further elaboration to become operational (definition of thresholds or limit reference points). In this moment two indicators (NatRang and Trend) are subject to an expert assessment.
Important difficulty is the lack of understanding the ecosystem consequences of the structural and functional changes in the food web, or the value that society should attribute to it. Indicators require further elaboration to become operational (definition of thresholds or limit reference points). In this moment two indicators (NatRang and Trend) are subject to an expert assessment.
Important difficulty is the lack of understanding the ecosystem consequences of the structural and functional changes in the food web, or the value that society should attribute to it. Indicators require further elaboration to become operational (definition of thresholds or limit reference points). In this moment two indicators (NatRang and Trend) are subject to an expert assessment.
Important difficulty is the lack of understanding the ecosystem consequences of the structural and functional changes in the food web, or the value that society should attribute to it. Indicators require further elaboration to become operational (definition of thresholds or limit reference points). In this moment two indicators (NatRang and Trend) are subject to an expert assessment.
Important difficulty is the lack of understanding the ecosystem consequences of the structural and functional changes in the food web, or the value that society should attribute to it. Indicators require further elaboration to become operational (definition of thresholds or limit reference points). In this moment two indicators (NatRang and Trend) are subject to an expert assessment.
Important difficulty is the lack of understanding the ecosystem consequences of the structural and functional changes in the food web, or the value that society should attribute to it. Indicators require further elaboration to become operational (definition of thresholds or limit reference points). In this moment two indicators (NatRang and Trend) are subject to an expert assessment.
Important difficulty is the lack of understanding the ecosystem consequences of the structural and functional changes in the food web, or the value that society should attribute to it. Indicators require further elaboration to become operational (definition of thresholds or limit reference points). In this moment two indicators (NatRang and Trend) are subject to an expert assessment.
Important difficulty is the lack of understanding the ecosystem consequences of the structural and functional changes in the food web, or the value that society should attribute to it. Indicators require further elaboration to become operational (definition of thresholds or limit reference points). In this moment two indicators (NatRang and Trend) are subject to an expert assessment.
Important difficulty is the lack of understanding the ecosystem consequences of the structural and functional changes in the food web, or the value that society should attribute to it. Indicators require further elaboration to become operational (definition of thresholds or limit reference points). In this moment two indicators (NatRang and Trend) are subject to an expert assessment.
Important difficulty is the lack of understanding the ecosystem consequences of the structural and functional changes in the food web, or the value that society should attribute to it. Indicators require further elaboration to become operational (definition of thresholds or limit reference points). In this moment two indicators (NatRang and Trend) are subject to an expert assessment.
Important difficulty is the lack of understanding the ecosystem consequences of the structural and functional changes in the food web, or the value that society should attribute to it. Indicators require further elaboration to become operational (definition of thresholds or limit reference points). In this moment two indicators (NatRang and Trend) are subject to an expert assessment.
Important difficulty is the lack of understanding the ecosystem consequences of the structural and functional changes in the food web, or the value that society should attribute to it. Indicators require further elaboration to become operational (definition of thresholds or limit reference points). In this moment two indicators (NatRang and Trend) are subject to an expert assessment.
Important difficulty is the lack of understanding the ecosystem consequences of the structural and functional changes in the food web, or the value that society should attribute to it. Indicators require further elaboration to become operational (definition of thresholds or limit reference points). In this moment two indicators (NatRang and Trend) are subject to an expert assessment.
Important difficulty is the lack of understanding the ecosystem consequences of the structural and functional changes in the food web, or the value that society should attribute to it. Indicators require further elaboration to become operational (definition of thresholds or limit reference points). In this moment two indicators (NatRang and Trend) are subject to an expert assessment.
Related targets
  • D4T1 - SpecCompDivers
  • D4T2 - LongTermStability
  • D4T3 - SizeDistrib
  • D4T1 - SpecCompDivers
  • D4T2 - LongTermStability
  • D4T3 - SizeDistrib
  • D4T1 - SpecCompDivers
  • D4T2 - LongTermStability
  • D4T3 - SizeDistrib
  • D4T1 - SpecCompDivers
  • D4T2 - LongTermStability
  • D4T3 - SizeDistrib
  • D4T1 - SpecCompDivers
  • D4T2 - LongTermStability
  • D4T3 - SizeDistrib
  • D4T1 - SpecCompDivers
  • D4T2 - LongTermStability
  • D4T3 - SizeDistrib
  • D4T1 - SpecCompDivers
  • D4T2 - LongTermStability
  • D4T3 - SizeDistrib
  • D4T1 - SpecCompDivers
  • D4T2 - LongTermStability
  • D4T3 - SizeDistrib
  • D4T1 - SpecCompDivers
  • D4T2 - LongTermStability
  • D4T3 - SizeDistrib
  • D4T1 - SpecCompDivers
  • D4T2 - LongTermStability
  • D4T3 - SizeDistrib
  • D4T1 - SpecCompDivers
  • D4T2 - LongTermStability
  • D4T3 - SizeDistrib
  • D4T1 - SpecCompDivers
  • D4T2 - LongTermStability
  • D4T3 - SizeDistrib
  • D4T1 - SpecCompDivers
  • D4T2 - LongTermStability
  • D4T3 - SizeDistrib
  • D4T1 - SpecCompDivers
  • D4T2 - LongTermStability
  • D4T3 - SizeDistrib
  • D4T1 - SpecCompDivers
  • D4T2 - LongTermStability
  • D4T3 - SizeDistrib
Coverage of targets
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Related measures
Coverage of measures
Related monitoring programmes
  • MADHR-D01-05
  • MADHR-D03-02
  • MADHR-D01-05
  • MADHR-D03-02
  • MADHR-D01-05
  • MADHR-D03-02
  • MADHR-D01-05
  • MADHR-D03-02
  • MADHR-D01-05
  • MADHR-D03-02
  • MADHR-D01-05
  • MADHR-D03-02
  • MADHR-D01-05
  • MADHR-D03-02
  • MADHR-D01-05
  • MADHR-D03-02
  • MADHR-D01-05
  • MADHR-D03-02
  • MADHR-D01-05
  • MADHR-D03-02
  • MADHR-D01-05
  • MADHR-D03-02
  • MADHR-D01-05
  • MADHR-D03-02
  • MADHR-D01-05
  • MADHR-D03-02
  • MADHR-D01-05
  • MADHR-D03-02
  • MADHR-D01-05
  • MADHR-D03-02
Programme code
MADHR-D01-05
MADHR-D01-05
MADHR-D01-05
MADHR-D01-05
MADHR-D01-05
MADHR-D01-05
MADHR-D01-05
MADHR-D01-05
MADHR-D03-02
MADHR-D03-02
MADHR-D03-02
MADHR-D03-02
MADHR-D03-02
MADHR-D03-02
MADHR-D03-02
Programme name
Pelagic habitats - community characteristics
Pelagic habitats - community characteristics
Pelagic habitats - community characteristics
Pelagic habitats - community characteristics
Pelagic habitats - community characteristics
Pelagic habitats - community characteristics
Pelagic habitats - community characteristics
Pelagic habitats - community characteristics
Activities extracting living resources (fisheries including recreational, maerl, seaweed)
Activities extracting living resources (fisheries including recreational, maerl, seaweed)
Activities extracting living resources (fisheries including recreational, maerl, seaweed)
Activities extracting living resources (fisheries including recreational, maerl, seaweed)
Activities extracting living resources (fisheries including recreational, maerl, seaweed)
Activities extracting living resources (fisheries including recreational, maerl, seaweed)
Activities extracting living resources (fisheries including recreational, maerl, seaweed)
Update type
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Old programme codes
  • MADHR-D014-05
  • MADHR-D014-05
  • MADHR-D014-05
  • MADHR-D014-05
  • MADHR-D014-05
  • MADHR-D014-05
  • MADHR-D014-05
  • MADHR-D014-05
Programme description
Plankton (microscopic plants and animals) play a fundamental role in the marine food web. Planktonic species generally have short life cycles and respond quickly to environmental changes and thus require spatially and temporally denser monitoring than species with longer life span and slower reproduction. Apart from the variations dependent on prevailing natural conditions and climate change, plankton communities are also impacted by human pressures, such as eutrophication, introduction of non-indigenous species and fisheries. The proposed indicators (biodiversity-based and stock-based) aim to discriminate changes in the plankton communities of the Croatian Adriatic due to human pressure from those caused by natural spatial-temporal variability. Sampling sites along the eastern Adriatic coast encompass open and coastal waters, with coastal sites reflecting areas under anthropogenic pressures. The samples collected will provide information on community composition and species abundances. Monitoring of plankton communities contributes to demonstrating the achievement of GES in the pelagic habitat, reflecting not only on the plankton but also on other species and habitats.
Plankton (microscopic plants and animals) play a fundamental role in the marine food web. Planktonic species generally have short life cycles and respond quickly to environmental changes and thus require spatially and temporally denser monitoring than species with longer life span and slower reproduction. Apart from the variations dependent on prevailing natural conditions and climate change, plankton communities are also impacted by human pressures, such as eutrophication, introduction of non-indigenous species and fisheries. The proposed indicators (biodiversity-based and stock-based) aim to discriminate changes in the plankton communities of the Croatian Adriatic due to human pressure from those caused by natural spatial-temporal variability. Sampling sites along the eastern Adriatic coast encompass open and coastal waters, with coastal sites reflecting areas under anthropogenic pressures. The samples collected will provide information on community composition and species abundances. Monitoring of plankton communities contributes to demonstrating the achievement of GES in the pelagic habitat, reflecting not only on the plankton but also on other species and habitats.
Plankton (microscopic plants and animals) play a fundamental role in the marine food web. Planktonic species generally have short life cycles and respond quickly to environmental changes and thus require spatially and temporally denser monitoring than species with longer life span and slower reproduction. Apart from the variations dependent on prevailing natural conditions and climate change, plankton communities are also impacted by human pressures, such as eutrophication, introduction of non-indigenous species and fisheries. The proposed indicators (biodiversity-based and stock-based) aim to discriminate changes in the plankton communities of the Croatian Adriatic due to human pressure from those caused by natural spatial-temporal variability. Sampling sites along the eastern Adriatic coast encompass open and coastal waters, with coastal sites reflecting areas under anthropogenic pressures. The samples collected will provide information on community composition and species abundances. Monitoring of plankton communities contributes to demonstrating the achievement of GES in the pelagic habitat, reflecting not only on the plankton but also on other species and habitats.
Plankton (microscopic plants and animals) play a fundamental role in the marine food web. Planktonic species generally have short life cycles and respond quickly to environmental changes and thus require spatially and temporally denser monitoring than species with longer life span and slower reproduction. Apart from the variations dependent on prevailing natural conditions and climate change, plankton communities are also impacted by human pressures, such as eutrophication, introduction of non-indigenous species and fisheries. The proposed indicators (biodiversity-based and stock-based) aim to discriminate changes in the plankton communities of the Croatian Adriatic due to human pressure from those caused by natural spatial-temporal variability. Sampling sites along the eastern Adriatic coast encompass open and coastal waters, with coastal sites reflecting areas under anthropogenic pressures. The samples collected will provide information on community composition and species abundances. Monitoring of plankton communities contributes to demonstrating the achievement of GES in the pelagic habitat, reflecting not only on the plankton but also on other species and habitats.
Plankton (microscopic plants and animals) play a fundamental role in the marine food web. Planktonic species generally have short life cycles and respond quickly to environmental changes and thus require spatially and temporally denser monitoring than species with longer life span and slower reproduction. Apart from the variations dependent on prevailing natural conditions and climate change, plankton communities are also impacted by human pressures, such as eutrophication, introduction of non-indigenous species and fisheries. The proposed indicators (biodiversity-based and stock-based) aim to discriminate changes in the plankton communities of the Croatian Adriatic due to human pressure from those caused by natural spatial-temporal variability. Sampling sites along the eastern Adriatic coast encompass open and coastal waters, with coastal sites reflecting areas under anthropogenic pressures. The samples collected will provide information on community composition and species abundances. Monitoring of plankton communities contributes to demonstrating the achievement of GES in the pelagic habitat, reflecting not only on the plankton but also on other species and habitats.
Plankton (microscopic plants and animals) play a fundamental role in the marine food web. Planktonic species generally have short life cycles and respond quickly to environmental changes and thus require spatially and temporally denser monitoring than species with longer life span and slower reproduction. Apart from the variations dependent on prevailing natural conditions and climate change, plankton communities are also impacted by human pressures, such as eutrophication, introduction of non-indigenous species and fisheries. The proposed indicators (biodiversity-based and stock-based) aim to discriminate changes in the plankton communities of the Croatian Adriatic due to human pressure from those caused by natural spatial-temporal variability. Sampling sites along the eastern Adriatic coast encompass open and coastal waters, with coastal sites reflecting areas under anthropogenic pressures. The samples collected will provide information on community composition and species abundances. Monitoring of plankton communities contributes to demonstrating the achievement of GES in the pelagic habitat, reflecting not only on the plankton but also on other species and habitats.
Plankton (microscopic plants and animals) play a fundamental role in the marine food web. Planktonic species generally have short life cycles and respond quickly to environmental changes and thus require spatially and temporally denser monitoring than species with longer life span and slower reproduction. Apart from the variations dependent on prevailing natural conditions and climate change, plankton communities are also impacted by human pressures, such as eutrophication, introduction of non-indigenous species and fisheries. The proposed indicators (biodiversity-based and stock-based) aim to discriminate changes in the plankton communities of the Croatian Adriatic due to human pressure from those caused by natural spatial-temporal variability. Sampling sites along the eastern Adriatic coast encompass open and coastal waters, with coastal sites reflecting areas under anthropogenic pressures. The samples collected will provide information on community composition and species abundances. Monitoring of plankton communities contributes to demonstrating the achievement of GES in the pelagic habitat, reflecting not only on the plankton but also on other species and habitats.
Plankton (microscopic plants and animals) play a fundamental role in the marine food web. Planktonic species generally have short life cycles and respond quickly to environmental changes and thus require spatially and temporally denser monitoring than species with longer life span and slower reproduction. Apart from the variations dependent on prevailing natural conditions and climate change, plankton communities are also impacted by human pressures, such as eutrophication, introduction of non-indigenous species and fisheries. The proposed indicators (biodiversity-based and stock-based) aim to discriminate changes in the plankton communities of the Croatian Adriatic due to human pressure from those caused by natural spatial-temporal variability. Sampling sites along the eastern Adriatic coast encompass open and coastal waters, with coastal sites reflecting areas under anthropogenic pressures. The samples collected will provide information on community composition and species abundances. Monitoring of plankton communities contributes to demonstrating the achievement of GES in the pelagic habitat, reflecting not only on the plankton but also on other species and habitats.
Monitoring of commercially exploited species of pelagic fish - sardines and anchovies, will be sampled on a monthly basis throughout the year. Samples will be collected from commercial fishing vessels, which fish with the purse seine nets in the fishing zones A, B, E and G.
Monitoring of commercially exploited species of pelagic fish - sardines and anchovies, will be sampled on a monthly basis throughout the year. Samples will be collected from commercial fishing vessels, which fish with the purse seine nets in the fishing zones A, B, E and G.
Monitoring of commercially exploited species of pelagic fish - sardines and anchovies, will be sampled on a monthly basis throughout the year. Samples will be collected from commercial fishing vessels, which fish with the purse seine nets in the fishing zones A, B, E and G.
Monitoring of commercially exploited species of pelagic fish - sardines and anchovies, will be sampled on a monthly basis throughout the year. Samples will be collected from commercial fishing vessels, which fish with the purse seine nets in the fishing zones A, B, E and G.
Monitoring of commercially exploited species of pelagic fish - sardines and anchovies, will be sampled on a monthly basis throughout the year. Samples will be collected from commercial fishing vessels, which fish with the purse seine nets in the fishing zones A, B, E and G.
Monitoring of commercially exploited species of pelagic fish - sardines and anchovies, will be sampled on a monthly basis throughout the year. Samples will be collected from commercial fishing vessels, which fish with the purse seine nets in the fishing zones A, B, E and G.
Monitoring of commercially exploited species of pelagic fish - sardines and anchovies, will be sampled on a monthly basis throughout the year. Samples will be collected from commercial fishing vessels, which fish with the purse seine nets in the fishing zones A, B, E and G.
Monitoring purpose
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Effectiveness of measures
  • Pressures in the marine environment
  • Effectiveness of measures
  • Pressures in the marine environment
  • Effectiveness of measures
  • Pressures in the marine environment
  • Effectiveness of measures
  • Pressures in the marine environment
  • Effectiveness of measures
  • Pressures in the marine environment
  • Effectiveness of measures
  • Pressures in the marine environment
  • Effectiveness of measures
  • Pressures in the marine environment
Other policies and conventions
  • Water Framework Directive
  • Water Framework Directive
  • Water Framework Directive
  • Water Framework Directive
  • Water Framework Directive
  • Water Framework Directive
  • Water Framework Directive
  • Water Framework Directive
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
Regional cooperation - coordinating body
Regional cooperation - countries involved
Regional cooperation - implementation level
Monitoring details
Frequency: Phytoplankton: Profiles of middle and northern Adriatic minimal 10 times a year. Lim, Bakar, ZOI 7 times a year. The rest 4 times a year Zooplankton: minimum 2 x per year
Frequency: Phytoplankton: Profiles of middle and northern Adriatic minimal 10 times a year. Lim, Bakar, ZOI 7 times a year. The rest 4 times a year Zooplankton: minimum 2 x per year
Frequency: Phytoplankton: Profiles of middle and northern Adriatic minimal 10 times a year. Lim, Bakar, ZOI 7 times a year. The rest 4 times a year Zooplankton: minimum 2 x per year
Frequency: Phytoplankton: Profiles of middle and northern Adriatic minimal 10 times a year. Lim, Bakar, ZOI 7 times a year. The rest 4 times a year Zooplankton: minimum 2 x per year
Frequency: Phytoplankton: Profiles of middle and northern Adriatic minimal 10 times a year. Lim, Bakar, ZOI 7 times a year. The rest 4 times a year Zooplankton: minimum 2 x per year
Frequency: Phytoplankton: Profiles of middle and northern Adriatic minimal 10 times a year. Lim, Bakar, ZOI 7 times a year. The rest 4 times a year Zooplankton: minimum 2 x per year
Frequency: Phytoplankton: Profiles of middle and northern Adriatic minimal 10 times a year. Lim, Bakar, ZOI 7 times a year. The rest 4 times a year Zooplankton: minimum 2 x per year
Frequency: Phytoplankton: Profiles of middle and northern Adriatic minimal 10 times a year. Lim, Bakar, ZOI 7 times a year. The rest 4 times a year Zooplankton: minimum 2 x per year
Estimation of the population biomass of both sardines and anchovies inhabiting the entire Adriatic Sea (GSA17, GSA18) is done once a year within the competent scientific institutions such as GFCM and / or STECF together with all participants in Adriatic.
Estimation of the population biomass of both sardines and anchovies inhabiting the entire Adriatic Sea (GSA17, GSA18) is done once a year within the competent scientific institutions such as GFCM and / or STECF together with all participants in Adriatic.
Estimation of the population biomass of both sardines and anchovies inhabiting the entire Adriatic Sea (GSA17, GSA18) is done once a year within the competent scientific institutions such as GFCM and / or STECF together with all participants in Adriatic.
Estimation of the population biomass of both sardines and anchovies inhabiting the entire Adriatic Sea (GSA17, GSA18) is done once a year within the competent scientific institutions such as GFCM and / or STECF together with all participants in Adriatic.
Estimation of the population biomass of both sardines and anchovies inhabiting the entire Adriatic Sea (GSA17, GSA18) is done once a year within the competent scientific institutions such as GFCM and / or STECF together with all participants in Adriatic.
Estimation of the population biomass of both sardines and anchovies inhabiting the entire Adriatic Sea (GSA17, GSA18) is done once a year within the competent scientific institutions such as GFCM and / or STECF together with all participants in Adriatic.
Estimation of the population biomass of both sardines and anchovies inhabiting the entire Adriatic Sea (GSA17, GSA18) is done once a year within the competent scientific institutions such as GFCM and / or STECF together with all participants in Adriatic.
Features
Other pelagic habitats
Coastal ecosystems
Shelf ecosystems
Coastal ecosystems
Shelf ecosystems
Coastal ecosystems
Shelf ecosystems
Eutrophication
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Coastal ecosystems
Shelf ecosystems
Coastal ecosystems
Shelf ecosystems
Elements
  • Phytoplankton communities
  • Zooplankton communities
  • Primary producers
  • Secondary producers
  • Primary producers
  • Secondary producers
  • Primary producers
  • Secondary producers
  • Primary producers
  • Secondary producers
  • Primary producers
  • Secondary producers
  • Primary producers
  • Secondary producers
  • Phytoplankton communities
  • Engraulis encrasicolus
  • Sardina pilchardus
  • Engraulis encrasicolus
  • Sardina pilchardus
  • Engraulis encrasicolus
  • Sardina pilchardus
  • Planktivores
  • Planktivores
  • Planktivores
  • Planktivores
GES criteria
D1C6
D4C1
D4C1
D4C2
D4C2
D4C4
D4C4
D5C3
D3C1
D3C2
D3C3
D4C2
D4C2
D4C3
D4C3
Parameters
  • Other
  • Other
  • Other
  • Abundance (number of individuals)
  • Biomass
  • Abundance (number of individuals)
  • Biomass
  • Productivity
  • Productivity
  • Frequency
  • Mortality rate
  • Biomass of Spawning Stock (SSB)
  • Size distribution
  • Abundance (number of individuals)
  • Biomass
  • Abundance (number of individuals)
  • Biomass
  • Size distribution
  • Size distribution
Parameter Other
Abundance/Biomass, species composition
Species composition
Species composition
Spatial scope
  • Territorial waters
  • Territorial waters
  • Territorial waters
  • Territorial waters
  • Territorial waters
  • Territorial waters
  • Territorial waters
  • Territorial waters
  • Territorial waters
  • Territorial waters
  • Territorial waters
  • Territorial waters
  • Territorial waters
  • Territorial waters
  • Territorial waters
Marine reporting units
  • MAD-HR-MRU_1
  • MAD-HR-MRU_1
  • MAD-HR-MRU_1
  • MAD-HR-MRU_1
  • MAD-HR-MRU_1
  • MAD-HR-MRU_1
  • MAD-HR-MRU_1
  • MAD-HR-MRU_1
  • MAD-HR-MRU_1
  • MAD-HR-MRU_1
  • MAD-HR-MRU_1
  • MAD-HR-MRU_1
  • MAD-HR-MRU_1
  • MAD-HR-MRU_1
  • MAD-HR-MRU_1
Temporal scope (start date - end date)
2021-2026
2021-2026
2021-2026
2021-2026
2021-2026
2021-2026
2021-2026
2021-2026
2021-2026
2021-2026
2021-2026
2021-2026
2021-2026
2021-2026
2021-2026
Monitoring frequency
Other
Other
Other
Other
Other
Other
Other
Other
Monthly
Monthly
Monthly
Monthly
Monthly
Monthly
Monthly
Monitoring type
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
Monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
Monitoring method other
Roger Harris, Peter Wiebe, Jürgen Lenz, Hein Rune Skjoldal and Mark Huntley. 2000. ICES Zooplankton Methodology Manual Utermöhl, von H. 1931. Neue Wege in der quantitativen Erfassung des Planktons. (Mit besondere Beriicksichtigung des Ultraplanktons). Verh. Int. Verein. Theor. Angew. Limnol., 5, 567–595. Marie, D., Partensky, F., Jacquet, S., Vaulot, D., (1997). Enumeration and cell cycle analysis of natural populations of marine picoplankton by flow cytometry using the nucleic acid stain SYBR Green I. Appl. Environ. Microb., 63, 186-193. Marie, D., Brussaard, C., Partensky, F., Vaulot, D. 1999. Flow cytometric analysis of phytoplankton, bacteria and viruses. In Current Protocols in Cytometry. John Wiley & Sons, Inc., pp. 11.11.1- 11.11.15. Fuhrman, J.A., Azam, F. (1982) Thymidine incorporation as a measure of heterotrophic bacterioplankton production in marine surface waters: evaluation and field results. Mar. Biol., 66, 109-120. doi: 10.1007/BF00397184 Sampling procedure has been described in Marasovic I., Krstulovic, N., Leder, N., Loncar, G., Precali, R., Šolic, M., Loncar,.G., Beg- Paklar, G., Bojanic, N., Cvitkovic, I., Dadic, V., Despalatovic, M., Dulcic, J., Grbec, B., Kušpilic, G., Nincevic-Gladan, Ž., P. Tutman, Ujevic, I., Vrgoc, N., Vukadin, P., Žuljevic, A. Coastal cities water pollution control project, Part C1: Monitoring and Observation System for Ongoing Assessment of the Adriatic sea under the Adriatic sea Monitoring Programme, Phase II. Interim report (IR), December, 2013. https://jadran.izor.hr/jadranski_projekt_2/MJERNE-METODE-I-OPREMA.pdf
Roger Harris, Peter Wiebe, Jürgen Lenz, Hein Rune Skjoldal and Mark Huntley. 2000. ICES Zooplankton Methodology Manual Utermöhl, von H. 1931. Neue Wege in der quantitativen Erfassung des Planktons. (Mit besondere Beriicksichtigung des Ultraplanktons). Verh. Int. Verein. Theor. Angew. Limnol., 5, 567–595. Marie, D., Partensky, F., Jacquet, S., Vaulot, D., (1997). Enumeration and cell cycle analysis of natural populations of marine picoplankton by flow cytometry using the nucleic acid stain SYBR Green I. Appl. Environ. Microb., 63, 186-193. Marie, D., Brussaard, C., Partensky, F., Vaulot, D. 1999. Flow cytometric analysis of phytoplankton, bacteria and viruses. In Current Protocols in Cytometry. John Wiley & Sons, Inc., pp. 11.11.1- 11.11.15. Fuhrman, J.A., Azam, F. (1982) Thymidine incorporation as a measure of heterotrophic bacterioplankton production in marine surface waters: evaluation and field results. Mar. Biol., 66, 109-120. doi: 10.1007/BF00397184 Sampling procedure has been described in Marasovic I., Krstulovic, N., Leder, N., Loncar, G., Precali, R., Šolic, M., Loncar,.G., Beg- Paklar, G., Bojanic, N., Cvitkovic, I., Dadic, V., Despalatovic, M., Dulcic, J., Grbec, B., Kušpilic, G., Nincevic-Gladan, Ž., P. Tutman, Ujevic, I., Vrgoc, N., Vukadin, P., Žuljevic, A. Coastal cities water pollution control project, Part C1: Monitoring and Observation System for Ongoing Assessment of the Adriatic sea under the Adriatic sea Monitoring Programme, Phase II. Interim report (IR), December, 2013. https://jadran.izor.hr/jadranski_projekt_2/MJERNE-METODE-I-OPREMA.pdf
Roger Harris, Peter Wiebe, Jürgen Lenz, Hein Rune Skjoldal and Mark Huntley. 2000. ICES Zooplankton Methodology Manual Utermöhl, von H. 1931. Neue Wege in der quantitativen Erfassung des Planktons. (Mit besondere Beriicksichtigung des Ultraplanktons). Verh. Int. Verein. Theor. Angew. Limnol., 5, 567–595. Marie, D., Partensky, F., Jacquet, S., Vaulot, D., (1997). Enumeration and cell cycle analysis of natural populations of marine picoplankton by flow cytometry using the nucleic acid stain SYBR Green I. Appl. Environ. Microb., 63, 186-193. Marie, D., Brussaard, C., Partensky, F., Vaulot, D. 1999. Flow cytometric analysis of phytoplankton, bacteria and viruses. In Current Protocols in Cytometry. John Wiley & Sons, Inc., pp. 11.11.1- 11.11.15. Fuhrman, J.A., Azam, F. (1982) Thymidine incorporation as a measure of heterotrophic bacterioplankton production in marine surface waters: evaluation and field results. Mar. Biol., 66, 109-120. doi: 10.1007/BF00397184 Sampling procedure has been described in Marasovic I., Krstulovic, N., Leder, N., Loncar, G., Precali, R., Šolic, M., Loncar,.G., Beg- Paklar, G., Bojanic, N., Cvitkovic, I., Dadic, V., Despalatovic, M., Dulcic, J., Grbec, B., Kušpilic, G., Nincevic-Gladan, Ž., P. Tutman, Ujevic, I., Vrgoc, N., Vukadin, P., Žuljevic, A. Coastal cities water pollution control project, Part C1: Monitoring and Observation System for Ongoing Assessment of the Adriatic sea under the Adriatic sea Monitoring Programme, Phase II. Interim report (IR), December, 2013. https://jadran.izor.hr/jadranski_projekt_2/MJERNE-METODE-I-OPREMA.pdf
Roger Harris, Peter Wiebe, Jürgen Lenz, Hein Rune Skjoldal and Mark Huntley. 2000. ICES Zooplankton Methodology Manual Utermöhl, von H. 1931. Neue Wege in der quantitativen Erfassung des Planktons. (Mit besondere Beriicksichtigung des Ultraplanktons). Verh. Int. Verein. Theor. Angew. Limnol., 5, 567–595. Marie, D., Partensky, F., Jacquet, S., Vaulot, D., (1997). Enumeration and cell cycle analysis of natural populations of marine picoplankton by flow cytometry using the nucleic acid stain SYBR Green I. Appl. Environ. Microb., 63, 186-193. Marie, D., Brussaard, C., Partensky, F., Vaulot, D. 1999. Flow cytometric analysis of phytoplankton, bacteria and viruses. In Current Protocols in Cytometry. John Wiley & Sons, Inc., pp. 11.11.1- 11.11.15. Fuhrman, J.A., Azam, F. (1982) Thymidine incorporation as a measure of heterotrophic bacterioplankton production in marine surface waters: evaluation and field results. Mar. Biol., 66, 109-120. doi: 10.1007/BF00397184 Sampling procedure has been described in Marasovic I., Krstulovic, N., Leder, N., Loncar, G., Precali, R., Šolic, M., Loncar,.G., Beg- Paklar, G., Bojanic, N., Cvitkovic, I., Dadic, V., Despalatovic, M., Dulcic, J., Grbec, B., Kušpilic, G., Nincevic-Gladan, Ž., P. Tutman, Ujevic, I., Vrgoc, N., Vukadin, P., Žuljevic, A. Coastal cities water pollution control project, Part C1: Monitoring and Observation System for Ongoing Assessment of the Adriatic sea under the Adriatic sea Monitoring Programme, Phase II. Interim report (IR), December, 2013. https://jadran.izor.hr/jadranski_projekt_2/MJERNE-METODE-I-OPREMA.pdf
Roger Harris, Peter Wiebe, Jürgen Lenz, Hein Rune Skjoldal and Mark Huntley. 2000. ICES Zooplankton Methodology Manual Utermöhl, von H. 1931. Neue Wege in der quantitativen Erfassung des Planktons. (Mit besondere Beriicksichtigung des Ultraplanktons). Verh. Int. Verein. Theor. Angew. Limnol., 5, 567–595. Marie, D., Partensky, F., Jacquet, S., Vaulot, D., (1997). Enumeration and cell cycle analysis of natural populations of marine picoplankton by flow cytometry using the nucleic acid stain SYBR Green I. Appl. Environ. Microb., 63, 186-193. Marie, D., Brussaard, C., Partensky, F., Vaulot, D. 1999. Flow cytometric analysis of phytoplankton, bacteria and viruses. In Current Protocols in Cytometry. John Wiley & Sons, Inc., pp. 11.11.1- 11.11.15. Fuhrman, J.A., Azam, F. (1982) Thymidine incorporation as a measure of heterotrophic bacterioplankton production in marine surface waters: evaluation and field results. Mar. Biol., 66, 109-120. doi: 10.1007/BF00397184 Sampling procedure has been described in Marasovic I., Krstulovic, N., Leder, N., Loncar, G., Precali, R., Šolic, M., Loncar,.G., Beg- Paklar, G., Bojanic, N., Cvitkovic, I., Dadic, V., Despalatovic, M., Dulcic, J., Grbec, B., Kušpilic, G., Nincevic-Gladan, Ž., P. Tutman, Ujevic, I., Vrgoc, N., Vukadin, P., Žuljevic, A. Coastal cities water pollution control project, Part C1: Monitoring and Observation System for Ongoing Assessment of the Adriatic sea under the Adriatic sea Monitoring Programme, Phase II. Interim report (IR), December, 2013. https://jadran.izor.hr/jadranski_projekt_2/MJERNE-METODE-I-OPREMA.pdf
Roger Harris, Peter Wiebe, Jürgen Lenz, Hein Rune Skjoldal and Mark Huntley. 2000. ICES Zooplankton Methodology Manual Utermöhl, von H. 1931. Neue Wege in der quantitativen Erfassung des Planktons. (Mit besondere Beriicksichtigung des Ultraplanktons). Verh. Int. Verein. Theor. Angew. Limnol., 5, 567–595. Marie, D., Partensky, F., Jacquet, S., Vaulot, D., (1997). Enumeration and cell cycle analysis of natural populations of marine picoplankton by flow cytometry using the nucleic acid stain SYBR Green I. Appl. Environ. Microb., 63, 186-193. Marie, D., Brussaard, C., Partensky, F., Vaulot, D. 1999. Flow cytometric analysis of phytoplankton, bacteria and viruses. In Current Protocols in Cytometry. John Wiley & Sons, Inc., pp. 11.11.1- 11.11.15. Fuhrman, J.A., Azam, F. (1982) Thymidine incorporation as a measure of heterotrophic bacterioplankton production in marine surface waters: evaluation and field results. Mar. Biol., 66, 109-120. doi: 10.1007/BF00397184 Sampling procedure has been described in Marasovic I., Krstulovic, N., Leder, N., Loncar, G., Precali, R., Šolic, M., Loncar,.G., Beg- Paklar, G., Bojanic, N., Cvitkovic, I., Dadic, V., Despalatovic, M., Dulcic, J., Grbec, B., Kušpilic, G., Nincevic-Gladan, Ž., P. Tutman, Ujevic, I., Vrgoc, N., Vukadin, P., Žuljevic, A. Coastal cities water pollution control project, Part C1: Monitoring and Observation System for Ongoing Assessment of the Adriatic sea under the Adriatic sea Monitoring Programme, Phase II. Interim report (IR), December, 2013. https://jadran.izor.hr/jadranski_projekt_2/MJERNE-METODE-I-OPREMA.pdf
Roger Harris, Peter Wiebe, Jürgen Lenz, Hein Rune Skjoldal and Mark Huntley. 2000. ICES Zooplankton Methodology Manual Utermöhl, von H. 1931. Neue Wege in der quantitativen Erfassung des Planktons. (Mit besondere Beriicksichtigung des Ultraplanktons). Verh. Int. Verein. Theor. Angew. Limnol., 5, 567–595. Marie, D., Partensky, F., Jacquet, S., Vaulot, D., (1997). Enumeration and cell cycle analysis of natural populations of marine picoplankton by flow cytometry using the nucleic acid stain SYBR Green I. Appl. Environ. Microb., 63, 186-193. Marie, D., Brussaard, C., Partensky, F., Vaulot, D. 1999. Flow cytometric analysis of phytoplankton, bacteria and viruses. In Current Protocols in Cytometry. John Wiley & Sons, Inc., pp. 11.11.1- 11.11.15. Fuhrman, J.A., Azam, F. (1982) Thymidine incorporation as a measure of heterotrophic bacterioplankton production in marine surface waters: evaluation and field results. Mar. Biol., 66, 109-120. doi: 10.1007/BF00397184 Sampling procedure has been described in Marasovic I., Krstulovic, N., Leder, N., Loncar, G., Precali, R., Šolic, M., Loncar,.G., Beg- Paklar, G., Bojanic, N., Cvitkovic, I., Dadic, V., Despalatovic, M., Dulcic, J., Grbec, B., Kušpilic, G., Nincevic-Gladan, Ž., P. Tutman, Ujevic, I., Vrgoc, N., Vukadin, P., Žuljevic, A. Coastal cities water pollution control project, Part C1: Monitoring and Observation System for Ongoing Assessment of the Adriatic sea under the Adriatic sea Monitoring Programme, Phase II. Interim report (IR), December, 2013. https://jadran.izor.hr/jadranski_projekt_2/MJERNE-METODE-I-OPREMA.pdf
Roger Harris, Peter Wiebe, Jürgen Lenz, Hein Rune Skjoldal and Mark Huntley. 2000. ICES Zooplankton Methodology Manual Utermöhl, von H. 1931. Neue Wege in der quantitativen Erfassung des Planktons. (Mit besondere Beriicksichtigung des Ultraplanktons). Verh. Int. Verein. Theor. Angew. Limnol., 5, 567–595. Marie, D., Partensky, F., Jacquet, S., Vaulot, D., (1997). Enumeration and cell cycle analysis of natural populations of marine picoplankton by flow cytometry using the nucleic acid stain SYBR Green I. Appl. Environ. Microb., 63, 186-193. Marie, D., Brussaard, C., Partensky, F., Vaulot, D. 1999. Flow cytometric analysis of phytoplankton, bacteria and viruses. In Current Protocols in Cytometry. John Wiley & Sons, Inc., pp. 11.11.1- 11.11.15. Fuhrman, J.A., Azam, F. (1982) Thymidine incorporation as a measure of heterotrophic bacterioplankton production in marine surface waters: evaluation and field results. Mar. Biol., 66, 109-120. doi: 10.1007/BF00397184 Sampling procedure has been described in Marasovic I., Krstulovic, N., Leder, N., Loncar, G., Precali, R., Šolic, M., Loncar,.G., Beg- Paklar, G., Bojanic, N., Cvitkovic, I., Dadic, V., Despalatovic, M., Dulcic, J., Grbec, B., Kušpilic, G., Nincevic-Gladan, Ž., P. Tutman, Ujevic, I., Vrgoc, N., Vukadin, P., Žuljevic, A. Coastal cities water pollution control project, Part C1: Monitoring and Observation System for Ongoing Assessment of the Adriatic sea under the Adriatic sea Monitoring Programme, Phase II. Interim report (IR), December, 2013. https://jadran.izor.hr/jadranski_projekt_2/MJERNE-METODE-I-OPREMA.pdf
Sampling procedure has been described in Marasovic I., Krstulovic, N., Leder, N., Loncar, G., Precali, R., Šolic, M., Loncar, G., Beg- Paklar, G., Bojanic, N., Cvitkovic, I., Dadic, V., Despalatovic, M., Dulcic, J., Grbec, B., Kušpilic, G., Nincevic-Gladan, Ž., P. Tutman, Ujevic, I., Vrgoc, N., Vukadin, P., Žuljevic, A. Coastal cities water pollution control project, Part C1: Monitoring and Observation System for Ongoing Assessment of the Adriatic sea under the Adriatic sea Monitoring Programme, Phase II. Interim report (IR), December, 2013. https://jadran.izor.hr/jadranski_projekt_2/MJERNE-METODE-I-OPREMA.pdf
Sampling procedure has been described in Marasovic I., Krstulovic, N., Leder, N., Loncar, G., Precali, R., Šolic, M., Loncar, G., Beg- Paklar, G., Bojanic, N., Cvitkovic, I., Dadic, V., Despalatovic, M., Dulcic, J., Grbec, B., Kušpilic, G., Nincevic-Gladan, Ž., P. Tutman, Ujevic, I., Vrgoc, N., Vukadin, P., Žuljevic, A. Coastal cities water pollution control project, Part C1: Monitoring and Observation System for Ongoing Assessment of the Adriatic sea under the Adriatic sea Monitoring Programme, Phase II. Interim report (IR), December, 2013. https://jadran.izor.hr/jadranski_projekt_2/MJERNE-METODE-I-OPREMA.pdf
Sampling procedure has been described in Marasovic I., Krstulovic, N., Leder, N., Loncar, G., Precali, R., Šolic, M., Loncar, G., Beg- Paklar, G., Bojanic, N., Cvitkovic, I., Dadic, V., Despalatovic, M., Dulcic, J., Grbec, B., Kušpilic, G., Nincevic-Gladan, Ž., P. Tutman, Ujevic, I., Vrgoc, N., Vukadin, P., Žuljevic, A. Coastal cities water pollution control project, Part C1: Monitoring and Observation System for Ongoing Assessment of the Adriatic sea under the Adriatic sea Monitoring Programme, Phase II. Interim report (IR), December, 2013. https://jadran.izor.hr/jadranski_projekt_2/MJERNE-METODE-I-OPREMA.pdf
Sampling procedure has been described in Marasovic I., Krstulovic, N., Leder, N., Loncar, G., Precali, R., Šolic, M., Loncar, G., Beg- Paklar, G., Bojanic, N., Cvitkovic, I., Dadic, V., Despalatovic, M., Dulcic, J., Grbec, B., Kušpilic, G., Nincevic-Gladan, Ž., P. Tutman, Ujevic, I., Vrgoc, N., Vukadin, P., Žuljevic, A. Coastal cities water pollution control project, Part C1: Monitoring and Observation System for Ongoing Assessment of the Adriatic sea under the Adriatic sea Monitoring Programme, Phase II. Interim report (IR), December, 2013. https://jadran.izor.hr/jadranski_projekt_2/MJERNE-METODE-I-OPREMA.pdf
Sampling procedure has been described in Marasovic I., Krstulovic, N., Leder, N., Loncar, G., Precali, R., Šolic, M., Loncar, G., Beg- Paklar, G., Bojanic, N., Cvitkovic, I., Dadic, V., Despalatovic, M., Dulcic, J., Grbec, B., Kušpilic, G., Nincevic-Gladan, Ž., P. Tutman, Ujevic, I., Vrgoc, N., Vukadin, P., Žuljevic, A. Coastal cities water pollution control project, Part C1: Monitoring and Observation System for Ongoing Assessment of the Adriatic sea under the Adriatic sea Monitoring Programme, Phase II. Interim report (IR), December, 2013. https://jadran.izor.hr/jadranski_projekt_2/MJERNE-METODE-I-OPREMA.pdf
Sampling procedure has been described in Marasovic I., Krstulovic, N., Leder, N., Loncar, G., Precali, R., Šolic, M., Loncar, G., Beg- Paklar, G., Bojanic, N., Cvitkovic, I., Dadic, V., Despalatovic, M., Dulcic, J., Grbec, B., Kušpilic, G., Nincevic-Gladan, Ž., P. Tutman, Ujevic, I., Vrgoc, N., Vukadin, P., Žuljevic, A. Coastal cities water pollution control project, Part C1: Monitoring and Observation System for Ongoing Assessment of the Adriatic sea under the Adriatic sea Monitoring Programme, Phase II. Interim report (IR), December, 2013. https://jadran.izor.hr/jadranski_projekt_2/MJERNE-METODE-I-OPREMA.pdf
Sampling procedure has been described in Marasovic I., Krstulovic, N., Leder, N., Loncar, G., Precali, R., Šolic, M., Loncar, G., Beg- Paklar, G., Bojanic, N., Cvitkovic, I., Dadic, V., Despalatovic, M., Dulcic, J., Grbec, B., Kušpilic, G., Nincevic-Gladan, Ž., P. Tutman, Ujevic, I., Vrgoc, N., Vukadin, P., Žuljevic, A. Coastal cities water pollution control project, Part C1: Monitoring and Observation System for Ongoing Assessment of the Adriatic sea under the Adriatic sea Monitoring Programme, Phase II. Interim report (IR), December, 2013. https://jadran.izor.hr/jadranski_projekt_2/MJERNE-METODE-I-OPREMA.pdf
Quality control
As used in the reported monitoring method.
As used in the reported monitoring method.
As used in the reported monitoring method.
As used in the reported monitoring method.
As used in the reported monitoring method.
As used in the reported monitoring method.
As used in the reported monitoring method.
As used in the reported monitoring method.
As used in the reported monitoring method.
As used in the reported monitoring method.
As used in the reported monitoring method.
As used in the reported monitoring method.
As used in the reported monitoring method.
As used in the reported monitoring method.
As used in the reported monitoring method.
Data management
Data access
Related indicator/name
Contact
References