Member State report / Art11 / 2020 / D5 / 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 | D5 Eutrophication |
| Member State | Croatia |
| Region/subregion | Mediterranean: Adriatic Sea |
| Reported by | Institute of Oceanography and Fisheries |
| Report date | 2020-10-15 |
| Report access |
Descriptor |
D5 |
D5 |
D5 |
D5 |
D5 |
D5 |
D5 |
D5 |
D5 |
D5 |
D5 |
D5 |
D5 |
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Monitoring strategy description |
The Driver-Pressure-State-Impact-Response (DPSIR) approach considers human activities as an integral part of the ecosystem. Main drivers for eutrophication are agriculture and livestock, aquaculture, fishery and tourism. As a pressure of these activities, nutrienst concentration were measured, while microalgal biomass and oxygen concentration were used for assessment of impact. Responses include measures against nutrient loading. |
The Driver-Pressure-State-Impact-Response (DPSIR) approach considers human activities as an integral part of the ecosystem. Main drivers for eutrophication are agriculture and livestock, aquaculture, fishery and tourism. As a pressure of these activities, nutrienst concentration were measured, while microalgal biomass and oxygen concentration were used for assessment of impact. Responses include measures against nutrient loading. |
The Driver-Pressure-State-Impact-Response (DPSIR) approach considers human activities as an integral part of the ecosystem. Main drivers for eutrophication are agriculture and livestock, aquaculture, fishery and tourism. As a pressure of these activities, nutrienst concentration were measured, while microalgal biomass and oxygen concentration were used for assessment of impact. Responses include measures against nutrient loading. |
The Driver-Pressure-State-Impact-Response (DPSIR) approach considers human activities as an integral part of the ecosystem. Main drivers for eutrophication are agriculture and livestock, aquaculture, fishery and tourism. As a pressure of these activities, nutrienst concentration were measured, while microalgal biomass and oxygen concentration were used for assessment of impact. Responses include measures against nutrient loading. |
The Driver-Pressure-State-Impact-Response (DPSIR) approach considers human activities as an integral part of the ecosystem. Main drivers for eutrophication are agriculture and livestock, aquaculture, fishery and tourism. As a pressure of these activities, nutrienst concentration were measured, while microalgal biomass and oxygen concentration were used for assessment of impact. Responses include measures against nutrient loading. |
The Driver-Pressure-State-Impact-Response (DPSIR) approach considers human activities as an integral part of the ecosystem. Main drivers for eutrophication are agriculture and livestock, aquaculture, fishery and tourism. As a pressure of these activities, nutrienst concentration were measured, while microalgal biomass and oxygen concentration were used for assessment of impact. Responses include measures against nutrient loading. |
The Driver-Pressure-State-Impact-Response (DPSIR) approach considers human activities as an integral part of the ecosystem. Main drivers for eutrophication are agriculture and livestock, aquaculture, fishery and tourism. As a pressure of these activities, nutrienst concentration were measured, while microalgal biomass and oxygen concentration were used for assessment of impact. Responses include measures against nutrient loading. |
The Driver-Pressure-State-Impact-Response (DPSIR) approach considers human activities as an integral part of the ecosystem. Main drivers for eutrophication are agriculture and livestock, aquaculture, fishery and tourism. As a pressure of these activities, nutrienst concentration were measured, while microalgal biomass and oxygen concentration were used for assessment of impact. Responses include measures against nutrient loading. |
The Driver-Pressure-State-Impact-Response (DPSIR) approach considers human activities as an integral part of the ecosystem. Main drivers for eutrophication are agriculture and livestock, aquaculture, fishery and tourism. As a pressure of these activities, nutrienst concentration were measured, while microalgal biomass and oxygen concentration were used for assessment of impact. Responses include measures against nutrient loading. |
The Driver-Pressure-State-Impact-Response (DPSIR) approach considers human activities as an integral part of the ecosystem. Main drivers for eutrophication are agriculture and livestock, aquaculture, fishery and tourism. As a pressure of these activities, nutrienst concentration were measured, while microalgal biomass and oxygen concentration were used for assessment of impact. Responses include measures against nutrient loading. |
The Driver-Pressure-State-Impact-Response (DPSIR) approach considers human activities as an integral part of the ecosystem. Main drivers for eutrophication are agriculture and livestock, aquaculture, fishery and tourism. As a pressure of these activities, nutrienst concentration were measured, while microalgal biomass and oxygen concentration were used for assessment of impact. Responses include measures against nutrient loading. |
The Driver-Pressure-State-Impact-Response (DPSIR) approach considers human activities as an integral part of the ecosystem. Main drivers for eutrophication are agriculture and livestock, aquaculture, fishery and tourism. As a pressure of these activities, nutrienst concentration were measured, while microalgal biomass and oxygen concentration were used for assessment of impact. Responses include measures against nutrient loading. |
The Driver-Pressure-State-Impact-Response (DPSIR) approach considers human activities as an integral part of the ecosystem. Main drivers for eutrophication are agriculture and livestock, aquaculture, fishery and tourism. As a pressure of these activities, nutrienst concentration were measured, while microalgal biomass and oxygen concentration were used for assessment of impact. Responses include measures against nutrient loading. |
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 |
Gaps and plans |
Provide funds for regular monitoring programme implementation. |
Provide funds for regular monitoring programme implementation. |
Provide funds for regular monitoring programme implementation. |
Provide funds for regular monitoring programme implementation. |
Provide funds for regular monitoring programme implementation. |
Provide funds for regular monitoring programme implementation. |
Provide funds for regular monitoring programme implementation. |
Provide funds for regular monitoring programme implementation. |
Provide funds for regular monitoring programme implementation. |
Provide funds for regular monitoring programme implementation. |
Provide funds for regular monitoring programme implementation. |
Provide funds for regular monitoring programme implementation. |
Provide funds for regular monitoring programme implementation. |
Related targets |
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Coverage of targets |
Adequate monitoring was in place by 2018 |
Adequate monitoring was in place by 2018 |
Adequate monitoring was in place by 2018 |
Adequate monitoring was in place by 2018 |
Adequate monitoring was in place by 2018 |
Adequate monitoring was in place by 2018 |
Adequate monitoring was in place by 2018 |
Adequate monitoring was in place by 2018 |
Adequate monitoring was in place by 2018 |
Adequate monitoring was in place by 2018 |
Adequate monitoring was in place by 2018 |
Adequate monitoring was in place by 2018 |
Adequate monitoring was in place by 2018 |
Related measures |
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Coverage of measures |
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Related monitoring programmes |
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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-D05-01 |
MADHR-D05-02 |
MADHR-D05-05 |
MADHR-D07-05 |
MADHR-D07-05 |
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 |
Nutrient levels - in water column |
Plankton blooms (biomass, frequency) |
Water column - chemical characteristics |
Water column - hydrological characteristics |
Water column - hydrological characteristics |
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 |
Modified from 2014 |
Modified from 2014 |
Old programme codes |
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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. |
Eutrophication in the Croatian part of the Adriatic Sea is mainly manifested at the local level. Areas under significant anthropogenic influence have unresolved urban waste water drainage system. Within reporting units are sampling stations for the parameters of the criteria within Descriptor 5. In the open sea area, the following stations are proposed: in the northern part Adriatic on the profile of the Po river delta - Rovinj (North Adriatic profile), the middle Adriatic Šibenik - Ortona (Jabuka profile), Split - Gargano (Palagruža profile), and the southern part of the Adriatic along the profile Dubrovnik - Bari (South Adriatic profile). In coastal area, locations have been proposed that are part of the regular monitoring of the state of the Adriatic according to the WFD
(2000/60 / EC) which include sites under anthropogenic pressure such as the Gulf of Rijeka and Bakar, the Port of Pula, the western coast of Istria, Bay of Šibenik, Bay of Kaštela and the mouth of the river Neretva. |
Eutrophication in the Croatian part of the Adriatic Sea is mainly manifested at the local level. Areas under significant anthropogenic influence have unresolved urban waste water drainage system. Within reporting units are sampling stations for the parameters of the criteria within Descriptor 5. In the open sea area, the following stations are proposed: in the northern part Adriatic on the profile of the Po river delta - Rovinj (North Adriatic profile), the middle Adriatic Šibenik - Ortona (Jabuka profile), Split - Gargano (Palagruža profile), and the southern part of the Adriatic along the profile Dubrovnik - Bari (South Adriatic profile). In coastal area, locations have been proposed that are part of the regular monitoring of the state of the Adriatic according to the WFD
(2000/60 / EC) which include sites under anthropogenic pressure such as the Gulf of Rijeka and Bakar, the Port of Pula, the western coast of Istria, Bay of Šibenik, Bay of Kaštela and the mouth of the river Neretva. |
Eutrophication in the Croatian part of the Adriatic Sea is mainly manifested at the local level. Areas under significant anthropogenic influence have unresolved urban waste water drainage system. Within reporting units are sampling stations for the parameters of the criteria within Descriptor 5. In the open sea area, the following stations are proposed: in the northern part Adriatic on the profile of the Po river delta - Rovinj (North Adriatic profile), the middle Adriatic Šibenik - Ortona (Jabuka profile), Split - Gargano (Palagruža profile), and the southern part of the Adriatic along the profile Dubrovnik - Bari (South Adriatic profile). In coastal area, locations have been proposed that are part of the regular monitoring of the state of the Adriatic according to the WFD
(2000/60 / EC) which include sites under anthropogenic pressure such as the Gulf of Rijeka and Bakar, the Port of Pula, the western coast of Istria, Bay of Šibenik, Bay of Kaštela and the mouth of the river Neretva. |
In the Adriatic Sea, spatially and timely significant changes in the temperature, salinity and transparency are key parameters that determine dynamics of ecosystems.In the Adriatic Sea, the observed significant changes in temperature and salinity, and hence the change of water masses and thermohaline circulation have been caused by sudden change of climate in the northern hemisphere. These changes can have permanent effects on the ecosystem by changing the composition and relationships in the food chain. The consequences of these changes are different along the coast and on the open seas because the hydrographic conditions are different. |
In the Adriatic Sea, spatially and timely significant changes in the temperature, salinity and transparency are key parameters that determine dynamics of ecosystems.In the Adriatic Sea, the observed significant changes in temperature and salinity, and hence the change of water masses and thermohaline circulation have been caused by sudden change of climate in the northern hemisphere. These changes can have permanent effects on the ecosystem by changing the composition and relationships in the food chain. The consequences of these changes are different along the coast and on the open seas because the hydrographic conditions are different. |
Monitoring purpose |
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Other policies and conventions |
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Regional cooperation - coordinating body |
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Regional cooperation - countries involved |
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Regional cooperation - implementation level |
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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 |
Temperatures, salinity and transparency will be measured in coastal waters four times a year, and more often if necessary, and certainly as much as predicted by Descriptor D5, along the Split - Gargano profile (Palagruža profile) measurements would be performed once a month (10 times a year) , and in the South Adriatic and on the Jabučki profile measurements would be carried out 4 times a year (seasonally). In the northern Adriatic at the eastern stations of the profile from Rovinj to the mouth of the river Po measurements should
perform at least 6 times a year, and more often if necessary, and certainly as much as provided by Descriptor D5. The amount of suspended matter will be sampled in the surface and bottom layers of the water column and at a depth of 10 m during field trips. |
Temperatures, salinity and transparency will be measured in coastal waters four times a year, and more often if necessary, and certainly as much as predicted by Descriptor D5, along the Split - Gargano profile (Palagruža profile) measurements would be performed once a month (10 times a year) , and in the South Adriatic and on the Jabučki profile measurements would be carried out 4 times a year (seasonally). In the northern Adriatic at the eastern stations of the profile from Rovinj to the mouth of the river Po measurements should
perform at least 6 times a year, and more often if necessary, and certainly as much as provided by Descriptor D5. The amount of suspended matter will be sampled in the surface and bottom layers of the water column and at a depth of 10 m during field trips. |
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Features |
Other pelagic habitats
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Coastal ecosystems
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Shelf ecosystems
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Coastal ecosystems
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Shelf ecosystems
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Coastal ecosystems
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Shelf ecosystems
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Eutrophication
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Eutrophication
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Eutrophication
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Eutrophication
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Eutrophication
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Hydrographical changes
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Elements |
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GES criteria |
D1C6 |
D4C1 |
D4C1 |
D4C2 |
D4C2 |
D4C4 |
D4C4 |
D5C3 |
D5C1 |
D5C2 |
D5C5 |
D5C4 |
D7C1 |
Parameters |
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Parameter Other |
Abundance/Biomass, species composition |
Species composition |
Species composition |
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Spatial scope |
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Marine reporting units |
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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 |
Monitoring frequency |
Other |
Other |
Other |
Other |
Other |
Other |
Other |
Other |
6-yearly |
6-yearly |
6-yearly |
Other |
Other |
Monitoring type |
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Monitoring method |
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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 |
Determination of nutrient concentrations in seawater samples (Grasshoff, K.: Methods of Seawater Analysis, Verlag Chemie, New York, 307 pp.)
Determination of the oxygen concentration in seawater samples (Grasshoff, K.: Methods of Seawater Analysis, Verlag Chemie, New York, 307 pp.)
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. (Ftp://baltazar.izor.hr) |
Strickland, J.D.H., Parsons, T.R., 1972. A practical handbook of seawater analysis. J. Fish. Res. Board Can. 167, 1–310.
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. (Ftp://baltazar.izor.hr) |
Determination of the oxygen concentration in seawater samples (Grasshoff, K.: Methods of Seawater Analysis, Verlag Chemie, New York, 307 pp.)
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. (Ftp://baltazar.izor.hr) |
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.
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As used in the reported monitoring method.
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As used in the reported monitoring method.
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As used in the reported monitoring method.
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As used in the reported monitoring method.
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As used in the reported monitoring method.
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As used in the reported monitoring method.
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As used in the reported monitoring method.
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As used in the reported monitoring method. QUASIMEME |
As used in the reported monitoring method. QUASIMEME - proficiency testing scheme. |
As used in the reported monitoring method.
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As used in the reported monitoring method.
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As used in the reported monitoring method.
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Data management |
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