Member State report / Art11 / 2020 / D7 / Baltic
| Report type | Member State report to Commission |
| MSFD Article | Art. 11 Monitoring programmes (and Art. 17 updates) |
| Report due | 2020-10-15 |
| GES Descriptor | D7 Hydrographical changes |
| Region/subregion | Baltic |
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Monitoring strategy description |
Die hydrografischen Basisparameter unterliegen einer hohen natürlichen Variabilität und können in der Regel nicht unmittelbar und großräumig durch menschliche Eingriffe beeinflusst werden. Um signifikante Veränderungen im System feststellen zu können, sind langfristige und großräumig angelegte Zeitreihen erforderlich um zu erkennen, ob und in welchem Maße sich Parameter in einer Art verändern, die nicht mehr durch die natürliche Variabilität zu erklären ist. Dem Monitoring liegen eine Vielzahl von Einzelmessaktivitäten zugrunde, die sich jedoch thematisch in einem Monitoringprogramm zusammenfassen lassen. Die dort genannten hydrographischen Basisparameter werden im Rahmen regelmäßiger Messfahrten sowie mit ortsfesten Dauermessstationen (MARNET) erfasst.
Ein risikobasierter Ansatz kommt für diesen Deskriptor nicht in Betracht.
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Die hydrografischen Basisparameter unterliegen einer hohen natürlichen Variabilität und können in der Regel nicht unmittelbar und großräumig durch menschliche Eingriffe beeinflusst werden. Um signifikante Veränderungen im System feststellen zu können, sind langfristige und großräumig angelegte Zeitreihen erforderlich um zu erkennen, ob und in welchem Maße sich Parameter in einer Art verändern, die nicht mehr durch die natürliche Variabilität zu erklären ist. Dem Monitoring liegen eine Vielzahl von Einzelmessaktivitäten zugrunde, die sich jedoch thematisch in einem Monitoringprogramm zusammenfassen lassen. Die dort genannten hydrographischen Basisparameter werden im Rahmen regelmäßiger Messfahrten sowie mit ortsfesten Dauermessstationen (MARNET) erfasst.
Ein risikobasierter Ansatz kommt für diesen Deskriptor nicht in Betracht.
|
Die hydrografischen Basisparameter unterliegen einer hohen natürlichen Variabilität und können in der Regel nicht unmittelbar und großräumig durch menschliche Eingriffe beeinflusst werden. Um signifikante Veränderungen im System feststellen zu können, sind langfristige und großräumig angelegte Zeitreihen erforderlich um zu erkennen, ob und in welchem Maße sich Parameter in einer Art verändern, die nicht mehr durch die natürliche Variabilität zu erklären ist. Dem Monitoring liegen eine Vielzahl von Einzelmessaktivitäten zugrunde, die sich jedoch thematisch in einem Monitoringprogramm zusammenfassen lassen. Die dort genannten hydrographischen Basisparameter werden im Rahmen regelmäßiger Messfahrten sowie mit ortsfesten Dauermessstationen (MARNET) erfasst.
Ein risikobasierter Ansatz kommt für diesen Deskriptor nicht in Betracht.
|
Die hydrografischen Basisparameter unterliegen einer hohen natürlichen Variabilität und können in der Regel nicht unmittelbar und großräumig durch menschliche Eingriffe beeinflusst werden. Um signifikante Veränderungen im System feststellen zu können, sind langfristige und großräumig angelegte Zeitreihen erforderlich um zu erkennen, ob und in welchem Maße sich Parameter in einer Art verändern, die nicht mehr durch die natürliche Variabilität zu erklären ist. Dem Monitoring liegen eine Vielzahl von Einzelmessaktivitäten zugrunde, die sich jedoch thematisch in einem Monitoringprogramm zusammenfassen lassen. Die dort genannten hydrographischen Basisparameter werden im Rahmen regelmäßiger Messfahrten sowie mit ortsfesten Dauermessstationen (MARNET) erfasst.
Ein risikobasierter Ansatz kommt für diesen Deskriptor nicht in Betracht.
|
Die hydrografischen Basisparameter unterliegen einer hohen natürlichen Variabilität und können in der Regel nicht unmittelbar und großräumig durch menschliche Eingriffe beeinflusst werden. Um signifikante Veränderungen im System feststellen zu können, sind langfristige und großräumig angelegte Zeitreihen erforderlich um zu erkennen, ob und in welchem Maße sich Parameter in einer Art verändern, die nicht mehr durch die natürliche Variabilität zu erklären ist. Dem Monitoring liegen eine Vielzahl von Einzelmessaktivitäten zugrunde, die sich jedoch thematisch in einem Monitoringprogramm zusammenfassen lassen. Die dort genannten hydrographischen Basisparameter werden im Rahmen regelmäßiger Messfahrten sowie mit ortsfesten Dauermessstationen (MARNET) erfasst.
Ein risikobasierter Ansatz kommt für diesen Deskriptor nicht in Betracht.
|
Die hydrografischen Basisparameter unterliegen einer hohen natürlichen Variabilität und können in der Regel nicht unmittelbar und großräumig durch menschliche Eingriffe beeinflusst werden. Um signifikante Veränderungen im System feststellen zu können, sind langfristige und großräumig angelegte Zeitreihen erforderlich um zu erkennen, ob und in welchem Maße sich Parameter in einer Art verändern, die nicht mehr durch die natürliche Variabilität zu erklären ist. Dem Monitoring liegen eine Vielzahl von Einzelmessaktivitäten zugrunde, die sich jedoch thematisch in einem Monitoringprogramm zusammenfassen lassen. Die dort genannten hydrographischen Basisparameter werden im Rahmen regelmäßiger Messfahrten sowie mit ortsfesten Dauermessstationen (MARNET) erfasst.
Ein risikobasierter Ansatz kommt für diesen Deskriptor nicht in Betracht.
|
Die hydrografischen Basisparameter unterliegen einer hohen natürlichen Variabilität und können in der Regel nicht unmittelbar und großräumig durch menschliche Eingriffe beeinflusst werden. Um signifikante Veränderungen im System feststellen zu können, sind langfristige und großräumig angelegte Zeitreihen erforderlich um zu erkennen, ob und in welchem Maße sich Parameter in einer Art verändern, die nicht mehr durch die natürliche Variabilität zu erklären ist. Dem Monitoring liegen eine Vielzahl von Einzelmessaktivitäten zugrunde, die sich jedoch thematisch in einem Monitoringprogramm zusammenfassen lassen. Die dort genannten hydrographischen Basisparameter werden im Rahmen regelmäßiger Messfahrten sowie mit ortsfesten Dauermessstationen (MARNET) erfasst.
Ein risikobasierter Ansatz kommt für diesen Deskriptor nicht in Betracht.
|
Die hydrografischen Basisparameter unterliegen einer hohen natürlichen Variabilität und können in der Regel nicht unmittelbar und großräumig durch menschliche Eingriffe beeinflusst werden. Um signifikante Veränderungen im System feststellen zu können, sind langfristige und großräumig angelegte Zeitreihen erforderlich um zu erkennen, ob und in welchem Maße sich Parameter in einer Art verändern, die nicht mehr durch die natürliche Variabilität zu erklären ist. Dem Monitoring liegen eine Vielzahl von Einzelmessaktivitäten zugrunde, die sich jedoch thematisch in einem Monitoringprogramm zusammenfassen lassen. Die dort genannten hydrographischen Basisparameter werden im Rahmen regelmäßiger Messfahrten sowie mit ortsfesten Dauermessstationen (MARNET) erfasst.
Ein risikobasierter Ansatz kommt für diesen Deskriptor nicht in Betracht.
|
Die hydrografischen Basisparameter unterliegen einer hohen natürlichen Variabilität und können in der Regel nicht unmittelbar und großräumig durch menschliche Eingriffe beeinflusst werden. Um signifikante Veränderungen im System feststellen zu können, sind langfristige und großräumig angelegte Zeitreihen erforderlich um zu erkennen, ob und in welchem Maße sich Parameter in einer Art verändern, die nicht mehr durch die natürliche Variabilität zu erklären ist. Dem Monitoring liegen eine Vielzahl von Einzelmessaktivitäten zugrunde, die sich jedoch thematisch in einem Monitoringprogramm zusammenfassen lassen. Die dort genannten hydrographischen Basisparameter werden im Rahmen regelmäßiger Messfahrten sowie mit ortsfesten Dauermessstationen (MARNET) erfasst.
Ein risikobasierter Ansatz kommt für diesen Deskriptor nicht in Betracht.
|
Die hydrografischen Basisparameter unterliegen einer hohen natürlichen Variabilität und können in der Regel nicht unmittelbar und großräumig durch menschliche Eingriffe beeinflusst werden. Um signifikante Veränderungen im System feststellen zu können, sind langfristige und großräumig angelegte Zeitreihen erforderlich um zu erkennen, ob und in welchem Maße sich Parameter in einer Art verändern, die nicht mehr durch die natürliche Variabilität zu erklären ist. Dem Monitoring liegen eine Vielzahl von Einzelmessaktivitäten zugrunde, die sich jedoch thematisch in einem Monitoringprogramm zusammenfassen lassen. Die dort genannten hydrographischen Basisparameter werden im Rahmen regelmäßiger Messfahrten sowie mit ortsfesten Dauermessstationen (MARNET) erfasst.
Ein risikobasierter Ansatz kommt für diesen Deskriptor nicht in Betracht.
|
Hydrografiske forhold beskrives ud fra vandområdets fysiske karaktertræk, hvilket inkluderer temperatur, saltholdighed, havstrømme og bølgepåvirkning. Disse karakteristika er dels bestemt af naturlige forhold så som vind, tidevand, lufttryk og klima, men er også påvirket af menneskelige aktiviteter som f.eks. havvindmølleparker, offshore olieinstallationer mv. Deskriptor 7 omhandler permanente ændringer (mindst 12 års varighed) i de hydrografiske forhold og har fokus på ændringer i vandsøjlen, ved havbunden og i de bentiske habitattyper. Formålet med overvågningen af hydrografiske ændringer, under deskriptor 7, er at overvåge om permanente ændring af de hydrografiske egenskaber påvirker de marine økosystemer i negativ retning.
Overvågningsprogrammet har til formål at sikre, at miljøtilstanden, som den er defineret i basisanalysen for Danmarks Havstrategi II, løbende kan følges i de danske havområder. Overvågningsprogrammet og basisanalyserne skal sammen danne grundlag for udarbejdelsen af de indsatsprogrammer, der skal sikre opfyldelse af miljømålene. Overvågningen vil endvidere føre til en vurdering af indsatsprogrammets foranstaltninger i forhold til opnåelse eller opretholdelse af god miljøtilstand. Overvågningsprogrammet er således tilrettelagt for at vurdere fremskridt i forhold til GES, miljømål og indsatser.
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Hydrografiske forhold beskrives ud fra vandområdets fysiske karaktertræk, hvilket inkluderer temperatur, saltholdighed, havstrømme og bølgepåvirkning. Disse karakteristika er dels bestemt af naturlige forhold så som vind, tidevand, lufttryk og klima, men er også påvirket af menneskelige aktiviteter som f.eks. havvindmølleparker, offshore olieinstallationer mv. Deskriptor 7 omhandler permanente ændringer (mindst 12 års varighed) i de hydrografiske forhold og har fokus på ændringer i vandsøjlen, ved havbunden og i de bentiske habitattyper. Formålet med overvågningen af hydrografiske ændringer, under deskriptor 7, er at overvåge om permanente ændring af de hydrografiske egenskaber påvirker de marine økosystemer i negativ retning.
Overvågningsprogrammet har til formål at sikre, at miljøtilstanden, som den er defineret i basisanalysen for Danmarks Havstrategi II, løbende kan følges i de danske havområder. Overvågningsprogrammet og basisanalyserne skal sammen danne grundlag for udarbejdelsen af de indsatsprogrammer, der skal sikre opfyldelse af miljømålene. Overvågningen vil endvidere føre til en vurdering af indsatsprogrammets foranstaltninger i forhold til opnåelse eller opretholdelse af god miljøtilstand. Overvågningsprogrammet er således tilrettelagt for at vurdere fremskridt i forhold til GES, miljømål og indsatser.
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The aim of the monitoring strategy “SD7 – Hydrographic conditions” is to collect data on the hydrographic conditions and their changes in the Estonian marine area. Based on the gathered data, the physical characteristics of marine ecosystems are described and the changes in the hydrographic conditions due to human-induced pressures and activities are assessed. The following parameters and characteristics are monitored: temperature and ice cover, salinity, waves and currents, upwelling, mixing, residence time, freshwater input, sea level, bathymetry, turbidity and transparency, seabed substrate and morphology. The monitoring programmes involved are: “Hydrographic characteristics”, Water column – physical characteristics”, “Ice cover”, “Seabed physical and chemical characteristics”, “Coasts”, and “Physical loss and disturbance”. Information on the uses and human activities causing the alteration of hydrographic conditions is collected in the programme “Marine and coastal activities”. |
The aim of the monitoring strategy “SD7 – Hydrographic conditions” is to collect data on the hydrographic conditions and their changes in the Estonian marine area. Based on the gathered data, the physical characteristics of marine ecosystems are described and the changes in the hydrographic conditions due to human-induced pressures and activities are assessed. The following parameters and characteristics are monitored: temperature and ice cover, salinity, waves and currents, upwelling, mixing, residence time, freshwater input, sea level, bathymetry, turbidity and transparency, seabed substrate and morphology. The monitoring programmes involved are: “Hydrographic characteristics”, Water column – physical characteristics”, “Ice cover”, “Seabed physical and chemical characteristics”, “Coasts”, and “Physical loss and disturbance”. Information on the uses and human activities causing the alteration of hydrographic conditions is collected in the programme “Marine and coastal activities”. |
The aim of the monitoring strategy “SD7 – Hydrographic conditions” is to collect data on the hydrographic conditions and their changes in the Estonian marine area. Based on the gathered data, the physical characteristics of marine ecosystems are described and the changes in the hydrographic conditions due to human-induced pressures and activities are assessed. The following parameters and characteristics are monitored: temperature and ice cover, salinity, waves and currents, upwelling, mixing, residence time, freshwater input, sea level, bathymetry, turbidity and transparency, seabed substrate and morphology. The monitoring programmes involved are: “Hydrographic characteristics”, Water column – physical characteristics”, “Ice cover”, “Seabed physical and chemical characteristics”, “Coasts”, and “Physical loss and disturbance”. Information on the uses and human activities causing the alteration of hydrographic conditions is collected in the programme “Marine and coastal activities”. |
The aim of the monitoring strategy “SD7 – Hydrographic conditions” is to collect data on the hydrographic conditions and their changes in the Estonian marine area. Based on the gathered data, the physical characteristics of marine ecosystems are described and the changes in the hydrographic conditions due to human-induced pressures and activities are assessed. The following parameters and characteristics are monitored: temperature and ice cover, salinity, waves and currents, upwelling, mixing, residence time, freshwater input, sea level, bathymetry, turbidity and transparency, seabed substrate and morphology. The monitoring programmes involved are: “Hydrographic characteristics”, Water column – physical characteristics”, “Ice cover”, “Seabed physical and chemical characteristics”, “Coasts”, and “Physical loss and disturbance”. Information on the uses and human activities causing the alteration of hydrographic conditions is collected in the programme “Marine and coastal activities”. |
The aim of the monitoring strategy “SD7 – Hydrographic conditions” is to collect data on the hydrographic conditions and their changes in the Estonian marine area. Based on the gathered data, the physical characteristics of marine ecosystems are described and the changes in the hydrographic conditions due to human-induced pressures and activities are assessed. The following parameters and characteristics are monitored: temperature and ice cover, salinity, waves and currents, upwelling, mixing, residence time, freshwater input, sea level, bathymetry, turbidity and transparency, seabed substrate and morphology. The monitoring programmes involved are: “Hydrographic characteristics”, Water column – physical characteristics”, “Ice cover”, “Seabed physical and chemical characteristics”, “Coasts”, and “Physical loss and disturbance”. Information on the uses and human activities causing the alteration of hydrographic conditions is collected in the programme “Marine and coastal activities”. |
The aim of the monitoring strategy “SD7 – Hydrographic conditions” is to collect data on the hydrographic conditions and their changes in the Estonian marine area. Based on the gathered data, the physical characteristics of marine ecosystems are described and the changes in the hydrographic conditions due to human-induced pressures and activities are assessed. The following parameters and characteristics are monitored: temperature and ice cover, salinity, waves and currents, upwelling, mixing, residence time, freshwater input, sea level, bathymetry, turbidity and transparency, seabed substrate and morphology. The monitoring programmes involved are: “Hydrographic characteristics”, Water column – physical characteristics”, “Ice cover”, “Seabed physical and chemical characteristics”, “Coasts”, and “Physical loss and disturbance”. Information on the uses and human activities causing the alteration of hydrographic conditions is collected in the programme “Marine and coastal activities”. |
The aim of the monitoring strategy “SD7 – Hydrographic conditions” is to collect data on the hydrographic conditions and their changes in the Estonian marine area. Based on the gathered data, the physical characteristics of marine ecosystems are described and the changes in the hydrographic conditions due to human-induced pressures and activities are assessed. The following parameters and characteristics are monitored: temperature and ice cover, salinity, waves and currents, upwelling, mixing, residence time, freshwater input, sea level, bathymetry, turbidity and transparency, seabed substrate and morphology. The monitoring programmes involved are: “Hydrographic characteristics”, Water column – physical characteristics”, “Ice cover”, “Seabed physical and chemical characteristics”, “Coasts”, and “Physical loss and disturbance”. Information on the uses and human activities causing the alteration of hydrographic conditions is collected in the programme “Marine and coastal activities”. |
Hydrographic changes refer to anthropogenic changes in water flow, salinity, wave formation and temperature. The programme monitors pressure factors that cause local hydrographic changes to the sea temperature and salinity, such as the heat load from nuclear and thermal power plants and its catchment area, as well as activities affecting water flows and salinity (e.g. impoundment, terrace). Some of the information collected also serves the Energy Programme, including underwater noise. The programme is divided into two sub-programmes: Significant changes in temperature conditions and significant changes in salinity conditions and flows.
The programme covers descriptors 7 (criteria D7C1 and D7C2) and 11 and pressure âchanges in hydrological conditionsâ.
The second pressure associated with this descriptor (due to permanent alteration of the seabed substrate or morphology or exploitation of the seabed substrate) is dealt with in the context of the seabed integrity (Descriptor 6).
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Hydrographic changes refer to anthropogenic changes in water flow, salinity, wave formation and temperature. The programme monitors pressure factors that cause local hydrographic changes to the sea temperature and salinity, such as the heat load from nuclear and thermal power plants and its catchment area, as well as activities affecting water flows and salinity (e.g. impoundment, terrace). Some of the information collected also serves the Energy Programme, including underwater noise. The programme is divided into two sub-programmes: Significant changes in temperature conditions and significant changes in salinity conditions and flows.
The programme covers descriptors 7 (criteria D7C1 and D7C2) and 11 and pressure âchanges in hydrological conditionsâ.
The second pressure associated with this descriptor (due to permanent alteration of the seabed substrate or morphology or exploitation of the seabed substrate) is dealt with in the context of the seabed integrity (Descriptor 6).
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Vadovaujantis Valstybine 2018-2023 m. aplinkos monitoringo programa, hidrografinių sąlygų parametrai (bangos, druskingumas, temperatūra, vandens skaidrumas, pH, deguonis ir susiję meteorologiniai reiškiniai) Lietuvos jūriniuose vandenyse tiriami: kasmet 18-19 stočių, 4-7 kartus per metus (dažnumas skiriasi skirtinguose rajonuose: BAL-LT-AA-01 ir BAL-LT-AA-02 – 4-7 kartai per metus; BAL-LT-AA-03 rajone tyrimai atliekami 1-4 kartus per metus). Kitose 4 tyrimų vietose tyrimai vykdomi ekstensyviai. Srovių parametrai (kryptis, greitis) matuojami pavasario ir vasaros tyrimų reisų metu 3 monitoringo vietose.
Duomenys naudojami pelaginėms buveinėms pagal D1, hidrografinėms sąlygoms pagal D7 vertinti.
Hidrografinių sąlygų erdvinis pakitimas stebimas lokaliose Lietuvos jūros priekrantės dalyse, pvz.: arti uostų hidrotechninių įrenginių, pvz., uosto molų. Šie pokyčiai yra sunkiai įvertinami dėl didelės hidrografinių sąlygų priklausomybės nuo meteorologinių ir kitų gamtinių reiškinių. Smėlio pylimas fiziniams parametrams (temperatūra, druskingumas, srovių greitis, apvelingas) jokio poveikio neturi, nors lokaliai gali sumažinti bangų poveiki krantų ardymui. Jūros rajono aplinkos būklės vertinimo metu buvo atlikta hidrografinių charakteristikų (temperatūra, druskingumas, deguonis, pH, vandens skaidrumas) 2006–2011 ir 2012–2017 m. lyginamoji analizė, kuri neparodė reikšmingų fizinių-cheminių sąlygų pokyčių pelaginėse ir dugno buveinėse.
Hidrografinių pokyčių vertinimas atliekamas modeliuojant hidrografinių sąlygų, pavyzdžiui, srovių, bangų, dugno šlyties įtempimas, temperatūros ir/ar druskingumo, pokyčių, galimai paveiktoje zonoje, mastą ir pokyčių intensyvumą. Tokios studijos atliekamos mokslinių studijų metu, atskirų ūkio subjektų veiklos poveikio vertinimo metu.
D7C1 ir D7C2 kriterijams regiono mastu yra pasiūlyti rodikliai, kurie ateityje turėtų būti vystomi regioniniu ir nacionaliniu mastu.
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Vadovaujantis Valstybine 2018-2023 m. aplinkos monitoringo programa, hidrografinių sąlygų parametrai (bangos, druskingumas, temperatūra, vandens skaidrumas, pH, deguonis ir susiję meteorologiniai reiškiniai) Lietuvos jūriniuose vandenyse tiriami: kasmet 18-19 stočių, 4-7 kartus per metus (dažnumas skiriasi skirtinguose rajonuose: BAL-LT-AA-01 ir BAL-LT-AA-02 – 4-7 kartai per metus; BAL-LT-AA-03 rajone tyrimai atliekami 1-4 kartus per metus). Kitose 4 tyrimų vietose tyrimai vykdomi ekstensyviai. Srovių parametrai (kryptis, greitis) matuojami pavasario ir vasaros tyrimų reisų metu 3 monitoringo vietose.
Duomenys naudojami pelaginėms buveinėms pagal D1, hidrografinėms sąlygoms pagal D7 vertinti.
Hidrografinių sąlygų erdvinis pakitimas stebimas lokaliose Lietuvos jūros priekrantės dalyse, pvz.: arti uostų hidrotechninių įrenginių, pvz., uosto molų. Šie pokyčiai yra sunkiai įvertinami dėl didelės hidrografinių sąlygų priklausomybės nuo meteorologinių ir kitų gamtinių reiškinių. Smėlio pylimas fiziniams parametrams (temperatūra, druskingumas, srovių greitis, apvelingas) jokio poveikio neturi, nors lokaliai gali sumažinti bangų poveiki krantų ardymui. Jūros rajono aplinkos būklės vertinimo metu buvo atlikta hidrografinių charakteristikų (temperatūra, druskingumas, deguonis, pH, vandens skaidrumas) 2006–2011 ir 2012–2017 m. lyginamoji analizė, kuri neparodė reikšmingų fizinių-cheminių sąlygų pokyčių pelaginėse ir dugno buveinėse.
Hidrografinių pokyčių vertinimas atliekamas modeliuojant hidrografinių sąlygų, pavyzdžiui, srovių, bangų, dugno šlyties įtempimas, temperatūros ir/ar druskingumo, pokyčių, galimai paveiktoje zonoje, mastą ir pokyčių intensyvumą. Tokios studijos atliekamos mokslinių studijų metu, atskirų ūkio subjektų veiklos poveikio vertinimo metu.
D7C1 ir D7C2 kriterijams regiono mastu yra pasiūlyti rodikliai, kurie ateityje turėtų būti vystomi regioniniu ir nacionaliniu mastu.
|
Vadovaujantis Valstybine 2018-2023 m. aplinkos monitoringo programa, hidrografinių sąlygų parametrai (bangos, druskingumas, temperatūra, vandens skaidrumas, pH, deguonis ir susiję meteorologiniai reiškiniai) Lietuvos jūriniuose vandenyse tiriami: kasmet 18-19 stočių, 4-7 kartus per metus (dažnumas skiriasi skirtinguose rajonuose: BAL-LT-AA-01 ir BAL-LT-AA-02 – 4-7 kartai per metus; BAL-LT-AA-03 rajone tyrimai atliekami 1-4 kartus per metus). Kitose 4 tyrimų vietose tyrimai vykdomi ekstensyviai. Srovių parametrai (kryptis, greitis) matuojami pavasario ir vasaros tyrimų reisų metu 3 monitoringo vietose.
Duomenys naudojami pelaginėms buveinėms pagal D1, hidrografinėms sąlygoms pagal D7 vertinti.
Hidrografinių sąlygų erdvinis pakitimas stebimas lokaliose Lietuvos jūros priekrantės dalyse, pvz.: arti uostų hidrotechninių įrenginių, pvz., uosto molų. Šie pokyčiai yra sunkiai įvertinami dėl didelės hidrografinių sąlygų priklausomybės nuo meteorologinių ir kitų gamtinių reiškinių. Smėlio pylimas fiziniams parametrams (temperatūra, druskingumas, srovių greitis, apvelingas) jokio poveikio neturi, nors lokaliai gali sumažinti bangų poveiki krantų ardymui. Jūros rajono aplinkos būklės vertinimo metu buvo atlikta hidrografinių charakteristikų (temperatūra, druskingumas, deguonis, pH, vandens skaidrumas) 2006–2011 ir 2012–2017 m. lyginamoji analizė, kuri neparodė reikšmingų fizinių-cheminių sąlygų pokyčių pelaginėse ir dugno buveinėse.
Hidrografinių pokyčių vertinimas atliekamas modeliuojant hidrografinių sąlygų, pavyzdžiui, srovių, bangų, dugno šlyties įtempimas, temperatūros ir/ar druskingumo, pokyčių, galimai paveiktoje zonoje, mastą ir pokyčių intensyvumą. Tokios studijos atliekamos mokslinių studijų metu, atskirų ūkio subjektų veiklos poveikio vertinimo metu.
D7C1 ir D7C2 kriterijams regiono mastu yra pasiūlyti rodikliai, kurie ateityje turėtų būti vystomi regioniniu ir nacionaliniu mastu.
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Vadovaujantis Valstybine 2018-2023 m. aplinkos monitoringo programa, hidrografinių sąlygų parametrai (bangos, druskingumas, temperatūra, vandens skaidrumas, pH, deguonis ir susiję meteorologiniai reiškiniai) Lietuvos jūriniuose vandenyse tiriami: kasmet 18-19 stočių, 4-7 kartus per metus (dažnumas skiriasi skirtinguose rajonuose: BAL-LT-AA-01 ir BAL-LT-AA-02 – 4-7 kartai per metus; BAL-LT-AA-03 rajone tyrimai atliekami 1-4 kartus per metus). Kitose 4 tyrimų vietose tyrimai vykdomi ekstensyviai. Srovių parametrai (kryptis, greitis) matuojami pavasario ir vasaros tyrimų reisų metu 3 monitoringo vietose.
Duomenys naudojami pelaginėms buveinėms pagal D1, hidrografinėms sąlygoms pagal D7 vertinti.
Hidrografinių sąlygų erdvinis pakitimas stebimas lokaliose Lietuvos jūros priekrantės dalyse, pvz.: arti uostų hidrotechninių įrenginių, pvz., uosto molų. Šie pokyčiai yra sunkiai įvertinami dėl didelės hidrografinių sąlygų priklausomybės nuo meteorologinių ir kitų gamtinių reiškinių. Smėlio pylimas fiziniams parametrams (temperatūra, druskingumas, srovių greitis, apvelingas) jokio poveikio neturi, nors lokaliai gali sumažinti bangų poveiki krantų ardymui. Jūros rajono aplinkos būklės vertinimo metu buvo atlikta hidrografinių charakteristikų (temperatūra, druskingumas, deguonis, pH, vandens skaidrumas) 2006–2011 ir 2012–2017 m. lyginamoji analizė, kuri neparodė reikšmingų fizinių-cheminių sąlygų pokyčių pelaginėse ir dugno buveinėse.
Hidrografinių pokyčių vertinimas atliekamas modeliuojant hidrografinių sąlygų, pavyzdžiui, srovių, bangų, dugno šlyties įtempimas, temperatūros ir/ar druskingumo, pokyčių, galimai paveiktoje zonoje, mastą ir pokyčių intensyvumą. Tokios studijos atliekamos mokslinių studijų metu, atskirų ūkio subjektų veiklos poveikio vertinimo metu.
D7C1 ir D7C2 kriterijams regiono mastu yra pasiūlyti rodikliai, kurie ateityje turėtų būti vystomi regioniniu ir nacionaliniu mastu.
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1. The monitoring relies on administrative data gathering, e.g., any new activity with a capacity to alter hydrographic conditions is scrutinized and extent of hydrographic changes estimated.
2. The monitoring relies on data/information generated by program LV-4.7.1., LV-4.6.5.1. and LV-4.6.5.2. |
1. The monitoring relies on administrative data gathering, e.g., any new activity with a capacity to alter hydrographic conditions is scrutinized and extent of hydrographic changes estimated.
2. The monitoring relies on data/information generated by program LV-4.7.1., LV-4.6.5.1. and LV-4.6.5.2. |
The goal of the strategy is to use information on human activities resulting in permanent alteration of hydrographical conditions gathered within strategy for Descriptor D6 and apply it along with information on water column physical characteristics to assess spatial extent and distribution of permanent alteration of hydrographical conditions to the seabed and water column. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. |
The goal of the strategy is to use information on human activities resulting in permanent alteration of hydrographical conditions gathered within strategy for Descriptor D6 and apply it along with information on water column physical characteristics to assess spatial extent and distribution of permanent alteration of hydrographical conditions to the seabed and water column. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. |
The goal of the strategy is to use information on human activities resulting in permanent alteration of hydrographical conditions gathered within strategy for Descriptor D6 and apply it along with information on water column physical characteristics to assess spatial extent and distribution of permanent alteration of hydrographical conditions to the seabed and water column. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. |
The goal of the strategy is to use information on human activities resulting in permanent alteration of hydrographical conditions gathered within strategy for Descriptor D6 and apply it along with information on water column physical characteristics to assess spatial extent and distribution of permanent alteration of hydrographical conditions to the seabed and water column. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. |
The goal of the strategy is to use information on human activities resulting in permanent alteration of hydrographical conditions gathered within strategy for Descriptor D6 and apply it along with information on water column physical characteristics to assess spatial extent and distribution of permanent alteration of hydrographical conditions to the seabed and water column. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. |
The goal of the strategy is to use information on human activities resulting in permanent alteration of hydrographical conditions gathered within strategy for Descriptor D6 and apply it along with information on water column physical characteristics to assess spatial extent and distribution of permanent alteration of hydrographical conditions to the seabed and water column. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. |
The goal of the strategy is to use information on human activities resulting in permanent alteration of hydrographical conditions gathered within strategy for Descriptor D6 and apply it along with information on water column physical characteristics to assess spatial extent and distribution of permanent alteration of hydrographical conditions to the seabed and water column. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. |
The goal of the strategy is to use information on human activities resulting in permanent alteration of hydrographical conditions gathered within strategy for Descriptor D6 and apply it along with information on water column physical characteristics to assess spatial extent and distribution of permanent alteration of hydrographical conditions to the seabed and water column. The strategy is compliant with Commission Directive (EU) 2017/845 of 17 May 2017 and criteria laid down in Commission Decision (EU) 2017/848 of 17 May 2017. |
"Hydrographic conditions include physical qualities of seawater such as temperature, ice conditions, salinity, depth conditions, currents, waves and turbidity, all of which are of great importance to marine ecosystems. Anthropogenic changes in hydrographic conditions can adversely affect ecosystems. For example, changes in salinity and temperature can affect the spread of nutrients and oxygenation in the marine environment. Plankton communities are very sensitive to changes in these conditions, with side effects also for organisms higher up in the food web.
In addition to changes in the hydrographic conditions as a result of physical impact, these can also be affected by climate change. The monitoring must therefore provide a basis for being able to distinguish these effects. In Sweden, descriptor 7 is assessed to achieve good status without a direct risk of deteriorating. Therefore, no indicators have been developed.
The monitoring however helps to insure that effects on hydrographic conditions dont occur, in accordance with the target D.3. This also apply to the measures linked to D7 since they are all preventive to make sure impacts will not occur.
" |
"Hydrographic conditions include physical qualities of seawater such as temperature, ice conditions, salinity, depth conditions, currents, waves and turbidity, all of which are of great importance to marine ecosystems. Anthropogenic changes in hydrographic conditions can adversely affect ecosystems. For example, changes in salinity and temperature can affect the spread of nutrients and oxygenation in the marine environment. Plankton communities are very sensitive to changes in these conditions, with side effects also for organisms higher up in the food web.
In addition to changes in the hydrographic conditions as a result of physical impact, these can also be affected by climate change. The monitoring must therefore provide a basis for being able to distinguish these effects. In Sweden, descriptor 7 is assessed to achieve good status without a direct risk of deteriorating. Therefore, no indicators have been developed.
The monitoring however helps to insure that effects on hydrographic conditions dont occur, in accordance with the target D.3. This also apply to the measures linked to D7 since they are all preventive to make sure impacts will not occur.
" |
"Hydrographic conditions include physical qualities of seawater such as temperature, ice conditions, salinity, depth conditions, currents, waves and turbidity, all of which are of great importance to marine ecosystems. Anthropogenic changes in hydrographic conditions can adversely affect ecosystems. For example, changes in salinity and temperature can affect the spread of nutrients and oxygenation in the marine environment. Plankton communities are very sensitive to changes in these conditions, with side effects also for organisms higher up in the food web.
In addition to changes in the hydrographic conditions as a result of physical impact, these can also be affected by climate change. The monitoring must therefore provide a basis for being able to distinguish these effects. In Sweden, descriptor 7 is assessed to achieve good status without a direct risk of deteriorating. Therefore, no indicators have been developed.
The monitoring however helps to insure that effects on hydrographic conditions dont occur, in accordance with the target D.3. This also apply to the measures linked to D7 since they are all preventive to make sure impacts will not occur.
" |
"Hydrographic conditions include physical qualities of seawater such as temperature, ice conditions, salinity, depth conditions, currents, waves and turbidity, all of which are of great importance to marine ecosystems. Anthropogenic changes in hydrographic conditions can adversely affect ecosystems. For example, changes in salinity and temperature can affect the spread of nutrients and oxygenation in the marine environment. Plankton communities are very sensitive to changes in these conditions, with side effects also for organisms higher up in the food web.
In addition to changes in the hydrographic conditions as a result of physical impact, these can also be affected by climate change. The monitoring must therefore provide a basis for being able to distinguish these effects. In Sweden, descriptor 7 is assessed to achieve good status without a direct risk of deteriorating. Therefore, no indicators have been developed.
The monitoring however helps to insure that effects on hydrographic conditions dont occur, in accordance with the target D.3. This also apply to the measures linked to D7 since they are all preventive to make sure impacts will not occur.
" |
"Hydrographic conditions include physical qualities of seawater such as temperature, ice conditions, salinity, depth conditions, currents, waves and turbidity, all of which are of great importance to marine ecosystems. Anthropogenic changes in hydrographic conditions can adversely affect ecosystems. For example, changes in salinity and temperature can affect the spread of nutrients and oxygenation in the marine environment. Plankton communities are very sensitive to changes in these conditions, with side effects also for organisms higher up in the food web.
In addition to changes in the hydrographic conditions as a result of physical impact, these can also be affected by climate change. The monitoring must therefore provide a basis for being able to distinguish these effects. In Sweden, descriptor 7 is assessed to achieve good status without a direct risk of deteriorating. Therefore, no indicators have been developed.
The monitoring however helps to insure that effects on hydrographic conditions dont occur, in accordance with the target D.3. This also apply to the measures linked to D7 since they are all preventive to make sure impacts will not occur.
" |
"Hydrographic conditions include physical qualities of seawater such as temperature, ice conditions, salinity, depth conditions, currents, waves and turbidity, all of which are of great importance to marine ecosystems. Anthropogenic changes in hydrographic conditions can adversely affect ecosystems. For example, changes in salinity and temperature can affect the spread of nutrients and oxygenation in the marine environment. Plankton communities are very sensitive to changes in these conditions, with side effects also for organisms higher up in the food web.
In addition to changes in the hydrographic conditions as a result of physical impact, these can also be affected by climate change. The monitoring must therefore provide a basis for being able to distinguish these effects. In Sweden, descriptor 7 is assessed to achieve good status without a direct risk of deteriorating. Therefore, no indicators have been developed.
The monitoring however helps to insure that effects on hydrographic conditions dont occur, in accordance with the target D.3. This also apply to the measures linked to D7 since they are all preventive to make sure impacts will not occur.
" |
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 is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
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 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 is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
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 |
Die zzt. bestehende Überwachung ist ausreichend. Da die Datengewinnung auf See eines großen logistischen und zeitlichen Aufwandes bedarf und zudem See- und Wetterbedingungen den Erfolg der Messungen und Messreihen beeinflussen, während die natürlichen Schwankungen auf sehr kurzen Zeitskalen stattfinden können, besteht naturgemäß das Risiko von Datenlücken. Bei den ortsfesten Dauermessungen können lokal Lücken auftreten, die durch technische Defekte, Beschädigungen durch Seeschifffahrt und Fischerei oder durch notwendige technische Kontrollen entstehen. Diese Lücken gefährden aber den Erfolg der generellen Überwachung nicht.
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Die zzt. bestehende Überwachung ist ausreichend. Da die Datengewinnung auf See eines großen logistischen und zeitlichen Aufwandes bedarf und zudem See- und Wetterbedingungen den Erfolg der Messungen und Messreihen beeinflussen, während die natürlichen Schwankungen auf sehr kurzen Zeitskalen stattfinden können, besteht naturgemäß das Risiko von Datenlücken. Bei den ortsfesten Dauermessungen können lokal Lücken auftreten, die durch technische Defekte, Beschädigungen durch Seeschifffahrt und Fischerei oder durch notwendige technische Kontrollen entstehen. Diese Lücken gefährden aber den Erfolg der generellen Überwachung nicht.
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Die zzt. bestehende Überwachung ist ausreichend. Da die Datengewinnung auf See eines großen logistischen und zeitlichen Aufwandes bedarf und zudem See- und Wetterbedingungen den Erfolg der Messungen und Messreihen beeinflussen, während die natürlichen Schwankungen auf sehr kurzen Zeitskalen stattfinden können, besteht naturgemäß das Risiko von Datenlücken. Bei den ortsfesten Dauermessungen können lokal Lücken auftreten, die durch technische Defekte, Beschädigungen durch Seeschifffahrt und Fischerei oder durch notwendige technische Kontrollen entstehen. Diese Lücken gefährden aber den Erfolg der generellen Überwachung nicht.
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Die zzt. bestehende Überwachung ist ausreichend. Da die Datengewinnung auf See eines großen logistischen und zeitlichen Aufwandes bedarf und zudem See- und Wetterbedingungen den Erfolg der Messungen und Messreihen beeinflussen, während die natürlichen Schwankungen auf sehr kurzen Zeitskalen stattfinden können, besteht naturgemäß das Risiko von Datenlücken. Bei den ortsfesten Dauermessungen können lokal Lücken auftreten, die durch technische Defekte, Beschädigungen durch Seeschifffahrt und Fischerei oder durch notwendige technische Kontrollen entstehen. Diese Lücken gefährden aber den Erfolg der generellen Überwachung nicht.
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Die zzt. bestehende Überwachung ist ausreichend. Da die Datengewinnung auf See eines großen logistischen und zeitlichen Aufwandes bedarf und zudem See- und Wetterbedingungen den Erfolg der Messungen und Messreihen beeinflussen, während die natürlichen Schwankungen auf sehr kurzen Zeitskalen stattfinden können, besteht naturgemäß das Risiko von Datenlücken. Bei den ortsfesten Dauermessungen können lokal Lücken auftreten, die durch technische Defekte, Beschädigungen durch Seeschifffahrt und Fischerei oder durch notwendige technische Kontrollen entstehen. Diese Lücken gefährden aber den Erfolg der generellen Überwachung nicht.
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Die zzt. bestehende Überwachung ist ausreichend. Da die Datengewinnung auf See eines großen logistischen und zeitlichen Aufwandes bedarf und zudem See- und Wetterbedingungen den Erfolg der Messungen und Messreihen beeinflussen, während die natürlichen Schwankungen auf sehr kurzen Zeitskalen stattfinden können, besteht naturgemäß das Risiko von Datenlücken. Bei den ortsfesten Dauermessungen können lokal Lücken auftreten, die durch technische Defekte, Beschädigungen durch Seeschifffahrt und Fischerei oder durch notwendige technische Kontrollen entstehen. Diese Lücken gefährden aber den Erfolg der generellen Überwachung nicht.
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Die zzt. bestehende Überwachung ist ausreichend. Da die Datengewinnung auf See eines großen logistischen und zeitlichen Aufwandes bedarf und zudem See- und Wetterbedingungen den Erfolg der Messungen und Messreihen beeinflussen, während die natürlichen Schwankungen auf sehr kurzen Zeitskalen stattfinden können, besteht naturgemäß das Risiko von Datenlücken. Bei den ortsfesten Dauermessungen können lokal Lücken auftreten, die durch technische Defekte, Beschädigungen durch Seeschifffahrt und Fischerei oder durch notwendige technische Kontrollen entstehen. Diese Lücken gefährden aber den Erfolg der generellen Überwachung nicht.
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Die zzt. bestehende Überwachung ist ausreichend. Da die Datengewinnung auf See eines großen logistischen und zeitlichen Aufwandes bedarf und zudem See- und Wetterbedingungen den Erfolg der Messungen und Messreihen beeinflussen, während die natürlichen Schwankungen auf sehr kurzen Zeitskalen stattfinden können, besteht naturgemäß das Risiko von Datenlücken. Bei den ortsfesten Dauermessungen können lokal Lücken auftreten, die durch technische Defekte, Beschädigungen durch Seeschifffahrt und Fischerei oder durch notwendige technische Kontrollen entstehen. Diese Lücken gefährden aber den Erfolg der generellen Überwachung nicht.
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Die zzt. bestehende Überwachung ist ausreichend. Da die Datengewinnung auf See eines großen logistischen und zeitlichen Aufwandes bedarf und zudem See- und Wetterbedingungen den Erfolg der Messungen und Messreihen beeinflussen, während die natürlichen Schwankungen auf sehr kurzen Zeitskalen stattfinden können, besteht naturgemäß das Risiko von Datenlücken. Bei den ortsfesten Dauermessungen können lokal Lücken auftreten, die durch technische Defekte, Beschädigungen durch Seeschifffahrt und Fischerei oder durch notwendige technische Kontrollen entstehen. Diese Lücken gefährden aber den Erfolg der generellen Überwachung nicht.
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Die zzt. bestehende Überwachung ist ausreichend. Da die Datengewinnung auf See eines großen logistischen und zeitlichen Aufwandes bedarf und zudem See- und Wetterbedingungen den Erfolg der Messungen und Messreihen beeinflussen, während die natürlichen Schwankungen auf sehr kurzen Zeitskalen stattfinden können, besteht naturgemäß das Risiko von Datenlücken. Bei den ortsfesten Dauermessungen können lokal Lücken auftreten, die durch technische Defekte, Beschädigungen durch Seeschifffahrt und Fischerei oder durch notwendige technische Kontrollen entstehen. Diese Lücken gefährden aber den Erfolg der generellen Überwachung nicht.
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Overvågningsprogrammet vurderes at være tilstrækkeligt. For at kunne sikre vidensdeling og en øget udvikling på området nedsætte der som beskrevet i programmet en tværministriel arbejdsgruppe som har til formål at fastlægge rammerne for, hvad der skal inkluderes og evt. måles af hydrografiske forhold, når der sker menneskelige aktiviteter på havet. Arbejdet i myndighedsgruppen skal sikre en løbende vidensdeling og koordinering for disse emner, samt udarbejdelse af fælles retningslinjer.
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Overvågningsprogrammet vurderes at være tilstrækkeligt. For at kunne sikre vidensdeling og en øget udvikling på området nedsætte der som beskrevet i programmet en tværministriel arbejdsgruppe som har til formål at fastlægge rammerne for, hvad der skal inkluderes og evt. måles af hydrografiske forhold, når der sker menneskelige aktiviteter på havet. Arbejdet i myndighedsgruppen skal sikre en løbende vidensdeling og koordinering for disse emner, samt udarbejdelse af fælles retningslinjer.
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There are no monitoring stations, where the vertical distribution of water temperature and salinity are continuously recorded. There are also no monitoring stations, where regular wave and current measurements are done. The measurements, which can be used to assess changes in hydrographic conditions, are mostly project-based. In order to describe hydrographic changes in the whole marine area and potentially affected areas, it is necessary to apply mathematical models, but there are no sufficient validation data at the moment, including local measurements.
There is a need for systematic monitoring of coastal areas to be carried out using an updated monitoring methodology. According to the updated methodology, the measurements should cover the entire coastal zone, i.e the part of the coastal slope and the beach. For geophysical surveys of the underwater coastal slope, bottom profiles and side-view sonar are used to determine the morphology of the seabed and the distribution and composition of sediments. The remote sensing methods could be taken into consideration for mapping the shallow coastal sea, pilot studies need to be carried out.
D7 indicators need to be developed and established. An indicator for assessing the spatial extent of disturbed infralittoral and circalittoral habitat types should be developed under D7C2. |
There are no monitoring stations, where the vertical distribution of water temperature and salinity are continuously recorded. There are also no monitoring stations, where regular wave and current measurements are done. The measurements, which can be used to assess changes in hydrographic conditions, are mostly project-based. In order to describe hydrographic changes in the whole marine area and potentially affected areas, it is necessary to apply mathematical models, but there are no sufficient validation data at the moment, including local measurements.
There is a need for systematic monitoring of coastal areas to be carried out using an updated monitoring methodology. According to the updated methodology, the measurements should cover the entire coastal zone, i.e the part of the coastal slope and the beach. For geophysical surveys of the underwater coastal slope, bottom profiles and side-view sonar are used to determine the morphology of the seabed and the distribution and composition of sediments. The remote sensing methods could be taken into consideration for mapping the shallow coastal sea, pilot studies need to be carried out.
D7 indicators need to be developed and established. An indicator for assessing the spatial extent of disturbed infralittoral and circalittoral habitat types should be developed under D7C2. |
There are no monitoring stations, where the vertical distribution of water temperature and salinity are continuously recorded. There are also no monitoring stations, where regular wave and current measurements are done. The measurements, which can be used to assess changes in hydrographic conditions, are mostly project-based. In order to describe hydrographic changes in the whole marine area and potentially affected areas, it is necessary to apply mathematical models, but there are no sufficient validation data at the moment, including local measurements.
There is a need for systematic monitoring of coastal areas to be carried out using an updated monitoring methodology. According to the updated methodology, the measurements should cover the entire coastal zone, i.e the part of the coastal slope and the beach. For geophysical surveys of the underwater coastal slope, bottom profiles and side-view sonar are used to determine the morphology of the seabed and the distribution and composition of sediments. The remote sensing methods could be taken into consideration for mapping the shallow coastal sea, pilot studies need to be carried out.
D7 indicators need to be developed and established. An indicator for assessing the spatial extent of disturbed infralittoral and circalittoral habitat types should be developed under D7C2. |
There are no monitoring stations, where the vertical distribution of water temperature and salinity are continuously recorded. There are also no monitoring stations, where regular wave and current measurements are done. The measurements, which can be used to assess changes in hydrographic conditions, are mostly project-based. In order to describe hydrographic changes in the whole marine area and potentially affected areas, it is necessary to apply mathematical models, but there are no sufficient validation data at the moment, including local measurements.
There is a need for systematic monitoring of coastal areas to be carried out using an updated monitoring methodology. According to the updated methodology, the measurements should cover the entire coastal zone, i.e the part of the coastal slope and the beach. For geophysical surveys of the underwater coastal slope, bottom profiles and side-view sonar are used to determine the morphology of the seabed and the distribution and composition of sediments. The remote sensing methods could be taken into consideration for mapping the shallow coastal sea, pilot studies need to be carried out.
D7 indicators need to be developed and established. An indicator for assessing the spatial extent of disturbed infralittoral and circalittoral habitat types should be developed under D7C2. |
There are no monitoring stations, where the vertical distribution of water temperature and salinity are continuously recorded. There are also no monitoring stations, where regular wave and current measurements are done. The measurements, which can be used to assess changes in hydrographic conditions, are mostly project-based. In order to describe hydrographic changes in the whole marine area and potentially affected areas, it is necessary to apply mathematical models, but there are no sufficient validation data at the moment, including local measurements.
There is a need for systematic monitoring of coastal areas to be carried out using an updated monitoring methodology. According to the updated methodology, the measurements should cover the entire coastal zone, i.e the part of the coastal slope and the beach. For geophysical surveys of the underwater coastal slope, bottom profiles and side-view sonar are used to determine the morphology of the seabed and the distribution and composition of sediments. The remote sensing methods could be taken into consideration for mapping the shallow coastal sea, pilot studies need to be carried out.
D7 indicators need to be developed and established. An indicator for assessing the spatial extent of disturbed infralittoral and circalittoral habitat types should be developed under D7C2. |
There are no monitoring stations, where the vertical distribution of water temperature and salinity are continuously recorded. There are also no monitoring stations, where regular wave and current measurements are done. The measurements, which can be used to assess changes in hydrographic conditions, are mostly project-based. In order to describe hydrographic changes in the whole marine area and potentially affected areas, it is necessary to apply mathematical models, but there are no sufficient validation data at the moment, including local measurements.
There is a need for systematic monitoring of coastal areas to be carried out using an updated monitoring methodology. According to the updated methodology, the measurements should cover the entire coastal zone, i.e the part of the coastal slope and the beach. For geophysical surveys of the underwater coastal slope, bottom profiles and side-view sonar are used to determine the morphology of the seabed and the distribution and composition of sediments. The remote sensing methods could be taken into consideration for mapping the shallow coastal sea, pilot studies need to be carried out.
D7 indicators need to be developed and established. An indicator for assessing the spatial extent of disturbed infralittoral and circalittoral habitat types should be developed under D7C2. |
There are no monitoring stations, where the vertical distribution of water temperature and salinity are continuously recorded. There are also no monitoring stations, where regular wave and current measurements are done. The measurements, which can be used to assess changes in hydrographic conditions, are mostly project-based. In order to describe hydrographic changes in the whole marine area and potentially affected areas, it is necessary to apply mathematical models, but there are no sufficient validation data at the moment, including local measurements.
There is a need for systematic monitoring of coastal areas to be carried out using an updated monitoring methodology. According to the updated methodology, the measurements should cover the entire coastal zone, i.e the part of the coastal slope and the beach. For geophysical surveys of the underwater coastal slope, bottom profiles and side-view sonar are used to determine the morphology of the seabed and the distribution and composition of sediments. The remote sensing methods could be taken into consideration for mapping the shallow coastal sea, pilot studies need to be carried out.
D7 indicators need to be developed and established. An indicator for assessing the spatial extent of disturbed infralittoral and circalittoral habitat types should be developed under D7C2. |
No gaps.
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No gaps.
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Jūros rajono aplinkos būklės vertinimo metu buvo atlikta hidrografinių charakteristikų (temperatūra, druskingumas, deguonis, pH, vandens skaidrumas) 2006–2011 ir 2012–2017 m. lyginamoji analizė, kuri neparodė reikšmingų fizinių-cheminių sąlygų pokyčių pelaginėse ir dugno buveinėse.
Hidrografinių pokyčių vertinimas atliekamas modeliuojant hidrografinių sąlygų, pavyzdžiui, srovių, bangų, dugno šlyties įtempimas, temperatūros ir/ar druskingumo, pokyčių, galimai paveiktoje zonoje, mastą ir pokyčių intensyvumą. Tokios studijos atliekamos mokslinių studijų metu, atskirų ūkio subjektų veiklos poveikio vertinimo metu.
D7C1 ir D7C2 kriterijams regiono mastu yra pasiūlyti rodikliai, kurie ateityje turėtų būti vystomi regioniniu ir nacionaliniu mastu.
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Jūros rajono aplinkos būklės vertinimo metu buvo atlikta hidrografinių charakteristikų (temperatūra, druskingumas, deguonis, pH, vandens skaidrumas) 2006–2011 ir 2012–2017 m. lyginamoji analizė, kuri neparodė reikšmingų fizinių-cheminių sąlygų pokyčių pelaginėse ir dugno buveinėse.
Hidrografinių pokyčių vertinimas atliekamas modeliuojant hidrografinių sąlygų, pavyzdžiui, srovių, bangų, dugno šlyties įtempimas, temperatūros ir/ar druskingumo, pokyčių, galimai paveiktoje zonoje, mastą ir pokyčių intensyvumą. Tokios studijos atliekamos mokslinių studijų metu, atskirų ūkio subjektų veiklos poveikio vertinimo metu.
D7C1 ir D7C2 kriterijams regiono mastu yra pasiūlyti rodikliai, kurie ateityje turėtų būti vystomi regioniniu ir nacionaliniu mastu.
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Jūros rajono aplinkos būklės vertinimo metu buvo atlikta hidrografinių charakteristikų (temperatūra, druskingumas, deguonis, pH, vandens skaidrumas) 2006–2011 ir 2012–2017 m. lyginamoji analizė, kuri neparodė reikšmingų fizinių-cheminių sąlygų pokyčių pelaginėse ir dugno buveinėse.
Hidrografinių pokyčių vertinimas atliekamas modeliuojant hidrografinių sąlygų, pavyzdžiui, srovių, bangų, dugno šlyties įtempimas, temperatūros ir/ar druskingumo, pokyčių, galimai paveiktoje zonoje, mastą ir pokyčių intensyvumą. Tokios studijos atliekamos mokslinių studijų metu, atskirų ūkio subjektų veiklos poveikio vertinimo metu.
D7C1 ir D7C2 kriterijams regiono mastu yra pasiūlyti rodikliai, kurie ateityje turėtų būti vystomi regioniniu ir nacionaliniu mastu.
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Jūros rajono aplinkos būklės vertinimo metu buvo atlikta hidrografinių charakteristikų (temperatūra, druskingumas, deguonis, pH, vandens skaidrumas) 2006–2011 ir 2012–2017 m. lyginamoji analizė, kuri neparodė reikšmingų fizinių-cheminių sąlygų pokyčių pelaginėse ir dugno buveinėse.
Hidrografinių pokyčių vertinimas atliekamas modeliuojant hidrografinių sąlygų, pavyzdžiui, srovių, bangų, dugno šlyties įtempimas, temperatūros ir/ar druskingumo, pokyčių, galimai paveiktoje zonoje, mastą ir pokyčių intensyvumą. Tokios studijos atliekamos mokslinių studijų metu, atskirų ūkio subjektų veiklos poveikio vertinimo metu.
D7C1 ir D7C2 kriterijams regiono mastu yra pasiūlyti rodikliai, kurie ateityje turėtų būti vystomi regioniniu ir nacionaliniu mastu.
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None
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None
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Not applicable
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Not applicable
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Not applicable
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Not applicable
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Not applicable
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Not applicable
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Not applicable
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Not applicable
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"Sweden has a built-in system that prevents hydrographic conditions from changing as a result of human activities, as new activities are reviewed in accordance with the Swedish Environmental Code - which requires environmental impact assessments as part of the review. An approved permit can also entail conditions to minimize the impact.
However, to make sure that the system is followed and that negative effects of water activities do not arise, data from the monitoring programmes can be used for qualitative assessment of the hydrographic conditions.
For WFD management, a follow-up of more local effects in the coastal environment as a result of human activities is needed. The monitoring programme for Physical disturbance and loss, when fully developed, is expected to provide a basis for assessment at both the local level and the large-scale level in offshore areas.
" |
"Sweden has a built-in system that prevents hydrographic conditions from changing as a result of human activities, as new activities are reviewed in accordance with the Swedish Environmental Code - which requires environmental impact assessments as part of the review. An approved permit can also entail conditions to minimize the impact.
However, to make sure that the system is followed and that negative effects of water activities do not arise, data from the monitoring programmes can be used for qualitative assessment of the hydrographic conditions.
For WFD management, a follow-up of more local effects in the coastal environment as a result of human activities is needed. The monitoring programme for Physical disturbance and loss, when fully developed, is expected to provide a basis for assessment at both the local level and the large-scale level in offshore areas.
" |
"Sweden has a built-in system that prevents hydrographic conditions from changing as a result of human activities, as new activities are reviewed in accordance with the Swedish Environmental Code - which requires environmental impact assessments as part of the review. An approved permit can also entail conditions to minimize the impact.
However, to make sure that the system is followed and that negative effects of water activities do not arise, data from the monitoring programmes can be used for qualitative assessment of the hydrographic conditions.
For WFD management, a follow-up of more local effects in the coastal environment as a result of human activities is needed. The monitoring programme for Physical disturbance and loss, when fully developed, is expected to provide a basis for assessment at both the local level and the large-scale level in offshore areas.
" |
"Sweden has a built-in system that prevents hydrographic conditions from changing as a result of human activities, as new activities are reviewed in accordance with the Swedish Environmental Code - which requires environmental impact assessments as part of the review. An approved permit can also entail conditions to minimize the impact.
However, to make sure that the system is followed and that negative effects of water activities do not arise, data from the monitoring programmes can be used for qualitative assessment of the hydrographic conditions.
For WFD management, a follow-up of more local effects in the coastal environment as a result of human activities is needed. The monitoring programme for Physical disturbance and loss, when fully developed, is expected to provide a basis for assessment at both the local level and the large-scale level in offshore areas.
" |
"Sweden has a built-in system that prevents hydrographic conditions from changing as a result of human activities, as new activities are reviewed in accordance with the Swedish Environmental Code - which requires environmental impact assessments as part of the review. An approved permit can also entail conditions to minimize the impact.
However, to make sure that the system is followed and that negative effects of water activities do not arise, data from the monitoring programmes can be used for qualitative assessment of the hydrographic conditions.
For WFD management, a follow-up of more local effects in the coastal environment as a result of human activities is needed. The monitoring programme for Physical disturbance and loss, when fully developed, is expected to provide a basis for assessment at both the local level and the large-scale level in offshore areas.
" |
"Sweden has a built-in system that prevents hydrographic conditions from changing as a result of human activities, as new activities are reviewed in accordance with the Swedish Environmental Code - which requires environmental impact assessments as part of the review. An approved permit can also entail conditions to minimize the impact.
However, to make sure that the system is followed and that negative effects of water activities do not arise, data from the monitoring programmes can be used for qualitative assessment of the hydrographic conditions.
For WFD management, a follow-up of more local effects in the coastal environment as a result of human activities is needed. The monitoring programme for Physical disturbance and loss, when fully developed, is expected to provide a basis for assessment at both the local level and the large-scale level in offshore areas.
" |
Related targets |
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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 |
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 will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
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 |
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Related measures |
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Coverage of measures |
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 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 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 |
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Related monitoring programmes |
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Programme code |
BALDE_MPr_098_MP_035 |
BALDE_MPr_098_MP_107 |
BALDE_MPr_098_MP_110 |
BALDE_MPr_098_MP_111 |
BALDE_MPr_098_MP_127 |
BALDE_MPr_099_MP_035 |
BALDE_MPr_099_MP_107 |
BALDE_MPr_099_MP_110 |
BALDE_MPr_099_MP_111 |
BALDE_MPr_099_MP_127 |
DK-D07-01 |
DK-D07-02 |
BALEE-D00-40_MarineAndCoastalActivities |
BALEE-D01040607-15_SeabedPhysChemGeol |
BALEE-D01040607-16_PhysDisturb |
BALEE-D0507-25_WaterColumnPhys |
BALEE-D07-26_PhysCharWaves |
BALEE-D07-27_Ice |
BALEE-D07-28_SeaCoast |
BALFI-D07-1 |
BALFI-D07-2 |
BALLT-D057_WaterPhys |
BALLT-D05_WaterChem |
BALLT-D07_HydroMeteo |
BALLT-D07_WavesCurrents |
LV-4.7.1. (D7C1) |
LV-4.7.2. (D7C2) |
PL-D06-01 |
PL-D06-01 |
PL-D06-02 |
PL-D06-02 |
PL-D06-03 |
PL-D06-03 |
PL-D07-01 |
PL-D07-01 |
SE-D1D2D7-outfalls |
SE-D1D4D6D7-benthab |
SE-D1D5D7-remote |
SE-D1D7-tempsalinity |
SE-D1D7-wavecurrents |
SE-D6D7-physicaldisturbance |
Programme name |
Wassersäule - hydrologische Merkmale (Wellenschlag, Strömung, Meeresspiegel): Sichttiefe (Ostsee) |
Wassersäule - hydrologische Merkmale (Wellenschlag, Strömung, Meeresspiegel): Marines Umweltmessnetz MARNET (Ostsee) |
Wassersäule - hydrologische Merkmale (Wellenschlag, Strömung, Meeresspiegel): Meeresoberflächentemperatur (SST) Karten (Ostsee) |
Wassersäule - hydrologische Merkmale (Wellenschlag, Strömung, Meeresspiegel): Eisdienst (Ostsee) |
Wassersäule - hydrologische Merkmale (Wellenschlag, Strömung, Meeresspiegel): Hydrographische Basisparameter (Hoheitsgewässer Ostsee) |
Wassersäule - physikalische Merkmale (Temperatur, Salzgehalt, Trübung, Lichtdurchlässigkeit): Sichttiefe (Ostsee) |
Wassersäule - physikalische Merkmale (Temperatur, Salzgehalt, Trübung, Lichtdurchlässigkeit): Marines Umweltmessnetz MARNET (Ostsee) |
Wassersäule - physikalische Merkmale (Temperatur, Salzgehalt, Trübung, Lichtdurchlässigkeit): Meeresoberflächentemperatur (SST) Karten (Ostsee) |
Wassersäule - physikalische Merkmale (Temperatur, Salzgehalt, Trübung, Lichtdurchlässigkeit): Eisdienst (Ostsee) |
Wassersäule - physikalische Merkmale (Temperatur, Salzgehalt, Trübung, Lichtdurchlässigkeit): Hydrographische Basisparameter (Hoheitsgewässer Ostsee) |
Activities extracting non-living resources (sand, gravel, dredging) |
Activities with permanent infrastructures (e.g. renewable energi, oil & gas, ports) or structural changes (e.g. coastal defences) |
Marine and coastal activities |
Seabed physical and chemical characteristics |
Physical loss and disturbance – from different human activities |
Water column – physical characteristics |
Hydrological characteristics |
Ice cover |
Coasts |
Permanent changes in temperature |
Permanent changes in salinity and hydrography |
BALLT-D057_WaterPhys |
BALLT-D05_WaterChem |
BALLT-D07_HydroMeteo |
BALLT-D07_WavesCurrents |
Water column and seabed extent and spatial distribution of permanent changes of hydrological characteristics caused by physical losses of natural seabed |
Seabed habitats spatial distribution and extent of affected areas |
Seabed habitats - community characteristics |
Seabed habitats - community characteristics |
Benthic species – abundance or biomass |
Benthic species – abundance or biomass |
Seabed habitats - physical and chemical characteristics |
Seabed habitats - physical and chemical characteristics |
Water column - physical characteristics |
Water column - physical characteristics |
Effects of outfalls from power stations |
Benthic habitats |
Remote sensing of the water column |
Water column – physical characteristics (temp, ice cover, salinity) |
Water column – hydrological characteristics (currents, wave action, sea-level) |
Physical disturbance and loss |
Update type |
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 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Same programme as in 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 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
New programme |
New programme |
New programme |
New programme |
New programme |
New programme |
New programme |
New programme |
New programme |
New programme |
Modified from 2014 |
New programme |
New programme |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Old programme codes |
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Programme description |
Das Monitoring-Programm besteht aus den/dem folgenden Messprogramm/en (=MP): || BALDE_MP_35 || Sichttiefe (Ostsee) || -- MISSING DATA ID: 98--
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Das Monitoring-Programm besteht aus den/dem folgenden Messprogramm/en (=MP): || BALDE_MP_107 || Marines Umweltmessnetz MARNET (Ostsee) || -- MISSING DATA ID: 98--
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Das Monitoring-Programm besteht aus den/dem folgenden Messprogramm/en (=MP): || BALDE_MP_110 || Meeresoberflächentemperatur (SST) Karten (Ostsee) || -- MISSING DATA ID: 98--
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Das Monitoring-Programm besteht aus den/dem folgenden Messprogramm/en (=MP): || BALDE_MP_111 || Eisdienst (Ostsee) || -- MISSING DATA ID: 98--
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Das Monitoring-Programm besteht aus den/dem folgenden Messprogramm/en (=MP): || BALDE_MP_127 || Hydrographische Basisparameter (Hoheitsgewässer Ostsee) || -- MISSING DATA ID: 98--
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Das Monitoring-Programm besteht aus den/dem folgenden Messprogramm/en (=MP): || BALDE_MP_35 || Sichttiefe (Ostsee) || Um den physikalischen Zustand der deutschen Küsten-, Hoheits- und AWZ-Gewässer der Ostsee und die Ursachen potentieller Veränderungen gemäß den Verpflichtungen aus WRRL, MSRL, HELCOM und dem BLMP/BLANO ("Bund/Länder-Messprogramm" / "Bund/Länder-Arbeitsgemeinschaft Nord- und Ostsee") bewerten zu können, werden regelmäßige Messfahrten zur Datenerhebung durchgeführt. Das Gebiet für die In-Situ-Messungen wird durch die Erreichbarkeit für kleinere Messschiffe limitiert. Die räumliche Abdeckung der Satelliten bestimmt die Gebiete, in denen relevante hydrographische Parameter (z.B. SST, Sichttiefe, Trübung) regelmäßig durch Fernerkundung erfasst werden können.
Je nach Verfügbarkeit von Schiffen werden mehrmals im Jahr die Ostseegewässer durch In-Situ-Messungen beprobt. Ferner werden permanente Messungen auf den ortsfesten Stationen des MARNET durchgeführt. Bei Eisbildung erstellt der Eisdienst des BSH tägliche Eisberichte.
Aufgrund der großen thematischen Redundanz wurden die Monitoringprogramme (frühere Sub-Programme) BALDE_Sub_099 und 098 zusammengefasst, da es sich inhaltlich und hinsichtlich der Durchführung um einen nicht zu trennenden thematischen Komplex handelt.
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Das Monitoring-Programm besteht aus den/dem folgenden Messprogramm/en (=MP): || BALDE_MP_107 || Marines Umweltmessnetz MARNET (Ostsee) || Um den physikalischen Zustand der deutschen Küsten-, Hoheits- und AWZ-Gewässer der Ostsee und die Ursachen potentieller Veränderungen gemäß den Verpflichtungen aus WRRL, MSRL, HELCOM und dem BLMP/BLANO ("Bund/Länder-Messprogramm" / "Bund/Länder-Arbeitsgemeinschaft Nord- und Ostsee") bewerten zu können, werden regelmäßige Messfahrten zur Datenerhebung durchgeführt. Das Gebiet für die In-Situ-Messungen wird durch die Erreichbarkeit für kleinere Messschiffe limitiert. Die räumliche Abdeckung der Satelliten bestimmt die Gebiete, in denen relevante hydrographische Parameter (z.B. SST, Sichttiefe, Trübung) regelmäßig durch Fernerkundung erfasst werden können.
Je nach Verfügbarkeit von Schiffen werden mehrmals im Jahr die Ostseegewässer durch In-Situ-Messungen beprobt. Ferner werden permanente Messungen auf den ortsfesten Stationen des MARNET durchgeführt. Bei Eisbildung erstellt der Eisdienst des BSH tägliche Eisberichte.
Aufgrund der großen thematischen Redundanz wurden die Monitoringprogramme (frühere Sub-Programme) BALDE_Sub_099 und 098 zusammengefasst, da es sich inhaltlich und hinsichtlich der Durchführung um einen nicht zu trennenden thematischen Komplex handelt.
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Das Monitoring-Programm besteht aus den/dem folgenden Messprogramm/en (=MP): || BALDE_MP_110 || Meeresoberflächentemperatur (SST) Karten (Ostsee) || Um den physikalischen Zustand der deutschen Küsten-, Hoheits- und AWZ-Gewässer der Ostsee und die Ursachen potentieller Veränderungen gemäß den Verpflichtungen aus WRRL, MSRL, HELCOM und dem BLMP/BLANO ("Bund/Länder-Messprogramm" / "Bund/Länder-Arbeitsgemeinschaft Nord- und Ostsee") bewerten zu können, werden regelmäßige Messfahrten zur Datenerhebung durchgeführt. Das Gebiet für die In-Situ-Messungen wird durch die Erreichbarkeit für kleinere Messschiffe limitiert. Die räumliche Abdeckung der Satelliten bestimmt die Gebiete, in denen relevante hydrographische Parameter (z.B. SST, Sichttiefe, Trübung) regelmäßig durch Fernerkundung erfasst werden können.
Je nach Verfügbarkeit von Schiffen werden mehrmals im Jahr die Ostseegewässer durch In-Situ-Messungen beprobt. Ferner werden permanente Messungen auf den ortsfesten Stationen des MARNET durchgeführt. Bei Eisbildung erstellt der Eisdienst des BSH tägliche Eisberichte.
Aufgrund der großen thematischen Redundanz wurden die Monitoringprogramme (frühere Sub-Programme) BALDE_Sub_099 und 098 zusammengefasst, da es sich inhaltlich und hinsichtlich der Durchführung um einen nicht zu trennenden thematischen Komplex handelt.
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Das Monitoring-Programm besteht aus den/dem folgenden Messprogramm/en (=MP): || BALDE_MP_111 || Eisdienst (Ostsee) || Um den physikalischen Zustand der deutschen Küsten-, Hoheits- und AWZ-Gewässer der Ostsee und die Ursachen potentieller Veränderungen gemäß den Verpflichtungen aus WRRL, MSRL, HELCOM und dem BLMP/BLANO ("Bund/Länder-Messprogramm" / "Bund/Länder-Arbeitsgemeinschaft Nord- und Ostsee") bewerten zu können, werden regelmäßige Messfahrten zur Datenerhebung durchgeführt. Das Gebiet für die In-Situ-Messungen wird durch die Erreichbarkeit für kleinere Messschiffe limitiert. Die räumliche Abdeckung der Satelliten bestimmt die Gebiete, in denen relevante hydrographische Parameter (z.B. SST, Sichttiefe, Trübung) regelmäßig durch Fernerkundung erfasst werden können.
Je nach Verfügbarkeit von Schiffen werden mehrmals im Jahr die Ostseegewässer durch In-Situ-Messungen beprobt. Ferner werden permanente Messungen auf den ortsfesten Stationen des MARNET durchgeführt. Bei Eisbildung erstellt der Eisdienst des BSH tägliche Eisberichte.
Aufgrund der großen thematischen Redundanz wurden die Monitoringprogramme (frühere Sub-Programme) BALDE_Sub_099 und 098 zusammengefasst, da es sich inhaltlich und hinsichtlich der Durchführung um einen nicht zu trennenden thematischen Komplex handelt.
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Das Monitoring-Programm besteht aus den/dem folgenden Messprogramm/en (=MP): || BALDE_MP_127 || Hydrographische Basisparameter (Hoheitsgewässer Ostsee) || Um den physikalischen Zustand der deutschen Küsten-, Hoheits- und AWZ-Gewässer der Ostsee und die Ursachen potentieller Veränderungen gemäß den Verpflichtungen aus WRRL, MSRL, HELCOM und dem BLMP/BLANO ("Bund/Länder-Messprogramm" / "Bund/Länder-Arbeitsgemeinschaft Nord- und Ostsee") bewerten zu können, werden regelmäßige Messfahrten zur Datenerhebung durchgeführt. Das Gebiet für die In-Situ-Messungen wird durch die Erreichbarkeit für kleinere Messschiffe limitiert. Die räumliche Abdeckung der Satelliten bestimmt die Gebiete, in denen relevante hydrographische Parameter (z.B. SST, Sichttiefe, Trübung) regelmäßig durch Fernerkundung erfasst werden können.
Je nach Verfügbarkeit von Schiffen werden mehrmals im Jahr die Ostseegewässer durch In-Situ-Messungen beprobt. Ferner werden permanente Messungen auf den ortsfesten Stationen des MARNET durchgeführt. Bei Eisbildung erstellt der Eisdienst des BSH tägliche Eisberichte.
Aufgrund der großen thematischen Redundanz wurden die Monitoringprogramme (frühere Sub-Programme) BALDE_Sub_099 und 098 zusammengefasst, da es sich inhaltlich und hinsichtlich der Durchführung um einen nicht zu trennenden thematischen Komplex handelt.
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Ifølge EU kommissions afgørelse 2017/848 [1] skal overvågningen under deskriptor 7 fokusere på ændringer forbundet med infrastrukturudvikling, enten på kysten eller offshore. Kortlægningen af hydrografiske ændringer er præget af, at der ikke findes fælles standarder for afgrænsning af de forskellige presfaktorers påvirkning på de hydrografiske forhold. I den kommende overvågningsperiode vil der blive nedsat en tværministeriel arbejdsgruppe, som kan være med til at fastlægge rammerne for, hvad der skal inkluderes og evt. måles af hydrografiske forhold, når der sker menneskelige aktiviteter på havet. Arbejdet i myndighedsgruppen skal sikre en løbende vidensdeling og koordinering for disse emner, samt udarbejdelse af fælles retningslinjer.
Derudover vil der i den kommende overvågningsperiode blive gennemført et projekt, der skal redegøre for ændringer i hydrografiske forhold i perioden fra 2017 til 2023, ved at undersøge:
• Den geografiske udstrækning og fordeling af ændringer i de hydrografiske forhold på havbunden og i vandsøjlen, som især er forbundet med fysiske tab af den naturlige havbund (D7C1).
• Den geografiske udstrækning af havbundens habitattyper, der er påvirket negativt som følge af permanent ændring af de hydrografiske forhold (D7C2).
Projektet vil tage udgangspunkt i de offentliggjorte VVM-redegørelser for større anlægsopgaver, hvor anlægsperioden er påbegyndt, i gang eller afsluttet i 2017-2023. Endvidere skal større anlægsopga-ver, der er planlagt eller vedtaget i perioden (dvs. VVM-redegørelser er sendt til høring eller projektet har opnået tilladelse i perioden), inddrages. De opnåede resultater skal sammenlignes med et lig-nende projekt gennemført for perioden 1983-2016.
Herefter igangsættes et andet projekt, der kan klarlægge og formulere, hvad og hvor meget hydrografiske forhold ændres grundet menneskelige aktiviteter. Udførelse og omfang er ikke afklaret endnu.
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Ifølge EU kommissions afgørelse 2017/848 [1] skal overvågningen under deskriptor 7 fokusere på ændringer forbundet med infrastrukturudvikling, enten på kysten eller offshore. Kortlægningen af hydrografiske ændringer er præget af, at der ikke findes fælles standarder for afgrænsning af de forskellige presfaktorers påvirkning på de hydrografiske forhold. I den kommende overvågningsperiode vil der blive nedsat en tværministeriel arbejdsgruppe, som kan være med til at fastlægge rammerne for, hvad der skal inkluderes og evt. måles af hydrografiske forhold, når der sker menneskelige aktiviteter på havet. Arbejdet i myndighedsgruppen skal sikre en løbende vidensdeling og koordinering for disse emner, samt udarbejdelse af fælles retningslinjer.
Derudover vil der i den kommende overvågningsperiode blive gennemført et projekt, der skal redegøre for ændringer i hydrografiske forhold i perioden fra 2017 til 2023, ved at undersøge:
• Den geografiske udstrækning og fordeling af ændringer i de hydrografiske forhold på havbunden og i vandsøjlen, som især er forbundet med fysiske tab af den naturlige havbund (D7C1).
• Den geografiske udstrækning af havbundens habitattyper, der er påvirket negativt som følge af permanent ændring af de hydrografiske forhold (D7C2).
Projektet vil tage udgangspunkt i de offentliggjorte VVM-redegørelser for større anlægsopgaver, hvor anlægsperioden er påbegyndt, i gang eller afsluttet i 2017-2023. Endvidere skal større anlægsopga-ver, der er planlagt eller vedtaget i perioden (dvs. VVM-redegørelser er sendt til høring eller projektet har opnået tilladelse i perioden), inddrages. De opnåede resultater skal sammenlignes med et lig-nende projekt gennemført for perioden 1983-2016.
Herefter igangsættes et andet projekt, der kan klarlægge og formulere, hvad og hvor meget hydrografiske forhold ændres grundet menneskelige aktiviteter. Udførelse og omfang er ikke afklaret endnu.
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The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development.
The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism).
The programme is the further development of the programme presented in 2014. The code of the programme also changed. |
The aim of the programme is to collect data on the physical and chemical characteristics of the seabed, such as bathymetry, seabed substrate and morphology, as well as organic matter content in the sediments. Hydrographic surveying is the task of the Hydrographic service and data are made available via Maritime Administration. The seabed mapping process is continuous and the whole sea area is planned to be covered by 2030. Data on the seabed substrate and morphology is collected by project-based activities, and the distributions of seabed substrate and morphology in the Estonian waters are available at the Geological Survey and Land Board as well via the EMODnet Geology portal. Organic matter content is monitored at the macrozoobenthos stations and transects in the frames of the national environmental monitoring programme open sea monitoring programme. Data on organic matter are reported every year by 1 March and are made available via environmental database KESE.
Monitoring is not HELCOM regionally coordinated, partly coordinated in collaboration with EMODnet Geology.
The programme corresponds to the following monitoring programmes in the indicative list: Seabed habitats – physical and chemical characteristics. |
The aim of the programme is to assess physical loss and disturbance of seabed caused by human activities. It provides data to monitoring strategies „ SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats“ and “SD7 – Changes in hydrographic conditions”. The programme is related to GES Descriptor D6, Criteria D6C1, D6C2, D6C3 and D6C4; Descriptor D7, Criteria D7C1 and D7C2. Data are gathered through permitting database KOTKAS as well as project-based research. The program data collection is regionally coordinated (data delivered separately by each country) via HELCOM.
There have been some updates, changes in programme structure and indicator developments since 2014.
The programme corresponds to the following monitoring programmes in the indicative list: Physical loss - distribution and extent (from e.g. infrastructure, coastal protection); Physical disturbance - from dredging and disposal of dredged material; Physical disturbance - from sand and gravel extraction. |
The aim of the programme is to monitor physical characteristics (water temperature, salinity, transparency) in the water column to assess the indirect effects of eutrophication and describe the physical conditions of the pelagic habitats. It provides data to monitoring strategy “SD5 – Eutrophication” and is related to GES Descriptor D5, Criterion D5C4. Data are gathered to assess the environmental status in the coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM sub-divisions). Monitoring is conducted yearly or at least once in six years with a frequency of 6 to 12 times a year at the designated monitoring stations (at least three stations in each coastal water body and 18 in the Estonian off-shore areas). The program data collection is regionally coordinated via HELCOM and the HELCOM guidelines are followed, but data are delivered separately by each country (except CMEMS/BOOS monitoring with joint data collection). The data are yearly reported to the environmental monitoring database KESE (by 1 March), HELCOM ICES database (by 1 May) and online data delivery into CMEMS/BOOS databases.
The programme is essentially the same as in 2014, only minor changes in some monitoring stations and frequencies were undertaken.
The programme corresponds to the following monitoring programmes in the indicative list: Water column – physical characteristics. |
The aim of the programme is to monitor hydrological characteristics in the marine areas to describe the physical/hydrological conditions of the benthic and pelagic habitats. Data on sea level, waves, and currents are acquired at sea, mostly using autonomous devices and numerical models. Both, coastal water bodies and the off-shore sub-basins of the Baltic Sea (HELCOM division) are monitored. Monitoring is conducted continuously. The program is regionally coordinated via BOOS and Baltic CMEMS (joint data collection). The data are delivered near real-time.
The programme is essentially the same as in 2014, only minor changes in some monitoring stations and frequencies were undertaken.
The programme corresponds to the following monitoring programmes in the indicative list: Water column – hydrological characteristics. |
The aim of the programme is to monitor characteristics of the ice cover. Data are collected by visual observations and remote sensing. Both, coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM sub-divisions) are monitored. Monitoring is conducted continuously during winter. The program is regionally coordinated (joint data collection) via Baltic Sea Ice Services and a common product is produced. The data are delivered daily.
The programme corresponds to the following monitoring programmes in the indicative list: Ice cover. |
The aim of the programme is to collect data on coastal morphology and dynamics (including erosion processes). It assesses changes of coasts (incl erosion, etc.) due to natural processes (storms, wave activity) and human-induced pressures. The coastal profile on-shore and in near-shore water, as well as the characteristics of the substrate, are recorded. Data on the substrate and morphology are collected yearly at the selected monitoring sites along the Estonian coasts by the Geological Survey. Data are reported every year by 1 March and are made available via national environmental database KESE. |
Surveillance monitoring of the outflow water from industry and power plants as well as human activities causing changes in currents, water flows, salinity, wave regime and temperature. |
Monitoring of changes in salinity and water flow is carried out by surveillance monitoring by industry and power plants as well as impact assessments of various construction projects at sea. |
Valstybinis aplinkos monitoringas vykdomas pagal Valstybinę 2018-2023 m. programą. Monitoringo programos dalis BALLT-D057_WaterPhys apima vandens temperatūros, druskingumo, skaidrumo matavimus Baltijos jūros tyrimų rajonuose BAL-LT-AA-01; BAL-LT-AA-02; BAL-LT-AA-03. Monitoringas vykdomas mokslinių tyrimų laivu „Vėjūnas“. Duomenys renkami viso 23 monitoringo vietose (19 vietų intensyviai, 4 vietose ekstensyviai). Tyrimai vykdomi vidutiniškai 4-7 kartus per metus (dažnumas skiriasi skirtinguose rajonuose: BAL-LT-AA-01 ir BAL-LT-AA-02 – 4-7 kartai per metus; BAL-LT-AA-03 rajone tyrimai atliekami 1-4 kartus per metus).
Duomenys naudojami pelaginėms buveinėms pagal D1, hidrografinėms sąlygoms pagal D7 vertinti.
Renkamų duomenų pagrindu vertinami D5 rodikliai: 1) Vidutinis vandens skaidrumas vasarą (BAL-LT-AA-01 ir BAL-LT-AA-03); 2) Vidutinis metinis vandens skaidrumas (BAL-LT-AA-03).
Duomenys kaupiami Lietuvos aplinkos apsaugos agentūros duomenų bazėje. Kasmet teikiami ICES, WISE.
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Valstybinis aplinkos monitoringas vykdomas pagal Valstybinę 2018-2023 m. programą. Monitoringo programos dalis BALLT-D05_WaterChem apima ištirpusio deguonies, pH, sieros vandenilio (giluminiame jūros rajone) matavimus Baltijos jūros tyrimų rajonuose BAL-LT-AA-01; BAL-LT-AA-02; BAL-LT-AA-03. Monitoringas vykdomas mokslinių tyrimų laivu „Vėjūnas“. Parametrai matuojami kasmet, 18 tyrimų vietų, vidutiniškai 4-7 kartus per metus (dažnumas skiriasi skirtinguose rajonuose: BAL-LT-AA-01 ir BAL-LT-AA-02 – 4-7 kartai per metus; BAL-LT-AA-03 rajone tyrimai atliekami 1-4 kartus per metus). Kitose 4 tyrimų vietose tyrimai vykdomi ekstensyviai.
Duomenys naudojami vertinant pelagines buveines pagal D1, eutrofikacijai pagal D5, hidrografinėms sąlygoms pagal D7 vertinti.
Duomenys kaupiami Lietuvos aplinkos apsaugos agentūros duomenų bazėje.
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Valstybinis aplinkos monitoringas vykdomas pagal Valstybinę 2018-2023 m. programą. Monitoringo programos dalis BALLT-D07_HydroMeteo apima hidrometeorologinių parametrų matavimus Baltijos jūros tyrimų rajonuose BAL-LT-AA-01; BAL-LT-AA-02; BAL-LT-AA-03. Matuojami parametrai: oro temperatūra, vėjo kryptis, greitis, atmosferos slėgis, oro drėgnis, matomumas, debesys (kiekiai, formos, aukštis), ledo reiškiniai (ledų kiekis, forma, storis). Monitoringas vykdomas mokslinių tyrimų laivu „Vėjūnas“. Parametrai matuojami kasmet, 19 tyrimų vietų, vidutiniškai 4-7 kartus per metus (dažnumas skiriasi skirtinguose rajonuose: BAL-LT-AA-01 ir BAL-LT-AA-02 – 4-7 kartai per metus; BAL-LT-AA-03 rajone tyrimai atliekami 1-4 kartus per metus). Kitose 4 tyrimų vietose tyrimai vykdomi ekstensyviai.
Duomenys papildomai naudojami vertinant hidrologinius duomenis pelaginėms buveinėms pagal D1, hidrografinėms sąlygoms pagal D7 vertinti. Atsižvelgiama vertinant vandens skaidrumą pagal D5.
Duomenys kaupiami Lietuvos aplinkos apsaugos agentūros duomenų bazėje.
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Valstybinis aplinkos monitoringas vykdomas pagal Valstybinę 2018-2023 m. programą. Monitoringo programos dalis BALLT-D07_WavesCurrents apima vandens bangų ir srovių matavimus Baltijos jūros tyrimų rajonuose BAL-LT-AA-01; BAL-LT-AA-02; BAL-LT-AA-03. Monitoringas vykdomas mokslinių tyrimų laivu „Vėjūnas“. Bangų rodikliai (kryptis, periodas, aukštis) matuojami kasmet, 19 tyrimų vietų, vidutiniškai 4-7 kartus per metus (dažnumas skiriasi skirtinguose rajonuose: BAL-LT-AA-01 ir BAL-LT-AA-02 – 4-7 kartai per metus; BAL-LT-AA-03 rajone tyrimai atliekami 1-4 kartus per metus). Srovių parametrai (kryptis, greitis) matuojami pavasario ir vasaros tyrimų reisų metu 3 monitoringo vietose.
Duomenys naudojami pelaginėms buveinėms pagal D1, hidrografinėms sąlygoms pagal D7 vertinti.
Duomenys kaupiami Lietuvos aplinkos apsaugos agentūros duomenų bazėje.
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The purpose of the monitoring is to assess whether the anthropogenic activities which caused physical disturbances and losses of seabed has permanent adverse impact on hydrological characteristics of water column and natural seabed.
HELCOM Monitoring Programme topics "Seabed habitat distribution and extent" and "Hydrographic changes ", programmes "Seabed habitat physical characteristics" and "Water column hydrological characteristics".
At present in the HELCOM area there is no coordinated monitoring for extent and spatial distribution of permanent changes of hydrological characteristics of water column (Partly coordinated. Missing component: common database: partly available via Copernicus marine service and EMODnet Physics database) and seabed (coordinated monitoring is under development).
Assessment will be made based on the results of monitoring performed in the frame of activities in the sub-programme LV-4.6. described. |
The purpose of the monitoring is to assess whether the changes in hydrological characteristics of water column and natural seabed has permanent adverse impact on benthic habitats.
HELCOM Monitoring Programme topic "Seabed habitat distribution and extent", programme "Seabed habitat physical characteristics".
At present in the HELCOM area there is no coordinated monitoring for affected seabed habitat spatial distribution and extent.
Assessment will be made based on the information obtained in the implementation of monitoring activities in the sub-programme LV-4.7.1 described. |
The community characteristics is monitored each year in accordance with the HELCOM methodology, including parameters necessary for the assessment of benthic habitats. Monitoring includes sampling of macrozoobenthos at 16 stations and macrophyte and angiosperms at places of occurrence within PMA.
For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection |
The community characteristics is monitored each year in accordance with the HELCOM methodology, including parameters necessary for the assessment of benthic habitats. Monitoring includes sampling of macrozoobenthos at 16 stations and macrophyte and angiosperms at places of occurrence within PMA.
For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection |
The abundance and/or biomass of species is monitored each year in accordance with the HELCOM methodology, including parameters necessary for the assessment of benthic habitats. Monitoring includes sampling of macrozoobenthos at 16 stations and macrophyte and angiosperms at places of occurrence within PMA.
For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection |
The abundance and/or biomass of species is monitored each year in accordance with the HELCOM methodology, including parameters necessary for the assessment of benthic habitats. Monitoring includes sampling of macrozoobenthos at 16 stations and macrophyte and angiosperms at places of occurrence within PMA.
For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection |
Monitoring of parameters in scope of the seabed habitats - physical and chemical characteristics programme includes monitoring of hydromorphological parameters that characterize morphological conditions, morphometric conditions, change in depth and quantitative structure and physical and chemical characteristics of the seabed and is carried out within the WFD waterbodies at measurement points and profiles. Additional supplementary parameters are meteorological data on wind speed and direction at stations and hydrological data on sea levels obtained at stations. Monitoring will be carried out once in the period 2020-2025. In the current water management cycle, covering the period 2016-2021, hydromorphological monitoring was carried out in 2019. Another hydromorphological monitoring is scheduled to be carried out in the next water management cycle, that is, in the period 2022-2027, not later than 6 years after the preceding hydromorphological monitoring is performed in accordance with the Regulation of Minister of maritime economy and inland navigation of 9 October 2019 on the form and method of monitoring of surface water and groundwater bodies (Journal of Laws, item 2147). |
Monitoring of parameters in scope of the seabed habitats - physical and chemical characteristics programme includes monitoring of hydromorphological parameters that characterize morphological conditions, morphometric conditions, change in depth and quantitative structure and physical and chemical characteristics of the seabed and is carried out within the WFD waterbodies at measurement points and profiles. Additional supplementary parameters are meteorological data on wind speed and direction at stations and hydrological data on sea levels obtained at stations. Monitoring will be carried out once in the period 2020-2025. In the current water management cycle, covering the period 2016-2021, hydromorphological monitoring was carried out in 2019. Another hydromorphological monitoring is scheduled to be carried out in the next water management cycle, that is, in the period 2022-2027, not later than 6 years after the preceding hydromorphological monitoring is performed in accordance with the Regulation of Minister of maritime economy and inland navigation of 9 October 2019 on the form and method of monitoring of surface water and groundwater bodies (Journal of Laws, item 2147). |
Monitoring of physical parameters is carried out in the assessment units in accordance with the recent HELCOM guidelines. Monitoring includes in-situ measurements carried out annually at 30 monitoring stations located in the deep sea and shallow water zones, as well as in the Vistula Lagoon and the Gulf of Gdańsk. Annual frequency of research is 6 times a year, with an exception of a high frequency station monitored 12 times a year and 6 shallow water stations monitored from 1 to 6 times a year.
For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection.
In order to increase the frequency and resolution of data, in-situ measurements of temperature and salinity can be supplemented by continuous measurements from the Ferry Box (automatic measurement system installed on board of vessels, usualy ferries, the marine water parameters are measured on the route, the system also enables collection of in-situ samples for analysis in on-land laboratories) and satellite data (for the temperature of seawater only). |
Monitoring of physical parameters is carried out in the assessment units in accordance with the recent HELCOM guidelines. Monitoring includes in-situ measurements carried out annually at 30 monitoring stations located in the deep sea and shallow water zones, as well as in the Vistula Lagoon and the Gulf of Gdańsk. Annual frequency of research is 6 times a year, with an exception of a high frequency station monitored 12 times a year and 6 shallow water stations monitored from 1 to 6 times a year.
For the transitional and coastal waterbodies monitoring will be carried out for 19 monitoring points in 2020-2021 and 11 monitoring points in 2022-2025 in accordance with the WFD monitoring programme, carried out under the surface water monitoring programme for the years 2020-2025 ("Strategic State Environmental Monitoring Programme for the years 2020-2025"), approved by the Competent Minister of Climate in 2020 and the surface water executive programme for a specific year of research approved annually by the Chief Inspector of Environmental Protection.
In order to increase the frequency and resolution of data, in-situ measurements of temperature and salinity can be supplemented by continuous measurements from the Ferry Box (automatic measurement system installed on board of vessels, usualy ferries, the marine water parameters are measured on the route, the system also enables collection of in-situ samples for analysis in on-land laboratories) and satellite data (for the temperature of seawater only). |
A nuclear power plant affects the marine environment mainly through the use of large volumes of seawater for cooling. The cooling water is purified at the intake, which to some extent reduces the loss of organisms that would otherwise accompany the intake, but for those who follow, mortality occurs mechanically and thermally when the water passes through the power plant. The outgoing cooling water is 10° C warmer than the water taken in. The hot water is then spread over relatively large areas, where the organisms can be affected. The warm water can also make it easier for non-indigenous species to get established than in other areas.
To control the effects of cooling water use, extensive control programmes have been established at and around the Swedish nuclear power plants since the nuclear power plants were established. In Sweden, there are nuclear power plants at one site in the North Sea (Ringhals nuclear power plant) and two in the Baltic Sea (Forsmark nuclear power plant and Oskarshamnsverket). Electricity production at the power plant in Barsebäck by the Sound ceased in 2005.
Monitoring in the North sea started in 1968 and in the Baltic sea in 1969. Monitoring frequency varies from daily during spring/summer, to monthly or yearly depending on the parameter, location and purpose. Details are described in the monitoring fact sheet linked below.
The nuclear power plants are undergoing a slow decommissioning, for example at Ringhals, two out of four reactors are planned to be shut down in the near future. As the monitoring is connected to the industry, it will also in the long run be phased out after the activity has ended and the effects have ceased. |
Mapping and monitoring of benthic habitats is of crucial importance for all environmental management at sea, from a functioning ecosystem-based marine environment management to meeting the various requirements of environmental legislation. The need for continuous and comprehensive monitoring covering the biological components of the MSFD, the Habitats Directive and the WFD has been clarified in recent reporting cycles. Corresponding needs also exist within the national environmental goals, from the Convention on Biological Diversity and the current challenges of tackling climate change. The new objectives of the EU Biodiversity Strategy (2021-2030) require functioning monitoring systems that provide comprehensive information for protection, assessment of permits, action planning and evaluation (of protection, permit modification and implemented measures).
Monitoring is needed for sustainable fisheries regulation and coastal planning linked to exploitation, as well as for the management of transport routes and energy production, and last but not least to ensure a functioning network of protected areas and a functioning beach protection.
The monitoring of benthic habitats is largely dependent on technical solutions. Methods for monitoring are under development and will, together with monitoring of pressures (see program Physical disturbance and loss), provide a basis for assessing the condition of the benthic habitats and how they are affected by various human activities. The Habitats Directive's assessment in 2019 shows that physical impact on conservation status in the form of construction, ports, dredging and bottom trawling predominates in the North Sea, while water quality, hazardous substances and nutrient load instead have a greater derogatory impact on habitats in the Baltic Sea.
In order to be able to respond to the requirements in an integrated manner, a development of coordinated methods is underway that can deliver the necessary data on benthic habitats. The pilot phase of a survey and monitoring of shallow marine areas using satellite, aerial and drone images and biological sampling will be completed in 2020 and the established monitoring method will be tested and fine-tuned in 2021. The studies include testing of methods from satellite to biological sampling both in the Baltic Sea and on the West Coast. The overall monitoring of shallow benthic environments strives to be able to annually measure shallow marine areas completely (all of Sweden) w |
The Sentinel family is a number of satellites that are part of the European space program Copernicus and can be used for environmental monitoring. With their large geographical coverage, satellites are an excellent complement to field measurements of the water column (for example chlorophyll) provided that the satellite products are locally adapted with acceptable accuracy. With the data collected by the satellites and their instruments, various variables can be calculated that can provide better knowledge of the condition in pelagic habitats and the possible extent of the effects of eutrophication. The monitoring complements the field measurements described in the programmes Phytoplankton, Water column - physical characteristics and Water column - optical properties.
Sentinel 3A was launched in 2016, and Sentinel 3B in 2018. Data are collected from other satellites further back in time, for example from NASA's SeaWiFS (1997 - 2010). Sentinel 3D, the last of that generation, will be launched in 2021. In addition to monitoring harmful algal blooms during the summer (mainly cyanobacteria in the Baltic Sea), there is no ongoing programme for calculating data obtained by remote sensing, but it is under development. Since 2019, SMHI has been tasked with creating an infrastructure for the production of aquatic products, such as chlorophyll maps (data files), adapted to cover all of Sweden's land and water surfaces, as well as making them publically available. The goal is to have the monitoring in operation by 2022. |
The purpose of the monitoring is to study long-term changes in the marine environment with regard to temperature, ice conditions and salinity, which are basic physical parameters in the sea. These, together with pressure, determine the density of the water. The density determines the stratification, which in turn affects the mixture of seawater. Density gradients can impede the transport of substances (for example, the flow of oxygen) to the deep water. Horizontal density gradients create large-scale currents, such as the Baltic surface current along Sweden's west coast. Because marine organisms are adapted to certain temperature and salinity ranges, changes in temperature and salinity can affect the entire food web. Changes can occur because of climate change, but also locally because of the construction of sea-based structures, see also the programme Physical disturbance and loss.
The current regular environmental monitoring started in 1993, but measurements have been performed since 1880, for example from Swedish lightships.
In-situ data are collected at a high frequency but reworked to give, for example, an average value over a ten-minute measurement period every hour from buoys, or an average value for each half-meter depth from a CTD profile. Measurements with CTD profiles are performed between 1 and 24 times a year, usually in connection with eutrophication sampling. Satellites and merchant ships also contribute with data. Since international collaborations such as EuroGOOS (the European Global Ocean Observing System) make other countries' data available, model products that use this data cover almost the entire North Sea and the entire Baltic Sea. Daily ice maps of the entire Baltic Sea are produced during the period November to May based on satellite data and in-situ data from icebreakers and ice reporters.
Work is underway to develop new methods for monitoring using automated sampling and measurements, for example from ferry box systems or bottom- or buoy-mounted measurement systems. Methods are already in place and routines are being developed for automated measurements of temperature, salt and oxygen by the use of probes on ships, buoys and measuring systems, or on moving gliders.
Comment: D7C2 was not in the list for the feature Hydrographical changes, but this criteria is relevant for this programme. |
The purpose of the monitoring is to study long-term changes in the marine environment with regard to the hydrological condition of the sea. Currents, waves and water levels give rise to a physical impact on marine habitats and in addition have effects on human activities. Currents transport water masses and can thus change the pelagic habitat in a few minutes and gaining insight into how the water masses move is thus central to the understanding of the ecosystem. An example is the inflows to the Baltic Sea, where salty oxygen-rich water enters through the Sound (the strait that separates Sweden and Denmark) during severe storms. This salty oxygen-rich water can replace low-oxygen water in bottom areas in the southern Baltic Sea and improve the oxygen situation for at least a couple of months.
Waves are of course also important for both maritime activities and marine life. Waves can both give a resuspension of nutrients in shallow areas (the bottom sediment is stirred up and nutrients, as well as any hazardous substances, can get into the water mass), affect currents and have effects on beach areas (erosion and more). Waves and currents also transport nutrients, organisms and marine litter to the coasts of Sweden from other countries.
In addition to a climate indicator, the sea level is a prerequisite for life in the tidal zone and not at least for blue growth. The Swedish Meterological and Hydrological Institiute (SMHI) send out warnings at extreme water levels. High sea levels can have major effects on communities by leading to floods. Low sea levels can affect shipping that may be forced to take detours or go with less cargo. Another example is nuclear power plants whose cooling can potentially be affected.
The Swedish measurements of currents began in the early 1880s with measurements from lightships. Data on currents, however, are available from earliest 1945, but the first regular observations started in 1978 when currents began to be measured from lighthouses. Since then, the measurements have developed.
Wave measurements by SMHI started in 1978.
The serie of measurements of seawater levels in Stockholm is the longest in the world. The measurements started as early as 1774 at Slussen in Stockholm. In 1889, a mareograph was built on Skeppsholmen, which is still active.
To complement the current programme, mobile sea level gauges have been tested successfully. There are plans to improve the spatial coverage of current patterns and waves by developing n |
This programme include monitoring of physical disturbance or loss of the sea's bottom and coastal environment through human activities such as bottom trawling, dredging, dumping, land claim, constructions and other activities that cause physical change of the bottom (water depth, sediment distribution and habitat loss) and possible the sediment dynamic conditions and hydrographic conditions (eg currents and water exchange).
Physical impact can be identified based on registered information about where and when different activities are carried out. Such information is found, for example, in permits and exemptions or notifications made in accordance with the Environmental Code and can also be produced through, for example, analysis of aerial photographs, VMS and logbooks for fishing activities as well as hydroacoustic measurements with, for example, multibeam sonar. After coordinating geographical and temporal information about human impact with information about ecosystem components in an area, the impact can be assessed.
To estimate the physical impact on benthic habitats, the plan is to use data on human activities and their pressures, together with data from e.g. the programmes Benthic habitats and Macrozoobenthos - on the seafloor. The latter also includes documenting traces of trawling when monitoring the seabed.
Different types of data are thus collected that could be used to estimate physical impact. However, methods for monitoring and assessment are still under development.
Benthic trawling began to be monitored in 1998. Dumping activities began to be reported to the Regional Sea Conventions in 1996. Since 2011, dredging activity linked to dumping has also been reported. Data on other activities have been collected from permits prior to certain reports, but ongoing collection is not yet in place. Regarding sand gravel and rock extraction, there are data on the volume of extraction in m3 per licensed area and year in Sweden from 1967.
In 2018, historical and new aerial images of Sweden's coastal areas were analyzed to identify physical disturbance within the project ”Physical impact in Swedish coastal waters - mapping, assessment and guidelines”. The results apply to the 1960s, and the present (2016). In order to get an idea of the rate of change, interpretations of five major sub-areas have been made for the years 1994 and 2008. The analyzes have been made through interpretations of orthophotos and are planned to be followed up once or twice during |
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 |
Agreed data collection methods |
Agreed data collection methods |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Joint data collection |
Joint data collection |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Coordinated data collection |
Joint data collection |
Coordinated data collection |
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Monitoring details |
|| MP_35 ||
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|| MP_107 ||
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|| MP_110 ||
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|| MP_111 || Eisbeobachter an Land und auf Schiffen
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|| MP_127 ||
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|| MP_35 ||
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|| MP_110 ||
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|| MP_111 || Eisbeobachter an Land und auf Schiffen
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|| MP_127 ||
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Ud over overvågning i regi af havstrategien varetages tilladelser om oprensning og genplacering af materiale fra fx uddybning af havne samt genplacering af materialet også af ministeriet. Det samme gælder tilladelser til råstofindvindning på havet. Læs mere her:
https://mst.dk/erhverv/klapning/
https://mst.dk/erhverv/raastoffer/
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Monitoring is performed by the Maritime Administration and the Geological Survey of Estonia as fulfilment of state obligations and project-based activities. The organic matter content of bottom sediments is determined within the national environmental monitoring programme.
Bathymetry surveys are performed with sonar. The seabed mapping is done using geophysical equipment – a seismic-acoustic profiler (operating frequency 0-450 Hz), a low-frequency acoustic profiler (24 kHz), an echo-sounder, side-scan sonar and probe tools. For determination of the organic matter content in sediment samples, loss on ignition method is used.
The bathymetric measurements are being performed continually unless the entire Estonian marine area is covered. The data on the seabed substrate and morphology is also collected by project-based activities. Organic matter sampling is performed annually once a year. |
The extent of adverse effects from anthropogenic pressures on the seabed is determined using the information on the following human activities: dredging, dumping, bottom trawling, mining, construction of facilities at sea, etc. A proportion (percentage) of the total extent of the habitat type directly affected by human activities is assessed using overlay analysis performed in the geographical information system. The precondition for the analysis is the existence of georeferenced spatial data layers with updated information on human activities (dredging, dumping, bottom trawling, etc). The extent of hydrographical changes is assessed with mathematical modelling.
For dredging and dumping works monitoring, in addition to volume and area measurements suspended matter and turbidity are measured in-situ (standard EVS-EN 872).
The monitoring frequency is irregular and/or as regulated by environmental permits.
The data are both raw data and based on it spatial (processed) data with no common place yet, where it could be accessed. |
The temperature is measured within water column from surface to bottom with CTD sondes. Transparency is assessed with 30 cm diameter white Secchi disk. As part of the Ferrybox monitoring, the temperature and salinity are registered at depths of 4-5 m from a predefined location on the route of the liner with automatic equipment. CTD water column measurements of temperature and salinity are also being performed at autonomous monitoring buoys.
Sampling is carried out annually up to 12 times per year (from June to September) at certain monitoring stations, and in rotation 6 times per year at least once in 6-year period at other monitoring stations. In the off-shore areas monitoring is conducted 6 times per year. Ferrybox, remote (satellite) measurements and measurements at autonomous buoys are being conducted continuously. |
Monitoring is conducted at stations with automatic measurement equipment installed (water level, waves and currents measurements). |
Ice monitoring is carried out as a part of national meteorological and hydrological monitoring (Estonian Environment Agency). Ice maps are produced in cooperation with Baltic Sea countries. TalTech Marine Systems Institute performs remote monitoring of ice on a project basis in cooperation with other Baltic Sea countries. |
On-shore and near-shore measurements of coastal slope are conducted during the monitoring. For slope surveys geophysical equipment – profilers, echo-sounder and side-scan sonar are used. The sediment type, composition and its distribution and seabed morphology are recorded.
The monitoring is carried out yearly with rotation at designated sites so that each site is monitored at least once in the 6-year period.
Additionally, remote sensing (satellite images, orthophotos) are used to assess the changes in coastal areas. |
Vandens temperatūra ir druskingumas matuojami CTD zondu, vandens skaidrumas – seki disku.
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Vandenyje ištirpęs deguonis, pH matuojami automatiškai, ant zondo pritvirtintais davikliais.
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Oro temperatūra, santykinė drėgmė, vėjo kryptis ir greitis, atmosferos slėgis matuojami davikliais laive, debesų, bangų, ledų parametrus ekspertas nustato vizualiai.
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Srovės matuojamos srovių matuokliu, bangos – vizualiai.
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Once in every 6 years, on the basis of the results of the monitoring activities described in monitoring sub-programmes LV-4.6., anthropogenic activities occurred during the reporting period and their potential impacts on hydrographic conditions will be evaluated. If the occurred anthropogenic activities have had the potential to affect hydrographic conditions, modelling of the relevant conditions will be made with a purpose to determine the spatial distribution and extent of changes in the hydrographic conditions of water column and natural seabed. |
Once in every 6 years period, on the basis of the information obtained in assessment of the changes in the hydrographic conditions in water column and seabed will be carried out assessment about possible adverse impacts on habitats caused by these changes. If adverse effect will be identified, the spatial distribution and extent of this impact will be assessed accordingly. |
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September). |
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September). |
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September). |
Macrozoobenthos data is collected once a year, macrophytes 2 times a year (June, September). |
The list of hydromorphological parameters constitutes of:
Morphological conditions:
Shore-normal profiles up to 1 NM from the shoreline
Parameter (A)
Morphometrical conditions:
- width of coastal zones - sb, sr, sg (10 m below sea level. and 1 NM)
- status of longshore bars – number and section area
Change in depth:
- behind surf zone
- behind breaker zone
- 1 NM from the shoreline
- the depth of the sampling point
Seabed structure and characteristics:
- grain size – median of grain diameter
- concentration of organic matter
- nutrient concentration (Ntot and Ptot)
- Chlorophyll a
- redox potential (Eh) and pH
- concentration of contaminants (Me, WWA, PCB, TBT) |
The list of hydromorphological parameters constitutes of:
Morphological conditions:
Shore-normal profiles up to 1 NM from the shoreline
Parameter (A)
Morphometrical conditions:
- width of coastal zones - sb, sr, sg (10 m below sea level. and 1 NM)
- status of longshore bars – number and section area
Change in depth:
- behind surf zone
- behind breaker zone
- 1 NM from the shoreline
- the depth of the sampling point
Seabed structure and characteristics:
- grain size – median of grain diameter
- concentration of organic matter
- nutrient concentration (Ntot and Ptot)
- Chlorophyll a
- redox potential (Eh) and pH
- concentration of contaminants (Me, WWA, PCB, TBT) |
The use of Ferry-Box data dependent on its availability.
The use of satellite products, information dependent on data availability. |
The use of Ferry-Box data dependent on its availability.
The use of satellite products, information dependent on data availability. |
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Coastal fish |
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Pelagic shelf fish |
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Demersal shelf fish |
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Benthic broad habitats |
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Other benthic habitats |
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Pelagic broad habitats |
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Coastal ecosystems |
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Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities) |
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Physical disturbance to seabed |
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Physical loss of the seabed |
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Input of nutrients – diffuse sources, point sources, atmospheric deposition |
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Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) – diffuse sources, point sources, atmospheric deposition, acute events |
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Input of litter (solid waste matter, including micro-sized litter) |
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Input of anthropogenic sound (impulsive, continuous) |
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Input of other forms of energy (including electromagnetic fields, light and heat) |
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Newly introduced non-indigenous species |
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Established non-indigenous species |
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Hydrographical changes |
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Eutrophication |
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Land claim |
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Canalisation and other watercourse modifications |
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Coastal defence and flood protection |
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Offshore structures (other than for oil/gas/renewables) |
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Extraction of minerals (rock, metal ores, gravel, sand, shell) |
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Extraction of oil and gas, including infrastructure |
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Extraction of water |
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Renewable energy generation (wind, wave and tidal power), including infrastructure |
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Non-renewable energy generation |
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Transmission of electricity and communications (cables) |
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Fish and shellfish harvesting (professional, recreational) |
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Marine plant harvesting |
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Hunting and collecting for other purposes |
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Aquaculture – marine, including infrastructure |
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Transport infrastructure |
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Transport – shipping |
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Waste treatment and disposal |
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Tourism and leisure infrastructure |
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Tourism and leisure activities |
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Military operations (subject to Article 2(2)) |
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Research, survey and educational activities |
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Chemical characteristics |
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Physical and hydrological characteristics |
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Restructuring of seabed morphology, including dredging and depositing of materials |
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Spatial scope |
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Marine reporting units |
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Temporal scope (start date - end date) |
1979-9999 |
2010-9999 |
1968-9999 |
1970-9999 |
1980-9999 |
1979-9999 |
2010-9999 |
1968-9999 |
1970-9999 |
1980-9999 |
1997-9999 |
1997-9999 |
2015-9999 |
1981-9999 |
1992-9999 |
1993-9999 |
1993-9999 |
2007-9999 |
1994-9999 |
2014-9999 |
2014-9999 |
1981-9999 |
1972-9999 |
1981-9999 |
1981-9999 |
9999-9999 |
9999-9999 |
2014-9999 |
2014-9999 |
1999-9999 |
1999-9999 |
2014-9999 |
2014-9999 |
2014 |
2014 |
1968-9999 |
2022-9999 |
2022-9999 |
1893-9999 |
1774-9999 |
1967-9999 |
Monitoring frequency |
Other |
Hourly |
Weekly |
As needed |
Monthly |
Other |
Hourly |
Weekly |
As needed |
Monthly |
As needed |
As needed |
Other |
Continually |
Other |
Yearly |
Continually |
Continually |
Yearly |
Continually |
As needed |
3-monthly |
3-monthly |
3-monthly |
3-monthly |
6-yearly |
6-yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Other |
Other |
Yearly |
Yearly |
Other |
Yearly |
Daily |
Other |
Hourly |
Other |
Monitoring type |
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Monitoring method |
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Monitoring method other |
|| MP_035 || |
|| MP_107 || Nationales marines Meeresumweltmessnetz mit autonomen Messgeräten |
|| MP_110 || In-situ Daten werden auf Schiffen und festen Plattformen in der Regel mit einer CTD erfasst. Die genutzten Satelliten sind mit speziellen Sensoren ausgerüstet, aus deren Messwerten sich die Oberflächentemperatur ableiten lässt. Fernerkundungsdaten |
|| MP_111 || In-situ Daten von Eisbeobachtern an Land sowie auf Schiffen, dazu Fernerkundungsdaten |
|| MP_127 || In-situ Daten werden auf Schiffen und festen Plattformen in der Regel mit einer CTD erfasst. Die genutzten Satelliten sind mit speziellen Sensoren ausgerüstet, aus deren Messwerten sich die Oberflächentemperatur ableiten lässt. |
|| MP_035 || |
|| MP_107 || Nationales marines Meeresumweltmessnetz mit autonomen Messgeräten |
|| MP_110 || In-situ Daten werden auf Schiffen und festen Plattformen in der Regel mit einer CTD erfasst. Die genutzten Satelliten sind mit speziellen Sensoren ausgerüstet, aus deren Messwerten sich die Oberflächentemperatur ableiten lässt. Fernerkundungsdaten |
|| MP_111 || In-situ Daten von Eisbeobachtern an Land sowie auf Schiffen, dazu Fernerkundungsdaten |
|| MP_127 || In-situ Daten werden auf Schiffen und festen Plattformen in der Regel mit einer CTD erfasst. Die genutzten Satelliten sind mit speziellen Sensoren ausgerüstet, aus deren Messwerten sich die Oberflächentemperatur ableiten lässt. |
Der findes pt. ikke nogen guidelines eller protokoller for, hvordan der bør foretages overvågning. |
Der findes pt. ikke nogen guidelines eller protokoller for, hvordan der bør foretages overvågning. |
There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan.
The frequency of monitoring depends on activity: from annually to once per the 6-year period. |
The description of methodology and technique that is used for bathymetry surveys is available at http://adam.vta.ee/teenused/hnt/yldinfo/tehnika.html. |
The description of the method is available from https://www.envir.ee/sites/default/files/msrd_lavivaartused_lopparuanne.pdf |
Automatic measurements and mathematical modelling - Copernicus marine service (http://marine.copernicus.eu/) and BOOS (http://www.boos.org/). |
The main characteristics of ice cover are measured using satellite observations or/and in combination - satellite images and visual observations. |
Nationally accredited methods, geodetical and geophysical surveys and measurements. |
Water temperature is measured from the outflow pipe and in the surrounding area of land based industries. The sub-program includes monitoring of temperature impacts on macrophytes and macrozoobenthos. As this is a surveillance monitoring the detailed monitoring method is laid out in the license. |
The sub-program includes monitoring of changes in salinity and water flow (current velocity) in outflow waters of industrial power plants as well as in the water affected by underwater constructions (eg. wind parks, dams, bridges). The methods follow the Finnish accredited standards but details may vary depending on the operator. |
Monitoring is carried out according to the HELCOM guidelines (see HELCOM Monitoring Manual: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual) Near real time data are collected as well |
Monitoring is carried out according to the HELCOM guidelines (see HELCOM Monitoring Manual: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual) |
Monitoring is carried out according to the HELCOM guidelines (see HELCOM Monitoring Manual: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual) Near real time data are collected as well |
Monitoring is carried out according to the HELCOM guidelines (see HELCOM Monitoring Manual: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual) Near real time data are collected as well |
Method description not applicable |
Method description not applicable |
Verified method of monitoring and hydromorphological assessment of transitional and coastal waters (GIOŚ 2018 or its update). www.gios.gov.pl |
Verified method of monitoring and hydromorphological assessment of transitional and coastal waters (GIOŚ 2018 or its update). www.gios.gov.pl |
Total organic carbon - Infrared spectroscopy PN-EN 14842. Methodology in accordance with the Regulation of the Minister of Maritime Economy and Inland Navigation of 9 October 2019 on the forms and method of monitoring surface water bodies and groundwater bodies (Office Journal of 2019, item 2147) http://prawo.sejm.gov.pl/isap.nsf/download.xsp/WDU20190002147/O/D20192147.pdf |
Total organic carbon - Infrared spectroscopy PN-EN 14842. Methodology in accordance with the Regulation of the Minister of Maritime Economy and Inland Navigation of 9 October 2019 on the forms and method of monitoring surface water bodies and groundwater bodies (Office Journal of 2019, item 2147) http://prawo.sejm.gov.pl/isap.nsf/download.xsp/WDU20190002147/O/D20192147.pdf |
"https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-i-ostersjons-kustomraden---djupstratifierat-provfiske-med-nordiska-kustoversiktsnat.html
https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/provfiske-med-kustoversiktsnat-natlankar-och-ryssjor-pa-kustnara-grunt-vatten.html
https://www.slu.se/institutioner/akvatiska-resurser/miljoanalys/datainsamling/biologisk-recipientkontroll-vid-kusten/
https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/vegetationskladda-bottnar-ostkust.html" |
A review of existing methods has shown that there is no single method that can meet all data needs. Therefore, the current focus is on developing a concept based on combined methods, where one or more sub-methods can deliver large-scale coverage while other sub-methods can deliver more accurate spatial and/or biological data. The results from the various sub-methods must be able to be seamlessly linked so that together they form a functioning monitoring system. One possibility that is being investigated is the use of Sentinel 2 satellite data to create a comprehensive and uniform image throughout Sweden (scale 10 x 10 meters) in combination with drones that can locally create image mosaics of benthic vegetation (with an accuracy of a few centimeters) and biological sampling of the vegetation, which in turn enables more accurate species identification and other biological factors. Pilot surveys in 2019 have shown that the method has the potential to cover benthic habitats down to medium visibility depths.
Deeper benthic environments (below the visibility depth limit) require monitoring based on comprehensive substrate and depth models based on data from different types of remote mapping (especially different sonar-based methods). The technical possibilities for producing and modeling bottom information in the same accuracy as shallower areas were initially investigated in 2019 within the National Marine Mapping (NMK) project and showed great potential. Development of reliable and usable models is, however, limited by the lack of measurement data of sufficiently high quality for parts of Sweden's sea area and by the fact that large parts of the existing data are unavailable. |
Sweden are monitoring coastal and marine waters using Copernicus Sentinel-2 and Sentinel-3 data with the general aim to better assess dynamics and state through integrated use of Earth Observation, models and in-situ data. |
https://www.havochvatten.se/vagledning-foreskrifter-och-lagar/vagledningar/ovriga-vagledningar/undersokningstyper-for-miljoovervakning/undersokningstyper/hydrografi-och-narsalter-trendovervakning.html |
Currents are often measured with ADCP, acoustic doppler current profiles, which are placed on the bottom and measure in the water column.
Waves are usually measured with a wave buoy that is equipped with an accelerometer. Data is transmitted via GSM or iridium (satellite link to the internet).
Sea levels are measured in mareographs using the stilling well technique; radar and/or pressure sensors with automatic data transfer to a data centre. |
Trawling – trawling is modelled using a combination of AIS-, VMS- and SAR-data and data from the ship´s logbook.
Data on human activities based on permits – See HELCOM and OSPAR guidelines for dredging. Data on other activities are collected in the same manner.
Interpretation of aerial imaging and detection from satellite data – A combination of remote sensing using aerial or satellite images, AIS and VMS is used to detect physical loss and disturbance in coastal waters.
A method standard is being developed and will be published in the end of 2021.
https://www.ospar.org/work-areas/eiha/dredging-dumping
https://helcom.fi/wp-content/uploads/2016/11/HELCOM-Guidelines-for-Management-of-Dredged-Material-at-Sea.pdf |
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Quality control |
|| MP_035 || DIN EN ISO 7027 - C2. Anmerkung: Die Vergleichbarkeit von Secchi-Tiefen hängt nicht nur von den Lichtverhältnissen und dem (Standort des) Betrachter(s) ab, sondern wird auch durch unterschiedlich große Scheiben erschwert. Hier ist weitere Standardisierung erforderlich. Qualitätssicherungsprogramm des Bund-Länder-Messprogramms (BLMP);
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|| MP_107 || unbekannt
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|| MP_110 || BSH Qualitätsmanagement (ISO 9001)
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|| MP_111 || BSH Qualitätsmanagement (ISO 9001)
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|| MP_127 || BSH Qualitätsmanagement (ISO 9001)
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|| MP_035 || DIN EN ISO 7027 - C2. Anmerkung: Die Vergleichbarkeit von Secchi-Tiefen hängt nicht nur von den Lichtverhältnissen und dem (Standort des) Betrachter(s) ab, sondern wird auch durch unterschiedlich große Scheiben erschwert. Hier ist weitere Standardisierung erforderlich. Qualitätssicherungsprogramm des Bund-Länder-Messprogramms (BLMP);
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|| MP_107 || unbekannt
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|| MP_110 || BSH Qualitätsmanagement (ISO 9001)
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|| MP_111 || BSH Qualitätsmanagement (ISO 9001)
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|| MP_127 || BSH Qualitätsmanagement (ISO 9001)
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I Danmark kvalitetssikres størstedelen af de danske overvågningsdata i den nationale database (VanDa) ved 3 kvalitetssikringsniveauer:
1. Elektronisk kontrol – den automatiske kontrol alle indtastninger undergår, når der registreres data i VanDa
2. Faglig kontrol – automatisk/manuel vurdering af data og data serier i VanDa.
3. Fagdatacenter kontrol – manuel vurdering af data og dataserier udført af fagdatacentret.
Hvis data ikke indrapporteres til den nationale database kvalitetssikres data af konsulenten, der udfører overvågningsopgaven, samt MFVM efter metoderne beskrevet i nationale tekniske anvisninger eller internationale guidelines.
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I Danmark kvalitetssikres størstedelen af de danske overvågningsdata i den nationale database (VanDa) ved 3 kvalitetssikringsniveauer:
1. Elektronisk kontrol – den automatiske kontrol alle indtastninger undergår, når der registreres data i VanDa
2. Faglig kontrol – automatisk/manuel vurdering af data og data serier i VanDa.
3. Fagdatacenter kontrol – manuel vurdering af data og dataserier udført af fagdatacentret.
Hvis data ikke indrapporteres til den nationale database kvalitetssikres data af konsulenten, der udfører overvågningsopgaven, samt MFVM efter metoderne beskrevet i nationale tekniske anvisninger eller internationale guidelines.
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Data quality control systems of relevant data sources. |
The quality of bathymetry surveys is guaranteed by IHO standard S44: http://www.iho.int/iho_pubs/standard/S-44_5E.pdf.
The quality of the data submitted by the Estonian Geological Survey is guaranteed by the respective licenses and accreditations. |
The quality is ensured by following standards and accreditation of experts and persons by whom the monitoring is performed, by local validation of the models used is made and by controls of the fulfilment of environmental permits' requirements and related reports. |
The quality is assured by following international standards, including CMEMS protocols and HELCOM guidelines, and by an accreditation of experts and persons by whom the monitoring is performed. |
The quality is assured by following WMO guidelines (weather service); operational measurements and mathematical modelling are in compliance with Copernicus maritime service quality system. |
WMO and CMEMS quality assurance system (Cal/Val).
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Quality is assured by fulfilling quality requirements for laboratories (incl. accreditation), following surveying instructions, properly calibrated measuring instruments and QA / QC of databases. |
Centre for Economic Development, Transport and the Environment (ELY) monitors process |
No quality control yet
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Aplinkos apsaugos agentūros laboratorijų darbe atliekamų tyrimų kokybė užtikrinama laikantis standarto LST EN ISO/IEC 17025 reikalavimų.
Be CTD matavimų, tyrimai dar atliekami ir rankiniais instrumentais (konduktometru), siekiant palyginti duomenis ir užtikrinti jų kokybę. Į duomenų bazę suvestus duomenis dar kartą patikrina kitas tyrėjas, ir tik tuomet duomenys tampa prieinami kitiems vartotojams, teikiami į ICES, WISE duomenų bazes.
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Aplinkos apsaugos agentūros laboratorijų darbe atliekamų tyrimų kokybė užtikrinama laikantis standarto LST EN ISO/IEC 17025 reikalavimų.
Be automatinių matavimų davikliais, tyrimai dar atliekami ir rankiniais instrumentais (oksimetru), siekiant palyginti duomenis ir užtikrinti jų kokybę. Į duomenų bazę suvestus duomenis dar kartą patikrina kitas tyrėjas, ir tik tuomet duomenys tampa prieinami kitiems vartotojams, teikiami į ICES, WISE duomenų bazes.
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Aplinkos apsaugos agentūros laboratorijų darbe atliekamų tyrimų kokybė užtikrinama laikantis standarto LST EN ISO/IEC 17025 reikalavimų.
Matavimus ir vertinimus paraleliai atlieka skirtingi tyrėjai, duomenys palyginami. Į duomenų bazę suvestus duomenis dar kartą patikrina kitas tyrėjas, ir tik tuomet duomenys tampa prieinami kitiems vartotojams.
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Aplinkos apsaugos agentūros laboratorijų darbe atliekamų tyrimų kokybė užtikrinama laikantis standarto LST EN ISO/IEC 17025 reikalavimų.
Matavimus paraleliai atlieka skirtingi tyrėjai, duomenys palyginami. Į duomenų bazę suvestus duomenis dar kartą patikrina kitas tyrėjas, ir tik tuomet duomenys tampa prieinami kitiems vartotojams.
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Description of QA/QC procedures no
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Description of QA/QC procedures no
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according HELCOM recommendations
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according HELCOM recommendations
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according HELCOM recommendations
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according HELCOM recommendations
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according to Helcom guidlines.
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according to Helcom guidlines.
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according HELCOM recommendations
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according HELCOM recommendations
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https://internt.slu.se/stod-service/fortlopande-miljoanalys/verksamhetsstod/ingangssida/kvalitetsguide/
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Will be developed during test-phase
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Data from the satellites' sensors undergoes a regular recalibration, (called re-processing) where data is flagged as suspicious due to various factors such as clouds, solar reflections, impact from land pixels and more. For products such as chlorophyll, an automated quality control takes place depending on where they are sourced from. Usually there are one or more scientific publications that describe the methods (equations) and how well these correspond to reality (assessment of model quality, validation). |
The laboratories are Swedac-accredited according to ISO 17025. Profile data are reviewed according to ICES's advice and reported according to international standards such as IPTS-68, ITS-90 and PSS-78. Quality review takes place at national and international level (through ICES) and data is used in assimilation and research, which takes into account differences in measurement uncertainty. |
Data undergoes rigorous automated quality control. Extreme values are filtered out or flagged. Some manual review occurs. |
Trawling – Today, there is no automatic QC of VMS and AIS reports. VMS is sealed and there is a set of rules for functionality and handling in the event of errors. AIS is a maritime safety system, but in terms of monitoring, there are no legal requirements for functionality and error handling. Quality assurance of logbook information takes place via error reports. The errors are then corrected manually.
Data on human activities based on permits – When compiling data from permits and exemptions, the reasonableness of the values stated is assessed. There is also a follow-up of how the activity has been carried out compared to what is stated in the reports. The follow-up is done by contacting the supervisory authority or the contracter. Regarding sand gravel and rock extraction, there are conditions in the permit in accordance with the Continental Shelf Act for how control programmes and reporting are to take place.
Interpretation of aerial imaging and detection from satellite data – Map projection must be Sweref99TM. Screening is done with a pixel size of 25 meters. Raster files are created so that the pixels are distributed according to 0, 25, 50, 100 meters, etc. In addition, it is checked that measured maximum and minimum values are reasonable on retrieved data. |
Data management |
Die Bund/Länder-Arbeitsgemeinschaft Nord- und Ostsee (BLANO) erarbeitet gerade ein nationales Konzept zum Datenmanagement, um insbesondere die Berichterstattung und Umsetzung der MSRL zu unterstützen. Dabei werden bestehende Zielsysteme, wie die Datenabgabe an den ICES (für OSPAR und HELCOM), weitere EU-Richtlinien und die Bereitstellung von Diensten für INSPIRE berücksichtigt. Hierzu werden verschiedene Instrumente des Datenmanagements, wie ein Nationaler mariner Datenkatalog (NMDK) oder die Koordinierung der Datenhaltung von Geo-, Meta-, sowie Zeitreihendaten vorgesehen. Die Daten werden durch die verschiedenen föderalen Strukturen in den Küstenländern, Bundes- und Forschungseinrichtungen dezentral oder zentral durch die Meeresumweltdatenbank (MUDAB) bereitgestellt. Trotzdem sind einzelne Datenbestände noch nicht frei verfügbar. Die Daten werden von den Datenoriginatoren an die nationale Meeresumweltdatenbank MUDAB geliefert. Von dort werden sie an den ICES weitergegeben.
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The Federal Government/Länder Working Group on the North Sea and the Baltic Sea (BLANO) is currently developing a national data management plan to support, in particular, the reporting and implementation of the MSFD. It takes into account existing target systems, such as the submission of data to ICES (for OSPAR and HELCOM), other EU directives and the provision of services to INSPIRE. To this end, various data management tools, such as a National Marine Catalogue (NMDK) or the coordination of data retention of geospatial, meta and time series data, are foreseen. The data are provided on a decentralised basis or centrally by the Marine Environment Database (MUDAB) by the various federal structures in the coastal Länder, federal and research institutions. However, individual data sets are not yet freely available.
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Die Bund/Länder-Arbeitsgemeinschaft Nord- und Ostsee (BLANO) erarbeitet gerade ein nationales Konzept zum Datenmanagement, um insbesondere die Berichterstattung und Umsetzung der MSRL zu unterstützen. Dabei werden bestehende Zielsysteme, wie die Datenabgabe an den ICES (für OSPAR und HELCOM), weitere EU-Richtlinien und die Bereitstellung von Diensten für INSPIRE berücksichtigt. Hierzu werden verschiedene Instrumente des Datenmanagements, wie ein Nationaler mariner Datenkatalog (NMDK) oder die Koordinierung der Datenhaltung von Geo-, Meta-, sowie Zeitreihendaten vorgesehen. Die Daten werden durch die verschiedenen föderalen Strukturen in den Küstenländern, Bundes- und Forschungseinrichtungen dezentral oder zentral durch die Meeresumweltdatenbank (MUDAB) bereitgestellt. Trotzdem sind einzelne Datenbestände noch nicht frei verfügbar. Die Daten werden im BSH weitgehend automatisch aufbereitet und archiviert und stehen binnen einer Stunde Nutzern beispielsweise als Eis- und Oberflächentemperaturkarten zur Verfügung. In den Karten werden überwiegend mehrere Überflüge der Satelliten zusammengefasst, wodurch Datenlücken auf Grund von Bewölkung weitgehend geschlossen werden können.
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The Federal Government/Länder Working Group on the North Sea and the Baltic Sea (BLANO) is currently developing a national data management plan to support, in particular, the reporting and implementation of the MSFD. It takes into account existing target systems, such as the submission of data to ICES (for OSPAR and HELCOM), other EU directives and the provision of services to INSPIRE. To this end, various data management tools, such as a National Marine Catalogue (NMDK) or the coordination of data retention of geospatial, meta and time series data, are foreseen. The data are provided on a decentralised basis or centrally by the Marine Environment Database (MUDAB) by the various federal structures in the coastal Länder, federal and research institutions. However, individual data sets are not yet freely available.
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The Federal Government/Länder Working Group on the North Sea and the Baltic Sea (BLANO) is currently developing a national data management plan to support, in particular, the reporting and implementation of the MSFD. It takes into account existing target systems, such as the submission of data to ICES (for OSPAR and HELCOM), other EU directives and the provision of services to INSPIRE. To this end, various data management tools, such as a National Marine Catalogue (NMDK) or the coordination of data retention of geospatial, meta and time series data, are foreseen. The data are provided on a decentralised basis or centrally by the Marine Environment Database (MUDAB) by the various federal structures in the coastal Länder, federal and research institutions. However, individual data sets are not yet freely available.
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Die Bund/Länder-Arbeitsgemeinschaft Nord- und Ostsee (BLANO) erarbeitet gerade ein nationales Konzept zum Datenmanagement, um insbesondere die Berichterstattung und Umsetzung der MSRL zu unterstützen. Dabei werden bestehende Zielsysteme, wie die Datenabgabe an den ICES (für OSPAR und HELCOM), weitere EU-Richtlinien und die Bereitstellung von Diensten für INSPIRE berücksichtigt. Hierzu werden verschiedene Instrumente des Datenmanagements, wie ein Nationaler mariner Datenkatalog (NMDK) oder die Koordinierung der Datenhaltung von Geo-, Meta-, sowie Zeitreihendaten vorgesehen. Die Daten werden durch die verschiedenen föderalen Strukturen in den Küstenländern, Bundes- und Forschungseinrichtungen dezentral oder zentral durch die Meeresumweltdatenbank (MUDAB) bereitgestellt. Trotzdem sind einzelne Datenbestände noch nicht frei verfügbar. Die Daten werden von den Datenoriginatoren an die nationale Meeresumweltdatenbank MUDAB geliefert. Von dort werden sie an den ICES weitergegeben.
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The Federal Government/Länder Working Group on the North Sea and the Baltic Sea (BLANO) is currently developing a national data management plan to support, in particular, the reporting and implementation of the MSFD. It takes into account existing target systems, such as the submission of data to ICES (for OSPAR and HELCOM), other EU directives and the provision of services to INSPIRE. To this end, various data management tools, such as a National Marine Catalogue (NMDK) or the coordination of data retention of geospatial, meta and time series data, are foreseen. The data are provided on a decentralised basis or centrally by the Marine Environment Database (MUDAB) by the various federal structures in the coastal Länder, federal and research institutions. However, individual data sets are not yet freely available.
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Die Bund/Länder-Arbeitsgemeinschaft Nord- und Ostsee (BLANO) erarbeitet gerade ein nationales Konzept zum Datenmanagement, um insbesondere die Berichterstattung und Umsetzung der MSRL zu unterstützen. Dabei werden bestehende Zielsysteme, wie die Datenabgabe an den ICES (für OSPAR und HELCOM), weitere EU-Richtlinien und die Bereitstellung von Diensten für INSPIRE berücksichtigt. Hierzu werden verschiedene Instrumente des Datenmanagements, wie ein Nationaler mariner Datenkatalog (NMDK) oder die Koordinierung der Datenhaltung von Geo-, Meta-, sowie Zeitreihendaten vorgesehen. Die Daten werden durch die verschiedenen föderalen Strukturen in den Küstenländern, Bundes- und Forschungseinrichtungen dezentral oder zentral durch die Meeresumweltdatenbank (MUDAB) bereitgestellt. Trotzdem sind einzelne Datenbestände noch nicht frei verfügbar. Die Daten werden im BSH weitgehend automatisch aufbereitet und archiviert und stehen binnen einer Stunde Nutzern beispielsweise als Eis- und Oberflächentemperaturkarten zur Verfügung. In den Karten werden überwiegend mehrere Überflüge der Satelliten zusammengefasst, wodurch Datenlücken auf Grund von Bewölkung weitgehend geschlossen werden können.
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The Federal Government/Länder Working Group on the North Sea and the Baltic Sea (BLANO) is currently developing a national data management plan to support, in particular, the reporting and implementation of the MSFD. It takes into account existing target systems, such as the submission of data to ICES (for OSPAR and HELCOM), other EU directives and the provision of services to INSPIRE. To this end, various data management tools, such as a National Marine Catalogue (NMDK) or the coordination of data retention of geospatial, meta and time series data, are foreseen. The data are provided on a decentralised basis or centrally by the Marine Environment Database (MUDAB) by the various federal structures in the coastal Länder, federal and research institutions. However, individual data sets are not yet freely available.
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The Federal Government/Länder Working Group on the North Sea and the Baltic Sea (BLANO) is currently developing a national data management plan to support, in particular, the reporting and implementation of the MSFD. It takes into account existing target systems, such as the submission of data to ICES (for OSPAR and HELCOM), other EU directives and the provision of services to INSPIRE. To this end, various data management tools, such as a National Marine Catalogue (NMDK) or the coordination of data retention of geospatial, meta and time series data, are foreseen. The data are provided on a decentralised basis or centrally by the Marine Environment Database (MUDAB) by the various federal structures in the coastal Länder, federal and research institutions. However, individual data sets are not yet freely available.
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I Miljøstyrelsen udvikles der lige nu en ny national database, som har til formål, at samle og opbevare alle de data som styrelsen er ansvarlige for at indsamle. Når databasen er færdigudviklet, vil data efter en kvalitetssikring blive udstillet således, at det er tilgængeligt for offentligheden.
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I Miljøstyrelsen udvikles der lige nu en ny national database, som har til formål, at samle og opbevare alle de data som styrelsen er ansvarlige for at indsamle. Når databasen er færdigudviklet, vil data efter en kvalitetssikring blive udstillet således, at det er tilgængeligt for offentligheden.
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The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment. |
The data of the distribution of seabed substrate and morphology in the Estonian waters are available at the Geological Survey and Land Board and uploaded to the EMODnet Geology portal. Data on organic matter are reported every year by 1 March and are made available via national environmental database KESE.
Spatial data (processed data) is created and made available based on measurements of raw data. |
The data is compiled and updated at least once in the 6-year period. The common place, where the data access could be provided is still under development. |
The data are yearly reported to the national environmental monitoring database KESE (by 1 March). The data on autonomous buoys measurements are stored at CMEMS/EMODnet Physics. |
The data are stored at Estonian Environment Agency (Weather Service) in WISKI database, TalTech Marine Systems Institute (BOOS) and CMEMS in situ data. Automatic measurements and modelled data are available through Copernicus Marine Service and/or EMODnet Physics. |
The data are stored at Estonian Environment Agency, TalTech Marine Systems Institute (http://sahm.ttu.ee/balticseapic/index.php?do=ice) and Baltic Sea Ice Services (http://www.bsis-ice.de/). |
The processed data are yearly reported to the national environmental monitoring database KESE. The original raw data are stored at the Geological Survey. Orthophotos are stored in Land Board. |
Industry and power plants submit data yearly into YLVA - https://www.ymparisto.fi/fi-FI/Kartat_ja_tilastot/Tietojarjestelmat/Ymparistonsuojelun_valvonnan_sahkoinen_asiointijarjestelma_YLVA |
Duomenys kaupiami Aplinkos apsaugos agentūros duomenų bazėje. Naudojami vertinant jūros aplinkos būklę pagal Bendrąją vandens politikos direktyvą, Jūrų strategijos pagrindų direktyvą, stebint daugiametes tendencijas. Kasmet teikiami ICES, WISE. Pagal prašymus teikiami visuomenei, juridiniams asmenims (prašymai siunčiami elektroniniu paštu aaa@aaa.am.lt).
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Duomenys kaupiami Aplinkos apsaugos agentūros duomenų bazėje. Naudojami vertinant jūros aplinkos būklę, stebint daugiametes tendencijas. Pagal prašymus teikiami visuomenei, juridiniams asmenims (prašymai siunčiami Aplinkos apsaugos agentūrai (www.gamta.lt) elektroniniu paštu aaa@aaa.am.lt). Teikiami į ICES, WISE duomenų bazes.
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Duomenys kaupiami Aplinkos apsaugos agentūros duomenų bazėje. Naudojami vertinant jūros aplinkos būklę, stebint daugiametes tendencijas. Pagal prašymus teikiami visuomenei, juridiniams asmenims (prašymai siunčiami Aplinkos apsaugos agentūrai (www.gamta.lt) elektroniniu paštu aaa@aaa.am.lt).
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Duomenys kaupiami Aplinkos apsaugos agentūros duomenų bazėje. Naudojami vertinant jūros aplinkos būklę, stebint daugiametes tendencijas. Pagal prašymus teikiami visuomenei, juridiniams asmenims (prašymai siunčiami Aplinkos apsaugos agentūrai (www.gamta.lt) elektroniniu paštu aaa@aaa.am.lt).
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Data holder is Latvian Institute of Aquatic Ecology (LIAE).
QA/QC procedures for data no.
Data are available in LIAE. |
Data holder will be Latvian Institute of Aquatic Ecology (LIAE).
QA/QC procedures for data no.
Data will be available in LIAE. |
The raw data collected is stored in SLU Aqua's databases KUL (nets) and is updated annually. The results from the surveys are compiled annually in the Aqua reports by the Department of Aquatic Resources at SLU. Fish fry data and data on Non-indigenous species in Ringhals are stored in simpler databases (Excel and Access). All data is owned by the respective power company, which must give its approval for the data to be used in other contexts. For access to raw data, it is required for the time being to contact the Coastal Laboratory at SLU, which in turn must obtain approval from the data owner to disclose data. Inquiries about aggregated data can be made to datavard-fisk@slu.se |
Reports from the initial pilot study will be published in the spring of 2021. For the time being, the data collected during the development work will be stored and managed by SwAM, but the management will be reviewed and may be transferred to another agency. |
Reprocessed ocean color data is available with daily average images from 2016 to today, at the Copernicus Marine Environment Monitoring Service. Eventually, data will also be available from SMHI, who are developing a publically available infrastructure for the production of aquatic products adapted to cover all of Sweden's land and water surfaces. |
Observation data from the monitoring is made available at the national data host SMHI through several services including Sharkweb, Sharkdata and SeaDataNet. Modeled data are available via SMHI and Copernicus marine services. Daily Ice Maps during November to May are available at SMHI's ice service |
Data is stored at SMHI and shared in the networks BOOS, NOOS, Seadatacloud and Copernicus marine services. The Swedish Maritime Administration's measurements are available in a system called ViVa (Wind and Water Information) via the web and an app. |
Trawling – The raw data that is collected is stored at the SwAM and processed data that is not confidential is made available upon request to havochvatten@havochvatten.se. Data collected and stored by other actors (Coast Guard, EMSA, other Member States or third countries) are not disclosed.
Data on human activities based on permits – There is no national dredging and dumping. This information is stored at each decision-making authority. The data compiled by SwAM annually is stored at the agency and disclosed upon request to havochvatten@havochvatten.se. Data delivered to HELCOM is presented in the Helcom Map and Data Service.
SGU reports annual sand extractions in Swedish coastal waters through the Working Group on the Effects of Extraction of Marine Sediments on the Marine Ecosystem within ICES. The reporting is also done to HELCOM and OSPAR. Annual data for extractions in Sweden and for all countries in the ICES region are reported in each ICES WGXT annual report.
Interpretation of aerial imaging and detection from satellite data – Work is underway to build up a management structure for produced data and models. In parallel with this, work is being done to classify the information, in order to determine what may be made publicly accessible and under what conditions. The ambition is that the basic impact components collected by SwAM through mapping will be made available via the SwAMs data portal for geographical information (under development). |
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Contact |
Geschäftsstelle Meeresschutz, geschaeftsstelle-meeresschutz@mu.niedersachsen.de |
Geschäftsstelle Meeresschutz, geschaeftsstelle-meeresschutz@mu.niedersachsen.de |
Geschäftsstelle Meeresschutz, geschaeftsstelle-meeresschutz@mu.niedersachsen.de |
Geschäftsstelle Meeresschutz, geschaeftsstelle-meeresschutz@mu.niedersachsen.de |
Geschäftsstelle Meeresschutz, geschaeftsstelle-meeresschutz@mu.niedersachsen.de |
Geschäftsstelle Meeresschutz, geschaeftsstelle-meeresschutz@mu.niedersachsen.de |
Geschäftsstelle Meeresschutz, geschaeftsstelle-meeresschutz@mu.niedersachsen.de |
Geschäftsstelle Meeresschutz, geschaeftsstelle-meeresschutz@mu.niedersachsen.de |
Geschäftsstelle Meeresschutz, geschaeftsstelle-meeresschutz@mu.niedersachsen.de |
Geschäftsstelle Meeresschutz, geschaeftsstelle-meeresschutz@mu.niedersachsen.de |
nilun@mst.dk |
nilun@mst.dk |
Estonian Maritime Administration, Hydrography Department: Peeter Väling, peeter.valing@vta.ee; Peeter Ingerma, peeter.ingerma@vta.ee;
The Geological Survey of Estonia, Department of Marine Geology and Geophysics: Sten Suuroja, sten.suuroja@egt.ee;
Land Board, Geology: Ivo Sibul, ivo.sibul@maaamet.ee. |
The Ministry of the Environment: Kaspar Anderson, kaspar.anderson@envir.ee; Eda Andresmaa, eda.andresmaa@envir.ee);
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee. |
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee |
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee |
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee |
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee |
Latvian Institute of Aquatic Ecology
e-mail: juris.aigars@lhei.lv |
Latvian Institute of Aquatic Ecology
e-mail: juris.aigars@lhei.lv |
miljoovervakning@havochvatten.se |
miljoovervakning@havochvatten.se |
miljoovervakning@havochvatten.se |
miljoovervakning@havochvatten.se |
miljoovervakning@havochvatten.se |
miljoovervakning@havochvatten.se |
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References |
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The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian). |
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian). |
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian). |
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian). |
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian). |
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian). |
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian). |